Approval and Promulgation of Implementation Plans and Designation of Areas for Air Quality Planning Purposes; Ohio; Indiana; Redesignation of the Ohio and Indiana Portions of the Cincinnati-Hamilton Area to Attainment for Ozone, 8871-8888 [2010-3680]
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Dated: February 22, 2010.
´
Thelma Melendez de Santa Ana,
Assistant Secretary for Elementary and
Secondary Education.
[FR Doc. 2010–3963 Filed 2–25–10; 8:45 am]
BILLING CODE 4000–01–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 52 and 81
[EPA–R05–OAR–2009–0928; EPA–R05–
OAR–2010–0046; FRL–9116–7]
Approval and Promulgation of
Implementation Plans and Designation
of Areas for Air Quality Planning
Purposes; Ohio; Indiana;
Redesignation of the Ohio and Indiana
Portions of the Cincinnati-Hamilton
Area to Attainment for Ozone
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
SUMMARY: EPA is proposing to approve
the requests of Ohio and Indiana to
redesignate the Ohio and Indiana
portions of the Cincinnati-Hamilton,
OH-KY-IN 8-hour ozone nonattainment
area, ‘‘the Cincinnati-Hamilton area,’’ to
attainment for that standard, because
these requests meet the statutory
requirements for redesignation under
the Clean Air Act (CAA). The Ohio
Environmental Protection Agency (Ohio
EPA) and the Indiana Department of
Environmental Management (IDEM)
submitted these requests on December
14, 2009, and January 21, 2010,
respectively. (EPA will address the
Kentucky portion of the CincinnatiHamilton area in a separate rulemaking
action.)
These proposed approvals involve
several related actions. EPA is
proposing to determine that the
Cincinnati-Hamilton area has attained
the 8-hour ozone National Ambient Air
Quality Standard (NAAQS). The
Cincinnati-Hamilton area includes
Butler, Clermont, Clinton, Hamilton,
and Warren Counties in Ohio,
Lawrenceburg Township in Dearborn
County, Indiana, and Boone, Campbell,
and Kenton Counties in Kentucky. This
determination is based on three years of
complete, quality-assured ambient air
quality monitoring data for the 2007–
2009 ozone seasons that demonstrate
that the 8-hour ozone NAAQS has been
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attained in the area. EPA is also
proposing to approve, as revisions to the
Ohio and Indiana State Implementation
Plans (SIPs), the States’ plans for
maintaining the 8-hour ozone NAAQS
through 2020 in the area.
EPA is proposing to approve the 2002
base year emissions inventory submitted
by IDEM on June 13, 2007, as meeting
the base year emissions inventory
requirement of the CAA for the Indiana
portion of the Cincinnati-Hamilton area.
EPA is proposing to approve the 2005
base year emissions inventory submitted
by Ohio EPA as part of its redesignation
request as meeting the base year
emissions inventory requirements of the
CAA for the Ohio portion of the
Cincinnati-Hamilton area. Finally, EPA
finds adequate and is proposing to
approve the States’ 2015 and 2020
Motor Vehicle Emission Budgets
(MVEBs) for the Ohio and Indiana
portion of the Cincinnati-Hamilton area.
DATES: Comments must be received on
or before March 29, 2010.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R05–
OAR–2009–0928 and EPA–R05–OAR–
2010–0046, by one of the following
methods:
1. https://www.regulations.gov: Follow
the online instructions for submitting
comments.
2. E-mail: damico.genevieve@epa.gov.
3. Fax: (312) 692–2511.
4. Mail: Genevieve Damico, Acting
Chief, Criteria Pollutant Section, Air
Programs Branch (AR–18J), U.S.
Environmental Protection Agency, 77
West Jackson Boulevard, Chicago,
Illinois 60604.
5. Hand delivery: Genevieve Damico,
Acting Chief, Criteria Pollutant Section,
Air Programs Branch (AR–18J), U.S.
Environmental Protection Agency, 77
West Jackson Boulevard, 18th floor,
Chicago, Illinois 60604. Such deliveries
are only accepted during the Regional
Office normal hours of operation, and
special arrangements should be made
for deliveries of boxed information. The
Regional Office official hours of
business 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–2009–
0928 and EPA–R05–OAR–2010–0046.
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
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whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
https://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 https://
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, any form of
encryption, and be free of any defects or
viruses. For additional instructions on
submitting comments, go to section I of
this document, ‘‘What Should I Consider
as I Prepare My Comments for EPA?’’
Docket: All documents in the docket
are listed in the https://
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 hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Environmental Protection Agency,
Region 5, Air and Radiation Division, 77
West Jackson Boulevard, Chicago,
Illinois 60604. This facility is open from
8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays. We
recommend that you telephone
Kathleen D’Agostino, Environmental
Engineer, at (312) 886–1767 before
visiting the Region 5 office.
FOR FURTHER INFORMATION CONTACT:
Kathleen D’Agostino, Environmental
Engineer, Criteria Pollutant Section, Air
Programs Branch (AR–18J), U.S.
Environmental Protection Agency,
Region 5, 77 West Jackson Boulevard,
Chicago, Illinois 60604, (312) 886–1767,
dagostino.kathleen@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
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EPA. This supplementary information
section is arranged as follows:
Table of Contents
I. What Should I Consider as I Prepare My
Comments for EPA?
II. What Action Is EPA Proposing To Take?
III. What Is the Background for These
Actions?
A. What Is the General Background
Information?
B. What Are the Impacts of the December
22, 2006, and June 8, 2007, United States
Court of Appeals Decisions Regarding
EPA’s Phase 1 Implementation Rule?
IV. What Are the Criteria for Redesignation?
V. What Is the Effect of These Actions?
VI. What Is EPA’s Analysis of the Request?
A. Attainment Determination and
Redesignation
B. Adequacy of the MVEBs
C. 2005 Base Year Emissions Inventory for
the Ohio Portion of the CincinnatiHamilton Area
D. 2002 Base Year Emissions Inventory for
the Indiana Portion of the CincinnatiHamilton Area
VII. What Action Is EPA Taking?
VIII. Statutory and Executive Order Reviews
I. What Should I Consider as I Prepare
My Comments for EPA?
When submitting comments,
remember to:
1. Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
2. Follow directions—EPA may ask
you to respond to specific questions or
organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
3. Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
4. Describe any assumptions and
provide any technical information and/
or data that you used.
5. If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
6. Provide specific examples to
illustrate your concerns, and suggest
alternatives.
7. Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
8. Make sure to submit your
comments by the comment period
deadline identified.
II. What Action Is EPA Proposing To
Take?
EPA is proposing to take several
related actions. EPA is proposing to
determine that the Cincinnati-Hamilton
nonattainment area has attained the
1997 8-hour ozone standard and that the
Ohio and Indiana portions of this area
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have met the requirements for
redesignation under section 107(d)(3)(E)
of the CAA. EPA is thus proposing to
approve requests from Ohio EPA and
IDEM to change the legal designation of
the Ohio and Indiana portions of the
Cincinnati-Hamilton area from
nonattainment to attainment for the 8hour ozone NAAQS. EPA is also
proposing to approve, as revisions to the
Ohio and Indiana SIPs, the States’
maintenance plans (such approval being
one of the CAA criteria for redesignation
to attainment status). The maintenance
plans are designed to keep the
Cincinnati-Hamilton area in attainment
of the ozone NAAQS through 2020. EPA
is proposing to approve the 2005 base
year emissions inventory for the Ohio
portion of the Cincinnati-Hamilton area,
and the 2002 base year emissions
inventory for Dearborn County, Indiana,
as meeting the requirements of section
172(c)(3) of the CAA. If EPA’s
determination of attainment is finalized,
under the provisions of 40 CFR 51.918,
the requirement to submit certain
planning SIPs related to attainment (the
Reasonably Available Control Measure
(RACM) requirement of section 172(c)(1)
of the CAA, the Reasonable Further
Progress (RFP) and attainment
demonstration requirements of sections
172(c)(2) and (6) of the CAA, and the
requirement for contingency measures
of section 172(c)(9) of the CAA) are not
applicable to the area as long as it
continues to attain the NAAQS and
would cease to be applicable upon
redesignation. In addition, as set forth in
more detail below, in the context of
redesignations, EPA has interpreted
requirements related to attainment as
not applicable for purposes of
redesignation. Finally, EPA finds
adequate and is proposing to approve
the newly established 2015 and 2020
MVEBs for the Ohio and Indiana portion
of the Cincinnati-Hamilton area. The
adequacy comment period for the
MVEBs began on December 10, 2009,
with EPA’s posting of the availability of
the submittal on EPA’s Adequacy Web
site (at https://www.epa.gov/otaq/
stateresources/transconf/
adequacy.htm). The adequacy comment
period for these MVEBs ended on
January 11, 2010. EPA did not receive
any requests for this submittal, or
adverse comments on this submittal
during the adequacy comment period.
In letters dated January 14, 2010, EPA
informed Ohio EPA and IDEM that we
had found the 2015 and 2020 MVEBs to
be adequate for use in transportation
conformity analyses. Please see section
VI. B. of this rulemaking, ‘‘Adequacy of
the MVEBs,’’ for further explanation of
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this process. Therefore, we find
adequate, and are proposing to approve,
the States’ 2015 and 2020 MVEBs for
transportation conformity purposes.
III. What Is the Background for These
Actions?
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A. What Is the General Background
Information?
Ground-level ozone is not emitted
directly by sources. Rather, emissions of
nitrogen oxides (NOX) and volatile
organic compounds (VOCs) react in the
presence of sunlight to form groundlevel ozone. NOX and VOCs are referred
to as precursors of ozone.
The CAA establishes a process for air
quality management through the
NAAQS. Before promulgation of the 8hour standard, the ozone NAAQS was
based on a 1-hour standard. On
November 6, 1991 (56 FR 56693 and
56813), the Cincinnati-Hamilton area
was designated as a moderate
nonattainment area under the 1-hour
ozone NAAQS. Dearborn County,
Indiana, was not included as part of the
Cincinnati-Hamilton area, and was
designated as attainment/unclassifiable
under the 1-hour standard. The Ohio
portion of the Cincinnati-Hamilton area
was subsequently redesignated to
attainment of the 1-hour standard
effective June 14, 2005. (See 70 FR
35946, published June 21, 2005). This
attainment designation was thus in
effect at the time EPA revoked the 1hour ozone NAAQS, on June 15, 2005.
On July 18, 1997 (62 FR 38856), EPA
promulgated an 8-hour ozone standard
of 0.08 parts per million parts (ppm). On
April 30, 2004 (69 FR 23857), EPA
published a final rule designating and
classifying areas under the 8-hour ozone
NAAQS. These designations and
classifications became effective June 15,
2004. EPA designated as nonattainment
any area that was violating the 8-hour
ozone NAAQS based on the three most
recent years of air quality data, 2001–
2003.
The CAA contains two sets of
provisions, subpart 1 and subpart 2, that
address planning and control
requirements for nonattainment areas.
(Both are found in Title I, part D, of the
CAA; 42 U.S.C. 7501–7509a and 7511–
7511f, respectively.) Subpart 1 contains
general requirements for nonattainment
areas for any pollutant, including ozone,
governed by a NAAQS. Subpart 2
provides more specific requirements for
ozone nonattainment areas.
Under EPA’s implementation rule for
the 1997 8-hour ozone standard, (69 FR
23951 (April 30, 2004)), an area was
classified under subpart 2 based on its
8-hour ozone design value (i.e. the
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three-year average annual fourth-highest
daily maximum 8-hour average ozone
concentration), if it had a 1-hour design
value at the time of designation at or
above 0.121 ppm (the lowest 1-hour
design value in Table 1 of subpart 2) (69
FR 23954). All other areas were covered
under subpart 1, based upon their 8hour design values (69 FR 23958). The
Cincinnati-Hamilton area was
designated as a subpart 1, 8-hour ozone
nonattainment area by EPA on April 30,
2004 (69 FR 23857, 23900, 23905, and
23926), based on air quality monitoring
data from 2001–2003 (69 FR 23860).
40 CFR 50.10 and 40 CFR part 50,
Appendix I provide that the 8-hour
ozone standard is attained when the
three-year average of the annual fourthhighest daily maximum 8-hour average
ozone concentration is less than or
equal to 0.08 ppm, when rounded. The
data completeness requirement is met
when the average percent of days with
valid ambient monitoring data is greater
than 90%, and no single year has less
than 75% data completeness. See 40
CFR part 50, Appendix I, 2.3(d).
The Ohio EPA and IDEM submitted
requests to redesignate the Ohio and
Indiana portions of the CincinnatiHamilton area to attainment for the 8hour ozone standard on December 14,
2009, and January 21, 2010,
respectively. The redesignation requests
included three years of complete,
quality-assured data for the period of
2007 through 2009, indicating the 8hour NAAQS for ozone, as promulgated
in 1997, had been attained for the
Cincinnati-Hamilton area. Under the
CAA, nonattainment areas may be
redesignated to attainment if sufficient
complete, quality-assured data are
available for the Administrator to
determine that the area has attained the
standard, and the area meets the other
CAA redesignation requirements in
section 107(d)(3)(E).
On March 27, 2008 (73 FR 16436),
EPA promulgated a revised 8-hour
ozone standard of 0.075 ppm. In May
2008, States, environmental groups and
industry groups filed petitions with the
DC Circuit Court of Appeals for review
of the 2008 ozone standards. In March
2009, the court granted EPA’s request to
stay the litigation so EPA could review
the standards and determine whether
they should be reconsidered. On
September 16, 2009, we announced that
we are reconsidering our 2008 decision
setting national standards for groundlevel ozone. The designation process for
that standard has been stayed. On
January 6, 2010, EPA proposed to set the
level of the primary 8-hour ozone
standard within the range of 0.060 to
0.070 ppm, rather than at 0.075 ppm.
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We expect by August 2010 to have
completed our reconsideration of the
standard and also expect that thereafter
we will proceed with designations. The
actions addressed in today’s proposed
rulemaking relate only to the 1997 8hour ozone standard.
B. What Are the Impacts of the
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, in South
Coast Air Quality Management Dist. v.
EPA, the U.S. Court of Appeals for the
District of Columbia Circuit vacated
EPA’s Phase 1 Implementation Rule for
the 8-hour Ozone Standard (69 FR
23951, April 30, 2004). 472 F.3d 882
(D.C. Cir. 2006). On June 8, 2007, in
response to several petitions for
rehearing, the DC Circuit Court clarified
that the Phase 1 Rule was vacated only
with regard to those parts of the rule
that had been successfully challenged.
Id., Docket No. 04 1201. Therefore,
several provisions of the Phase 1 Rule
remain effective: 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 for emissions reductions
needed for attainment of the 8-hour
ozone NAAQS. The June 8, 2007,
decision also 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 standard
and those anti-backsliding provisions of
the Phase 1 Rule that had not been
successfully challenged. The June 8,
2007, decision reaffirmed the December
22, 2006, decision that EPA had
improperly failed to retain four
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
fees for 1-hour severe or extreme
nonattainment areas; (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; and (4)
certain transportation conformity
requirements for certain types of Federal
actions. The June 8, 2007, decision
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clarified that the Court’s reference to
conformity requirements was limited to
requiring the continued use of 1-hour
motor vehicle emissions budgets until 8hour budgets were available for 8-hour
conformity determinations.
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 or 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
Standard
With respect to the 8-hour standard,
the Court’s ruling rejected EPA’s reasons
for classifying areas under subpart 1 for
the 8-hour standard, and remanded that
matter to the Agency. In its January 16,
2009, proposed rulemaking in response
to the South Coast decision, EPA has
proposed to classify CincinnatiHamilton under subpart 2 as a moderate
area. 74 FR 2936, 2944. If EPA finalizes
this rulemaking, the requirements under
subpart 2 will become applicable when
they are due, a deadline that EPA has
proposed to be one year after the
effective date of a final rulemaking
classifying areas as moderate or
marginal. 74 FR 2940–2941. Although a
future final decision by EPA to classify
this area under subpart 2 would trigger
additional future requirements for the
area, EPA believes that this does not
mean that redesignation cannot now go
forward. This belief is based upon: (1)
EPA’s longstanding policy of evaluating
requirements in accordance with the
requirements due at the time the request
is submitted; and, (2) consideration of
the inequity of applying retroactively
any requirements that might be applied
in the future.
First, at the time the redesignation
request was submitted, the CincinnatiHamilton area was not classified under
subpart 2, nor were there any subpart 2
requirements yet due for this area.
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
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the submittal of a complete
redesignation request. See 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 Michael Shapiro
Memorandum, September 17, 1993, and
60 FR 12459, 12465–66 (March 7, 1995)
(Redesignation of Detroit-Ann Arbor).
See Sierra Club v. EPA, 375 F.3d 537
(7th Cir. 2004), which upheld EPA’s
redesignation rulemaking applying 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 request was submitted. The
DC Circuit has recognized the inequity
in such retroactive rulemaking. In Sierra
Club v. Whitman, 285 F. 3d 63 (D.C. Cir.
2002), 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 time frame, 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 or yet due at the time
it submitted its redesignation request.
3. Requirements Under the 1-Hour
Standard
With respect to the 1-hour standard
requirements, the Cincinnati-Hamilton
area was an attainment area subject to
a CAA section 175A maintenance plan
under the 1-hour standard. The DC
Circuit’s decisions with respect to 1hour nonattainment anti-backsliding
requirements do not impact
redesignation requests for these types of
areas, except to the extent that the Court
in its June 8, 2007, decision clarified
that for those areas with 1-hour motor
vehicle emissions budgets in their
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,
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conformity determinations in such areas
must comply with the applicable
requirements of EPA’s conformity
regulations at 40 CFR part 93.
With respect to the three other antibacksliding provisions for the 1-hour
standard that the Court found were not
properly retained, the CincinnatiHamilton area is an attainment area
subject to a maintenance plan for the 1hour standard, and the NSR,
contingency measure (pursuant to
section 172(c)(9) or 182(c)(9)), and fee
provision requirements no longer apply
to an area that has been redesignated to
attainment of the 1-hour standard.
