Redesignation of the Toledo, Ohio Area to Attainment for the 8-Hour Ozone Standard, 32246-32257 [E7-11305]

Agencies

• ENVIRONMENTAL PROTECTION AGENCY

[Federal Register Volume 72, Number 112 (Tuesday, June 12, 2007)]
[Proposed Rules]
[Pages 32246-32257]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-11305]


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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Parts 52 and 81

[EPA-R05-OAR-2007-0001; FRL-8326-4]


Redesignation of the Toledo, Ohio Area to Attainment for the 8-
Hour Ozone Standard

AGENCY: Environmental Protection Agency (EPA).

ACTION: Proposed rule.

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SUMMARY: The Ohio Environmental Protection Agency (Ohio EPA) submitted 
a request on December 22, 2006, and supplemented it on March 9, 2007, 
for redesignation of the Toledo, Ohio area which includes Lucas and

[[Page 32247]]

Wood Counties to attainment for the 8-hour ozone standard. EPA is 
proposing to approve several elements associated with of this request. 
First, EPA is making a determination that complete, quality-assured 
ambient air quality data indicate that the Toledo area has attained the 
8-hour ozone standard. Second, EPA is proposing to approve, as 
revisions to the Ohio State Implementation Plan (SIP), the State's 
plans for maintaining the 8-hour ozone NAAQS through 2018. Third, EPA 
is proposing to redesignate the Toledo area to attainment for the 8-
hour ozone standard, based on a finding that the requirements for this 
redesignation have been satisfied. Fourth, EPA finds adequate and is 
proposing to approve the State's 2009 and 2018 Motor Vehicle Emission 
Budgets (MVEBs) for the Toledo area.

DATES: Comments must be received on or before July 12, 2007.

ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R05-
OAR-2007-0001, by one of the following methods:
     https://www.regulations.gov/. Follow the on-line 
instructions for submitting comments.
     E-mail: mooney.john@epa.gov.
     Fax: (312) 886-5824.
     Mail: John M. Mooney, Chief, Criteria Pollutant Section, 
Air Programs Branch, (AR-18J), U.S. Environmental Protection Agency, 77 
West Jackson Boulevard, Chicago, Illinois 60604.
     Hand delivery: John M. Mooney, Chief, Criteria Pollutant 
Section, Air Programs Branch, (AR-18J), U.S. Environmental Protection 
Agency, 77 West Jackson Boulevard, 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-
2007-0001. EPA's policy is that all comments received will be included 
in the public docket without change and may be made available online at 
www.regulations.gov, including any personal information provided, 
unless the comment includes information claimed to be Confidential 
Business Information (CBI) or other information whose disclosure is 
restricted by statute. Do not submit information that you consider to 
be CBI or otherwise protected through www.regulations.gov or e-mail. 
The www.regulations.gov Web site is an ``anonymous access'' system, 
which means EPA will not know your identity or contact information 
unless you provide it in the body of your comment. If you send an e-
mail comment directly to EPA without going through www.regulations.gov, 
your 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 the 
SUPPLEMENTARY INFORMATION section of this document.
    Docket: All documents in the docket are listed in the 
www.regulations.gov index. Although listed in the index, some 
information is not publicly available, e.g., CBI or other information 
whose disclosure is restricted by statute. Certain other material, such 
as copyrighted material, will be publicly available only in hard copy. 
Publicly available docket materials are available either electronically 
in 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 legal holidays. We 
recommend that you telephone Michael Leslie, Environmental Engineer, at 
(312) 353-6680 before visiting the Region 5 office.

FOR FURTHER INFORMATION CONTACT: Michael Leslie, Environmental 
Engineer, Criteria Pollutant Section, Air Programs Branch (AR-18J), 
Environmental Protection Agency, Region 5, 77 West Jackson Boulevard, 
Chicago, Illinois 60604, (312) 353-6680, leslie.michael@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 Actions Is EPA Proposing To Take?
III. What Is the Background for These Actions?
IV. What Are the Criteria for Redesignation?
V. Why Is EPA Proposing To Take These Actions?
VI. What Is the Effect of These Actions?
VII. What Is EPA's Analysis of the Request?
    A. Attainment Determination and Redesignation
    B. Adequacy of Ohio's Motor Vehicle Emissions Budgets
VIII. What Actions Is EPA Taking Today?
IX. 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--The 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 Actions Is EPA Proposing To Take?

    EPA is proposing to take several related actions. EPA is proposing 
to determine that the Toledo nonattainment area has attained the 8-hour 
ozone standard. EPA is also proposing to approve Ohio's maintenance 
plan SIP revision for the Toledo area. The maintenance plan is designed 
to keep the Toledo nonattainment area in attainment of the ozone NAAQS 
through 2018. EPA is proposing that the Toledo area has met the 
requirements for redesignation under Section 107(d)(3)(E) of the Clean 
Air Act (CAA). EPA is thus proposing to approve Ohio's request to 
change the legal determination of Toledo area from nonattainment to 
attainment for the 8-hour ozone National Ambient Air Quality Standard 
(NAAQS). Finally, EPA is announcing its action on the Adequacy Process 
for the newly established 2009 and 2018 MVEBs for

[[Page 32248]]

the area. The adequacy comment period for the 2009 and 2018 MVEBs began 
on March 6, 2007, with EPA's posting of the availability of these 
submittals on EPA's Adequacy Web site (https://www.epa.gov/otaq/
stateresources/transconf/adequacy.htm). The adequacy comment period for 
these MVEBs ended on April 5, 2007. EPA did not receive any requests 
for these submittals or adverse comments on these submittals during the 
adequacy comment period. Therefore, we find adequate and are proposing 
to approve the State's 2009 and 2018 MVEBs for transportation 
conformity purposes.

