Source: https://www.federalregister.gov/documents/2013/08/07/2013-18951/approval-and-promulgation-of-air-quality-implementation-plans-ohio-redesignation-of-the
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Federal Register :: Approval and Promulgation of Air Quality Implementation Plans; Ohio; Redesignation of the Canton-Massillon Area to Attainment of the 1997 Annual and 2006 24-Hour Standards for Fine Particulate Matter
Approval and Promulgation of Air Quality Implementation Plans; Ohio; Redesignation of the Canton-Massillon Area to Attainment of the 1997 Annual and 2006 24-Hour Standards for Fine Particulate Matter
A Proposed Rule by the Environmental Protection Agency on 08/07/2013
78 FR 48087
48087-48103 (17 pages)
FRL-9844-2
2013-18951
EPA Air Quality Modeling Final Rule, Technical Support...
Canton-Massillon, Ohio - 1997 PM2.5 Annual and 2006 PM2.5...
a. Ohio Has Met All Applicable Requirements for Purposes of Redesignation of the Canton-Massillon Area Under Section 110 and Part D of the CAA
(1). Subpart 1
(a). Section 172 Requirements.
(2). Effect of the January 4, 2013, D.C. Circuit Decision Regarding PM2.5 Implementation under Subpart 4
(b). Proposal on This Issue
(i). Applicable Requirements for Purposes of Evaluating the Redesignation Request
(ii). Subpart 4 Requirements and Ohio Redesignation Request
(iii). Subpart 4 and Control of PM2.5 Precursors
b. The Canton-Massillon Area Has a Fully Approved Applicable SIP Under Section 110(k) of the CAA
5. Adequacy of Ohio's MVEB
a. How are MVEBs developed and what are the MVEBs for the Canton-Massillon area?
https://www.federalregister.gov/d/2013-18951 https://www.federalregister.gov/d/2013-18951
On June 26, 2012, the Ohio Environmental Protection Agency submitted a request for EPA to redesignate the Canton-Massillon area (Stark County), Ohio, nonattainment area to attainment of the 1997 annual and 2006 24-hour standards for fine particulate matter (PM2.5). EPA is proposing to grant Ohio's request. EPA is proposing to determine that the Canton-Massillon area attains the 1997 annual and the 2006 24-hour PM2.5 standard, based on the most recent three years of certified air quality data. EPA is proposing to approve, as revisions to the Ohio state implementation plan (SIP), the state's plan for maintaining the 1997 annual and 2006 24-hour PM2.5 national ambient air quality standard (NAAQS or standard) through 2025 for the area. EPA is proposing to approve the 2005 and 2008 emissions inventories for the Canton-Massillon area as meeting the comprehensive emissions inventory requirement of the Clean Air Act (CAA or Act). Ohio's maintenance plan submission includes a motor vehicle emission budget (MVEB) for the mobile source contribution of PM2.5 and nitrogen oxides (NOX) to the Canton-Massillon area for transportation conformity purposes; EPA is proposing to approve the MVEBs for 2015 and 2025 into the Ohio SIP for transportation conformity purposes.
Submit your comments, identified by Docket ID No. EPA-R05-OAR-2012-0564, by one of the following methods:
4. Mail: Pamela Blakley, Chief, Control Strategies Section (AR-18J), U.S. Environmental Protection Agency, 77 West Jackson Boulevard, Chicago, Illinois 60604.Start Printed Page 48088
Instructions: Direct your comments to Docket ID No. EPA-R05-OAR-2012-0564. 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 email. 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 email comment directly to EPA without going through www.regulations.gov your email 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.
EPA is proposing to take several actions related to redesignation of the Canton-Massillon area to attainment for the 1997 annual and 2006 24-hour PM2.5 NAAQS. EPA is proposing to determine that the area is attaining the NAAQS for PM2.5, based on quality-assured and state certified ambient air monitoring data for 2010-2012, the most recent three years of quality-assured data for the area. EPA is proposing to find that Ohio meets the requirements for redesignation of the Canton-Massillon area to attainment of the 1997 and 2006 24-hour PM2.5 NAAQS under section 107(d)(3)(E) of the CAA.
Second, EPA is proposing to approve Ohio's annual PM2.5 maintenance plan for the Canton-Massillon area as a revision to the Ohio SIP, including the MVEB for PM2.5 and NOX emissions for the mobile source contribution of the Canton-Massillon area.
Finally, EPA is proposing to approve Ohio's emissions inventories as satisfying the requirement in section 172(c)(3) of the CAA for a current, accurate and comprehensive emission inventory. These emission inventories include primary PM2.5, NOX and sulfur dioxide (SO2) inventories included in its June 26, 2012, initial submittal and 2007 emissions for volatile organic compounds (VOCs) and ammonia inventories included in a supplemental submission to EPA on April 29, 2013.
Therefore, EPA is proposing to grant the request from the state of Ohio to change the designation of Stark County (the Canton-Massillon area) from nonattainment to attainment of the 1997 annual and 2006 24-hour PM2.5 NAAQS.
Fine particulate pollution can be emitted directly from a source (primary PM2.5) or formed secondarily through chemical reactions in the atmosphere involving precursor pollutants emitted from a variety of sources. Sulfates are a type of secondary particulate formed from SO2 emissions from power plants Start Printed Page 48089and industrial facilities. Nitrates, another common type of secondary particulate, are formed from combustion emissions of NOX from power plants, mobile sources and other combustion sources.