Thus, the decision in South Coast Air
Quality Management Dist. would not
preclude EPA from finalizing the
redesignation of this area.
IV. What Are the Criteria for
Redesignation?
The CAA provides the requirements
for redesignating a nonattainment area
to attainment. Specifically, section
107(d)(3)(E) allows for redesignation
provided that: (1) The Administrator
determines that the area has attained the
applicable NAAQS; (2) the
Administrator has fully approved the
applicable implementation plan for the
area under section 110(k); (3) the
Administrator determines that the
improvement in air quality is due to
permanent and enforceable reductions
in emissions resulting from
implementation of the applicable SIP
and applicable Federal air pollutant
control regulations and other permanent
and enforceable reductions; (4) the
Administrator has fully approved a
maintenance plan for the area as
meeting the requirements of section
175A; and, (5) the State containing such
area has met all requirements applicable
to the area under section 110 and part
D.
EPA provided guidance on
redesignation in the General Preamble
for the Implementation of Title I of the
CAA Amendments of 1990 on April 16,
1992 (57 FR 13498), and supplemented
this guidance on April 28, 1992 (57 FR
18070). EPA has provided further
guidance on processing redesignation
requests in the following documents:
‘‘Ozone and Carbon Monoxide Design
Value Calculations,’’ Memorandum from
William G. Laxton, Director Technical
Support Division, June 18, 1990;
‘‘Maintenance Plans for Redesignation
of Ozone and Carbon Monoxide
Nonattainment Areas,’’ Memorandum
from G. T. Helms, Chief, Ozone/Carbon
Monoxide Programs Branch, April 30,
1992;
‘‘Contingency Measures for Ozone and
Carbon Monoxide (CO) Redesignations,’’
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Memorandum from G. T. Helms, Chief,
Ozone/Carbon Monoxide Programs
Branch, June 1, 1992;
‘‘Procedures for Processing Requests
to Redesignate Areas to Attainment,’’
Memorandum from John Calcagni,
Director, Air Quality Management
Division, September 4, 1992;
‘‘State Implementation Plan (SIP)
Actions Submitted in Response to Clean
Air Act (ACT) Deadlines,’’
Memorandum from John Calcagni,
Director, Air Quality Management
Division, October 28, 1992;
‘‘Technical Support Documents
(TSD’s) for Redesignation Ozone and
Carbon Monoxide (CO) Nonattainment
Areas,’’ Memorandum from G. T. Helms,
Chief, Ozone/Carbon Monoxide
Programs Branch, August 17, 1993;
‘‘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 for Air and
Radiation, September 17, 1993;
‘‘Use of Actual Emissions in
Maintenance Demonstrations for Ozone
and CO Nonattainment Areas,’’
Memorandum from D. Kent Berry,
Acting Director, Air Quality
Management Division, to Air Division
Directors, Regions 1–10, November 30,
1993.
‘‘Part D New Source Review (part D
NSR) Requirements for Areas
Requesting Redesignation to
Attainment,’’ Memorandum from Mary
D. Nichols, Assistant Administrator for
Air and Radiation, October 14, 1994;
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.
V. What Is the Effect of These Actions?
Approval of the redesignation
requests would change the official
designation of the Ohio and Indiana
portions of the Cincinnati-Hamilton area
for the 1997 8-hour ozone NAAQS
found at 40 CFR part 81. It would also
incorporate into the Ohio and Indiana
SIPs, plans for maintaining the 8-hour
ozone NAAQS through 2020. The
maintenance plans include contingency
measures as required under CAA
section 175A to remedy future
violations of the 8-hour NAAQS. They
also establish MVEBs for the Ohio and
Indiana portions of the CincinnatiHamilton area of 31.73 and 28.82 tons
per day (tpd) VOC and 49.00 and 34.39
tpd NOX for the years 2015 and 2020,
respectively.
VI. What Is EPA’s Analysis of the
Request?
A. Attainment Determination and
Redesignation
EPA is proposing to determine that
the Cincinnati-Hamilton area has
attained the 1997 8-hour ozone standard
and that the area has met all other
applicable redesignation criteria under
CAA section 107(d)(3)(E). The basis for
EPA’s proposed approvals of the
redesignation requests is as follows:
1. The Area Has Attained the 8-hour
Ozone NAAQS (Section 107(d)(3)(E)(i))
EPA is proposing to make a
determination that the CincinnatiHamilton area has attained the 1997 8-
8875
hour ozone NAAQS. An area may be
considered to be attaining the 8-hour
ozone NAAQS if there are no violations,
as determined in accordance with 40
CFR 50.10 and part 50, Appendix I,
based on three complete, consecutive
calendar years of quality-assured air
quality monitoring data. To attain this
standard, the three-year average of the
fourth-highest daily maximum 8-hour
average ozone concentrations measured
at each monitor within an area over
each year must not exceed 0.08 ppm.
Based on the rounding convention
described in 40 CFR part 50, Appendix
I, the standard is attained if the design
value is 0.084 ppm or below. The data
must be collected and quality-assured in
accordance with 40 CFR part 58, and
recorded in the EPA’s Air Quality
System (AQS). The monitors generally
should have remained at the same
location for the duration of the
monitoring period required for
demonstrating attainment.
Ohio and Indiana included in their
redesignation requests ozone monitoring
data for the 2007 to 2009 ozone seasons.
Monitoring data for 2007 and 2008 have
been certified by the States; 2009 data
has not yet been certified. However,
Ohio and Kentucky have qualityassured all of the ambient monitoring
data in accordance with 40 CFR 58.10,
and have recorded it in the AQS
database. (There are no monitoring
locations in Dearborn County, Indiana.)
The data meet the completeness criteria
in 40 CFR 50, Appendix I, which
requires a minimum completeness of 75
percent annually and 90 percent over
each three-year period. Monitoring data
are presented in Table 1 below.
TABLE 1—ANNUAL 4TH HIGH DAILY MAXIMUM 8-HOUR OZONE CONCENTRATION AND THREE YEAR AVERAGES OF 4TH
HIGH DAILY MAXIMUM 8-HOUR OZONE CONCENTRATIONS
2007–2009
average
(ppm)
2007 4th high
(ppm)
2008 4th high
(ppm)
2009 4th high
(ppm)
Hamilton ...................................
39–017–0004 ...........................
0.091
0.071
0.073
0.078
Middletown ...............................
39–017–1004 ...........................
0.091
0.079
0.076
0.082
Clermont ...............
Batavia .....................................
39–025–0022 ...........................
0.086
0.071
0.069
0.075
Clinton ...................
Wilmington ...............................
39–027–1002 ...........................
0.082
0.076
0.070
0.076
Hamilton ................
Grooms Rd., Cincinnati ...........
39–061–0006 ...........................
0.089
0.086
0.072
0.082
County
Monitor
Ohio ........................
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State
Butler .....................
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TABLE 1—ANNUAL 4TH HIGH DAILY MAXIMUM 8-HOUR OZONE CONCENTRATION AND THREE YEAR AVERAGES OF 4TH
HIGH DAILY MAXIMUM 8-HOUR OZONE CONCENTRATIONS—Continued
2007–2009
average
(ppm)
2007 4th high
(ppm)
2008 4th high
(ppm)
2009 4th high
(ppm)
Cleves ......................................
39–061–0010 ...........................
0.086
0.077
0.065
0.076
250 Wm. Howard Taft, Cincinnati.
39–061–0040 ...........................
0.086
0.080
0.074
0.080
Warren ..................
Lebanon ...................................
39–165–0007 ...........................
0.088
0.082
0.077
0.082
Boone ....................
KY 338 & Lower River Road ...
21–015–0003 ...........................
0.078
0.064
0.064
0.068
Campbell ...............
Highland Heights .....................
21–037–3002 ...........................
0.086
0.075
0.068
0.076
Kenton ...................
State
Covington .................................
21–117–0007 ...........................
0.085
0.073
0.074
0.077
County
Kentucky .................
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In addition, as discussed below with
respect to the Ohio maintenance plan,
Ohio EPA has committed to continue to
operate an EPA-approved monitoring
network as necessary to demonstrate
ongoing compliance with the NAAQS.
Ohio EPA commits to continue
monitoring ozone at the sites indicated
in Table 1 and to consult with EPA prior
to making changes to the existing
monitoring network, should changes
become necessary in the future. Ohio
EPA remains obligated to continue to
quality assure monitoring data in
accordance with 40 CFR part 58 and
enter all data into AQS in accordance
with Federal guidelines. Indiana does
not operate any ozone monitors in
Dearborn County, which contains
Lawrenceburg Township, the Indiana
portion of the Cincinnati-Hamilton area.
In summary, EPA believes that the data
show that the Cincinnati-Hamilton area
has attained the 8-hour ozone NAAQS.
2. The Area Has Met All Applicable
Requirements Under Section 110 and
Part D; and the Area Has a Fully
Approved SIP Under Section 110(k)
(Sections 107(d)(3)(E)(v) and
107(d)(3)(E)(ii))
We have determined that Ohio and
Indiana have met all currently
applicable SIP requirements for
purposes of redesignation for the
Cincinnati-Hamilton area under section
110 of the CAA (general SIP
requirements). We are also proposing to
determine that the Ohio and Indiana
SIPs meet all SIP requirements currently
applicable for purposes of redesignation
under part D of Title I of the CAA
(requirements specific to subpart 1
nonattainment areas), in accordance
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with section 107(d)(3)(E)(v). In addition,
with the exception of the base year
emissions inventory, we have
determined that the Ohio and Indiana
SIPs are fully approved with respect to
all applicable requirements for purposes
of redesignation, in accordance with
section 107(d)(3)(E)(ii). As discussed
below, in this action EPA is proposing
to approve Ohio’s 2005 base year
emissions inventory and Indiana’s 2002
base year emissions inventory as
meeting the section 172(c)(3) emissions
inventory requirement.
In proposing these determinations, we
have ascertained which SIP
requirements are applicable to the area
for purposes of redesignation, and have
determined that there are SIP measures
meeting those requirements and that
they are fully approved under section
110(k) of the CAA. As discussed more
fully below, for purposes of evaluating
a redesignation request, SIPs must be
fully approved only with respect to
requirements that became due prior to
the submission of the redesignation
request.
The September 4, 1992, Calcagni
memorandum (see ‘‘Procedures for
Processing Requests to Redesignate
Areas to Attainment,’’ Memorandum
from John Calcagni, Director, Air
Quality Management Division,
September 4, 1992) describes EPA’s
interpretation of section 107(d)(3)(E) of
the CAA. Under this interpretation, a
State and the area it wishes to
redesignate must meet the relevant CAA
requirements that are 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 60 FR 12459,
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12465–12466 (March 7, 1995)
(Redesignation of Detroit-Ann Arbor).
Applicable requirements of the CAA
that come due subsequent to the State’s
submittal of a complete request remain
applicable until a redesignation to
attainment is approved, but are not
required as a prerequisite to
redesignation. See section 175A(c) of
the CAA. Sierra Club v. EPA, 375 F.3d
537 (7th Cir. 2004). See also 68 FR
25424, 25427 (May 12, 2003)
(Redesignation of St. Louis).
Since EPA is proposing here to
determine that the area has attained the
1997 8-hour ozone standard, under 40
CFR 51.918, if that determination is
finalized, the requirements to submit
certain planning SIPs related to
attainment, including attainment
demonstration requirements (the RACM
requirement of section 172(c)(1) of the
CAA, the RFP and attainment
demonstration requirements of sections
172(c)(2) and (c)(6) of the CAA, and the
requirement for contingency measures
of section 172(c)(9) of the CAA) would
not be applicable to the area as long as
it continues to attain the NAAQS and
would cease to apply upon
redesignation. In addition, in the
context of redesignations, EPA has
interpreted requirements related to
attainment as not applicable for
purposes of redesignation. For example,
in the General Preamble EPA stated that:
[t]he section 172(c)(9) requirements are
directed at ensuring RFP and attainment by
the applicable date. These requirements no
longer apply when an area has attained the
standard and is eligible for redesignation.
Furthermore, section 175A for maintenance
plans * * * provides specific requirements
for contingency measures that effectively
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supersede the requirements of section
172(c)(9) for these areas. ‘‘General Preamble
for the Interpretation of Title I of the Clean
Air Act Amendments of 1990,’’ (General
Preamble) 57 FR 13498, 13564 (April 16,
1992).
See also Calcagni memorandum at 6
(‘‘The requirements for reasonable
further progress and other measures
needed for attainment will not apply for
redesignations because they only have
meaning for areas not attaining the
standard’’).
a. The Ohio and Indiana Portions of the
Cincinnati-Hamilton Area Have Met All
Applicable Requirements for Purposes
of Redesignation Under Section 110 and
Part D of the CAA
i. Section 110 General SIP Requirements
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Section 110(a) of Title I of the CAA
contains the general requirements for a
SIP. Section 110(a)(2) provides that the
implementation plan submitted by a
State must have been adopted by the
State after reasonable public notice and
hearing, and that, among other things, it
includes enforceable emission
limitations and other control measures,
means or techniques necessary to meet
the requirements of the CAA; provides
for establishment and operation of
appropriate devices, methods, systems
and procedures necessary to monitor
ambient air quality; provides for
implementation of a source permit
program to regulate the modification
and construction of any stationary
source within the areas covered by the
plan; includes provisions for the
implementation of part C, Prevention of
Significant Deterioration (PSD) and part
D, NSR permit programs; includes
criteria for stationary source emission
control measures, monitoring, and
reporting; includes provisions for air
quality modeling; and provides for
public and local agency participation in
planning and emission control rule
development.
Section 110(a)(2)(D) of the CAA
requires that SIPs contain measures to
prevent sources in a State from
significantly contributing to air quality
problems in another State. To
implement this provision, EPA has
required certain States to establish
programs to address transport of air
pollutants (NOX SIP Call 1 and Clean Air
1 On October 27, 1998 (63 FR 57356), EPA issued
a NOX SIP Call requiring the District of Columbia
and 22 States to reduce emissions of NOX in order
to reduce the transport of ozone and ozone
precursors. In compliance with EPA’s NOX SIP Call,
both Ohio EPA and IDEM have developed rules
governing the control of NOX emissions from
Electric Generating Units (EGUs), major non-EGU
industrial boilers, major cement kilns, and internal
combustion engines. EPA approved Ohio’s rules as
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Interstate Rule (CAIR) (70 FR 25162,
May 12, 2005)). However, the section
110(a)(2)(D) requirements for a State are
not linked with a particular
nonattainment area’s designation and
classification. EPA believes that the
requirements linked with a particular
nonattainment area’s 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. Thus, 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
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 a particular area’s designation and
classification are the relevant measures
which we may consider in evaluating 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), (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 1-hour
ozone redesignation (65 FR 37890, June
19, 2000), and in the Pittsburgh,
Pennsylvania 1-hour ozone
redesignation (66 FR 50399, October 19,
2001).
We have reviewed Ohio’s SIP and
have concluded that it meets the general
SIP requirements under section 110 of
the CAA to the extent they are
applicable for purposes of
redesignation. EPA has previously
fulfilling Phase I of the NOX SIP Call on August 5,
2003 (68 FR 46089) and June 27, 2005 (70 FR
36845), and as meeting Phase II of the NOX SIP Call
on February 4, 2008 (73 FR 6427). EPA approved
Indiana’s rules as fulfilling requirements of Phase
I of the NOX SIP Call on November 8, 2001 (66 FR
56465) and December 11, 2003 (68 FR 69025), and
as meeting Phase II of the NOX SIP Call on October
1, 2007 (72 FR 55664).
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8877
approved provisions of the Ohio SIP
addressing section 110 elements under
the 1-hour ozone standard (40 CFR
52.1870). Further, in submittals dated
December 5, 2007 and September 19,
2008, Ohio confirmed that the State
continues to meet the section 110
requirements for the 8-hour ozone
standard. EPA has not yet taken
rulemaking action on these submittals;
however, such approval is not necessary
for redesignation.
We have also reviewed Indiana’s SIP
and have concluded that it meets the
general SIP requirements under section
110 of the CAA to the extent they are
applicable for purposes of
redesignation. EPA has previously
approved provisions of the Indiana SIP
addressing section 110 elements under
the 1-hour ozone standard (40 CFR
52.773). Further, in a submittal dated
December 10, 2007, Indiana confirmed
that the State continues to meet the
section 110 requirements for the 8-hour
ozone standard. EPA has not yet taken
rulemaking action on this submittal;
however, such approval is not necessary
for redesignation.
ii. Part D Requirements
EPA has determined that, if EPA
finalizes the approval of the base year
emissions inventories discussed in
section VI.C. and D. of this rulemaking,
the Ohio and Indiana SIPs will meet the
applicable SIP requirements for their
portions of the Cincinnati-Hamilton area
applicable for purposes of redesignation
under part D of the CAA. Subpart 1 of
part D, found in sections 172–176 of the
CAA, sets forth the basic nonattainment
requirements applicable to all
nonattainment areas. Subpart 2 of part
D, which includes section 182 of the
CAA, establishes additional specific
requirements depending on the area’s
nonattainment classification.
Since the Cincinnati-Hamilton area
was not classified under subpart 2 of
Part D at the time its redesignation
request was submitted, the subpart 2
requirements do not apply for purposes
of evaluating the States’ redesignation
requests. The applicable subpart 1
requirements are contained in sections
172(c)(1)–(9) and in section 176.
Subpart 1 Section 172 Requirements
For purposes of evaluating this
redesignation request, the applicable
section 172 SIP requirements for the
Cincinnati-Hamilton area are contained
in sections 172(c)(1)–(9). A thorough
discussion of the requirements
contained in section 172 can be found
in the General Preamble for
Implementation of Title I (57 FR 13498,
April 16, 1992).
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Section 172(c)(1) requires the plans
for all nonattainment areas to provide
for the implementation of all RACM as
expeditiously as practicable and to
provide for attainment of the national
primary ambient air quality standards.