III. What Is the Background for These Actions?

    On December 22, 2006, Ohio requested that EPA redesignate the 
Toledo area to attainment for the 8-hour ozone standard. The request 
was supplemented on March 9, 2007. The redesignation request included 
three years of complete, quality-assured data for the periods of 2004 
through 2006, indicating that the 8-hour NAAQS for ozone has been 
attained for the Toledo 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).

A. General Background Information

    EPA has determined that ground-level ozone is detrimental to human 
health. On July 18, 1997, EPA promulgated an 8-hour ozone NAAQS of 0.08 
parts per million parts of air (0.08 ppm) (80 parts per billion (ppb)) 
(62 FR 38856). This 8-hour ozone standard replaced a prior 1-hour ozone 
NAAQS, which had been promulgated on February 8, 1979 (44 FR 8202), and 
which was revoked on June 15, 2005 (69 FR 23858).
    Ground-level ozone is not emitted directly by sources. Rather, 
emitted NOX and VOC react in the presence of sunlight to 
form ground-level ozone along with other secondary compounds. 
NOX and VOC are referred to as ``ozone precursors.'' Control 
of ground-level ozone concentrations is achieved through controlling 
VOC and NOX emissions.
    The CAA required EPA to designate as nonattainment any area that 
violated the 8-hour ozone NAAQS. The Federal Register notice 
promulgating these designations and classifications was published on 
April 30, 2004 (69 FR 23857).
    The CAA contains two sets of provisions--subpart 1 and subpart 2--
that address planning and emission control requirements for 
nonattainment areas. Both are found in title I, part D of the CAA. 
Subpart 1 contains general, less prescriptive requirements for all 
nonattainment areas for any pollutant governed by a NAAQS. Subpart 2 
contains more specific requirements for certain ozone nonattainment 
areas, and applies to ozone nonattainment areas classified under 
section 181 of the CAA.
    In the April 30, 2004, designation rulemaking, EPA divided 8-hour 
ozone nonattainment areas into the categories of subpart 1 
nonattainment (``basic'' nonattainment) and subpart 2 nonattainment 
(``classified'' nonattainment). EPA based this division on the area's 
8-hour ozone design values (i.e., on the three-year averages of the 
annual fourth-highest daily maximum 8-hour ozone concentrations at the 
worst-case monitoring sites in the areas) and on their 1-hour ozone 
design values (i.e., on the fourth-highest daily maximum 1-hour ozone 
concentrations over the three-year period at the worst-case monitoring 
sites in the areas). EPA classified 8-hour ozone nonattainment areas 
with 1-hour ozone design values equaling or exceeding 121 ppb as 
subpart 2, classified nonattainment areas. EPA classified all other 8-
hour nonattainment areas as subpart 1, basic nonattainment areas. The 
basis for area classification was explained in a separate April 30, 
2004, final rule (the Phase 1 implementation rule) (69 FR 23951).
    Emission control requirements for classified nonattainment areas 
are linked to area classifications. Areas with more serious ozone 
pollution problems are subject to more prescribed requirements and 
later attainment dates. The prescribed emission control requirements 
are designed to bring areas into attainment by their specified 
attainment dates.
    In the April 30, 2004, ozone designation/classification rulemaking, 
EPA designated the Toledo area as a subpart 1 basic nonattainment area 
for the 8-hour ozone NAAQS. EPA based the designation on ozone data 
collected during the 2001-2003 period.
    On December 22, 2006, the State of Ohio requested redesignation of 
Toledo area to attainment of the 8-hour ozone NAAQS based on ozone data 
collected in this area counties from 2004-2006.

B. What Is the Impact of the December 22, 2006, United States Court of 
Appeals Decision Regarding EPA's Phase 1 Implementation Rule?