The first air quality standards for PM2.5 were promulgated on July 18, 1997, at 62 FR 38652. EPA promulgated an annual standard at a level of 15 micrograms per cubic meter (µg/m3) of ambient air, based on a three year average of the annual mean PM2.5 concentrations at each monitoring site. In the same rulemaking, EPA promulgated a 24-hour PM2.5 standard at 65 µg/m3, based on a three year average of the 98th percentile of 24-hour PM2.5 concentrations at each monitoring site.
On January 5, 2005, at 70 FR 944, EPA published air quality area designations for the 1997 annual PM2.5 standard based on air quality data for calendar years 2001-2003. In that rulemaking, EPA designated the Canton-Massillon area as nonattainment for the 1997 annual PM2.5 standard.
On October 17, 2006, at 71 FR 61144, EPA retained the annual PM2.5 standard at 15 µg/m3 (2006 annual PM2.5 standard), but revised the 24-hour standard to 35 µg/m3, based again on the three-year average of the annual 98th percentile of the 24-hour PM2.5 concentrations. In response to legal challenges of the 2006 annual PM2.5 standard, the U.S. Court of Appeals for the District of Columbia Circuit (D.C. Circuit or Court) remanded this standard to EPA for further consideration. See American Farm Bureau Federation and National Pork Producers Council, et al. v. EPA, 559 F.3d 512 (D.C. Cir. 2009). On December 14, 2012, EPA finalized a rule revising the PM2.5 annual standard to 12 µg/m3 based on current scientific evidence regarding the protection of public health. Since the Canton-Massillon area is designated as nonattainment for the 1997 annual and 2006 24-hour PM2.5 standards, today's proposed action addresses redesignation to attainment only for these standards.
In this proposed redesignation, EPA takes into account the January 4, 2013, Court ruling in Natural Resources Defense Council v. EPA, in which the D.C. Circuit remanded to EPA the “Final Clean Air Fine Particle Implementation Rule” (72 FR 20586, April 25, 2007) and the “Implementation of the New Source Review (NSR) Program for Particulate Matter Less than 2.5 Micrometers (PM2.5)” final rule (73 FR 28321, May 16, 2008). 706 F.3d 428 (D.C. Cir. 2013).
Also noted are the decisions of the D.C. Circuit regarding the status of the Cross-State Air Pollution Rule (CSAPR). In the first of the two Court decisions, the D.C. Circuit, on August 21, 2012, issued EME Homer City Generation, L.P. v. EPA, 696 F.3d 7 (D.C. Cir. 2012), which vacated and remanded CSAPR and ordered EPA to continue administering the Clean Air Interstate Rule (CAIR) “pending . . . development of a valid replacement.” EME Homer City at 38. The D.C. Circuit denied all petitions for rehearing on January 24, 2013. On August 21, 2012, the D.C. Circuit issued a decision to vacate CSAPR. In that decision, the Court also ordered EPA to continue administering CAIR “pending the promulgation of a valid replacement.” EME Homer City, 696 F.3d at 38. The D.C. Circuit denied all petitions for rehearing on January 24, 2013. EPA and other parties filed petitions for certiorari to the U.S. Supreme Court. On June 24, 2013, the Supreme Court granted certiorari and agreed to review the D.C. Circuit's decision in EME Homer City. The Supreme Court's grant of certiorari, by itself, does not alter the status of CAIR or CSAPR. At this time, CAIR remains in place. EPA has determined that the status of both CSAPR and CAIR do not affect the ability of the Canton-Massillon area to attain or maintain the PM NAAQS, which is discussed in more detail in section V.3.aii.
EPA is proposing to redesignate the Canton-Massillon area to attainment of the 1997 annual and 2006 24-hour PM2.5 NAAQS and is proposing to approve Ohio's maintenance plan for the area and other related SIP revisions. The bases for these actions follow.
EPA is proposing to determine that the Canton-Massillon area is attaining the 1997 annual and 2006 24-hour PM2.5 NAAQS based upon the most recent three years of complete, certified and quality-assured data. Under EPA's regulations at 40 CFR 50.7, the annual primary and secondary PM2.5 standards are met when the annual arithmetic mean concentration, as determined in accordance with 40 CFR part 50, appendix N, is less than or equal to 15.0 µg/m3 at all monitoring sites in the area. Under EPA regulations in 40 CFR 50.13 and in accordance with 40 CFR part 50, appendix N, the 24-hour primary and secondary PM2.5 standards are met when the 98th percentile 24-hour concentration is less than or equal to 35 µg/m3.
EPA has reviewed the ambient air quality monitoring data in the Canton-Massillon area, consistent with the requirements contained at 40 CFR part 50. EPA's review focused on state certified data recorded in the EPA Air Quality System (AQS) database for the Canton-Massillon PM2.5 nonattainment area for 2009-2011 and for 2010-2012.