The EPA interprets this requirement to
impose a duty on all nonattainment
areas to consider all available control
measures and to adopt and implement
such measures as are reasonably
available for implementation in each
area as components of the area’s
attainment demonstration. On June 15,
2007 and April 22, 2008, Ohio EPA
submitted an attainment demonstration
and identified the control measures
necessary to attain the NAAQS in the
Cincinnati-Hamilton area. Indiana
submitted an attainment demonstration
for the Cincinnati-Hamilton area on
June 13, 2007. However, because
attainment has been reached, no
additional measures are needed to
provide for attainment, and section
172(c)(1) requirements are no longer
considered to be applicable as long as
the area continues to attain the standard
until redesignation. 40 CFR 51.918. If
EPA finalizes approval of the
redesignation of the Ohio and Indiana
portions of the Cincinnati-Hamilton
area, EPA will take no further action on
the attainment demonstrations
submitted by Ohio and Indiana for the
area.
The RFP requirement under section
172(c)(2) is defined as progress that
must be made toward attainment. This
requirement is not relevant for purposes
of redesignation because the CincinnatiHamilton area has monitored attainment
of the ozone NAAQS. (General
Preamble, 57 FR 13564). See also 40
CFR 51.918. In addition, because the
Cincinnati-Hamilton area has attained
the ozone NAAQS and is no longer
subject to an RFP requirement, the
requirement to submit the section
172(c)(9) contingency measures is not
applicable for purposes of
redesignation. Id.
Section 172(c)(3) requires submission
and approval of a comprehensive,
accurate and current inventory of actual
emissions. As part of Ohio’s
redesignation request for the CincinnatiHamilton area, the State submitted a
2005 base year emissions inventory. As
discussed below in section VI.C., EPA is
proposing to approve the 2005 base year
inventory that Ohio submitted with the
redesignation request as meeting the
section 172(c)(3) emissions inventory
requirement. As part of Indiana’s June
13, 2007, attainment demonstration
submittal for the Cincinnati-Hamilton
area, IDEM included a 2002 base year
emissions inventory. As discussed
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below in section VI.D., EPA is proposing
to approve Indiana’s 2002 base year
inventory as meeting the section
172(c)(3) emissions inventory
requirement.
Section 172(c)(4) requires the
identification and quantification of
allowable emissions for major new and
modified stationary sources to be
allowed in an area, and section 172(c)(5)
requires source permits for the
construction and operation of new and
modified major stationary sources
anywhere in the nonattainment area.
EPA has determined that, since PSD
requirements will apply after
redesignation, 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
NAAQS without part D NSR. 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.’’ Ohio and
Indiana have demonstrated that the
Cincinnati-Hamilton area will be able to
maintain the standard without part D
NSR in effect; therefore, EPA concludes
that the States need not have fully
approved part D NSR programs prior to
approval of the redesignation request.
The States’ PSD programs will become
effective in the Cincinnati-Hamilton
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); and Grand Rapids,
Michigan (61 FR 31834–31837, June 21,
1996).
Section 172(c)(6) requires the SIP to
contain control measures necessary to
provide for attainment of the standard.
Because attainment has been reached,
no additional measures are needed to
provide for attainment.
Section 172(c)(7) requires the SIP to
meet the applicable provisions of
section 110(a)(2). As noted above, we
believe the Ohio and Indiana SIPs meet
the requirements of section 110(a)(2)
applicable for purposes of
redesignation.
Subpart 1 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 quality planning goals in the
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applicable SIPs. The requirement to
determine conformity applies to
transportation plans, programs and
projects developed, funded or approved
under Title 23 of the U.S. Code and the
Federal Transit Act (transportation
conformity) as well as to all other
Federally-supported or funded projects
(general conformity). State conformity
revisions must be consistent with
Federal conformity regulations relating
to consultation, enforcement, and
enforceability, which EPA promulgated
pursuant to CAA requirements.
EPA believes that it is reasonable to
interpret the conformity SIP
requirements as not applying for
purposes of evaluating the redesignation
request under section 107(d) for two
reasons. First, the requirement to submit
SIP revisions to comply with the
conformity provisions of the CAA
continues to apply to areas after
redesignation to attainment since such
areas would be subject to a section 175A
maintenance plan. Second, EPA’s
Federal conformity rules require the
performance of conformity analyses in
the absence of Federally-approved State
rules. Therefore, because areas are
subject to the conformity requirements
regardless of whether they are
redesignated to attainment and, because
they must implement conformity under
Federal rules if State rules are not yet
approved, EPA believes it is reasonable
to view these requirements as not
applying for purposes of evaluating a
redesignation request. See Wall v. EPA,
265 F.3d 426 (6th Cir. 2001), upholding
this interpretation. See also 60 FR
62748, 62749–62750 (Dec. 7, 1995)
(Tampa, Florida).
EPA approved Ohio’s general and
transportation conformity SIPs on
March 11, 1996 (61 FR 9646), and May
30, 2000 (65 FR 34395), respectively.
Section 176(c) of the CAA was amended
by provisions contained in the Safe,
Accountable, Flexible, Efficient
Transportation Equity Act: A Legacy for
Users (SAFETEALU), which was signed
into law on August 10, 2005 (Pub. L.
109–59). Among the changes Congress
made to this section of the CAA was to
streamline the requirements for State
conformity SIPs. Ohio is in the process
of updating its transportation
conformity SIP to meet these new
requirements. EPA approved Indiana’s
general conformity SIP on January 14,
1998 (63 FR 2146). Indiana does not
have a Federally-approved
transportation conformity SIP. However,
conformity analyses are performed
pursuant to EPA’s Federal conformity
rules. Ohio and Indiana have submitted
onroad motor vehicle budgets for the
Ohio and Indiana portion of the
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Cincinnati-Hamilton area of 31.73 and
28.82 tpd VOC and 49.00 and 34.39 tpd
NOX for the years 2015 and 2020,
respectively. The area must use the
MVEBs from the maintenance plan in
any conformity determination that is
effective on or after the effective date of
the maintenance plan approval.
sroberts on DSKD5P82C1PROD with PROPOSALS
b. The Ohio and Indiana Portions of the
Cincinnati-Hamilton Area Have Fully
Approved Applicable SIPs Under
Section 110(k) of the CAA
If EPA issues a final approval of the
base year emissions inventories, EPA
will have fully approved the Ohio and
Indiana SIPs for the CincinnatiHamilton area under section 110(k) of
the CAA for all requirements applicable
for purposes of redesignation. EPA may
rely on prior SIP approvals in approving
a redesignation request (See page 3 of
the September 4, 1992, John Calcagni
memorandum; Southwestern
Pennsylvania Growth Alliance v.
Browner, 144 F.3d 984, 989–990 (6th
Cir. 1998); 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
25413, 25426 (May 12, 2003). Since the
passage of the CAA of 1970, Ohio and
Indiana have adopted and submitted,
and EPA has fully approved, provisions
addressing various required SIP
elements under the 1-hour ozone
standard. In this action, EPA is
proposing to approve Ohio’s 2005 base
year emissions inventory and Indiana’s
2002 base year emissions inventory for
the Cincinnati-Hamilton area as meeting
the requirement of section 172(c)(3) of
the CAA. No Cincinnati-Hamilton area
SIP provisions are currently
disapproved, conditionally approved, or
partially approved.
3. The Improvement in Air Quality is
Due to Permanent and Enforceable
Reductions in Emissions Resulting From
Implementation of the SIP and
Applicable Federal Air Pollution
Control Regulations and Other
Permanent and Enforceable Reductions
(Section 107(d)(3)(E)(iii))
EPA finds that Ohio and Indiana have
demonstrated that the observed air
quality improvement in the CincinnatiHamilton area is due to permanent and
enforceable reductions in emissions
resulting from implementation of the
SIPs, Federal measures, and other Stateadopted measures.
In making this demonstration, Ohio
EPA and IDEM have calculated the
change in emissions between 2005 and
2008. Ohio and Indiana are using 2005
base year emissions inventories
developed in conjunction with the Lake
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Michigan Air Directors Consortium
(LADCO) as the nonattainment
inventories. The States developed an
attainment inventory for 2008, one of
the years the Cincinnati-Hamilton area
monitored attainment. The reduction in
emissions and the corresponding
improvement in air quality over this
time period can be attributed to a
number of regulatory control measures
that Cincinnati-Hamilton and upwind
areas have implemented in recent years.
a. Permanent and Enforceable Controls
Implemented
The following is a discussion of
permanent and enforceable measures
that have been implemented in the
areas:
i. Stationary Source NOX Rules
Ohio EPA and IDEM have developed
rules governing the control of NOX
emissions from Electric Generating
Units (EGUs), major non-EGU industrial
boilers, major cement kilns, and internal
combustion engines. EPA approved
Ohio’s rules as fulfilling Phase I of the
NOX SIP Call on August 5, 2003 (68 FR
46089), and June 27, 2005 (70 FR
36845), and as fulfilling Phase II of the
SIP Call on February 4, 2008 (73 FR
6427). EPA approved Indiana’s rules as
fulfilling requirements of Phase I of the
NOX SIP Call on November 8, 2001 (66
FR 56465), and December 11, 2003 (68
FR 69025), and as meeting Phase II of
the NOX SIP Call on October 1, 2007 (72
FR 55664). Ohio and Indiana began
complying with Phase I of this rule in
2004. Compliance with Phase II of the
SIP Call, which requires the control
NOX emissions from large internal
combustion engines, began in both Ohio
and Indiana in 2007, and was projected
to result in an 82 percent NOX reduction
from 1995 levels.
ii. Federal Emission Control Measures
Reductions in VOC and NOX
emissions have occurred statewide and
in upwind areas as a result of Federal
emission control measures, with
additional emission reductions expected
to occur in the future. Federal emission
control measures include the following.
Tier 2 Emission Standards for
Vehicles and Gasoline Sulfur Standards.
These emission control requirements
result in lower VOC and NOX emissions
from new cars and light duty trucks,
including sport utility vehicles. The
Federal rules were phased in between
2004 and 2009. The EPA has estimated
that, by the end of the phase-in period,
the following vehicle NOX emission
reductions will occur nationwide:
Passenger cars (light duty vehicles) (77
percent); light duty trucks, minivans,
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8879
and sports utility vehicles (86 percent);
and, larger sports utility vehicles, vans,
and heavier trucks (69 to 95 percent).
VOC emission reductions are expected
to range from 12 to 18 percent,
depending on vehicle class, over the
same period. Some of these emission
reductions occurred by the attainment
years (2007–2009) and additional
emission reductions will occur during
the maintenance period.
Heavy-Duty Diesel Engine Rule. EPA
issued this rule in July 2000. This rule
includes standards limiting the sulfur
content of diesel fuel, which went into
effect in 2004. A second phase took
effect in 2007 which further reduced the
highway diesel fuel sulfur content to 15
parts per million, leading to additional
reductions in combustion NOX and VOC
emissions. This rule is expected to
achieve a 95 percent reduction in NOX
emissions from diesel trucks and busses.
Non-Road Diesel Rule. EPA issued
this rule in 2004. This rule applies to
diesel engines used in industries, such
as construction, agriculture, and mining.
It is estimated that compliance with this
rule will cut NOX emissions from nonroad diesel engines by up to 90 percent.
This rule is currently achieving
emission reductions, but will not be
fully implemented until 2010.
iii. Control Measures in Upwind Areas
On October 27, 1998 (63 FR 57356),
EPA issued a NOX SIP Call requiring the
District of Columbia and 22 States to
reduce emissions of NOX. Affected
States were required to comply with
Phase I of the SIP Call beginning in
2004, and Phase II beginning in 2007.
The reduction in NOX emissions has
resulted in lower concentrations of
transported ozone entering the
Cincinnati-Hamilton area. Emission
reductions resulting from regulations
developed in response to the NOX SIP
Call are permanent and enforceable.
b. Emission Reductions
Ohio and Indiana are using 2005 base
year emissions inventories developed in
conjunction with the LADCO as the
nonattainment inventories. The main
purpose of LADCO is to provide
technical assessments for and assistance
to its member States on problems of air
quality. LADCO’s primary geographic
focus is the area encompassed by its
member States (Illinois, Indiana,
Michigan, Ohio and Wisconsin) and any
areas which affect air quality in its
member States. In developing the 2005
nonattainment year inventory, Ohio
EPA and IDEM provided point and area
source inventories to LADCO. LADCO
processed these inventories through the
Emission Modeling System (EMS) to
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generate summer weekday emissions for
VOC and NOX. The point source data
provided to LADCO is a combination of
EPA’s EGU inventory and source
specific data reported to Ohio EPA and
IDEM for non-EGU sources. Area source
emissions were estimated by Ohio EPA
and IDEM using published Emission
Inventory Improvement Program
methodologies or methodologies shared
by other States. The methodology used
for each area source category was
documented. Nonroad mobile emissions
were generated for LADCO using EPA’s
National Mobile Inventory Model
(NMIM), with the following exceptions:
Recreational motorboat populations and
spatial surrogates were updated;
emissions estimates were developed for
commercial marine vessels, aircraft, and
railroads, three nonroad categories not
included in NMIM. The States and
LADCO also developed emissions
inventories for 2009 and 2018 using
similar methodologies. Onroad mobile
emissions were prepared by the Ohio,
Kentucky and Indiana Council of
Governments (OKI) using the
MOBILE6.2 emissions model. Ohio has
submitted this 2005 emissions inventory
to meet the requirement for a base year
emissions inventory pursuant to section
172(c)(3) of the CAA.
Ohio and Indiana are using 2008 for
the attainment year inventory. Ohio
EPA used growth factors provided by
LADCO to project the area and nonroad
source sectors of the 2005 base year
inventory to 2008. IDEM used the 2005
nonattainment inventory and the 2009
emissions inventory prepared in
conjunction with LADCO to extrapolate
2008 emissions for the area and nonroad
mobile source sectors. Point source
emissions for 2008 were compiled from
Ohio EPA’s 2008 annual emissions
inventory database, IDEM’s 2008 annual
emissions statement database, and
EPA’s Clean Air Markets database.
Onroad mobile emissions were
calculated for 2008 by OKI using the
MOBILE6.2 emissions model.
Using the inventories described
above, as well as emissions inventories
provided by Kentucky, Ohio and
Indiana have documented changes in
VOC and NOX emissions from 2005 to
2008 for the Cincinnati-Hamilton area.
Emissions data are shown in Tables 2
through 5 below.
TABLE 2—CINCINNATI-HAMILTON AREA VOC AND NOX EMISSIONS FOR NONATTAINMENT YEAR 2005 (TPD)
VOC
NOX
County
Point
Area
Onroad
Nonroad
Total
Point
Area
Onroad
Nonroad
Total
Butler ............................................
Clermont .......................................
Clinton ..........................................
Hamilton .......................................
Warren ..........................................
Dearborn, IN .................................
Boone, KY ....................................
Campbell, KY ...............................
Kenton, KY ...................................
OH-IN Total ..................................
3.67
0.73
0.00
2.94
0.53
3.24
2.57
0.25
1.20
11.11
11.96
6.98
3.24
33.04
8.40
2.07
8.13
4.77
8.53
65.69
9.94
6.86
3.02
29.47
7.97
1.00
4.33
2.52
4.32
58.26
6.88
4.33
1.77
17.45
4.79
0.82
1.71
1.76
2.33
36.04
32.45
18.90
8.03
82.90
21.69
7.13
16.74
9.30
16.38
171.10
15.91
43.11
0.00
21.95
2.68
30.40
23.94
0.00
0.04
114.05
2.15
1.65
0.42
5.19
1.15
0.26
4.99
1.41
4.17
10.82
18.88
13.04
5.07
56.51
15.15
1.44
10.27
5.98
10.39
110.09
10.25
5.03
2.26
20.57
6.10
1.26
12.96
6.33
8.43
45.47
47.19
62.83
7.75
104.22
25.08
33.36
52.16
13.72
23.03
280.43
Area Total .............................
15.13
87.12
69.43
41.84
213.52
138.03
21.39
136.73
73.19
369.34
TABLE 3—CINCINNATI-HAMILTON VOC AND NOX EMISSIONS FOR ATTAINMENT YEAR 2008 (TPD)
VOC
NOX
County
Point
Area
Onroad
Nonroad
Total
Point
Area
Onroad
Nonroad
Total
Butler ............................................
Clermont .......................................
Clinton ..........................................
Hamilton .......................................
Warren ..........................................
Dearborn, IN .................................
Boone, KY ....................................
Campbell, KY ...............................
Kenton, KY ...................................
OH-IN Total ..................................
2.80
0.36
0.00
3.09
0.82
3.58
2.81
0.28
1.17
10.65
10.31
6.05
2.85
28.80
7.30
2.42
8.41
4.34
7.88
57.73
7.87
5.42
2.33
22.70
6.26
0.75
4.00
2.29
3.85
45.33
5.68
3.68
1.65
14.66
4.10
0.74
5.07
1.51
1.95
30.51
26.66
15.51
6.83
69.25
18.48
7.49
20.29
8.42
14.85
144.22
13.40
22.79
0.00
19.09
3.14
30.55
23.27
0.02
0.03
88.97
2.18
1.67
0.43
5.27
1.17
0.26
5.02
1.32
4.06
10.98
16.05
11.05
3.87
46.80
12.76
1.14
8.53
4.88
8.37
91.67
8.89
4.22
2.01
17.21
5.19
1.14
11.02
5.34
7.33
38.66
40.52
39.73
6.31
88.37
22.26
33.09
47.84
11.56
19.79
230.28
Area Total .............................
14.91
78.36
55.47
39.04
187.78
112.29
21.38
113.45
62.35
309.47
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TABLE 4—COMPARISON OF 2005 AND 2008 VOC AND NOX EMISSIONS FOR THE OHIO AND INDIANA PORTION OF THE
CINCINNATI-HAMILTON AREA (TPD)
VOC
2005
Point .........................................................
Area ..........................................................
Onroad .....................................................
Nonroad ...................................................