1. Summary of Court Decision
    On December 22, 2006, the U.S. Court of Appeals for the District of 
Columbia Circuit vacated EPA's Phase 1 Implementation Rule for the 8-
hour Ozone Standard. (69 FR 23951, April 30, 2004). South Coast Air 
Quality Management Dist. v. EPA, 472 F.3d 882 (D.C.Cir. 2006). The 
Court held that certain provisions of EPA's Phase 1 Rule were 
inconsistent with the requirements of the CAA. The Court rejected EPA's 
reasons for implementing the 8-hour standard in nonattainment areas 
under Subpart 1 in lieu of subpart 2 of Title I, part D of the Act. The 
Court also held that EPA 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 Act, 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 conformity 
requirements for certain types of Federal actions. The Court upheld 
EPA's authority to revoke the 1-hour standard provided there were 
adequate anti-backsliding provisions.
    This section sets forth EPA's views on the potential effect of the 
Court's ruling on this redesignation action. For the reasons set forth 
below, EPA does not believe that the Court's ruling alters any 
requirements relevant to this redesignation action so as to preclude 
redesignation, and does not prevent EPA from finalizing this 
redesignation. EPA believes that the Court's decision, as it currently 
stands, or as it may be modified based upon any petition for rehearing 
that has been filed, imposes no impediment to moving forward with 
redesignation of this area to attainment, because in either 
circumstance redesignation is appropriate under the relevant 
redesignation provisions of the Act 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

[[Page 32249]]

matter to the Agency. Consequently, it is possible that this area 
could, during a remand to EPA, be reclassified under Subpart 2. 
Although any future decision by EPA to classify this area under Subpart 
2 might trigger additional future requirements for 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 State submissions in accordance with the requirements due at 
the time the request is submitted; and, (2) consideration of the 
inequity of applying retroactively any future requirements.
    First, at the time the redesignation request was submitted, the 
Toledo area was classified under Subpart 1 and was obligated to meet 
Subpart 1 requirements. Under EPA's longstanding interpretation of 
section 107(d)(3)(E) of the CAA, to qualify for redesignation, states 
requesting redesignation to attainment must meet only the relevant SIP 
requirements that came due prior to the submittal of a complete 
redesignation request. September 4, 1992, Calcagni memorandum 
(``Procedures for Processing Requests to Redesignate Areas to 
Attainment,'' Memorandum from John Calcagni, Director, Air Quality 
Management Division) See also 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 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 D.C. Circuit has recognized the inequity in such 
retroactive rulemaking, See Sierra Club v. Whitman, 285 F. 3d 63 (D.C. 
Cir. 2002), in which the D.C. 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 at the time it submitted its redesignation request.
3. Requirements Under the 1-Hour Standard
    With respect to the requirements under the 1-hour standard, the 
Toledo area was an attainment area subject to a CAA section 175A 
maintenance plan under the 1-hour standard. The Court's ruling does not 
impact redesignation requests for these types of areas.
    First, there are no conformity requirements that are relevant for 
redesignation requests for any standard, including the requirement to 
submit a transportation conformity SIP. Under longstanding EPA policy, 
EPA believes that it is reasonable to interpret the conformity SIP 
requirement as not applying for purposes of evaluating a redesignation 
request under section 107(d) because State conformity rules are still 
required after redesignation and Federal conformity rules apply where 
State rules have not been approved. 40 CFR 51.390. See Wall v. EPA, 265 
F.3d 426 (6th Cir. 2001), upholding this interpretation. See also 60 FR 
62748 (Dec. 7, 1995) (Tampa, FL redesignation). Federal transportation 
conformity regulations apply in all States prior to approval of 
transportation conformity SIPs. The Toledo, Ohio 1-hour ozone area was 
redesignated to attainment without approved State transportation 
conformity regulations because the Federal regulations were in effect 
in Ohio. When challenged, these 1-hour ozone redesignations, which were 
approved without State regulations, were upheld by the courts. See Wall 
v. EPA, 265 F.3d 426 (6th Cir. 2001). See also 60 FR 62748 (December 7, 
1995) (Tampa, Florida). Although Ohio does not have approved State 
transportation conformity regulations, it has developed memoranda of 
understanding, signed by all parties involved in conformity, to address 
conformity consultation procedures. The Federal transportation 
conformity regulations, which apply in Ohio, require the approved 1-
hour ozone budgets to be used for transportation conformity purposes 
prior to 8-hour ozone budgets being approved.
    Second, with respect to the three other anti-backsliding provisions 
for the 1-hour standard that the Court found were not properly 
retained, the Toledo 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 should not alter requirements 
that would preclude EPA from finalizing the redesignation of this area.

IV. What Are the Criteria for Redesignation?

    Section 107(d)(3)(E) of the CAA allows for redesignation from 
nonattainment to attainment 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 several guidance documents. A listing of 
pertinent documents is provided in other redesignation actions 
including a September 9, 2005 notice; 70 FR 53606.

V. Why Is EPA Proposing To Take These Actions?

    On December 22, 2006, Ohio requested redesignation of the Toledo 
area to attainment for the 8-hour ozone standard. EPA believes that the 
area has attained the standard and has met the requirements for 
redesignation set forth in section 107(d)(3)(E) of the CAA.

VI. What Is the Effect of These Actions?

    Approval of the redesignation request would change the official 
designation of the Toledo area for the 8-hour ozone NAAQS found at 40 
CFR part 81. It would also incorporate into the Ohio SIP a plan for 
maintaining the 8-hour ozone NAAQS through 2018. The maintenance plans 
include contingency measures to remedy future violations of the 8-hour 
NAAQS. The maintenance

[[Page 32250]]

plan also established MVEBs for the years 2009 and 2018.