The Canton-Massillon area has two monitors located in Stark County, Ohio. Preliminary calculations of design values for 2010-2012, the most recent three full years of data, the two monitors had design values of 13.0 and 11.8 µg/m3 for the 1997 annual standard, and 29 and 26 µg/m3 for the 2006 24-hour standard. The monitors in the Canton-Massillon area recorded complete data for 2010-2012 in accordance with criteria set forth by EPA in 40 CFR part 50, appendix N, where a complete year of air quality data comprises four calendar quarters, with each quarter containing data with at least 75% capture of the scheduled sampling days. Available data are considered to be sufficient for comparison to the NAAQS if three consecutive complete years of data exist.Start Printed Page 48090
Table 1—The 1997 Annual and 2006 24-Hour PM2.5 Design Values for the Canton-Massillon Monitors (in µg/m3)
Stark, OH1 391510017 13.4 30 13.0 29
Stark, OH 391510020 11.9 28 11.8 26
1 Design values for the site 391510017 were incomplete for 2009-2011 due to one quarter in 2009, substitution analysis for 2009-2011 showed attainment for the annual standard. 2010-2012 data was complete for both standards.
EPA's review of these monitoring data supports EPA's determination that the Canton-Massillon area has monitored attainment for the most recent three years of data. Therefore, EPA proposes to determine that the Canton-Massillon area is attaining the 1997 annual and 2006 24-hour PM2.5 standards.
We believe that Ohio has met all currently applicable SIP requirements for purposes of redesignation for the Canton-Massillon area under section 110 of the CAA (general SIP requirements). We are also proposing to find that the Ohio SIP meets all SIP requirements currently applicable for purposes of redesignation under part D of title I of the CAA, in accordance with section 107(d)(3)(E)(v). We are proposing to find that all applicable requirements of the Ohio SIP for purposes of redesignation have been met, in accordance with section 107(d)(3)(E)(ii). As discussed below, in this action EPA is proposing to approve Ohio's 2005 and 2008 emissions inventory, as well as the supplemental submission to the emissions inventory of 2007 VOC and ammonia data made on April 30, 2013, as meeting the section 172(c)(3) comprehensive emissions inventory requirement. In making these proposed determinations, we have ascertained which SIP requirements are applicable for purposes of redesignation, and concluded that SIP measures meeting those requirements are approved or will be approved by the time of final rulemaking.
We have reviewed the Ohio 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 this redesignation. EPA has previously approved provisions of Ohio's SIP addressing section 110 requirements, including provisions addressing particulate matter, at 40 CFR 52.1870, respectively). On December 5, 2007, and September 4, 2009, Ohio made submittals addressing “infrastructure SIP” elements required under CAA section 110(a)(2). EPA proposed approval of the December 5, 2007, submittal on April 28, 2011, at 76 FR 23757, and published final approval on July 14, 2011, at 76 FR 41075. The requirements of section 110(a)(2), however, are statewide requirements that are not linked to the PM2.5 nonattainment status of the Canton-Massillon area. Therefore, EPA believes that these SIP elements are not applicable requirements for purposes of review of the state's PM2.5 redesignation request.
EPA is proposing to determine that, upon approval of the base year Start Printed Page 48091emissions inventories discussed in section V.6. of this rulemaking, the Ohio SIP will meet the SIP requirements for the Canton-Massillon area applicable for purposes of redesignation under part D of the CAA.
For purposes of evaluating this redesignation request, the applicable section 172 SIP requirements for the Canton-Massillon area are contained in section 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).
Section 172(c)(1) requires the plans for all nonattainment areas to provide for the implementation of all Reasonably Achievable Control Measures (RACM) as expeditiously as practicable and to provide for attainment of the primary NAAQS. 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. 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 51.1004(c).)
The Reasonable Further Progress (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 Canton-Massillon area has monitored attainment of the 1997 annual and 2006 24-hour PM2.5 NAAQS. (General Preamble, 57 FR 13564). See also 40 CFR 51.918. In addition, because the Canton-Massillon area has attained the 1997 annual and 2006 24-hour PM2.5 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. Ohio submitted a 2005 (nonattainment year) and 2008 (attainment year) emissions inventories for SO2, NOX, and directly emitted PM2.5 as part of their redesignation request, and Ohio supplemented these inventories with emission inventories for VOC and ammonia on April 29, 2013. As discussed below in section V.6, EPA is approving both the 2005 and 2008 base year inventory as meeting the section 172(c)(3) emissions inventory requirement for the Canton-Massillon area.
Section 172(c)(4) requires the identification and quantification of allowable emissions for major new and modified stationary sources 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 approved Ohio's current NSR program on January 10, 2003 (68 FR 1366). Nonetheless, since PSD requirements will apply after redesignation, the area need not have a fully-approved NSR program for purposes of this redesignation, provided that the area demonstrates maintenance of the NAAQS without part D NSR. A 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 has demonstrated that the Canton-Massillon area will be able to maintain the standard without part D NSR in effect; therefore, the state need not have a fully approved part D NSR program prior to approval of the redesignation request. The state's PSD program will become effective in the Canton-Massillon 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).