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Net change
(2005–2008)
2008
11.11
65.69
58.26
36.04
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10.65
57.73
45.33
30.51
Fmt 4702
Sfmt 4702
2005
¥0.46
¥7.96
¥12.93
¥5.53
E:\FR\FM\26FEP1.SGM
2008
114.05
10.82
110.09
45.47
26FEP1
88.97
10.98
91.67
38.66
Net change
(2005–2008)
¥25.08
0.16
¥18.42
¥6.81
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8881
TABLE 4—COMPARISON OF 2005 AND 2008 VOC AND NOX EMISSIONS FOR THE OHIO AND INDIANA PORTION OF THE
CINCINNATI-HAMILTON AREA (TPD)—Continued
VOC
2005
Total ..................................................
NOX
Net change
(2005–2008)
2008
171.10
2005
¥26.88
144.22
2008
280.43
230.28
Net change
(2005–2008)
¥50.15
TABLE 5—COMPARISON OF 2005 AND 2008 VOC AND NOX EMISSIONS FOR THE ENTIRE CINCINNATI-HAMILTON AREA
(TPD)
VOC
2005
NOX
Net change
(2005–2008)
2008
2005
2008
Net change
(2005–2008)
Point .........................................................
Area ..........................................................
Onroad .....................................................
Nonroad ...................................................
15.13
87.12
69.43
41.84
14.91
78.36
55.47
39.04
¥0.22
¥8.76
¥13.96
¥2.80
138.03
21.39
136.73
73.19
112.29
21.38
113.45
62.35
¥25.74
¥0.01
¥23.28
¥10.84
Total ..................................................
213.52
187.78
¥25.74
369.34
309.47
¥59.87
Table 4 shows that the Ohio and
Indiana portion of the CincinnatiHamilton area reduced VOC emissions
by 26.88 tpd and NOX emissions by
50.15 tpd between 2005 and 2008. As
shown in Table 5, the entire CincinnatiHamilton area reduced VOC emissions
by 25.74 tpd and NOX emissions by
59.87 tpd between 2005 and 2008.
Based on the information summarized
above, Ohio and Indiana have
adequately demonstrated that the
improvement in air quality is due to
permanent and enforceable emissions
reductions.
sroberts on DSKD5P82C1PROD with PROPOSALS
4. The Area has a Fully Approved
Maintenance Plan Pursuant to Section
175A of the CAA (Section
107(d)(3)(E)(iv))
In conjunction with their requests to
redesignate the Cincinnati-Hamilton
nonattainment area to attainment status,
Ohio and Indiana submitted SIP
revisions to provide for the maintenance
of the 8-hour ozone NAAQS in the area
through 2020.
a. Maintenance Plan Requirements
Section 175A of the CAA sets forth
the required elements of a maintenance
plan for areas seeking redesignation
from nonattainment to attainment.
Under section 175A, the plan must
demonstrate continued attainment of
the applicable NAAQS for at least ten
years after the Administrator approves a
redesignation to attainment. Eight years
after the redesignation, the State must
submit a revised maintenance plan
which demonstrates that attainment will
continue to be maintained for ten years
following the initial ten-year
maintenance period. To address the
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possibility of future NAAQS violations,
the maintenance plan must contain
contingency measures with a schedule
for implementation as EPA deems
necessary to assure prompt correction of
any future 8-hour ozone violations.
The September 4, 1992, John Calcagni
memorandum provides additional
guidance on the content of a
maintenance plan. The memorandum
clarifies that an ozone maintenance plan
should address the following items: The
attainment VOC and NOX emissions
inventories, a maintenance
demonstration showing maintenance for
the ten years of the maintenance period,
a commitment to maintain the existing
monitoring network, factors and
procedures to be used for verification of
continued attainment of the NAAQS,
and a contingency plan to prevent or
correct future violations of the NAAQS.
b. Attainment Inventory
The Ohio EPA and IDEM developed
emissions inventories for 2008, one of
the years used to demonstrate
monitored attainment of the 8-hour
NAAQS, as described above. The
attainment level of emissions is
summarized in Table 3, above.
c. Demonstration of Maintenance
Along with the redesignation
requests, Ohio EPA and IDEM submitted
revisions to the Ohio and Indiana 8hour ozone SIPs to include maintenance
plans for the Cincinnati-Hamilton area,
in compliance with section 175A of the
CAA. These demonstrations show
maintenance of the 8-hour ozone
standard through 2020 by showing that
current and future emissions of VOC
and NOX for the Cincinnati-Hamilton
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Fmt 4702
Sfmt 4702
area remain at or below attainment year
emission levels. A maintenance
demonstration need not be based on
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), 68 FR 25413, 25430–25432 (May
12, 2003).
Ohio and Indiana are using emissions
inventory projections for the years 2015
and 2020 to demonstrate maintenance.
OKI calculated onroad emissions for
2015 and 2020 using the MOBILE6.2
emissions model. Emissions estimates
for the remaining source categories were
based on future year inventories
developed by the States and LADCO for
the years 2009 and 2018. (See section
VI.A.3.b., above.) The 2015 interim year
emissions were estimated based on the
2009 and 2018 inventories, using
growth factors provided by LADCO. The
2020 maintenance year emissions were
estimated by applying growth factors
provided by LADCO to the 2018
inventory.
Ohio is in the process of revising its
State rules for its Best Available
Technology (BAT) minor source
permitting program. As discussed
above, a State can demonstrate
maintenance of the standard by showing
that future emissions of VOC and NOX
for the area remain at or below
attainment year emission levels. Ohio
EPA’s emissions projections for this
maintenance plan assume no emissions
benefits from implementation of the
BAT program. The LADCO growth
factors used to project future emissions
were developed using techniques
consistent among the LADCO States and
assume implementation of no minor
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source permitting programs for any
State, including Ohio. The emission
projections show that Ohio EPA does
not expect emissions in the CincinnatiHamilton area to exceed the level of the
2008 attainment year inventory during
the maintenance period. Ohio’s
maintenance plan demonstrates that the
area can maintain the standard through
2020 applying standard growth factors
and without the BAT program. EPA
believes that Ohio has provided
adequate demonstration of maintenance,
and that any changes to the BAT
program should not impact the
Cincinnati-Hamilton area’s ability to
attain or maintain the 1997 8-hour
ozone NAAQS. Therefore, the issues
associated with the BAT program are
not being considered for purposes of
this redesignation. Nothing in this rule
or redesignation is intended to affect the
SIP approvability or non-approvability
of any revised Ohio BAT rules, and EPA
will evaluate the approvability of such
rules when Ohio submits them.
Emissions data are shown in Tables 6–
9, below.
TABLE 6—CINCINNATI-HAMILTON AREA VOC AND NOX EMISSIONS FOR INTERIM YEAR 2015 (TPD)
VOC
NOX
County
Point
Area
Onroad
Nonroad
Total
Point
Area
Onroad
Nonroad
Total
Butler ............................................
Clermont .......................................
Clinton ..........................................
Hamilton .......................................
Warren ..........................................
Dearborn, IN .................................
Boone, KY ....................................
Campbell, KY ...............................
Kenton, KY ...................................
OH-IN Total ..................................
4.27
0.78
0.00
3.28
0.57
3.95
3.04
0.30
1.31
12.85
9.76
5.74
2.72
27.38
6.94
1.79
8.50
4.20
7.66
54.33
4.87
3.29
1.47
13.44
4.02
0.50
3.17
l.74
2.85
27.59
4.95
3.13
1.26
12.70
3.39
0.62
4.55
1.29
1.76
26.05
23.85
12.94
5.45
56.80
14.92
6.86
19.26
7.53
13.58
120.82
14.84
50.23
0.00
35.71
2.70
30.42
25.08
0.02
0.03
133.90
2.19
1.67
0.43
5.30
1.17
0.27
5.03
1.30
4.02
11.03
7.55
5.10
2.02
21.11
6.23
0.60
4.63
2.54
4.23
42.61
5.91
2.76
1.39
11.18
3.22
0.78
9.77
4.57
6.15
25.24
30.49
59.76
3.84
73.30
13.32
32.07
44.51
8.43
14.43
212.78
Area Total .............................
17.50
74.69
35.35
33.65
161.19
159.03
21.38
54.01
45.73
280.15
TABLE 7—CINCINNATI-HAMILTON AREA VOC AND NOX EMISSIONS FOR MAINTENANCE YEAR 2020 (TPD)
VOC
NOX
County
Point
Area
Onroad
Nonroad
Total
Point
Area
Onroad
Nonroad
Total
Butler ............................................
Clermont .......................................
Clinton ..........................................
Hamilton .......................................
Warren ..........................................
Dearborn, IN .................................
Boone, KY ....................................
Campbell, KY ...............................
Kenton, KY ...................................
OH-IN Total ..................................
4.58
0.80
0.00
3.43
0.57
4.15
3.20
0.31
1.42
13.53
9.76
5.74
2.72
27.38
6.94
1.79
8.50
4.20
7.66
54.33
4.50
3.04
1.22
12.00
3.88
0.42
2.96
1.55
2.56
25.06
4.80
2.96
1.08
12.19
3.15
0.60
4.36
1.22
1.73
24.78
23.64
12.54
5.02
55.00
14.54
6.96
19.02
7.28
13.37
117.70
14.86
51.65
0.00
36.69
2.70
31.22
26.47
0.03
0.03
137.12
2.19
1.67
0.43
5.30
1.17
0.27
5.03
1.30
4.02
11.03
5.37
3.63
1.41
14.44
4.63
0.42
3.45
1.81
3.01
29.90
4.64
2.17
1.13
8.73
2.38
0.65
9.48
4.34
5.75
19.70
27.06
59.12
2.97
65.16
10.88
32.56
44.43
7.48
12.81
197.75
Area Total .............................
18.46
74.69
32.13
32.09
157.37
163.65
21.38
38.17
39.27
262.47
TABLE 8—COMPARISON OF 2008, 2015 AND 2020 VOC AND NOX EMISSIONS FOR THE OHIO AND INDIANA PORTION OF
THE CINCINNATI-HAMILTON AREA (TPD)
VOC
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2008
2015
2020
NOX
Net
change
(2008–
2015)
Net
change
(2008–
2020)
2008
2015
2020
Net
change
(2008–
2015)
Net
change
(2008–
2020)
Point .............................................
Area ..............................................
Onroad .........................................
Nonroad ........................................
10.65
57.73
30.51
45.33
12.85
54.33
27.59
26.05
13.53
54.33
25.06
24.78
2.20
¥3.40
¥2.92
¥19.28
2.88
¥3.40
¥5.45
¥20.55
88.97
10.98
91.67
38.66
133.90
11.03
42.61
25.24
137.12
11.03
29.90
19.70
44.93
0.05
¥49.06
¥13.42
48.15
0.05
¥61.77
¥18.96
Total ......................................
144.22
120.82
117.70
¥23.40
¥26.52
230.28
212.78
197.75
¥17.50
¥32.53
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TABLE 9—COMPARISON OF 2008, 2015 AND 2020 VOC AND NOX EMISSIONS FOR THE ENTIRE CINCINNATI-HAMILTON
AREA (TPD)
VOC
2008
2015
2020
NOX
Net
change
(2008–
2015)
Net
change
(2008–
2020)
2008
2015
2020
Net
change
(2008–
2015)
Net
change
(2008–
2020)
Point .............................................
Area ..............................................
Onroad .........................................
Nonroad ........................................
14.91
78.36
55.47
39.04
17.50
74.69
35.35
33.65
18.46
74.69
32.13
32.09
2.59
¥3.67
¥20.12
¥5.39
3.55
¥3.67
¥23.34
¥6.95
112.29
21.38
113.45
62.35
159.03
21.38
54.01
45.73
163.65
21.38
38.17
39.27
46.74
0.00
¥59.44
¥16.62
51.36
0.00
¥75.28
¥23.08
Total ......................................
187.78
161.19
157.37
¥26.59
¥30.41
309.47
280.15
262.47
¥29.32
¥47.00
The emission projections show that
Ohio, Indiana, and Kentucky do not
expect emissions in the CincinnatiHamilton area to exceed the level of the
2008 attainment year inventory during
the maintenance period, even without
implementation of CAIR. (See also
discussion below.) As shown in Table 8,
VOC and NOX emissions in the Ohio
and Indiana portion of the CincinnatiHamilton area are projected to decrease
by 26.52 tpd and 32.53 tpd,
respectively, between 2008 and 2020.
As shown in Table 9, VOC and NOX
emissions in the entire CincinnatiHamilton area are projected to decrease
by 30.41 tpd and 47.00 tpd,
respectively, between 2008 and 2020.
In addition, LADCO performed a
regional modeling analysis to address
the effect of the recent court decision
vacating CAIR. This analysis is
documented in LADCO’s ‘‘Regional Air
Quality Analyses for Ozone, PM2.5, and
Regional Haze: Final Technical Support
Document (Supplement), September 12,
2008.’’ LADCO produced a base year
inventory for 2005 and future year
inventories for 2009, 2012, and 2018. To
estimate future EGU NOX emissions
without implementation of CAIR,
LADCO projected 2007 EGU NOX
emissions for all States in the modeling
domain based on Energy Information
Administration growth rates by State
(North American Electric Reliability
Corporation (NERC) region) and fuel
type for the years 2009, 2012 and 2018.
The assumed 2007–2018 growth rates
were 8.8% for Illinois, Iowa, Missouri
and Wisconsin; 13.5% for Indiana,
Kentucky, Michigan and Ohio; and
15.1% for Minnesota. Emissions were
adjusted by applying legally enforceable
controls, e.g., consent decree or rule.
EGU NOX emissions projections for the
States of Illinois, Indiana, Michigan,
Ohio, and Wisconsin are shown below
in Table 11. The emission projections
used for the modeling analysis do not
account for certain relevant factors such
as allowance trading and potential
changes in operation of existing control
devices. The NOX projections indicate
that, due to the NOX SIP Call, certain
State rules, consent decrees resulting
from enforcement cases, and ongoing
implementation of a number of mobile
source rules, EGU NOX is not expected
to increase in Ohio, Indiana, or any of
the States in the immediate region, and
overall NOX emissions in Ohio, Indiana,
and the nearby region are expected to
decrease substantially between 2005
and 2020.2 Total NOX emissions
projections are shown in Table 11,
below.
TABLE 10—EGU NOX EMISSIONS FOR THE STATES OF ILLINOIS, INDIANA, MICHIGAN, OHIO AND WISCONSIN (TPD) FOR
2007, 2009, 2012, AND 2018
2007
EGU .................................................................................................................
2009
2012
2018
1,582
1,552
1,516
1,524
TABLE 11—TOTAL NOX EMISSIONS FOR THE STATES OF ILLINOIS, INDIANA, MICHIGAN, OHIO AND WISCONSIN (TPD) FOR
THE YEARS 2005, 2009, 2012, AND 2018
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Total NOX ........................................................................................................
2009
2012
2018
8,260
6,778
6,076
4,759
Given that 2007 is one of the years
Ohio and Indiana used to demonstrate
monitored attainment of the 8-hour
NAAQS, Table 10 shows that EGU NOX
emissions will remain below attainment
levels through 2018. If the rate of
emissions increase between 2012 and
2018 continues through 2020, EGU NOX
emissions would still remain below
attainment levels in 2020. Furthermore,
as shown in Table 11, total NOX
emissions clearly continue to decrease
substantially throughout the
maintenance period.
Ozone modeling performed by
LADCO supports the conclusion that the
Cincinnati-Hamilton area will maintain
the standard throughout the
maintenance period. Peak modeled
ozone levels in the area for 2009, 2012
and 2018 are 0.082 ppm, 0.081 ppm,
and 0.078 ppm, respectively. These
projected ozone levels were modeled
applying only legally enforceable
controls; e.g., consent decrees, rules, the
NOX SIP Call, Federal motor vehicle
control programs, etc. Because these
programs will remain in place, emission
levels, and therefore ozone levels,
would not be expected to increase
2 There is more uncertainty about the use of SO
2
allowances and future projections for SO2
emissions; thus, further review and discussion will
be needed regarding the appropriateness of using
these emission projections for future PM2.5 SIP
approvals and redesignation requests.
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significantly between 2018 and 2020.
Given that projected emissions and
modeled ozone levels continue to
decrease substantially through 2018, it
is reasonable to infer that a 2020
modeling run would also show levels
well below the 1997 8-hour ozone
standard.
EPA has considered the relationship
of the maintenance plans to the
reductions required pursuant to CAIR.
This rule was remanded to EPA, and the
process of developing a replacement
rule is ongoing. However, the remand of
CAIR does not alter the requirements of
the NOX SIP Call, and Ohio and Indiana
have demonstrated maintenance
without any additional CAIR
requirements (beyond those required by
the NOX SIP Call). Therefore, EPA
believes that Ohio and Indiana’s
demonstration of maintenance under
sections 175A and 107(d)(3)(E) is valid.
The NOX SIP Call requires States to
make significant, specific emissions
reductions. It also provided a
mechanism, the NOX Budget Trading
Program, which States could use to
achieve those reductions. When EPA
promulgated CAIR, it discontinued
(starting in 2009) the NOX Budget
Trading Program, 40 CFR 51.121(r), but
created another mechanism, the CAIR
ozone season trading program, which
States could use to meet their SIP Call
obligations (70 FR 25289–90). EPA notes
that a number of States, when
submitting SIP revisions to require
sources to participate in the CAIR ozone
season trading program, removed the
SIP provisions that required sources to
participate in the NOX Budget Trading
Program. In addition, because the
provisions of CAIR, including the ozone
season NOX trading program, remain in
place during the remand, EPA is not
currently administering the NOX Budget
Trading Program. Nonetheless, all
States, regardless of the current status of
their regulations that previously
required participation in the NOX
Budget Trading Program, will remain
subject to all of the requirements in the
NOX SIP Call even if the existing CAIR
ozone season trading program is
withdrawn or altered. In addition, the
anti-backsliding provisions of 40 CFR
51.905(f) specifically provide that the
provisions of the NOX SIP Call,
including the statewide NOX emission
budgets, continue to apply after
revocation of the 1-hour standard.