        Motor Vehicle Emissions Budgets for the Toledo, Ohio Area
------------------------------------------------------------------------
                                                 VOC (tons/   NOX (tons/
                     Year                           day)         day)
------------------------------------------------------------------------
2009..........................................        18.99        33.75
2018..........................................        11.20        14.11
------------------------------------------------------------------------

    These proposed actions pertain to the designation of the Toledo 
area for the 8-hour ozone NAAQS and to the emission controls in the 
area related to the attainment and maintenance of the 8-hour ozone 
NAAQS. If you own or operate a VOC or NOX emissions source 
in this area or live in this area, this proposed rule may impact or 
apply to you. It may also impact you if you are involved in 
transportation planning or implementation of emission controls in this 
area. Finally, it may also impact you if you breathe the air in the 
Toledo area or the air which has passed through this Toledo area, or if 
you are concerned with clean air, human health or the environment.

VII. What Is EPA's Analysis of the Request?

A. Attainment Determination and Redesignation

    EPA is proposing to make a determination that the Toledo area has 
attained the 8-hour ozone standard and that the Toledo area has met all 
other applicable section 107(d)(3)(E) redesignation criteria. The basis 
for EPA's determinations is as follows:
1. The Area Has Attained the 8-Hour Ozone NAAQS, (Section 
107(d)(3)(E)(i))
    EPA is proposing to make the determination that the Toledo area has 
attained the 8-hour ozone NAAQS. For ozone, an area may be considered 
to be attaining the 8-hour ozone NAAQS if there are no violations, 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. For each monitor in the area, EPA computes 
the average of the fourth-highest daily maximum 8-hour average ozone 
concentrations from each of the three most recent years. The area is 
attaining the standard if all monitors have average concentrations at 
or below 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 Aerometric 
Information Retrieval System (AIRS). The monitors generally should have 
remained at the same location for the duration of the monitoring period 
required for demonstrating attainment.
    Ohio submitted 2004-2006 ozone monitoring data for the Toledo area. 
The Ohio EPA quality assured the ambient monitoring data in accordance 
with 40 CFR 58.10, and recorded it in the AIRS database, thus making 
the data publicly available. 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. A summary 
of the monitoring data is presented in Table 1 below.

Table 1.--Annual 4th High Daily Maximum 8-Hour Ozone Concentration and 3-Year Averages of 4th High Daily Maximum
                                           8-Hour Ozone Concentrations
----------------------------------------------------------------------------------------------------------------
                                                                                                      2004-2006
             Site ID                        County              2003 4th     2005 4th     2006 4th     average
                                                              high  (ppm)  high  (ppm)  high  (ppm)     (ppm)
----------------------------------------------------------------------------------------------------------------
39-095-0024.....................  Lucas.....................           67           80           75           74
39-095-0027.....................  Lucas.....................           74           84           69           75
39-095-0034.....................  Lucas.....................           78           87           74           79
39-095-0081.....................  Lucas.....................           78           87           74           79
39-73-0003......................  Wood......................           76           84           73           77
----------------------------------------------------------------------------------------------------------------

    In addition, as discussed below with respect to the maintenance 
plans, Ohio has committed to continue operating an EPA-approved 
monitoring network in accordance with 40 CFR part 58. In summary, EPA 
finds that the data submitted by Ohio provide an adequate demonstration 
that the Toledo 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 has met all currently applicable SIP 
requirements for purposes of redesignation for the Toledo area under 
Section 110 of the CAA (general SIP requirements). We have also 
determined that the Ohio SIP meets 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, we have 
determined that the SIP is fully approved with respect to all 
applicable requirements for purposes of redesignation, in accordance 
with section 107(d)(3)(E)(ii). In making these determinations, we have 
ascertained what SIP requirements are applicable to the area for 
purposes of redesignation, and have determined that the portions of the 
SIP meeting these requirements are fully approved under section 110(k) 
of the CAA. As discussed more fully below, SIPs must be fully approved 
only with respect to currently applicable requirements of the CAA.
a. Toledo, Ohio Has Met All Applicable Requirements Under Section 110 
and Part D of the CAA
    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, 12465-66 (March 7, 1995) (redesignation of 
Detroit-Ann Arbor, Michigan to attainment of the 1-hour ozone NAAQS). 
Applicable requirements of the CAA that come due subsequent to the 
State's submittal of a complete 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