As discussed above, on January 4, 2013, in Natural Resources Defense Council v. EPA, the D.C. Circuit Start Printed Page 48092remanded to EPA the “Final Clean Air Fine Particle Implementation Rule” (72 FR 20586, April 25, 2007) and the “Implementation of the New Source Review (NSR) Program for Particulate Matter Less than 2.5 Micrometers (PM2.5)” final rule (73 FR 28321, May 16, 2008) (collectively, “1997 PM2.5 Implementation Rule”). 706 F.3d 428 (D.C. Cir. 2013). The Court found that EPA erred in implementing the 1997 PM2.5 NAAQS pursuant to the general implementation provisions of subpart 1 of part D of title I of the CAA, rather than the particulate-matter-specific provisions of subpart 4 of part D of title I. Although the Court's ruling did not directly address the 2006 PM2.5 standard, EPA is taking into account the Court's position on subpart 4 and the 1997 PM2.5 standard in evaluating redesignations for the 2006 standard.
EPA is proposing to determine that the Court's January 4, 2013, decision does not prevent EPA from redesignating the Canton-Massillon area to attainment. Even in light of the Court's decision, redesignation for this area is appropriate under the CAA and EPA's longstanding interpretations of the CAA's provisions regarding redesignation. EPA first explains its longstanding interpretation that requirements that are imposed, or that become due, after a complete redesignation request is submitted for an area that is attaining the standard are not applicable for purposes of evaluating a redesignation request. Second, EPA then shows that, even if EPA applies the subpart 4 requirements to the Canton-Massillon redesignation request and disregards the provisions of its 1997 PM2.5 implementation rule recently remanded by the Court, the state's request for redesignation of this area still qualifies for approval. EPA's discussion takes into account the effect of the Court's ruling on the area's maintenance plan, which EPA views as approvable when subpart 4 requirements are considered.
With respect to the 1997 PM2.5 Implementation Rule, the Court's January 4, 2013, ruling rejected EPA's reasons for implementing the PM2.5 NAAQS solely in accordance with the provisions of subpart 1, and remanded that matter to EPA, so that it could address implementation of the 1997 PM2.5 NAAQS under subpart 4 of part D of the CAA, in addition to subpart 1. For the purposes of evaluating Ohio's redesignation request for the area, to the extent that implementation under subpart 4 would impose additional requirements for areas designated nonattainment, EPA believes that those requirements are not “applicable” for the purposes of CAA section 107(d)(3)(E), and thus EPA is not required to consider subpart 4 requirements with respect to the Canton-Massillon redesignation. Under its longstanding interpretation of the CAA, EPA has interpreted section 107(d)(3)(E) to mean, as a threshold matter, that the part D provisions which are “applicable” and which must be approved in order for EPA to redesignate an area include only those which came due prior to a state's submittal of a complete redesignation request. See “Procedures for Processing Requests to Redesignate Areas to Attainment,” Memorandum from John Calcagni, Director, Air Quality Management Division, September 4, 1992 (Calcagni memorandum). See also “State Implementation Plan (SIP) Requirements for Areas Submitting Requests for Redesignation to Attainment of the Ozone and Carbon Monoxide (CO) NAAQS on or after November 15, 1992,” Memorandum from Michael Shapiro, Acting Assistant Administrator, Air and Radiation, September 17, 1993 (Shapiro memorandum); Final Redesignation of Detroit-Ann Arbor, (60 FR 12459, 12465-66, March 7, 1995); Final Redesignation of St. Louis, Missouri, (68 FR 25418, 25424-27, May 12, 2003); Sierra Club v. EPA, 375 F.3d 537, 541 (7th Cir. 2004) (upholding EPA's redesignation rulemaking applying this interpretation and expressly rejecting Sierra Club's view that the meaning of “applicable” under the statute is “whatever should have been in the plan at the time of attainment rather than whatever actually was in the plan and already implemented or due at the time of attainment”).[1] In this case, at the time that Ohio submitted its redesignation request, requirements under subpart 4 were not due, [and indeed, were not yet known to apply.]
EPA's view that, for purposes of evaluating the Canton-Massillon redesignation, the subpart 4 requirements were not due at the time the state submitted the redesignation request is in keeping with the EPA's interpretation of subpart 2 requirements for subpart 1 ozone areas redesignated subsequent to the D.C. Circuit's decision in South Coast Air Quality Mgmt. Dist. v. EPA, 472 F.3d 882 (D.C. Cir. 2006). In South Coast, the Court found that EPA was not permitted to implement the 1997 8-hour ozone standard solely under subpart 1, and held that EPA was required under the statute to implement the standard under the ozone-specific requirements of subpart 2 as well. Subsequent to the South Coast decision, in evaluating and acting upon redesignation requests for the 1997 8-hour ozone standard that were submitted to EPA for areas under subpart 1, EPA applied its longstanding interpretation of the CAA that “applicable requirements”, for purposes of evaluating a redesignation, are those that had been due at the time the redesignation request was submitted. See, e.g., Proposed Redesignation of Manitowoc County and Door County Nonattainment Areas (75 FR 22047, 22050, April 27, 2010). In those actions, EPA therefore did not consider subpart 2 requirements to be “applicable” for the purposes of evaluating whether the area should be redesignated under section 107(d)(3)(E).