Indiana has submitted a SIP revision
which would discontinue the allocation
of NOX allowances under the NOX
Budget Trading Program beginning in
2010. EPA has not yet acted on this SIP
revision. Ohio currently retains the SIP
provisions requiring sources to
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participate in the NOX Budget Trading
Program. Ohio EPA is in the process of
promulgating a rule change stating that
the NOX Budget Trading Program would
not be applicable so long as CAIR or its
replacement remains in place. However,
the drafted rule revision also provides
that should CAIR requirements be
removed and not replaced with another
program, the NOX Budget Trading
Program would once again apply, on
condition that EPA maintains a NOX
Budget Trading Program.
All NOX SIP Call States have SIPs that
currently satisfy their obligations under
the SIP Call, the SIP Call reduction
requirements are being met, and EPA
will continue to enforce the
requirements of the NOX SIP Call even
after any response to the CAIR remand.
For these reasons, EPA believes that
regardless of the status of the CAIR
program, the NOX SIP Call requirements
can be relied upon in demonstrating
maintenance. Here, Ohio and Indiana
have demonstrated maintenance based
in part on those requirements.
As part of their maintenance plans,
the States elected to include a ‘‘safety
margin’’ for the area. A ‘‘safety margin’’
is the difference between the attainment
level of emissions (from all sources) and
the projected level of emissions (from
all sources) in the maintenance plan
which continues to demonstrate
attainment of the standard. The
attainment level of emissions is the
level of emissions during one of the
years in which the area met the NAAQS.
The Cincinnati-Hamilton area attained
the 8-hour ozone NAAQS during the
2007–2009 time period. Ohio and
Indiana used 2008 as the attainment
level of emissions for the area. For the
Ohio and Indiana portion of the
Cincinnati-Hamilton area, the emissions
from point, area, nonroad, and mobile
sources in 2008 equaled 144.22 tpd of
VOC. In the maintenance plans, Ohio
EPA and IDEM projected emission
levels for 2020. Ohio EPA and IDEM
projected VOC emissions for the year
2020 to be 117.70 tpd of VOC. The SIP
submissions demonstrate that the
Cincinnati-Hamilton area will continue
to maintain the standard with emissions
at this level. The safety margin for VOC
is calculated to be the difference
between these amounts or, in this case,
26.52 tpd of VOC for 2020. By this same
method, 32.53 tpd (i.e., 230.28 tpd less
197.75 tpd) is the safety margin for NOX
for 2020. The safety margin, or a portion
thereof, can be allocated to any of the
source categories, as long as the total
attainment level of emissions is
maintained.
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d. Monitoring Network
Indiana has no ozone monitor in
Dearborn County. Ohio currently
operates eight ozone monitors and
Kentucky operates three monitors in the
Cincinnati-Hamilton area. In its
redesignation request, Ohio EPA has
committed to continue to operate the
ozone monitors. Further, Ohio EPA
commits to consult with EPA prior to
making changes to the existing
monitoring network, should changes
become necessary in the future. Ohio
and Kentucky remain obligated to
continue to quality assure monitoring
data in accordance with 40 CFR part 58
and enter all data into the Air Quality
System in accordance with Federal
guidelines.
e. Verification of Continued Attainment
Continued attainment of the ozone
NAAQS in the Cincinnati-Hamilton area
depends, in part, on the States’ efforts
toward tracking indicators of continued
attainment during the maintenance
period. Ohio’s plan for verifying
continued attainment of the 8-hour
standard in the Cincinnati-Hamilton
area consists of plans to continue
ambient ozone monitoring in
accordance with the requirements of 40
CFR part 58. Ohio EPA and IDEM will
also continue to develop and submit
periodic emission inventories as
required by the Federal Consolidated
Emissions Reporting Rule (67 FR 39602,
June 10, 2002) to track future levels of
emissions.
f. Contingency Plan
The contingency plan provisions are
designed to promptly correct or prevent
a violation of the NAAQS that might
occur after redesignation of an area to
attainment. 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 occurs after
redesignation. The maintenance plan
should identify the contingency
measures to be adopted, a schedule and
procedure for adoption and
implementation of the 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 requirement that the
State will implement all measures with
respect to control of the pollutant(s) that
were contained in the SIP before
redesignation of the area to attainment.
See section 175A(d) of the CAA.
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As required by section 175A of the
CAA, Ohio and Indiana have adopted
contingency plans for the CincinnatiHamilton area to address possible future
ozone air quality problems. The
contingency plans adopted by Ohio and
Indiana have two levels of response, a
warning level response and an action
level response.
In Ohio’s plan, a warning level
response will be triggered when an
annual fourth high monitored value of
0.088 ppm or higher is monitored
within the maintenance area. In
Indiana’s plan, a warning level response
will be triggered when an annual fourth
high monitored value of 0.089 ppm or
higher occurs in a single ozone season,
or when a two-year average fourth high
value of 0.085 ppm or greater occurs
within the maintenance area. While the
triggers selected by Ohio and Indiana
differ slightly, both are acceptable. A
warning level response will consist of
Ohio EPA and IDEM conducting studies
to determine whether the ozone value
indicates a trend toward higher ozone
values or whether emissions appear to
be increasing. The studies will evaluate
whether the trend, if any, is likely to
continue and, if so, the control measures
necessary to reverse the trend. The
studies will consider ease and timing of
implementation as well as economic
and social impacts. Implementation of
necessary controls in response to a
warning level response trigger will take
place within 12 months from the
conclusion of the most recent ozone
season.
In the plans submitted by both Ohio
and Indiana, a violation of the standard
(a three-year average of the annual
fourth-highest daily maximum 8-hour
average ozone concentration of 0.085
ppm or greater) in the maintenance area
triggers an action level response. In
Ohio’s plan, an action level response is
also triggered when a two-year average
fourth high value of 0.085 ppm is
monitored within the maintenance area.
When an action level response is
triggered, Ohio EPA and IDEM will
determine what additional control
measures are needed to assure future
attainment of the ozone standard.
Control measures selected will be
adopted and implemented within 18
months from the close of the ozone
season that prompted the action level.
Ohio EPA and IDEM may also consider
if significant new regulations not
currently included as part of the
maintenance provisions will be
implemented in a timely manner and
would thus constitute an adequate
contingency measure response.
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Ohio EPA included the following list
of potential contingency measures in its
maintenance plan:
i. Implementation of an enhanced
motor vehicle inspection and
maintenance (I/M) program in Butler,
Clermont, Hamilton and Warren
Counties;
ii. Tighten or adopt VOC Reasonably
Available Control Technology (RACT)
on existing sources covered by EPA
Control Technique Guidelines issued
after the 1990 CAA;
iii. Apply VOC RACT to smaller
existing sources;
iv. One or more transportation control
measures sufficient to achieve at least
half a percent reduction in actual area
wide VOC emissions;
v. Alternative fuel and diesel retrofit
programs for fleet vehicle operations;
vi. Require VOC or NOX emission
offsets for new and modified major
sources;
vii. Increase the ratio of emission
offsets required for new sources;
viii. Require VOC or NOX emission
offsets for new and modified minor
sources; and,
ix. Adopt NOX RACT for existing
combustion sources.
IDEM included the following list of
potential contingency measures in its
maintenance plan:
i. Installation of an I/M program;
ii. Lower VOC formulation for asphalt
paving;
iii. Diesel exhaust retrofits;
iv. Traffic flow improvements;
v. Idle reduction programs;
vi. Portable fuel container regulation
statewide;
vii. Park and ride facilities;
viii. Rideshare/carpool program;
ix. VOC cap and trade program for
major stationary sources;
x. Commercial/consumer solvent
regulations statewide; and,
xi. NOX RACT.
g. Provisions for Future Updates of the
Ozone Maintenance Plan
As required by section 175A(b) of the
CAA, Ohio EPA and IDEM commit to
submit to the EPA updated ozone
maintenance plans eight years after
redesignation of the CincinnatiHamilton area to cover an additional
ten-year period beyond the initial tenyear maintenance period. As required
by section 175A of the CAA, Ohio and
Indiana have committed to retain the
VOC and NOX control measures
contained in the SIP prior to
redesignation.
EPA has concluded that the
maintenance plans adequately address
the five basic components of a
maintenance plan: attainment
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8885
inventory, maintenance demonstration,
monitoring network, verification of
continued attainment, and a
contingency plan. Thus EPA proposes to
find that the maintenance plan SIP
revisions submitted by Ohio and
Indiana for the Cincinnati-Hamilton
area meet the requirements of section
175A of the CAA.
B. Adequacy of the MVEBs
1. How Are MVEBs Developed and
What Are the MVEBs for the CincinnatiHamilton Area?
Under the CAA, States are required to
submit, at various times, control strategy
SIP revisions and ozone maintenance
plans for ozone nonattainment areas and
for areas seeking redesignations to
attainment of the ozone standard. These
emission control strategy SIP revisions
(e.g., RFP and attainment demonstration
SIP revisions) and ozone maintenance
plans create MVEBs based on onroad
mobile source emissions for criteria
pollutants and/or their precursors to
address pollution from cars and trucks.
The MVEBs are the portions of the total
allowable emissions that are allocated to
highway and transit vehicle use that,
together with emissions from other
sources in the area, will provide for
attainment or maintenance.
Under 40 CFR part 93, a MVEB for an
area seeking a redesignation to
attainment is established for the last
year of the maintenance plan. The
MVEB serves as a ceiling on emissions
from an area’s planned transportation
system. The MVEB concept is further
explained in the preamble to the
November 24, 1993, transportation
conformity rule (58 FR 62188).
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 SIP. Conformity to the SIP means
that transportation activities will not
cause new air quality violations, worsen
existing air quality violations, or delay
timely attainment of the NAAQS. If a
transportation plan does not conform,
most new transportation projects that
would expand the capacity of roadways
cannot go forward. Regulations at 40
CFR part 93 set forth EPA policy,
criteria, and procedures for
demonstrating and assuring conformity
of such transportation activities to a SIP.
When reviewing SIP revisions
containing MVEBs, including
attainment strategies, rate-of-progress
plans, and maintenance plans, EPA
must affirmatively approve or find that
the MVEBs are ‘‘adequate’’ for use in
determining transportation conformity.
Once EPA affirmatively approves or
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finds the submitted MVEBs to be
adequate for transportation conformity
purposes, the MVEBs must be used by
State and Federal agencies in
determining whether proposed
transportation projects conform to the
SIP as required by section 176(c) of the
CAA. EPA’s substantive criteria for
determining the adequacy of MVEBs are
set out in 40 CFR 93.118(e)(4).
EPA’s process for determining
adequacy of a MVEB consists of three
basic steps: (1) Providing public
notification of a SIP submission; (2)
providing the public the opportunity to
comment on the MVEB during a public
comment period; and, (3) EPA’s finding
of adequacy. The process of determining
the adequacy of submitted SIP MVEBs
is codified at 40 CFR 93.118.
The maintenance plans submitted by
Ohio and Indiana for the CincinnatiHamilton area contain new VOC and
NOX MVEBs for the Ohio and Indiana
portion of the area for the years 2015
and 2020. The availability of the SIP
submission with these 2015 and 2020
MVEBs was announced for public
comment on EPA’s Adequacy Web site
on December 10, 2009, at: https://
www.epa.gov/otaq/stateresources/
transconf/currsips.htm. The EPA public
comment period on adequacy of the
2015 and 2020 MVEBs for the Ohio and
Indiana portion of the CincinnatiHamilton area closed on January 11,
2010. No adverse comments on the
submittal were received during the
adequacy comment period.
EPA, through this rulemaking, has
found adequate and is proposing to
approve the MVEBs for use to determine
transportation conformity in the Ohio
and Indiana portion of the CincinnatiHamilton area because EPA has
determined that the area can maintain
attainment of the 8-hour ozone NAAQS
for the relevant maintenance period
with mobile source emissions at the
levels of the MVEBs. Ohio EPA and
IDEM have determined the 2015 MVEBs
for the Ohio and Indiana portion of the
Cincinnati-Hamilton area to be 31.73
tpd for VOC and 49.00 tpd for NOX.
Ohio EPA and IDEM have determined
the 2020 MVEBs for the Ohio and
Indiana portion of the CincinnatiHamilton area to be 28.82 tpd for VOC
and 34.39 tpd for NOX. These MVEBs
are consistent with the onroad mobile
source VOC and NOX emissions
projected by OKI for 2015 and 2020, as
summarized in Table 8 above. Ohio and
Indiana have demonstrated that the
Cincinnati-Hamilton area can maintain
the 8-hour ozone NAAQS with mobile
source emissions in Ohio and Indiana
portion of the area of 31.73 tpd and
28.82 tpd of VOC and 49.00 tpd and
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34.39 tpd of NOX in 2015 and 2020,
respectively, since emissions will
remain under attainment year emission
levels.
2. What Is a Safety Margin?
A ‘‘safety margin’’ is the difference
between the attainment level of
emissions (from all sources) and the
projected level of emissions (from all
sources) in the maintenance plan. As
noted in Table 8, the emissions in the
Ohio and Indiana portion of the
Cincinnati-Hamilton area are projected
to have safety margins of 23.40 tpd for
VOC and 17.50 tpd for NOX in 2015 (the
difference between the attainment year,
2008, emissions and the projected 2015
emissions for all sources in the Ohio
and Indiana portion of the CincinnatiHamilton area). For 2020, the emissions
in the Ohio and Indiana portion of the
Cincinnati-Hamilton area are projected
to have safety margins of 26.52 tpd for
VOC and 32.53 tpd for NOX. Even if
emissions reached the full level of the
safety margin, the counties would still
demonstrate maintenance since
emission levels would equal those in
the attainment year.
The MVEBs requested by Ohio EPA
and IDEM contain safety margins for
mobile sources smaller than the
allowable safety margins reflected in the
total emissions for the Ohio and Indiana
portion of the Cincinnati-Hamilton area.
The States are not requesting allocation
to the MVEBs of the entire available
safety margins reflected in the
demonstration of maintenance.
Therefore, even though the States are
requesting MVEBs that exceed the
projected onroad mobile source
emissions for 2015 and 2020 contained
in the demonstration of maintenance,
the increase in onroad mobile source
emissions that can be considered for
transportation conformity purposes is
well within the safety margins of the
ozone maintenance demonstration.
Further, once allocated to mobile
sources, these safety margins will not be
available for use by other sources.
C. 2005 Base Year Emissions Inventory
for the Ohio Portion of the CincinnatiHamilton Area
As discussed above, section 172(c)(3)
of the CAA requires areas to submit a
base year emissions inventory. As part
of Ohio’s request to redesignate the
Ohio portion of the Cincinnati-Hamilton
area, the State submitted a 2005 base
year emissions inventory to meet this
requirement. Emissions contained in the
submittal cover the general source
categories of point sources, area sources,
on-road mobile sources, and non-road
mobile sources. All emission summaries
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were accompanied by source-specific
descriptions of emission calculation
procedures and sources of input data.
To determine non-EGU point source
emissions, the State relied on data
reported in Ohio EPA’s STARShip
emissions database. These data are
reported by Title V facilities annually
and include emissions, process rates,
operating schedules, emissions control
data, and other relevant information.
The data entered by the sources are
reviewed by local air agencies and Ohio
EPA district and central office staff.
After review, the data are processed into
the Federally approved National
Emissions Inventory (NEI) database
format. The files are quality assured
again using EPA’s QA/QC software for
format and content. The data is then
submitted to LADCO for emissions
processing through the Emissions
Modeling System. Ohio used EPA’s EGU
inventory, which is based on facility
reported emissions as measured by
continuous emissions monitors.
Area source emissions were estimated
by Ohio EPA using published Emission
Inventory Improvement Program
methodologies or methodologies shared
by other States. The documentation
supplied in the submittal shows how
the county-specific emissions were
calculated for each area source category.
Non-road mobile source emissions
were generated using the NMIM
application. However, prior to running
NMIM, LADCO contracted to make the
following modifications and additions
to the NMIM input data: emission
factors were added for diesel tampers/
rammers, PM2.5 ratios were revised to
correct an error that was introduced
with NMIM2005 and didn’t exist in
NMIM2004, and gasoline parameters
(Reid Vapor Pressure, oxygenate content
and sulfur content) were revised using
updates provided by the States and the
contractor. In addition, recreational
motorboat populations and spatial
surrogates were updated and emissions
estimates were developed for
commercial marine vessels, aircraft, and
railroads, three nonroad categories not
included in NMIM.
Onroad mobile emissions were
prepared by the OKI using the
MOBILE6.2 emissions model.
Ohio EPA’s submittal documents
2005 emissions in the Ohio portion of
the Cincinnati-Hamilton area in units of
tons per summer day. The 2005 summer
day emissions of VOC and NOX are
summarized in Table 2, above. EPA is
proposing to approve this 2005 base
year inventory as meeting the section
172(c)(3) emissions inventory
requirement.
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D. 2002 Base Year Emissions Inventory
for the Indiana Portion of the
Cincinnati-Hamilton Area
IDEM submitted a 2002 base year
emissions inventory to meet the
requirement of section 172(c)(3) of the
CAA for Dearborn County on June 13,
2007, as part of Indiana’s attainment
demonstration for the area. Emissions
contained in the June 13, 2007,
submittal cover the general source
categories of point sources, area sources,
on-road mobile sources, non-road
mobile sources, and biogenic sources.
All emission summaries were
accompanied by source-specific
descriptions of emission calculation
procedures and sources of input data
along with sample calculations for
various counties in the State.
To determine point source emissions,
the State relied on data collected from
source facilities complying with the
State’s annual emissions reporting
requirements, 326 IAC 2–6. Major
sources are required to annually submit
to the State data specifying their annual
emissions of criteria pollutants along
with seasonal source activity
information to allow the calculation of
seasonal emissions. After completing
data quality assurance, IDEM submits
the point source data to EPA for
incorporation into the NEI, as required
by the Consolidated Emissions
Reporting Rule. The June 13, 2007,
submittal includes VOC, NOX, and CO
emissions for each reporting facility
statewide.
Area source emissions were
calculated using a variety of information
sources and guidance from the EPA. A
primary source of calculation
procedures and applied guidance was
EPA’s Emission Inventory Improvement
Program. Where appropriate, point
source emissions were subtracted from
the calculated area source emissions to
account for source coverage overlap
with the reported point source
emissions and to avoid double counting
of emissions in the emissions totals. The
documentation supplied in the June 13,
2007, submittal shows how the countyspecific emissions were calculated for
each area source category. Samples of
area source emission calculations were
provided.