[[Page 32251]]

v. EPA, 375 F.3d 537 (7th Cir. 2004). See also 68 FR 25424, 25427 (May 
12, 2003) (redesignation of the St. Louis/East St. Louis area to 
attainment of the 1-hour ozone NAAQS).
    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, New Source Review (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 (63 FR 57356), Clean Air 
Interstate Rule (CAIR) (70 FR 25162)). 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 classifications are the relevant 
measures to evaluate in reviewing a redesignation request. When the 
transport SIP submittal requirements are applicable to a State, they 
will continue to apply to the State regardless of the attainment 
designation of any one particular area in the State. Therefore, 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 ozone redesignation (65 FR 
37890, June 19, 2000), and in the Pittsburgh ozone redesignation (66 FR 
50399, October 19, 2001).
    As discussed above, we believe that section 110 elements which are 
not linked to the area's nonattainment status are not applicable for 
purposes of redesignation. Because there are no section 110 
requirements linked to the part D requirements for 8-hour ozone 
nonattainment areas that have become due, as explained below, there are 
no Part D requirements applicable for purposes of redesignation under 
the 8-hour standard.
    Part D Requirements. EPA has determined that the Ohio SIP meets 
applicable SIP requirements under part D of the CAA, since no 
requirements applicable for purposes of redesignation became due for 
the 8-hour ozone standard prior to Ohio's submission of the 
redesignation request for The Toledo area. Under part D, an area's 
classification determines the requirements to which it will be subject. 
Subpart 1 of part D, found in sections 172-176 of the CAA, sets forth 
the basic nonattainment requirements applicable to all nonattainment 
areas. Section 182 of the CAA, found in subpart 2 of part D, 
establishes additional specific requirements depending on the area's 
nonattainment classification. Toledo, Ohio, was classified as a subpart 
1 nonattainment area, and, therefore, subpart 2 requirements do not 
apply.
    Part D, Subpart 1 applicable SIP requirements. For purposes of 
evaluating these redesignation requests, the applicable part D, subpart 
1 SIP requirements for the Toledo area are contained in sections 
172(c)(1)-(9).
    No 8-hour ozone planning requirements applicable for purposes of 
redesignation under part D became due prior to submission of the 
redesignation request, and, therefore, none are applicable to the area 
for purposes of redesignation. Since Ohio has submitted a complete 
ozone redesignation request for the Toledo area prior to the deadline 
for any submissions required for purposes of redesignation, we have 
determined that these requirements do not apply to the Toledo area for 
purposes of redesignation.
    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 approved Ohio's general and transportation conformity SIPs on 
March 11, 1996 (61 FR 9646) and May 30, 2000 (65 FR 34395), 
respectively. In summary, the Toledo area has satisfied all applicable 
requirements under section 110 and part D of the CAA.
b. Toledo Has a Fully Approved Applicable SIP Under Section 110(k) of 
the CAA.
    EPA has fully approved the Ohio SIP for the Toledo area under 
section 110(k) of the CAA for all requirements applicable for purposes 
of redesignation. In approving a redesignation request, EPA may rely on 
prior SIP approvals plus any additional measures it may approve in 
conjunction with a redesignation action (See the September 4, 1992 John 
Calcagni memorandum, page 3, Southwestern Pennsylvania Growth Alliance 
v. Browner, 144 F.3d 984, 989-990 (6th Cir. 1998), Wall v. EPA, 265 
F.3d 426 (6th Cir. 2001)). Since the passage of the CAA of 1970, Ohio 
has adopted and submitted, and EPA has fully approved, provisions 
addressing the various required SIP elements applicable to the Toledo 
area under the 1-hour ozone standard. No Toledo area SIP provisions

[[Page 32252]]

are currently disapproved, conditionally approved, or partially 
approved.
3. The Improvement in Air Quality Is Due to Permanent and Enforceable 
Reductions in Emissions (Section 107(d)(3)(E)(iii))
    EPA finds that Ohio has demonstrated that the observed air quality 
improvement in the Toledo area is due to permanent and enforceable 
reductions in emissions resulting from implementation of the SIP, 
Federal measures, and other State-adopted measures.
    In making this demonstration, the State has calculated the change 
in emissions between 2002 and 2004, one of the years on which the 
Toledo 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 Ohio has 
implemented.
a. Permanent and Enforceable Controls Implemented.
    The following is a discussion of permanent and enforceable measures 
that have been implemented in the area:
    NOX rules. In compliance with EPA's NOX SIP call, Ohio 
developed rules to control NOX emissions from Electric 
Generating Units (EGUs), major non-EGU industrial boilers, and major 
cement kilns. These rules required sources to begin reducing 
NOX emissions in 2004. However, statewide NOX 
emissions actually had begun to decline before 2004, as sources phased 
in emission controls needed to comply with the State's NOX 
emission control regulations. From 2004 on, NOX emissions 
from EGUs in the Eastern United States have been capped at a level well 
below pre-2002 levels, such that EGU emissions in the Toledo area, and 
elsewhere in Ohio, can be expected to remain well below 2002 levels. 
Ohio expects that NOX emissions will further decline as the 
State meets the requirements of EPA's Phase II NOX SIP call 
(69 FR 21604 (April 21, 2004)).
    Federal Emission Control Measures. Reductions in VOC and 
NOX emissions have occurred statewide as a result of Federal 
emission control measures, with additional emission reductions expected 
to occur in the future as the State implements additional emission 
controls. Federal emission control measures include: Tier 2 emission 
standards for vehicles, gasoline sulfur limits, low sulfur diesel fuel 
standards, and heavy-duty diesel engine standards. In addition, in 
2004, EPA issued the Clean Air Non-road Diesel Rule (69 FR 38958 (July 
29, 2004)). EPA expects this rule to reduce off-road diesel emissions 
through 2010, with emission reductions starting in 2008.
b. Emission Reductions
    Ohio is using 2002 for the nonattainment inventory and included 
area, mobile and point source emissions. Area sources were taken from 
the Ohio 2002 periodic inventory submitted to EPA. These projections 
were made from the United States Department of Commerce Bureau of 
Economic Analysis growth factors, with some updated local information. 
Mobile source emissions were calculated from MOBILE6.2 produced 
emission factors. Non-road emissions were generated using the EPA's 
National Mobile Inventory Model (NMIM) 2002 application. Point source 
information was compiled from Ohio's 2002 annual emission inventory 
database and the 2002 EPA Clean Air Markets Acid Rain database.
    Based on the inventories described above, Ohio's submittal 
documents changes in VOC and NOX emissions from 2002 to 
2004. Summaries of emissions data are shown in Tables 2 through 4.