EPA's interpretation derives from the provisions of CAA Section 107(d)(3). Section 107(d)(3)(E)(v) states that, for an area to be redesignated, a state must meet “all requirements `applicable' to the area under section 110 and part D”. Section 107(d)(3)(E)(ii) provides that the EPA must have fully approved the “applicable” SIP for the area seeking redesignation. These two sections read together support EPA's interpretation of “applicable” as only those requirements that came due prior to submission of a complete redesignation request. First, holding states to an ongoing obligation to adopt new CAA requirements that arose after the state submitted its redesignation request, in order to be redesignated, would make it problematic or impossible for EPA to act on redesignation requests in accordance with the 18-month deadline Congress set for EPA action in section 107(d)(3)(D). If “applicable requirements” were interpreted to be a continuing flow of requirements with no reasonable limitation, states, after submitting a redesignation request, would be forced continuously to make additional SIP submissions that in turn would require EPA to undertake further notice-and-comment rulemaking actions to act on those submissions. This would create a regime of unceasing rulemaking that would delay action on the redesignation request beyond the 18-month timeframe provided by the CAA for this purpose.Start Printed Page 48093
To require the state's fully-completed and pending redesignation request to comply now with requirements of subpart 4 that the Court announced only in January, 2013, would be to give retroactive effect to such requirements when the state had no notice that it was required to meet them. The D.C. Circuit recognized the inequity of this type of retroactive impact in Sierra Club v. Whitman, 285 F.3d 63 (D.C. Cir. 2002),[2] where it upheld the District Court's ruling refusing to make retroactive EPA's determination that the St. Louis area did not meet its attainment deadline. In that case, petitioners urged the Court to make EPA's nonattainment determination effective as of the date that the statute required, rather than the later date on which EPA actually made the determination. The Court rejected this view, stating that applying it “would likely impose large costs on states, which would face fines and suits for not implementing air pollution prevention plans . . . even though they were not on notice at the time.” Id. at 68. Similarly, it would be unreasonable to penalize the state of Ohio by rejecting its redesignation request for an area that is already attaining the 1997 PM2.5 standard and that met all applicable requirements known to be in effect at the time of the request. For EPA now to reject the redesignation request solely because the state did not expressly address subpart 4 requirements of which it had no notice, would inflict the same unfairness condemned by the Court in Sierra Club v. Whitman.
Even if EPA were to take the view that the Court's January 4, 2013, decision requires that, in the context of pending redesignations, subpart 4 requirements were due and in effect at the time the state submitted its redesignation request, EPA proposes to determine that the Canton-Massillon area still qualifies for redesignation to attainment. As explained below, EPA believes that the redesignation request for the Canton-Massillon area, though not expressed in terms of subpart 4 requirements, substantively meets the requirements of that subpart for purposes of redesignating the area to attainment.
With respect to evaluating the relevant substantive requirements of subpart 4 for purposes of redesignating the Canton-Massillon area, EPA notes that subpart 4 incorporates components of subpart 1 of part D, which contains general air quality planning requirements for areas designated as nonattainment. See Section 172(c). Subpart 4 itself contains specific planning and scheduling requirements for PM10[3] nonattainment areas, and under the Court's January 4, 2013, decision in NRDC v. EPA, these same statutory requirements also apply for PM2.5 nonattainment areas. EPA has longstanding general guidance that interprets the 1990 amendments to the CAA, making recommendations to states for meeting the statutory requirements for SIPs for nonattainment areas. See, “State Implementation Plans; General Preamble for the Implementation of Title I of the Clear Air Act Amendments of 1990,” 57 FR 13498 (April 16, 1992) (the “General Preamble”). In the General Preamble, EPA discussed the relationship of subpart 1 and subpart 4 SIP requirements, and pointed out that subpart 1 requirements were to an extent “subsumed by, or integrally related to, the more specific PM-10 requirements.” 57 FR 13538 (April 16, 1992). The subpart 1 requirements include, among other things, provisions for attainment demonstrations, RACM, RFP, emissions inventories, and contingency measures.
For the purposes of this redesignation, in order to identify any additional requirements which would apply under subpart 4, we are considering the Canton-Massillon area to be a “moderate” PM2.5 nonattainment area. Under section 188 of the CAA, all areas designated nonattainment areas under subpart 4 would initially be classified by operation of law as “moderate” nonattainment areas, and would remain moderate nonattainment areas unless and until EPA reclassifies the area as a “serious” nonattainment area. Accordingly, EPA believes that it is appropriate to limit the evaluation of the potential impact of subpart 4 requirements to those that would be applicable to moderate nonattainment areas. Sections 189(a) and (c) of subpart 4 apply to moderate nonattainment areas and include the following: (1) An approved permit program for construction of new and modified major stationary sources (section 189(a)(1)(A)); (2) an attainment demonstration (section 189(a)(1)(B)); (3) provisions for RACM (section 189(a)(1)(C)); and (4) quantitative milestones demonstrating RFP toward attainment by the applicable attainment date (section 189(c)).
The permit requirements of subpart 4, as contained in section 189(a)(1)(A), refer to and apply the subpart 1 permit provisions requirements of sections 172 and 173 to PM10, without adding to them. Consequently, EPA believes that section 189(a)(1)(A) does not itself impose for redesignation purposes any additional requirements for moderate areas beyond those contained in subpart 1.[4] In any event, in the context of redesignation, EPA has long relied on the interpretation that a fully approved nonattainment new source review program is not considered an applicable requirement for redesignation, provided the area can maintain the standard with a PSD program after redesignation. A detailed rationale for this view is Start Printed Page 48094described 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.” See also 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).