The base year emission inventory
documentation included a detailed
description of the procedures and input
8887
data used to determine the mobile
source for 2002. The mobile source
emissions for Dearborn County were
obtained from EPA’s NEI.
Non-road mobile source VOC, NOX,
and CO emissions for 2002 were
generated by NMIM. To update and
quality assure the emissions for
locomotives, commercial and
recreational marine sources, and offroad mobile equipment sources, LADCO
contracted with several consultants to
update source population and
distribution levels. Summaries of the
consultants’ results and recommended
emissions changes were included in the
June 13, 2007, submittal.
Biogenic VOC, NOX, and CO
emissions for 2002 were taken directly
from the NEI.
The June 13, 2007 submittal
documents 2002 emissions in Dearborn
County in units of tons per summer day.
The 2002 summer day emissions of
VOC, NOX, and CO for Dearborn County
are summarized in Table 12, below. EPA
is proposing to approve this 2002 base
year inventory as meeting the section
172(c)(3) emissions inventory
requirement.
TABLE 12—DEARBORN COUNTY 2002 BASE YEAR EMISSIONS FOR CO, VOC, AND NOX (TPD)
Sector
CO
NOX
VOC
Area .............................................................................................................................................
Biogenic .......................................................................................................................................
Nonroad .......................................................................................................................................
Onroad .........................................................................................................................................
Point .............................................................................................................................................
0.57
1.40
11.70
36.79
2.27
0.31
0.32
1.95
5.60
50.63
2.02
9.60
.96
2.97
2.77
Total ......................................................................................................................................
52.73
58.81
18.32
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VII. What Actions Is EPA Taking?
EPA is proposing to make a
determination that the CincinnatiHamilton area has attained the 1997
8-hour ozone NAAQS. EPA is also
proposing to approve the maintenance
plan SIP revisions for the Ohio and
Indiana portions of the CincinnatiHamilton area. EPA’s proposed approval
of the maintenance plans is based on the
States’ demonstrations that the plans
meet the requirements of section 175A
of the CAA, as described more fully
above. After evaluating the
redesignation requests submitted by
Ohio and Indiana, EPA believes that the
requests meet the redesignation criteria
set forth in section 107(d)(3)(E) of the
CAA. Therefore, EPA is proposing to
approve the redesignation of the Ohio
and Indiana portions of the CincinnatiHamilton area from nonattainment to
attainment for the 1997 8-hour ozone
NAAQS. The final approval of these
VerDate Nov<24>2008
16:27 Feb 25, 2010
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redesignation requests would change
the official designation for the Ohio and
Indiana portions of the CincinnatiHamilton area from nonattainment to
attainment for the 1997 8-hour ozone
standard. EPA is proposing to approve
Ohio EPA’s 2005 base year emissions
inventory for the Ohio portion of the
Cincinnati-Hamilton area as meeting the
requirements of section 172(c)(3) of the
CAA. EPA is proposing to approve
IDEM’s 2002 base year emissions
inventory for Dearborn County as
meeting the requirements of section
172(c)(3) of the CAA for the Indiana
portion of the Cincinnati-Hamilton area.
Finally, EPA finds adequate and is
proposing to approve the States’ 2015
and 2020 MVEBs for Ohio and Indiana
portions of the Cincinnati-Hamilton
area.
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VIII. 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.).
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. Redesignation of an area to
E:\FR\FM\26FEP1.SGM
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Federal Register / Vol. 75, No. 38 / Friday, February 26, 2010 / Proposed Rules
attainment under section 107(d)(3)(E) of
the CAA does not impose any new
requirements on small entities.
Redesignation is an action that affects
the status of a geographical area and
does not impose any new regulatory
requirements on sources. Accordingly,
the Administrator certifies that this rule
will not have a significant economic
impact on a substantial number of small
entities under the Regulatory Flexibility
Act (5 U.S.C. 601 et seq.).
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
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). Redesignation is an
action that merely affects the status of
a geographical area, does not impose
any new requirements on sources, or
allows a State to avoid adopting or
implementing other requirements, and
does not alter the relationship or the
distribution of power and
responsibilities established in the CAA.
Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
sroberts on DSKD5P82C1PROD with PROPOSALS
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).
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.
16:27 Feb 25, 2010
Jkt 220001
Because it is not a ‘‘significant
regulatory action’’ under Executive
Order 12866 or a ‘‘significant energy
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 (NTTA), 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
impracticable. In reviewing program
submissions, EPA’s role is to approve
State choices, provided that they meet
the criteria of the CAA. Absent a prior
existing requirement for the State to use
voluntary consensus standards, EPA has
no authority to disapprove a program
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 CAA. Redesignation is
an action that affects the status of a
geographical area but does not impose
any new requirements on sources. Thus,
the requirements of section 12(d) of the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) do not apply.
List of Subjects
40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
relations, Nitrogen oxides, Ozone,
Volatile organic compounds.
40 CFR Part 81
Air pollution control, Environmental
protection, National parks, Wilderness
areas.
Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
VerDate Nov<24>2008
Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
Dated: February 10, 2010.
Walter W. Kovalick Jr.,
Acting Regional Administrator, Region 5.
[FR Doc. 2010–3680 Filed 2–25–10; 8:45 am]
BILLING CODE 6560–50–P
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–R09–OAR–2010–0044; FRL–9111–1]
Delegation of National Emission
Standards for Hazardous Air Pollutants
for Source Categories; State of
Arizona, Maricopa County Air Quality
Department; State of Nevada, Nevada
Division of Environmental Protection,
Washoe County District Health
Department
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
SUMMARY: Pursuant to section 112(l) of
the 1990 Clean Air Act, EPA granted
delegation of specific national emission
standards for hazardous air pollutants
(NESHAP) to the Maricopa County Air
Quality Department on April 28, 2009,
to the Nevada Division of
Environmental Protection on December
1, 2008, and to the Washoe County
District Health Department, Air Quality
Management Division on February 26,
2009. EPA is proposing to revise the
Code of Federal Regulations to reflect
the current delegation status of NESHAP
in Arizona and Nevada.
DATES: Any comments on this proposal
must arrive by March 29, 2010.
ADDRESSES: Submit comments,
identified by docket number EPA–R09–
OAR–2010–0044, by one of the
following methods:
1. Federal eRulemaking Portal:
https://www.regulations.gov. Follow the
on-line instructions.
2. E-mail: steckel.andrew@epa.gov.
3. Mail or deliver: Andrew Steckel
(AIR–4), U.S. Environmental Protection
Agency Region IX, 75 Hawthorne Street,
San Francisco, CA 94105–3901.
Instructions: All comments 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
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute. Information that
you consider CBI or otherwise protected
should be clearly identified as such and
should not be submitted through
https://www.regulations.gov or e-mail.
https://www.regulations.gov is an
‘‘anonymous access’’ system, and EPA
will not know your identity or contact
information unless you provide it in the
body of your comment. If you send
e-mail directly to EPA, your e-mail
address will be automatically captured
E:\FR\FM\26FEP1.SGM
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Agencies
[Federal Register Volume 75, Number 38 (Friday, February 26, 2010)]
[Proposed Rules]
[Pages 8871-8888]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-3680]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 52 and 81
[EPA-R05-OAR-2009-0928; EPA-R05-OAR-2010-0046; FRL-9116-7]
Approval and Promulgation of Implementation Plans and Designation
of Areas for Air Quality Planning Purposes; Ohio; Indiana;
Redesignation of the Ohio and Indiana Portions of the Cincinnati-
Hamilton Area to Attainment for Ozone
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to approve the requests of Ohio and Indiana
to redesignate the Ohio and Indiana portions of the Cincinnati-
Hamilton, OH-KY-IN 8-hour ozone nonattainment area, ``the Cincinnati-
Hamilton area,'' to attainment for that standard, because these
requests meet the statutory requirements for redesignation under the
Clean Air Act (CAA). The Ohio Environmental Protection Agency (Ohio
EPA) and the Indiana Department of Environmental Management (IDEM)
submitted these requests on December 14, 2009, and January 21, 2010,
respectively. (EPA will address the Kentucky portion of the Cincinnati-
Hamilton area in a separate rulemaking action.)
These proposed approvals involve several related actions. EPA is
proposing to determine that the Cincinnati-Hamilton area has attained
the 8-hour ozone National Ambient Air Quality Standard (NAAQS). The
Cincinnati-Hamilton area includes Butler, Clermont, Clinton, Hamilton,
and Warren Counties in Ohio, Lawrenceburg Township in Dearborn County,
Indiana, and Boone, Campbell, and Kenton Counties in Kentucky. This
determination is based on three years of complete, quality-assured
ambient air quality monitoring data for the 2007-2009 ozone seasons
that demonstrate that the 8-hour ozone NAAQS has been attained in the
area. EPA is also proposing to approve, as revisions to the Ohio and
Indiana State Implementation Plans (SIPs), the States' plans for
maintaining the 8-hour ozone NAAQS through 2020 in the area.
EPA is proposing to approve the 2002 base year emissions inventory
submitted by IDEM on June 13, 2007, as meeting the base year emissions
inventory requirement of the CAA for the Indiana portion of the
Cincinnati-Hamilton area. EPA is proposing to approve the 2005 base
year emissions inventory submitted by Ohio EPA as part of its
redesignation request as meeting the base year emissions inventory
requirements of the CAA for the Ohio portion of the Cincinnati-Hamilton
area. Finally, EPA finds adequate and is proposing to approve the
States' 2015 and 2020 Motor Vehicle Emission Budgets (MVEBs) for the
Ohio and Indiana portion of the Cincinnati-Hamilton area.
DATES: Comments must be received on or before March 29, 2010.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R05-
OAR-2009-0928 and EPA-R05-OAR-2010-0046, by one of the following
methods:
1. https://www.regulations.gov: Follow the online instructions for
submitting comments.
2. E-mail: damico.genevieve@epa.gov.
3. Fax: (312) 692-2511.
4. Mail: Genevieve Damico, Acting Chief, Criteria Pollutant
Section, Air Programs Branch (AR-18J), U.S. Environmental Protection
Agency, 77 West Jackson Boulevard, Chicago, Illinois 60604.
5. Hand delivery: Genevieve Damico, Acting Chief, Criteria
Pollutant Section, Air Programs Branch (AR-18J), U.S. Environmental
Protection Agency, 77 West Jackson Boulevard, 18th floor, Chicago,
Illinois 60604. Such deliveries are only accepted during the Regional
Office normal hours of operation, and special arrangements should be
made for deliveries of boxed information. The Regional Office official
hours of business 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-
2009-0928 and EPA-R05-OAR-2010-0046. 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
[[Page 8872]]
whose disclosure is restricted by statute. Do not submit information
that you consider to be CBI or otherwise protected through https://www.regulations.gov or e-mail. The https://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 https://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, any form of encryption, and be free of
any defects or viruses. For additional instructions on submitting
comments, go to section I of this document, ``What Should I Consider as
I Prepare My Comments for EPA?''
Docket: All documents in the docket are listed in the https://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 hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Environmental
Protection Agency, Region 5, Air and Radiation Division, 77 West
Jackson Boulevard, Chicago, Illinois 60604. This facility is open from
8:30 a.m. to 4:30 p.m., Monday through Friday, excluding Federal
holidays. We recommend that you telephone Kathleen D'Agostino,
Environmental Engineer, at (312) 886-1767 before visiting the Region 5
office.
FOR FURTHER INFORMATION CONTACT: Kathleen D'Agostino, Environmental
Engineer, Criteria Pollutant Section, Air Programs Branch (AR-18J),
U.S. Environmental Protection Agency, Region 5, 77 West Jackson
Boulevard, Chicago, Illinois 60604, (312) 886-1767,
dagostino.kathleen@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document whenever ``we,''
``us,'' or ``our'' is used, we mean EPA. This supplementary information
section is arranged as follows:
Table of Contents
I. What Should I Consider as I Prepare My Comments for EPA?
II. What Action Is EPA Proposing To Take?
III. What Is the Background for These Actions?
A. What Is the General Background Information?
B. What Are the Impacts of the December 22, 2006, and June 8,
2007, United States Court of Appeals Decisions Regarding EPA's Phase
1 Implementation Rule?
IV. What Are the Criteria for Redesignation?
V. What Is the Effect of These Actions?
VI. What Is EPA's Analysis of the Request?
A. Attainment Determination and Redesignation
B. Adequacy of the MVEBs
C. 2005 Base Year Emissions Inventory for the Ohio Portion of
the Cincinnati-Hamilton Area
D. 2002 Base Year Emissions Inventory for the Indiana Portion of
the Cincinnati-Hamilton Area
VII. What Action Is EPA Taking?
VIII. Statutory and Executive Order Reviews
I. What Should I Consider as I Prepare My Comments for EPA?
When submitting comments, remember to:
1. Identify the rulemaking by docket number and other identifying
information (subject heading, Federal Register date and page number).
2. Follow directions--EPA may ask you to respond to specific
questions or organize comments by referencing a Code of Federal
Regulations (CFR) part or section number.
3. Explain why you agree or disagree; suggest alternatives and
substitute language for your requested changes.
4. Describe any assumptions and provide any technical information
and/or data that you used.
5. If you estimate potential costs or burdens, explain how you
arrived at your estimate in sufficient detail to allow for it to be
reproduced.
6. Provide specific examples to illustrate your concerns, and
suggest alternatives.
7. Explain your views as clearly as possible, avoiding the use of
profanity or personal threats.
8. Make sure to submit your comments by the comment period deadline
identified.
II. What Action Is EPA Proposing To Take?
EPA is proposing to take several related actions. EPA is proposing
to determine that the Cincinnati-Hamilton nonattainment area has
attained the 1997 8-hour ozone standard and that the Ohio and Indiana
portions of this area have met the requirements for redesignation under
section 107(d)(3)(E) of the CAA. EPA is thus proposing to approve
requests from Ohio EPA and IDEM to change the legal designation of the
Ohio and Indiana portions of the Cincinnati-Hamilton area from
nonattainment to attainment for the 8-hour ozone NAAQS. EPA is also
proposing to approve, as revisions to the Ohio and Indiana SIPs, the
States' maintenance plans (such approval being one of the CAA criteria
for redesignation to attainment status). The maintenance plans are
designed to keep the Cincinnati-Hamilton area in attainment of the
ozone NAAQS through 2020. EPA is proposing to approve the 2005 base
year emissions inventory for the Ohio portion of the Cincinnati-
Hamilton area, and the 2002 base year emissions inventory for Dearborn
County, Indiana, as meeting the requirements of section 172(c)(3) of
the CAA. If EPA's determination of attainment is finalized, under the
provisions of 40 CFR 51.918, the requirement to submit certain planning
SIPs related to attainment (the Reasonably Available Control Measure
(RACM) requirement of section 172(c)(1) of the CAA, the Reasonable
Further Progress (RFP) and attainment demonstration requirements of
sections 172(c)(2) and (6) of the CAA, and the requirement for
contingency measures of section 172(c)(9) of the CAA) are not
applicable to the area as long as it continues to attain the NAAQS and
would cease to be applicable upon redesignation. In addition, as set
forth in more detail below, in the context of redesignations, EPA has
interpreted requirements related to attainment as not applicable for
purposes of redesignation. Finally, EPA finds adequate and is proposing
to approve the newly established 2015 and 2020 MVEBs for the Ohio and
Indiana portion of the Cincinnati-Hamilton area. The adequacy comment
period for the MVEBs began on December 10, 2009, with EPA's posting of
the availability of the submittal on EPA's Adequacy Web site (at https://www.epa.gov/otaq/stateresources/transconf/adequacy.htm). The adequacy
comment period for these MVEBs ended on January 11, 2010. EPA did not
receive any requests for this submittal, or adverse comments on this
submittal during the adequacy comment period. In letters dated January
14, 2010, EPA informed Ohio EPA and IDEM that we had found the 2015 and
2020 MVEBs to be adequate for use in transportation conformity
analyses. Please see section VI. B. of this rulemaking, ``Adequacy of
the MVEBs,'' for further explanation of
[[Page 8873]]
this process. Therefore, we find adequate, and are proposing to
approve, the States' 2015 and 2020 MVEBs for transportation conformity
purposes.
III. What Is the Background for These Actions?
A. What Is the General Background Information?
Ground-level ozone is not emitted directly by sources. Rather,
emissions of nitrogen oxides (NOX) and volatile organic
compounds (VOCs) react in the presence of sunlight to form ground-level
ozone. NOX and VOCs are referred to as precursors of ozone.
The CAA establishes a process for air quality management through
the NAAQS. Before promulgation of the 8-hour standard, the ozone NAAQS
was based on a 1-hour standard. On November 6, 1991 (56 FR 56693 and
56813), the Cincinnati-Hamilton area was designated as a moderate
nonattainment area under the 1-hour ozone NAAQS. Dearborn County,
Indiana, was not included as part of the Cincinnati-Hamilton area, and
was designated as attainment/unclassifiable under the 1-hour standard.
The Ohio portion of the Cincinnati-Hamilton area was subsequently
redesignated to attainment of the 1-hour standard effective June 14,
2005. (See 70 FR 35946, published June 21, 2005). This attainment
designation was thus in effect at the time EPA revoked the 1-hour ozone
NAAQS, on June 15, 2005.
On July 18, 1997 (62 FR 38856), EPA promulgated an 8-hour ozone
standard of 0.08 parts per million parts (ppm). On April 30, 2004 (69
FR 23857), EPA published a final rule designating and classifying areas
under the 8-hour ozone NAAQS. These designations and classifications
became effective June 15, 2004. EPA designated as nonattainment any
area that was violating the 8-hour ozone NAAQS based on the three most
recent years of air quality data, 2001-2003.
The CAA contains two sets of provisions, subpart 1 and subpart 2,
that address planning and control requirements for nonattainment areas.