       Table 2.--The Toledo, Ohio Area: Total VOC and NOX Emissions for Nonattainment Year 2002 (Tons/Day)
----------------------------------------------------------------------------------------------------------------
                                                                                        Total
                 Sector                     Lucas       Wood   ------------------------------------------------------
                                            county     county      VOC        NOX        VOC        NOX     VOC
---------------------------------------------------------------------------------------------------------- ----------
Point...................................       7.65      38.88       0.95       3.23       8.60      42.11
Area....................................      22.71       0.97       7.91       0.64      30.62       1.61
Non-Road Mobile.........................       8.49      16.80       2.86      10.06      11.35      26.86
On-Road Mobile..........................      19.77      31.51       9.93      18.73      29.70      50.24
                                         -----------------------------------------------------------------------
    Toledo Area Total...................  .........  .........  .........  .........      80.27     120.82
----------------------------------------------------------------------------------------------------------------


         Table 3.--The Toledo, Ohio Area Total VOC and NOX Emissions for Attainment Year 2004 (Tons/Day)
----------------------------------------------------------------------------------------------------------------
                                                       Lucas                 Wood                  Total
                                              ------------------------------------------------------------------
                                                  VOC        NOX        VOC        NOX        VOC         NOX
----------------------------------------------------------------------------------------------------------------
Point........................................       7.44      35.54       0.91       3.23       8.35       38.77
Area.........................................      22.71       1.03       7.43       0.67      30.55        1.7
Nonroad......................................       7.66      15.68       2.65       9.14      10.31       24.82
Onroad.......................................      16.57      27.05       8.41      16.26      24.98       43.31
                                              ------------------------------------------------------------------
    Total....................................  .........  .........  .........  .........      74.19      108.6
----------------------------------------------------------------------------------------------------------------


          Table 4.--The Toledo Area, Ohio: Comparison of 2002 and 2004 VOC and NOX Emissions (Tons/Day)
----------------------------------------------------------------------------------------------------------------
                                     VOC                                                      NOX
----------------------------------------------------------------------------------------------------------------
                                                                  Net change                          Net change
                 Sector                      2002        2004    (2002-2004)     2002       2004     (2002-2004)
----------------------------------------------------------------------------------------------------------------
Point...................................        8.6        8.35       -0.25       42.11       38.77       -3.34
Area....................................       30.62      30.55       -0.07        1.61        1.7         0.09

[[Page 32253]]

 
Nonroad.................................       11.35      10.31       -1.04       26.86       24.82       -2.04
Onroad..................................       29.7       24.98       -4.72       50.24       43.31       -6.93
                                         -----------------------------------------------------------------------
    Total...............................       80.27      74.19       -6.08      120.82      108.6       -12.22
----------------------------------------------------------------------------------------------------------------

    Table 4 shows that the area reduced VOC emissions by 6.08 tons/day, 
and NOX emissions by 12.22 tons/day, between 2002 and 2004. 
Based on the information summarized above, Ohio has adequately 
demonstrated that the improvement in air quality is due to permanent 
and enforceable emissions reductions.
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 its request to redesignate the Toledo area to 
attainment status, Ohio submitted SIP revisions to provide for the 
maintenance of the 8-hour ozone NAAQS in this area through 2018.
a. What is required in a maintenance plan?
    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 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
    Ohio developed a baseline emissions inventory for 2004, one of the 
years used to demonstrate monitored attainment of the 8-hour NAAQS. The 
attainment level of emissions is summarized in Table 5, below.

        Table 5.--The Toledo, Ohio Area, Total VOC and NOX Emissions for Attainment Year 2004 (Tons/Day)
----------------------------------------------------------------------------------------------------------------
                                                        Lucas                 Wood                  Total
                                               -----------------------------------------------------------------
                                                   VOC        NOX        VOC        NOX        VOC        NOX
----------------------------------------------------------------------------------------------------------------
Point.........................................       7.44      35.54       0.91       3.23       8.35      38.77
Area..........................................      22.78       1.03       7.77       0.67      30.55       1.70
Nonroad.......................................       7.66      15.68       2.65       9.14      10.31      24.82
Onroad........................................      16.57      27.05       8.41      16.26      24.98      43.31
                                               -----------------------------------------------------------------
    Total.....................................  .........  .........  .........  .........      74.19     108.60
----------------------------------------------------------------------------------------------------------------

c. Demonstration of Maintenance
    Ohio submitted revisions to the 8-hour ozone SIP to include 11-year 
maintenance plans for the Toledo area, in compliance with section 175A 
of the CAA. This demonstration shows maintenance of the 8-hour ozone 
standard by assuring that current and future emissions of VOC and 
NOX 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 is using projected inventories for the years 2009 and 2018. 
These emission estimates are presented in Table 6.