With respect to the specific attainment planning requirements under subpart 4,[5] when EPA evaluates a redesignation request under either subpart 1 and/or 4, any area that is attaining the PM2.5 standard is viewed as having satisfied the attainment planning requirements for these subparts. For redesignations, EPA has for many years interpreted attainment-linked requirements as not applicable for areas attaining the standard. In the General Preamble, EPA stated that:
It is evident that even if we were to consider the Court's January 4, 2013, decision in NRDC v. EPA to mean that attainment-related requirements specific to subpart 4 should be imposed retroactively [6] and thus are now past due, those requirements do not apply to an area that is attaining the 1997 and 2006 PM2.5 standard, for the purpose of evaluating a pending request to redesignate the area to attainment. EPA has consistently enunciated this interpretation of applicable requirements under section 107(d)(3)(E) since the General Preamble was published more than twenty years ago. Courts have recognized the scope of EPA's authority to interpret “applicable requirements” in the redesignation context. See Sierra Club v. EPA, 375 F.3d 537 (7th Cir. 2004).
Id. at 21, n.7. For a number of reasons, EPA believes that its proposed redesignation of the Canton-Massillon area is consistent with the Court's decision on this aspect of subpart 4. First, while the Court, citing section 189(e), stated that “for a PM10 area governed by subpart 4, a precursor is `presumptively regulated,'” the Court expressly declined to decide the specific challenge to EPA's 1997 PM2.5 implementation rule provisions regarding ammonia and VOC as precursors. The Court had no occasion to reach whether and how it was substantively necessary to regulate any specific precursor in a particular PM2.5 nonattainment area, and did not address what might be necessary for purposes of acting upon a redesignation request.
However, even if EPA takes the view that the requirements of subpart 4 were deemed applicable at the time the state submitted the redesignation request, and disregards the implementation rule's rebuttable presumptions regarding ammonia and VOC as PM2.5 precursors, (and any similar provisions reflected in the guidance for the 2006 PM2.5 standard) the regulatory consequence would be to consider the need for regulation of all precursors from any sources in the area to demonstrate attainment and to apply the section 189(e) provisions to major stationary sources of precursors. In the case of Canton-Massillon, EPA believes that doing so is consistent with proposing redesignation of the area for the 1997 PM2.5 standard. The Canton-Massillon area has attained both standards without any specific additional controls of VOC and ammonia emissions from any sources in the area.
Precursors in subpart 4 are specifically regulated under the provisions of section 189(e), which requires, with important exceptions, control requirements for major stationary sources of PM10 precursors.[7] Under subpart 1 and EPA's prior implementation rule, all major stationary sources of PM2.5 precursors were subject to regulation, with the exception of ammonia and VOC. Thus we must address here whether additional controls of ammonia and VOC from major stationary sources are required under section 189(e) of subpart 4 in order to redesignate the area for the 1997 PM2.5 standard. As explained below, we do not believe that any additional controls of ammonia and VOC are required in the context of this redesignation.
In the General Preamble, EPA discusses its approach to implementing section 189(e). See 57 FR 13538-13542. With regard to precursor regulation under section 189(e), the General Preamble explicitly stated that control of VOCs under other Act requirements may suffice to relieve a state from the need to adopt precursor controls under section 189(e) (57 FR 13542). EPA in this proposal proposes to determine that the SIP has met the provisions of section 189(e) with respect to ammonia and VOCs as precursors. This proposed determination is based on our findings that (1) the Canton-Massillon area contains no major stationary sources of ammonia, and (2) existing major stationary sources of VOC are adequately controlled under other provisions of the CAA regulating the ozone NAAQS.[8] In the alternative, EPA proposes to determine that, under the express exception provisions of section 189(e), and in the context of the redesignation of the area, which is attaining the 1997 annual PM2.5 standard, at present ammonia and VOC precursors from major stationary sources do not contribute significantly to levels exceeding the 1997 PM2.5 standard in the Canton-Massillon area. See 57 FR 13539-42.
Although, as EPA has emphasized, its consideration here of precursor requirements under subpart 4 is in the context of a redesignation to attainment, EPA's existing interpretation of subpart 4 requirements with respect to precursors in attainment plans for PM10 contemplates that states may develop attainment plans that regulate only those precursors that are necessary for purposes of attainment in the area in question, i.e., states may determine that only certain precursors need be regulated for attainment and control purposes.[9] Courts have upheld this approach to the requirements of subpart 4 for PM10.[10] EPA believes that application of this approach to PM2.5 precursors under subpart 4 is reasonable. Because the Canton-Massillon area has already attained the 1997 and 2006 PM2.5 NAAQS with its current approach to regulation of PM2.5 precursors, EPA believes that it is reasonable to conclude in the context of this redesignation that there is no need to revisit the attainment control strategy with respect to the treatment of precursors. Even if the Court's decision is construed to impose an obligation, in evaluating this redesignation request, to consider additional precursors under subpart 4, it would not affect EPA's approval here of Ohio's request for redesignation of the Canton-Massillon area. In the context of a redesignation, the area has shown that it has attained both standards. Moreover, the state has shown and EPA is proposing to determine that attainment in this area is due to permanent and enforceable emissions reductions on all precursors necessary to provide for continued attainment. It follows logically that no further control of additional precursors is necessary. Accordingly, EPA does not view the January 4, 2013, decision of the Court as precluding redesignation of the Canton-Massillon area to attainment for the 1997 PM2.5 NAAQS at this time.