(Both are found in Title I, part D, of the CAA; 42 U.S.C. 7501-7509a
and 7511-7511f, respectively.) Subpart 1 contains general requirements
for nonattainment areas for any pollutant, including ozone, governed by
a NAAQS. Subpart 2 provides more specific requirements for ozone
nonattainment areas.
Under EPA's implementation rule for the 1997 8-hour ozone standard,
(69 FR 23951 (April 30, 2004)), an area was classified under subpart 2
based on its 8-hour ozone design value (i.e. the three-year average
annual fourth-highest daily maximum 8-hour average ozone
concentration), if it had a 1-hour design value at the time of
designation at or above 0.121 ppm (the lowest 1-hour design value in
Table 1 of subpart 2) (69 FR 23954). All other areas were covered under
subpart 1, based upon their 8-hour design values (69 FR 23958). The
Cincinnati-Hamilton area was designated as a subpart 1, 8-hour ozone
nonattainment area by EPA on April 30, 2004 (69 FR 23857, 23900, 23905,
and 23926), based on air quality monitoring data from 2001-2003 (69 FR
23860).
40 CFR 50.10 and 40 CFR part 50, Appendix I provide that the 8-hour
ozone standard is attained when the three-year average of the annual
fourth-highest daily maximum 8-hour average ozone concentration is less
than or equal to 0.08 ppm, when rounded. The data completeness
requirement is met when the average percent of days with valid ambient
monitoring data is greater than 90%, and no single year has less than
75% data completeness. See 40 CFR part 50, Appendix I, 2.3(d).
The Ohio EPA and IDEM submitted requests to redesignate the Ohio
and Indiana portions of the Cincinnati-Hamilton area to attainment for
the 8-hour ozone standard on December 14, 2009, and January 21, 2010,
respectively. The redesignation requests included three years of
complete, quality-assured data for the period of 2007 through 2009,
indicating the 8-hour NAAQS for ozone, as promulgated in 1997, had been
attained for the Cincinnati-Hamilton area. Under the CAA, nonattainment
areas may be redesignated to attainment if sufficient complete,
quality-assured data are available for the Administrator to determine
that the area has attained the standard, and the area meets the other
CAA redesignation requirements in section 107(d)(3)(E).
On March 27, 2008 (73 FR 16436), EPA promulgated a revised 8-hour
ozone standard of 0.075 ppm. In May 2008, States, environmental groups
and industry groups filed petitions with the DC Circuit Court of
Appeals for review of the 2008 ozone standards. In March 2009, the
court granted EPA's request to stay the litigation so EPA could review
the standards and determine whether they should be reconsidered. On
September 16, 2009, we announced that we are reconsidering our 2008
decision setting national standards for ground-level ozone. The
designation process for that standard has been stayed. On January 6,
2010, EPA proposed to set the level of the primary 8-hour ozone
standard within the range of 0.060 to 0.070 ppm, rather than at 0.075
ppm. We expect by August 2010 to have completed our reconsideration of
the standard and also expect that thereafter we will proceed with
designations. The actions addressed in today's proposed rulemaking
relate only to the 1997 8-hour ozone standard.
B. What Are the Impacts of the 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, in South Coast Air Quality Management Dist.
v. EPA, the U.S. Court of Appeals for the District of Columbia Circuit
vacated EPA's Phase 1 Implementation Rule for the 8-hour Ozone Standard
(69 FR 23951, April 30, 2004). 472 F.3d 882 (D.C. Cir. 2006). On June
8, 2007, in response to several petitions for rehearing, the DC Circuit
Court clarified that the Phase 1 Rule was vacated only with regard to
those parts of the rule that had been successfully challenged. Id.,
Docket No. 04 1201. Therefore, several provisions of the Phase 1 Rule
remain effective: 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
for emissions reductions needed for attainment of the 8-hour ozone
NAAQS. The June 8, 2007, decision also 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 standard and those anti-backsliding provisions of the Phase 1 Rule
that had not been successfully challenged. The June 8, 2007, decision
reaffirmed the December 22, 2006, decision that EPA had improperly
failed to retain four 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 or extreme nonattainment areas; (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; and (4) certain transportation conformity requirements for
certain types of Federal actions. The June 8, 2007, decision
[[Page 8874]]
clarified that the Court's reference to conformity requirements was
limited to requiring the continued use of 1-hour motor vehicle
emissions budgets until 8-hour budgets were available for 8-hour
conformity determinations.
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 or 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 Standard
With respect to the 8-hour standard, the Court's ruling rejected
EPA's reasons for classifying areas under subpart 1 for the 8-hour
standard, and remanded that matter to the Agency. In its January 16,
2009, proposed rulemaking in response to the South Coast decision, EPA
has proposed to classify Cincinnati-Hamilton under subpart 2 as a
moderate area. 74 FR 2936, 2944. If EPA finalizes this rulemaking, the
requirements under subpart 2 will become applicable when they are due,
a deadline that EPA has proposed to be one year after the effective
date of a final rulemaking classifying areas as moderate or marginal.
74 FR 2940-2941. Although a future final decision by EPA to classify
this area under subpart 2 would trigger additional future requirements
for the area, EPA believes that this does not mean that redesignation
cannot now go forward. This belief is based upon: (1) EPA's
longstanding policy of evaluating requirements in accordance with the
requirements due at the time the request is submitted; and, (2)
consideration of the inequity of applying retroactively any
requirements that might be applied in the future.
First, at the time the redesignation request was submitted, the
Cincinnati-Hamilton area was not classified under subpart 2, nor were
there any subpart 2 requirements yet due for this area. 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. See
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 Michael
Shapiro Memorandum, September 17, 1993, and 60 FR 12459, 12465-66
(March 7, 1995) (Redesignation of Detroit-Ann Arbor). See Sierra Club
v. EPA, 375 F.3d 537 (7th Cir. 2004), which upheld EPA's redesignation
rulemaking applying 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 request was
submitted. The DC Circuit has recognized the inequity in such
retroactive rulemaking. In Sierra Club v. Whitman, 285 F. 3d 63 (D.C.
Cir. 2002), 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 time frame, 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 or
yet due at the time it submitted its redesignation request.
3. Requirements Under the 1-Hour Standard
With respect to the 1-hour standard requirements, the Cincinnati-
Hamilton area was an attainment area subject to a CAA section 175A
maintenance plan under the 1-hour standard. The DC Circuit's decisions
with respect to 1-hour nonattainment anti-backsliding requirements do
not impact redesignation requests for these types of areas, except to
the extent that the Court in its June 8, 2007, decision clarified that
for those areas with 1-hour motor vehicle emissions budgets in their
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 comply with the applicable requirements of EPA's
conformity regulations at 40 CFR part 93.
With respect to the three other anti-backsliding provisions for the
1-hour standard that the Court found were not properly retained, the
Cincinnati-Hamilton area is an attainment area subject to a maintenance
plan for the 1-hour standard, and the NSR, contingency measure
(pursuant to section 172(c)(9) or 182(c)(9)), and fee provision
requirements no longer apply to an area that has been redesignated to
attainment of the 1-hour standard.
Thus, the decision in South Coast Air Quality Management Dist.
would not preclude EPA from finalizing the redesignation of this area.
IV. What Are the Criteria for Redesignation?
The CAA provides the requirements for redesignating a nonattainment
area to attainment. Specifically, section 107(d)(3)(E) allows for
redesignation provided that: (1) The Administrator determines that the
area has attained the applicable NAAQS; (2) the Administrator has fully
approved the applicable implementation plan for the area under section
110(k); (3) the Administrator determines that the improvement in air
quality is due to permanent and enforceable reductions in emissions
resulting from implementation of the applicable SIP and applicable
Federal air pollutant control regulations and other permanent and
enforceable reductions; (4) the Administrator has fully approved a
maintenance plan for the area as meeting the requirements of section
175A; and, (5) the State containing such area has met all requirements
applicable to the area under section 110 and part D.
EPA provided guidance on redesignation in the General Preamble for
the Implementation of Title I of the CAA Amendments of 1990 on April
16, 1992 (57 FR 13498), and supplemented this guidance on April 28,
1992 (57 FR 18070). EPA has provided further guidance on processing
redesignation requests in the following documents:
``Ozone and Carbon Monoxide Design Value Calculations,'' Memorandum
from William G. Laxton, Director Technical Support Division, June 18,
1990;
``Maintenance Plans for Redesignation of Ozone and Carbon Monoxide
Nonattainment Areas,'' Memorandum from G. T. Helms, Chief, Ozone/Carbon
Monoxide Programs Branch, April 30, 1992;
``Contingency Measures for Ozone and Carbon Monoxide (CO)
Redesignations,''
[[Page 8875]]
Memorandum from G. T. Helms, Chief, Ozone/Carbon Monoxide Programs
Branch, June 1, 1992;
``Procedures for Processing Requests to Redesignate Areas to
Attainment,'' Memorandum from John Calcagni, Director, Air Quality
Management Division, September 4, 1992;
``State Implementation Plan (SIP) Actions Submitted in Response to
Clean Air Act (ACT) Deadlines,'' Memorandum from John Calcagni,
Director, Air Quality Management Division, October 28, 1992;
``Technical Support Documents (TSD's) for Redesignation Ozone and
Carbon Monoxide (CO) Nonattainment Areas,'' Memorandum from G. T.
Helms, Chief, Ozone/Carbon Monoxide Programs Branch, August 17, 1993;
``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 for Air and Radiation, September 17, 1993;
``Use of Actual Emissions in Maintenance Demonstrations for Ozone
and CO Nonattainment Areas,'' Memorandum from D. Kent Berry, Acting
Director, Air Quality Management Division, to Air Division Directors,
Regions 1-10, November 30, 1993.
``Part D New Source Review (part D NSR) Requirements for Areas
Requesting Redesignation to Attainment,'' Memorandum from Mary D.
Nichols, Assistant Administrator for Air and Radiation, October 14,
1994; 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.
V. What Is the Effect of These Actions?
Approval of the redesignation requests would change the official
designation of the Ohio and Indiana portions of the Cincinnati-Hamilton
area for the 1997 8-hour ozone NAAQS found at 40 CFR part 81. It would
also incorporate into the Ohio and Indiana SIPs, plans for maintaining
the 8-hour ozone NAAQS through 2020. The maintenance plans include
contingency measures as required under CAA section 175A to remedy
future violations of the 8-hour NAAQS. They also establish MVEBs for
the Ohio and Indiana portions of the Cincinnati-Hamilton area of 31.73
and 28.82 tons per day (tpd) VOC and 49.00 and 34.39 tpd NOX
for the years 2015 and 2020, respectively.
VI. What Is EPA's Analysis of the Request?
A. Attainment Determination and Redesignation
EPA is proposing to determine that the Cincinnati-Hamilton area has
attained the 1997 8-hour ozone standard and that the area has met all
other applicable redesignation criteria under CAA section 107(d)(3)(E).
The basis for EPA's proposed approvals of the redesignation requests is
as follows:
1. The Area Has Attained the 8-hour Ozone NAAQS (Section
107(d)(3)(E)(i))
EPA is proposing to make a determination that the Cincinnati-
Hamilton area has attained the 1997 8-hour ozone NAAQS. An area may be
considered to be attaining the 8-hour ozone NAAQS if there are no
violations, as determined in accordance with 40 CFR 50.10 and part 50,
Appendix I, based on three complete, consecutive calendar years of
quality-assured air quality monitoring data. To attain this standard,
the three-year average of the fourth-highest daily maximum 8-hour
average ozone concentrations measured at each monitor within an area
over each year must not exceed 0.08 ppm. Based on the rounding
convention described in 40 CFR part 50, Appendix I, the standard is
attained if the design value is 0.084 ppm or below. The data must be
collected and quality-assured in accordance with 40 CFR part 58, and
recorded in the EPA's Air Quality System (AQS). The monitors generally
should have remained at the same location for the duration of the
monitoring period required for demonstrating attainment.
Ohio and Indiana included in their redesignation requests ozone
monitoring data for the 2007 to 2009 ozone seasons. Monitoring data for
2007 and 2008 have been certified by the States; 2009 data has not yet
been certified. However, Ohio and Kentucky have quality-assured all of
the ambient monitoring data in accordance with 40 CFR 58.10, and have
recorded it in the AQS database. (There are no monitoring locations in
Dearborn County, Indiana.) The data meet the completeness criteria in
40 CFR 50, Appendix I, which requires a minimum completeness of 75
percent annually and 90 percent over each three-year period. Monitoring
data are presented in Table 1 below.
Table 1--Annual 4th High Daily Maximum 8-Hour Ozone Concentration and Three Year Averages of 4th High Daily Maximum 8-Hour Ozone Concentrations
--------------------------------------------------------------------------------------------------------------------------------------------------------
2007 4th high 2008 4th high 2009 4th high 2007-2009
State County Monitor (ppm) (ppm) (ppm) average (ppm)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Ohio................................. Butler................. Hamilton................ 0.091 0.071 0.073 0.078
39-017-0004.............
------------------------------------------------------------------------------------------------------------------
Middletown.............. 0.091 0.079 0.076 0.082
39-017-1004.............
��������������������������������������
Clermont............... Batavia................. 0.086 0.071 0.069 0.075
39-025-0022.............
��������������������������������������
Clinton................ Wilmington.............. 0.082 0.076 0.070 0.076
39-027-1002.............
��������������������������������������
Hamilton............... Grooms Rd., Cincinnati.. 0.089 0.086 0.072 0.082
39-061-0006.............
------------------------------------------------------------------------------------------------------------------
[[Page 8876]]
Cleves.................. 0.086 0.077 0.065 0.076
39-061-0010.............
------------------------------------------------------------------------------------------------------------------
250 Wm. Howard Taft, 0.086 0.080 0.074 0.080
Cincinnati.
39-061-0040.............
��������������������������������������
Warren................. Lebanon................. 0.088 0.082 0.077 0.082
39-165-0007.............
--------------------------------------------------------------------------------------------------------------------------------------------------------
Kentucky............................. Boone.................. KY 338 & Lower River 0.078 0.064 0.064 0.068
Road.
21-015-0003.............
��������������������������������������
Campbell............... Highland Heights........ 0.086 0.075 0.068 0.076
21-037-3002.............
��������������������������������������
Kenton................. Covington............... 0.085 0.073 0.074 0.077
21-117-0007.............
--------------------------------------------------------------------------------------------------------------------------------------------------------
In addition, as discussed below with respect to the Ohio
maintenance plan, Ohio EPA has committed to continue to operate an EPA-
approved monitoring network as necessary to demonstrate ongoing
compliance with the NAAQS. Ohio EPA commits to continue monitoring
ozone at the sites indicated in Table 1 and to consult with EPA prior
to making changes to the existing monitoring network, should changes
become necessary in the future. Ohio EPA remains obligated to continue
to quality assure monitoring data in accordance with 40 CFR part 58 and
enter all data into AQS in accordance with Federal guidelines. Indiana
does not operate any ozone monitors in Dearborn County, which contains
Lawrenceburg Township, the Indiana portion of the Cincinnati-Hamilton
area. In summary, EPA believes that the data show that the Cincinnati-
Hamilton area has attained the 8-hour ozone NAAQS.
2. The Area Has Met All Applicable Requirements Under Section 110 and
Part D; and the Area Has a Fully Approved SIP Under Section 110(k)
(Sections 107(d)(3)(E)(v) and 107(d)(3)(E)(ii))
We have determined that Ohio and Indiana have met all currently
applicable SIP requirements for purposes of redesignation for the
Cincinnati-Hamilton area under section 110 of the CAA (general SIP
requirements). We are also proposing to determine that the Ohio and
Indiana SIPs meet all SIP requirements currently applicable for
purposes of redesignation under part D of Title I of the CAA
(requirements specific to subpart 1 nonattainment areas), in accordance
with section 107(d)(3)(E)(v). In addition, with the exception of the
base year emissions inventory, we have determined that the Ohio and
Indiana SIPs are fully approved with respect to all applicable
requirements for purposes of redesignation, in accordance with section
107(d)(3)(E)(ii). As discussed below, in this action EPA is proposing
to approve Ohio's 2005 base year emissions inventory and Indiana's 2002
base year emissions inventory as meeting the section 172(c)(3)
emissions inventory requirement.
In proposing these determinations, we have ascertained which SIP
requirements are applicable to the area for purposes of redesignation,
and have determined that there are SIP measures meeting those
requirements and that they are fully approved under section 110(k) of
the CAA. As discussed more fully below, for purposes of evaluating a
redesignation request, SIPs must be fully approved only with respect to
requirements that became due prior to the submission of the
redesignation request.
The September 4, 1992, Calcagni memorandum (see ``Procedures for
Processing Requests to Redesignate Areas to Attainment,'' Memorandum
from John Calcagni, Director, Air Quality Management Division,
September 4, 1992) describes EPA's interpretation of section
107(d)(3)(E) of the CAA. Under this interpretation, a State and the
area it wishes to redesignate must meet the relevant CAA requirements
that are 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 60 FR 12459, 12465-12466 (March 7, 1995) (Redesignation
of Detroit-Ann Arbor). Applicable requirements of the CAA that come due
subsequent to the State's submittal of a complete request remain
applicable until a redesignation to attainment is approved, but are not
required as a prerequisite to redesignation. See section 175A(c) of the
CAA. Sierra Club v. EPA, 375 F.3d 537 (7th Cir. 2004). See also 68 FR
25424, 25427 (May 12, 2003) (Redesignation of St. Louis).
Since EPA is proposing here to determine that the area has attained
the 1997 8-hour ozone standard, under 40 CFR 51.918, if that
determination is finalized, the requirements to submit certain planning
SIPs related to attainment, including attainment demonstration
requirements (the RACM requirement of section 172(c)(1) of the CAA, the
RFP and attainment demonstration requirements of sections 172(c)(2) and
(c)(6) of the CAA, and the requirement for contingency measures of
section 172(c)(9) of the CAA) would not be applicable to the area as
long as it continues to attain the NAAQS and would cease to apply upon
redesignation. In addition, in the context of redesignations, EPA has
interpreted requirements related to attainment as not applicable for
purposes of redesignation. For example, in the General Preamble EPA
stated that:
[t]he section 172(c)(9) requirements are directed at ensuring
RFP and attainment by the applicable date. These requirements no
longer apply when an area has attained the standard and is eligible
for redesignation. Furthermore, section 175A for maintenance plans *
* * provides specific requirements for contingency measures that
effectively
[[Page 8877]]
supersede the requirements of section 172(c)(9) for these areas.