[[Page 32254]]



                                Table 6.--The Toledo, Ohio Area: Comparison of 2004-2018 VOC and NOX Emissions (Tons/Day)
--------------------------------------------------------------------------------------------------------------------------------------------------------
                                                                                    VOC                                          NOX
                                                              ------------------------------------------------------------------------------------------
                            Sector                                                                   Net                                          Net
                                                                  2004       2009        2018       change      2004        2009       2018      change
                                                                                                  2004-2018                                    2004-2018
--------------------------------------------------------------------------------------------------------------------------------------------------------
Point........................................................       8.35        7.81        8.64       0.29       38.77      30.35      16.03     -22.74
Area.........................................................      30.55       30.4        32.6        2.05        1.7        1.91       1.97       0.27
Nonroad......................................................      10.31        7.78        6.55      -3.76       24.82      19.76      14.91      -9.91
Onroad.......................................................      24.98       16.51        9.74     -15.24       43.31      29.35      12.27     -31.04
                                                              ------------------------------------------------------------------------------------------
    Total....................................................      74.19       62.50       57.53     -16.66      108.6       81.37      45.18     -63.42
--------------------------------------------------------------------------------------------------------------------------------------------------------

    The emission projections show that Ohio does not expect emissions 
in the area to exceed the level of the 2004 attainment year inventory 
during the maintenance period. In the area, Ohio projects that VOC and 
NOX emissions will decrease by 16.66 tons/day and 63.42 
tons/day, respectively.
    As part of its maintenance plan, the State 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. Ohio used 2004 as the 
attainment level of emissions for the area. In the maintenance plan, 
Ohio projected emission levels for 2018. The emissions from point, 
area, non-road, and mobile sources in 2004 equaled 74.19 tons/day of 
VOC and 108.6 tons/day of NOX. Ohio projected VOC emissions 
for the year 2018 to be 57.63 tons/day of VOC and 45.18 tons/day of 
NOX. The safety margin is calculated to be the difference 
between these amounts or, in this case, 16.66 tons/day of VOC and 63.42 
tons/day of NOX for 2018. 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. Ohio EPA 
allocated 1.46 tons/day of VOC and 1.84 tons/day of NOX to 
the MVEB. The SIP submission demonstrates that the area will continue 
to maintain the standard because emission will continue to be below the 
attainment level.
d. Monitoring Network
    Ohio currently operates five ozone monitors in The Toledo area. 
Ohio has committed to continue operating and maintaining their approved 
ozone monitor network in accordance with 40 CFR part 58.
e. Verification of Continued Attainment
    Continued attainment of the ozone NAAQS in the area depends, in 
part, on the State's efforts toward tracking indicators of continued 
attainment during the maintenance period. The State's plan for 
verifying continued attainment of the 8-hour standard in the area 
consists of plans to continue ambient ozone monitoring in accordance 
with the requirements of 40 CFR part 58. In addition, Ohio will 
periodically review and revise the VOC and NOX emissions 
inventories for the area, as required by the Consolidated Emissions 
Reporting Rule (40 CFR part 51), to track levels of emissions in the 
future.
f. Contingency Plan
    The contingency plan provisions of the CAA are designed to result 
in prompt correction or prevention of violations of the NAAQS that 
might occur after redesignation of an area to attainment of the NAAQS. 
Section 175A of the CAA requires that a maintenance plan include such 
contingency measures as EPA deems necessary to assure that the State 
will promptly correct a violation of the NAAQS that might occur after 
redesignation. The maintenance plan must identify the contingency 
measures to be considered for possible adoption, a schedule and 
procedure for adoption and implementation of the selected contingency 
measures, and a time limit for action by the State. The State should 
also identify specific indicators to be used to determine when the 
contingency measures need to be adopted and implemented. The 
maintenance plan must include a requirement that the State will 
implement all measures with respect to control of the pollutant(s) that 
were included in the SIP before the redesignation of the area to 
attainment. See section 175A(d) of the CAA.
    As required by section 175A of the CAA, Ohio has adopted a 
contingency plan to address possible future ozone air quality issues. 
The contingency plan has two levels of actions/responses depending on 
whether a violation of the 8-hour ozone standard is only threatened 
(Warning Level Response) or has actually occurred or appears to be very 
imminent (Action Level Response).
    A Warning Level Response will be triggered whenever an annual (1-
year) fourth-high monitored 8-hour ozone concentration of 88 ppb occurs 
within the ozone maintenance area (Toledo area). A Warning Level 
Response will consist of a study to determine whether the ozone value 
indicates a trend toward higher ozone concentrations or whether 
emissions appear to be increasing. The study will evaluate whether the 
trend, if any, is likely to continue and, if so, the control measures 
necessary to reverse the trend, taking into consideration ease and 
timing for implementation, as well as economic and social 
consideration. Implementation of necessary controls in response to a 
Warning Level Response triggering will take place as expeditiously as 
possible, but in no event later than 12 months from the conclusion of 
the most recent ozone season.
    An Action Level Response will be triggered whenever a two-year 
average annual fourth-high monitored 8-hour ozone concentration of 85 
ppb or greater occurs within the maintenance area (Toledo area). A 
violation of the 8-hour ozone standard (three-year average fourth-high 
value of 85 ppb or greater) will also prompt an Action Level Response. 
In the event that an Action Level Response is triggered and is not due 
to an exceptional event, malfunction, or noncompliance with a source 
permit condition or rule requirement, Ohio will determine the 
additional emission control measures needed to assure future attainment 
of the ozone NAAQS. Emission control measures that can be implemented 
in a short time will be selected in order to be in place within 18 
months from the close of the ozone season that prompted the Action 
Level Response. Any new