In sum, even if Ohio were required to address precursors for the Canton-Massillon area under subpart 4 rather than under subpart 1, as interpreted in EPA's remanded PM2.5 implementation rule, EPA would still conclude that the area had met all applicable requirements for purposes of Start Printed Page 48096redesignation in accordance with section 107(d)(3(E)(ii) and (v).
Upon final approval of Ohio's comprehensive emissions inventories, EPA will have fully approved the Ohio SIP for the Canton-Massillon area under section 110(k) of the CAA for all requirements applicable for purposes of redesignation to attainment for the 1997 annual and 2006 24-hour PM2.5 standard. EPA may rely on prior SIP approvals in approving a redesignation request (See page 3 of the 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 has adopted and submitted, and EPA has fully approved, provisions addressing various required SIP elements under particulate matter standards. In this action, as discussed in section V.6 EPA is proposing to approve Ohio's base year emissions inventories for the Canton-Massillon area as meeting the requirement of section 172(c)(3) of the CAA for the 1997 annual and 2006 24-hour PM2.5 standard.
Under section 172, states with nonattainment areas must submit plans providing for timely attainment and meeting a variety of other requirements. On July 16, 2008, Ohio submitted a state-wide attainment demonstration for PM2.5, including the Canton-Massillon area. However, EPA's determination that the area attained the 1997 PM2.5 annual and 2006 24-hour standards (76 FR 56641; 77 FR 28264, respectively) suspended the requirement to submit certain planning SIPs related to attainment, including attainment demonstration requirements, the Reasonably Achievable Control Technology (RACT)-RACM requirement of section 172(c)(1) of the CAA, the RFP and attainment demonstration requirements of sections 172(c)(2) and (6) and 182(b)(1) of the CAA and the requirement for contingency measures of section 172(c)(9) of the CAA).
As a result, the only remaining requirement under section 172 to be considered is the emissions inventory required under section 172(c)(3). As discussed in section V.6, EPA is proposing to approve the inventory that Ohio submitted as part of its maintenance plan as satisfying this requirement.
No SIP provisions applicable for redesignation of the Canton-Massillon area are currently disapproved, conditionally approved or partially approved. If EPA approves Ohio's Canton-Massillon area PM2.5 emissions inventories as proposed, Ohio will have a fully approved SIP for all requirements applicable for purposes of redesignation.
EPA believes that Ohio has demonstrated that the observed air quality improvement in the Canton-Massillon 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, Ohio has calculated the change in emissions between 2005, one of the years used to designate the Canton-Massillon area as nonattainment, and 2008, one of the years the Canton-Massillon 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 the Canton-Massillon area and contributing areas have implemented in recent years.
Tier 2 Emission Standards for Vehicles and Gasoline Sulfur Standards. These emission control requirements result in lower NOX and SO2 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, new vehicles will emit the following percentages less NOX: Passenger cars (light duty vehicles)—77%; light duty trucks, minivans, and sports utility vehicles—86%; and, larger sports utility vehicles, vans, and heavier trucks—69% to 95%. EPA expects fleet wide average emissions to come to decline by similar percentages as new vehicles replace older vehicles. The Tier 2 standards also reduced the sulfur content of gasoline to 30 parts per million (ppm) beginning in January 2006. Most gasoline sold in Ohio prior to January 2006 had a sulfur content of about 500 ppm.
Nonroad Large Spark-Ignition Engine and Recreational Engine Standards. In November 2002 EPA promulgated emission standards for groups of previously unregulated nonroad engines. These engines include large spark-ignition engines such as those used in forklifts and airport ground-service equipment; recreational vehicles using spark-ignition engines such as off-Start Printed Page 48097highway motorcycles, all-terrain vehicles and snowmobiles; and recreational marine diesel engines. Emission standards from large spark-ignition engines were implemented in two tiers, with Tier 1 starting in 2004 and Tier 2 in 2007. Recreational vehicle emission standards are being phased in from 2006 through 2012. Marine Diesel engine standards were phased in from 2006 through 2009. With full implementation of the nonroad spark-ignition engine and recreational engine standards, an 80% reduction in NOX expected by 2020. Some of these emission reductions occurred by the 2008-2010 period used to demonstrate attainment, and additional emission reductions will occur during the maintenance period.
NOX SIP Call. 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 with Phase II beginning in 2007. Emission reductions resulting from regulations developed in response to the NOX SIP Call are permanent and enforceable.
CAIR. The Canton-Massillon area has demonstrated that attainment of the 1997 8-hour ozone NAAQS will be maintained with or without the implementation of CAIR or CSAPR. The Canton-Massillon area has no local electric generating units (EGUs) that would be impacted by CAIR or CSAPR, and in fact, the area's emissions are dominated by mobile sources (Table 2). Mobile sources in the area comprise 85% of the NOX emissions, 38% of the SO2 emission, and 46% of the PM2.5 emissions from the base-year inventory. In addition, regional emissions will not affect the attainment or maintenance of the Canton-Massillon area. Modeling conducted by EPA during the CSAPR rulemaking process demonstrates that the counties in the Canton-Massillon PM2.5 nonattainment area will have concentrations below the 1997 annual and the 2006 24-hour PM2.5 standards in both 2012 and 2014 without taking into account emissions reductions from CAIR or CSAPR. See “Air Quality Modeling Final Rule Technical Support Document”, App. B. This modeling is available in the docket for this proposed redesignation action.