``General Preamble for the Interpretation of Title I of the Clean
Air Act Amendments of 1990,'' (General Preamble) 57 FR 13498, 13564
(April 16, 1992).
See also Calcagni memorandum at 6 (``The requirements for reasonable
further progress and other measures needed for attainment will not
apply for redesignations because they only have meaning for areas not
attaining the standard'').
a. The Ohio and Indiana Portions of the Cincinnati-Hamilton Area Have
Met All Applicable Requirements for Purposes of Redesignation Under
Section 110 and Part D of the CAA
i. Section 110 General SIP Requirements
Section 110(a) of Title I of the CAA contains the general
requirements for a SIP. Section 110(a)(2) provides that the
implementation plan submitted by a State must have been adopted by the
State after reasonable public notice and hearing, and that, among other
things, it includes enforceable emission limitations and other control
measures, means or techniques necessary to meet the requirements of the
CAA; provides for establishment and operation of appropriate devices,
methods, systems and procedures necessary to monitor ambient air
quality; provides for implementation of a source permit program to
regulate the modification and construction of any stationary source
within the areas covered by the plan; includes provisions for the
implementation of part C, Prevention of Significant Deterioration (PSD)
and part D, NSR permit programs; includes criteria for stationary
source emission control measures, monitoring, and reporting; includes
provisions for air quality modeling; and provides for public and local
agency participation in planning and emission control rule development.
Section 110(a)(2)(D) of the CAA requires that SIPs contain measures
to prevent sources in a State from significantly contributing to air
quality problems in another State. To implement this provision, EPA has
required certain States to establish programs to address transport of
air pollutants (NOX SIP Call \1\ and Clean Air Interstate
Rule (CAIR) (70 FR 25162, May 12, 2005)). However, the section
110(a)(2)(D) requirements for a State are not linked with a particular
nonattainment area's designation and classification. EPA believes that
the requirements linked with a particular nonattainment area's
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. Thus, we
believe that these requirements should not be construed to be
applicable requirements for purposes of redesignation.
---------------------------------------------------------------------------
\1\ On October 27, 1998 (63 FR 57356), EPA issued a
NOX SIP Call requiring the District of Columbia and 22
States to reduce emissions of NOX in order to reduce the
transport of ozone and ozone precursors. In compliance with EPA's
NOX SIP Call, both Ohio EPA and IDEM have developed rules
governing the control of NOX emissions from Electric
Generating Units (EGUs), major non-EGU industrial boilers, major
cement kilns, and internal combustion engines. EPA approved Ohio's
rules as fulfilling Phase I of the NOX SIP Call on August
5, 2003 (68 FR 46089) and June 27, 2005 (70 FR 36845), and as
meeting Phase II of the NOX SIP Call on February 4, 2008
(73 FR 6427). EPA approved Indiana's rules as fulfilling
requirements of Phase I of the NOX SIP Call on November
8, 2001 (66 FR 56465) and December 11, 2003 (68 FR 69025), and as
meeting Phase II of the NOX SIP Call on October 1, 2007
(72 FR 55664).
---------------------------------------------------------------------------
Further, we believe that the other section 110 elements described
above that are not connected with nonattainment plan submissions and
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 a particular area's designation and classification are the
relevant measures which we may consider in evaluating 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), (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 1-
hour ozone redesignation (65 FR 37890, June 19, 2000), and in the
Pittsburgh, Pennsylvania 1-hour ozone redesignation (66 FR 50399,
October 19, 2001).
We have reviewed Ohio's SIP and have concluded that it meets the
general SIP requirements under section 110 of the CAA to the extent
they are applicable for purposes of redesignation. EPA has previously
approved provisions of the Ohio SIP addressing section 110 elements
under the 1-hour ozone standard (40 CFR 52.1870). Further, in
submittals dated December 5, 2007 and September 19, 2008, Ohio
confirmed that the State continues to meet the section 110 requirements
for the 8-hour ozone standard. EPA has not yet taken rulemaking action
on these submittals; however, such approval is not necessary for
redesignation.
We have also reviewed Indiana's SIP and have concluded that it
meets the general SIP requirements under section 110 of the CAA to the
extent they are applicable for purposes of redesignation. EPA has
previously approved provisions of the Indiana SIP addressing section
110 elements under the 1-hour ozone standard (40 CFR 52.773). Further,
in a submittal dated December 10, 2007, Indiana confirmed that the
State continues to meet the section 110 requirements for the 8-hour
ozone standard. EPA has not yet taken rulemaking action on this
submittal; however, such approval is not necessary for redesignation.
ii. Part D Requirements
EPA has determined that, if EPA finalizes the approval of the base
year emissions inventories discussed in section VI.C. and D. of this
rulemaking, the Ohio and Indiana SIPs will meet the applicable SIP
requirements for their portions of the Cincinnati-Hamilton area
applicable for purposes of redesignation under part D of the CAA.
Subpart 1 of part D, found in sections 172-176 of the CAA, sets forth
the basic nonattainment requirements applicable to all nonattainment
areas. Subpart 2 of part D, which includes section 182 of the CAA,
establishes additional specific requirements depending on the area's
nonattainment classification.
Since the Cincinnati-Hamilton area was not classified under subpart
2 of Part D at the time its redesignation request was submitted, the
subpart 2 requirements do not apply for purposes of evaluating the
States' redesignation requests. The applicable subpart 1 requirements
are contained in sections 172(c)(1)-(9) and in section 176.
Subpart 1 Section 172 Requirements
For purposes of evaluating this redesignation request, the
applicable section 172 SIP requirements for the Cincinnati-Hamilton
area are contained in sections 172(c)(1)-(9). A thorough discussion of
the requirements contained in section 172 can be found in the General
Preamble for Implementation of Title I (57 FR 13498, April 16, 1992).
[[Page 8878]]
Section 172(c)(1) requires the plans for all nonattainment areas to
provide for the implementation of all RACM as expeditiously as
practicable and to provide for attainment of the national primary
ambient air quality standards. The EPA interprets this requirement to
impose a duty on all nonattainment areas to consider all available
control measures and to adopt and implement such measures as are
reasonably available for implementation in each area as components of
the area's attainment demonstration. On June 15, 2007 and April 22,
2008, Ohio EPA submitted an attainment demonstration and identified the
control measures necessary to attain the NAAQS in the Cincinnati-
Hamilton area. Indiana submitted an attainment demonstration for the
Cincinnati-Hamilton area on June 13, 2007. However, because attainment
has been reached, no additional measures are needed to provide for
attainment, and section 172(c)(1) requirements are no longer considered
to be applicable as long as the area continues to attain the standard
until redesignation. 40 CFR 51.918. If EPA finalizes approval of the
redesignation of the Ohio and Indiana portions of the Cincinnati-
Hamilton area, EPA will take no further action on the attainment
demonstrations submitted by Ohio and Indiana for the area.
The RFP requirement under section 172(c)(2) is defined as progress
that must be made toward attainment. This requirement is not relevant
for purposes of redesignation because the Cincinnati-Hamilton area has
monitored attainment of the ozone NAAQS. (General Preamble, 57 FR
13564). See also 40 CFR 51.918. In addition, because the Cincinnati-
Hamilton area has attained the ozone NAAQS and is no longer subject to
an RFP requirement, the requirement to submit the section 172(c)(9)
contingency measures is not applicable for purposes of redesignation.
Id.
Section 172(c)(3) requires submission and approval of a
comprehensive, accurate and current inventory of actual emissions. As
part of Ohio's redesignation request for the Cincinnati-Hamilton area,
the State submitted a 2005 base year emissions inventory. As discussed
below in section VI.C., EPA is proposing to approve the 2005 base year
inventory that Ohio submitted with the redesignation request as meeting
the section 172(c)(3) emissions inventory requirement. As part of
Indiana's June 13, 2007, attainment demonstration submittal for the
Cincinnati-Hamilton area, IDEM included a 2002 base year emissions
inventory. As discussed below in section VI.D., EPA is proposing to
approve Indiana's 2002 base year inventory as meeting the section
172(c)(3) emissions inventory requirement.
Section 172(c)(4) requires the identification and quantification of
allowable emissions for major new and modified stationary sources to be
allowed in an area, and section 172(c)(5) requires source permits for
the construction and operation of new and modified major stationary
sources anywhere in the nonattainment area. EPA has determined that,
since PSD requirements will apply after redesignation, 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 NAAQS without part D NSR. 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.'' Ohio and Indiana have demonstrated that
the Cincinnati-Hamilton area will be able to maintain the standard
without part D NSR in effect; therefore, EPA concludes that the States
need not have fully approved part D NSR programs prior to approval of
the redesignation request. The States' PSD programs will become
effective in the Cincinnati-Hamilton 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); and
Grand Rapids, Michigan (61 FR 31834-31837, June 21, 1996).
Section 172(c)(6) requires the SIP to contain control measures
necessary to provide for attainment of the standard. Because attainment
has been reached, no additional measures are needed to provide for
attainment.
Section 172(c)(7) requires the SIP to meet the applicable
provisions of section 110(a)(2). As noted above, we believe the Ohio
and Indiana SIPs meet the requirements of section 110(a)(2) applicable
for purposes of redesignation.
Subpart 1 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 quality planning goals
in the applicable SIPs. The requirement to determine conformity applies
to transportation plans, programs and projects developed, funded or
approved under Title 23 of the U.S. Code and the Federal Transit Act
(transportation conformity) as well as to all other Federally-supported
or funded projects (general conformity). State conformity revisions
must be consistent with Federal conformity regulations relating to
consultation, enforcement, and enforceability, which EPA promulgated
pursuant to CAA requirements.
EPA believes that it is reasonable to interpret the conformity SIP
requirements as not applying for purposes of evaluating the
redesignation request under section 107(d) for two reasons. First, the
requirement to submit SIP revisions to comply with the conformity
provisions of the CAA continues to apply to areas after redesignation
to attainment since such areas would be subject to a section 175A
maintenance plan. Second, EPA's Federal conformity rules require the
performance of conformity analyses in the absence of Federally-approved
State rules. Therefore, because areas are subject to the conformity
requirements regardless of whether they are redesignated to attainment
and, because they must implement conformity under Federal rules if
State rules are not yet approved, EPA believes it is reasonable to view
these requirements as not applying for purposes of evaluating a
redesignation request. See Wall v. EPA, 265 F.3d 426 (6th Cir. 2001),
upholding this interpretation. See also 60 FR 62748, 62749-62750 (Dec.
7, 1995) (Tampa, Florida).
EPA approved Ohio's general and transportation conformity SIPs on
March 11, 1996 (61 FR 9646), and May 30, 2000 (65 FR 34395),
respectively. Section 176(c) of the CAA was amended by provisions
contained in the Safe, Accountable, Flexible, Efficient Transportation
Equity Act: A Legacy for Users (SAFETEALU), which was signed into law
on August 10, 2005 (Pub. L. 109-59). Among the changes Congress made to
this section of the CAA was to streamline the requirements for State
conformity SIPs. Ohio is in the process of updating its transportation
conformity SIP to meet these new requirements. EPA approved Indiana's
general conformity SIP on January 14, 1998 (63 FR 2146). Indiana does
not have a Federally-approved transportation conformity SIP. However,
conformity analyses are performed pursuant to EPA's Federal conformity
rules. Ohio and Indiana have submitted onroad motor vehicle budgets for
the Ohio and Indiana portion of the
[[Page 8879]]
Cincinnati-Hamilton area of 31.73 and 28.82 tpd VOC and 49.00 and 34.39
tpd NOX for the years 2015 and 2020, respectively. The area
must use the MVEBs from the maintenance plan in any conformity
determination that is effective on or after the effective date of the
maintenance plan approval.
b. The Ohio and Indiana Portions of the Cincinnati-Hamilton Area Have
Fully Approved Applicable SIPs Under Section 110(k) of the CAA
If EPA issues a final approval of the base year emissions
inventories, EPA will have fully approved the Ohio and Indiana SIPs for
the Cincinnati-Hamilton area under section 110(k) of the CAA for all
requirements applicable for purposes of redesignation. EPA may rely on
prior SIP approvals in approving a redesignation request (See page 3 of
the September 4, 1992, John Calcagni memorandum; Southwestern
Pennsylvania Growth Alliance v. Browner, 144 F.3d 984, 989-990 (6th
Cir. 1998); 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 25413, 25426 (May 12, 2003). Since the passage of the
CAA of 1970, Ohio and Indiana have adopted and submitted, and EPA has
fully approved, provisions addressing various required SIP elements
under the 1-hour ozone standard. In this action, EPA is proposing to
approve Ohio's 2005 base year emissions inventory and Indiana's 2002
base year emissions inventory for the Cincinnati-Hamilton area as
meeting the requirement of section 172(c)(3) of the CAA. No Cincinnati-
Hamilton area SIP provisions are currently disapproved, conditionally
approved, or partially approved.
3. The Improvement in Air Quality is Due to Permanent and Enforceable
Reductions in Emissions Resulting From Implementation of the SIP and
Applicable Federal Air Pollution Control Regulations and Other
Permanent and Enforceable Reductions (Section 107(d)(3)(E)(iii))
EPA finds that Ohio and Indiana have demonstrated that the observed
air quality improvement in the Cincinnati-Hamilton area is due to
permanent and enforceable reductions in emissions resulting from
implementation of the SIPs, Federal measures, and other State-adopted
measures.
In making this demonstration, Ohio EPA and IDEM have calculated the
change in emissions between 2005 and 2008. Ohio and Indiana are using
2005 base year emissions inventories developed in conjunction with the
Lake Michigan Air Directors Consortium (LADCO) as the nonattainment
inventories. The States developed an attainment inventory for 2008, one
of the years the Cincinnati-Hamilton area monitored attainment. The
reduction in emissions and the corresponding improvement in air quality
over this time period can be attributed to a number of regulatory
control measures that Cincinnati-Hamilton and upwind areas have
implemented in recent years.
a. Permanent and Enforceable Controls Implemented
The following is a discussion of permanent and enforceable measures
that have been implemented in the areas:
i. Stationary Source NOX Rules
Ohio EPA and IDEM have developed rules governing the control of
NOX emissions from Electric Generating Units (EGUs), major
non-EGU industrial boilers, major cement kilns, and internal combustion
engines. EPA approved Ohio's rules as fulfilling Phase I of the
NOX SIP Call on August 5, 2003 (68 FR 46089), and June 27,
2005 (70 FR 36845), and as fulfilling Phase II of the SIP Call on
February 4, 2008 (73 FR 6427). EPA approved Indiana's rules as
fulfilling requirements of Phase I of the NOX SIP Call on
November 8, 2001 (66 FR 56465), and December 11, 2003 (68 FR 69025),
and as meeting Phase II of the NOX SIP Call on October 1,
2007 (72 FR 55664). Ohio and Indiana began complying with Phase I of
this rule in 2004. Compliance with Phase II of the SIP Call, which
requires the control NOX emissions from large internal
combustion engines, began in both Ohio and Indiana in 2007, and was
projected to result in an 82 percent NOX reduction from 1995
levels.
ii. Federal Emission Control Measures
Reductions in VOC and NOX emissions have occurred
statewide and in upwind areas as a result of Federal emission control
measures, with additional emission reductions expected to occur in the
future. Federal emission control measures include the following.
Tier 2 Emission Standards for Vehicles and Gasoline Sulfur
Standards. These emission control requirements result in lower VOC and
NOX emissions from new cars and light duty trucks, including
sport utility vehicles. The Federal rules were phased in between 2004
and 2009. The EPA has estimated that, by the end of the phase-in
period, the following vehicle NOX emission reductions will
occur nationwide: Passenger cars (light duty vehicles) (77 percent);
light duty trucks, minivans, and sports utility vehicles (86 percent);
and, larger sports utility vehicles, vans, and heavier trucks (69 to 95
percent). VOC emission reductions are expected to range from 12 to 18
percent, depending on vehicle class, over the same period. Some of
these emission reductions occurred by the attainment years (2007-2009)
and additional emission reductions will occur during the maintenance
period.
Heavy-Duty Diesel Engine Rule. EPA issued this rule in July 2000.
This rule includes standards limiting the sulfur content of diesel
fuel, which went into effect in 2004. A second phase took effect in
2007 which further reduced the highway diesel fuel sulfur content to 15
parts per million, leading to additional reductions in combustion
NOX and VOC emissions. This rule is expected to achieve a 95
percent reduction in NOX emissions from diesel trucks and
busses.
Non-Road Diesel Rule. EPA issued this rule in 2004. This rule
applies to diesel engines used in industries, such as construction,
agriculture, and mining. It is estimated that compliance with this rule
will cut NOX emissions from non-road diesel engines by up to
90 percent. This rule is currently achieving emission reductions, but
will not be fully implemented until 2010.
iii. Control Measures in Upwind Areas
On October 27, 1998 (63 FR 57356), EPA issued a NOX SIP
Call requiring the District of Columbia and 22 States to reduce
emissions of NOX. Affected States were required to comply
with Phase I of the SIP Call beginning in 2004, and Phase II beginning
in 2007. The reduction in NOX emissions has resulted in
lower concentrations of transported ozone entering the Cincinnati-
Hamilton area. Emission reductions resulting from regulations developed
in response to the NOX SIP Call are permanent and
enforceable.
b. Emission Reductions
Ohio and Indiana are using 2005 base year emissions inventories
developed in conjunction with the LADCO as the nonattainment
inventories. The main purpose of LADCO is to provide technical
assessments for and assistance to its member States on problems of air
quality. LADCO's primary geographic focus is the area encompassed by
its member States (Illinois, Indiana, Michigan, Ohio and Wisconsin) and
any areas which affect air quality in its member States. In developing
the 2005 nonattainment year inventory, Ohio EPA and IDEM provided point
and area source inventories to LADCO. LADCO processed these inventories
through the Emission Modeling Sy