[[Page 32255]]

emission control measure that is selected for implementation will be 
given a public review. If a new emission control measure is already 
promulgated and scheduled to be implemented at the Federal or State 
level and that emission control measure is determined to be sufficient 
to address the increase in peak ozone concentrations, additional local 
measures may be unnecessary. Ohio will submit to the EPA an analysis to 
assess whether the proposed emission control measures are adequate to 
reverse the increase in peak ozone concentrations and to maintain the 
8-hour ozone standard in the area. The selection of emission control 
measures will be based on cost-effectiveness, emission reduction 
potential, economic and social considerations, or other factors that 
Ohio deems to be appropriate. Selected emission control measures will 
be subject to public review and the State will seek public input prior 
to selecting new emission control measures.
    The State's ozone redesignation request lists the following 
possible emission control measures as contingency measures in the ozone 
maintenance portion of the State's submittal:
    i. Lower Reid vapor pressure gasoline requirements;
    ii. Tighten RACT on existing source covered by USEPA Control 
Techniques Guidelines issued in response to the 1990 CAA;
    iii. Apply 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. Transportation measures will be selected from the following, 
based upon the factors listed above after consultation with affected 
local governments:
    a. Trip reduction programs, including, but not limited to, 
employer-based transportation management plans, area wide rideshare 
programs, work schedule changes, and telecommuting;
    b. Traffic flow and transit improvements; and
    c. Other new or innovative transportation measures not yet in 
widespread use that affects State and local governments deemed 
appropriate.
    v. Alternative fuel and diesel retrofit programs for fleet vehicle 
operations.
    vi. Controls on consumer products consistent with those adopted 
elsewhere in the United States.
    vii. Require VOC and NOX emissions offsets for new and 
modified major sources.
    viii. Require VOC or NOX emission offsets for new or 
modified minor sources.
    ix. Increase the ratio of emission offsets required for new 
sources.
    x. Require VOC or NOX controls on new minor sources 
(less than 100 tons).
    g. Provisions for Future Updates of the Ozone Maintenance Plan.
    As required by section 175A(b) of the CAA, Ohio commits to submit 
to the EPA updated ozone maintenance plans eight years after 
redesignation to cover an additional 10-year period beyond the initial 
10-year maintenance period. Ohio has committed to retain the control 
measures for VOC and NOX emissions that were contained in 
the SIP before redesignation of the area to attainment, as required by 
section 175(A) of the CAA.
    EPA proposes that the maintenance plan adequately addresses the 
five basic components of a maintenance plan: Attainment inventory, 
maintenance demonstration, monitoring network, verification of 
continued attainment, and a contingency plan.

B. Adequacy of Ohio's Motor Vehicle Emissions Budgets (MVEBs)

1. How Are MVEBs Developed and What Are the MVEBs for the 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 redesignation to attainment 
of the ozone standard. These emission control strategy SIP revisions 
(e.g., reasonable further progress SIP 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). The preamble also describes how to establish the MVEB in the 
SIP and how to revise the MVEB if needed.
    Under section 176(c) of the CAA, new transportation projects, such 
as the construction of new highways, must ``conform'' to (i.e., be 
consistent with) the part of the SIP that addresses emissions from cars 
and trucks. 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 find that the MVEBs are ``adequate'' for use in 
determining transportation conformity. Once EPA affirmatively finds the 
submitted MVEBs to be adequate for transportation conformity purposes, 
the MVEBs are used by State and Federal agencies in determining whether 
proposed transportation projects conform to the 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 was initially 
outlined in EPA's May 14, 1999, guidance, ``Conformity Guidance on 
Implementation of March 2, 1999, Conformity Court Decision.'' This 
guidance was codified in the Transportation Conformity Rule Amendments 
for the ``New 8-Hour Ozone and PM2.5 National Ambient Air 
Quality Standards and Miscellaneous Revisions for Existing Areas; 
Transportation Conformity Rule