Moreover, in its August 2012 decision, the Court also ordered EPA to continue implementing CAIR. See EME Homer City Generation LP v. EPA, 696 F.3d 7 (D.C. Cir. 2012). In sum, neither the current status of CAIR nor the current status of CSAPR affects any of the criteria for proposed approval of this redesignation request for the Canton-Massillon area.
On December 31, 2012, the Marathon petroleum refinery in Canton was required by a Federal consent decree to shut down an open waste gas flare, resulting in reductions of VOCs, SO2 and direct PM. The Canton refinery is also required under this consent decree to meet specific limits on their capped gas flare that must be incorporated into the permanent construction permit. These emission reductions will add to continued reductions for other sources in the area throughout the maintenance period. In a 2011 state consent decree, Akron Iron & Metal, LLC, in Canton, added baghouse controls resulting in reductions of direct PM in the Canton area.
Ohio developed emissions inventories for NOX, direct PM2.5 and SO2 for 2005, one of the years used to designate the area as nonattainment, and 2008, one of the years the Canton-Massillon area monitored attainment of the standard.
Area source emissions the Canton-Massillon area for 2005 were taken from periodic emissions inventories.[11] These 2005 area source emission estimates were extrapolated to 2008. Source growth factors were supplied by the Lake Michigan Air Directors Consortium (LADCO).
On-road mobile source emissions were calculated using EPA's mobile source emission factor model, MOVES2010a, in conjunction with transportation model results developed by the Stark County Area Transportation Study (SCATS).
All emissions estimates discussed below were documented in the submittal and appendices of Ohio's redesignation request submittal from April 16, 2012, and their April 30, 2013, supplemental submittal. For these data and additional emissions inventory data, the reader is referred to EPA's digital docket for this rule, http://www.regulations.gov, which includes digital copies of Ohio's submittal.
Emissions data in tpy for the Canton-Massillon area are shown in Tables 2 and 3, below.
Table 2—Summary of 2005 Emissions of SO2, NOX, and Directly Emitted PM2.5 for the Canton-Massillon Area by Source Type
Point (EGU) 0.00 0.00 0.00
Non-EGU 553.14 1,129.41 380.10
On-road 191.33 14,004.65 433.47
Nonroad 261.01 2,801.96 231.64
Area 163.72 1,313.88 370.87
MAR 38.35 537.27 14.58
Total Canton-Massillon 1,207.55 19,787.17 1,430.66
Table 3—Comparison of PM2.5, NOX, and SO2 Emissions From a Nonattainment Year (2005) and Emissions for an Attainment Year (2008) for the Canton-Massillon Area
PM2.5 1,430.66 1,257.11 −173.55
NOX 19,787.17 16,227.26 −3,559.91
SO2 1,207.55 906.79 −300.76
Table 3 shows that the Canton-Massillon area shows a decrease in direct PM2.5 emissions by 173.55 tons, the area reduced NOX emissions by 3,559.91tons and SO2 emissions by 300.76 tons between 2005, a nonattainment year, and 2008, an attainment year. Ohio did not attribute attainment to any changes in VOC or ammonia emissions; instead to changes in SO2, NOX, and PM2.5 emissions. EPA agrees that emission reductions from sources of SO2, NOX, and PM2.5 brought the area into attainment, with most emission reductions occurring from Federal mobile source engine standards and fuel standards (Table 2 and 3). Based on the information summarized above, Ohio has adequately demonstrated that the improvement in air quality is due to permanent and enforceable emissions reductions.
In conjunction with Ohio's request to redesignate the Canton-Massillon nonattainment area to attainment status, Ohio has submitted a SIP revision to provide for maintenance of the 1997 annual and 2006 24-hour PM2.5 NAAQS in the area through 2025.
The Calcagni Memorandum provides additional guidance on the content of a maintenance plan. The memorandum states that a maintenance plan should address the following items: the attainment 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.
Ohio developed emissions inventories for NOX, direct PM2.5 and SO2 for 2008, one of the years in the period during which the Canton-Massillon area monitored attainment of the 1997 annual and 2006 24-hour PM2.5 standard, as described previously. The attainment levels of emissions for the area are summarized in Tables 3, above.
Along with the redesignation request, Ohio submitted a revision to its PM2.5 SIP to include a maintenance plan for the Canton-Massillon area, as required by section 175A of the CAA. Section 175A requires a state seeking redesignation to attainment to submit a SIP revision to provide for the maintenance of the NAAQS in the area “for at least 10 years after the redesignation.” EPA has interpreted this as a showing of maintenance “for a period of ten years following redesignation.” Calcagni Memorandum, p.9. Where the emissions inventory method of showing maintenance is used, its purpose is to show that emissions during the maintenance period will not increase over the attainment year inventory. Calcagni Memorandum, pp. 9-10.
Ohio's submission uses emissions inventory projections for the years 2015 and 2025 to demonstrate maintenance for the Canton-Massillon area. The projected emissions were estimated by Ohio, with assistance from LADCO and SCATS using the MOVES2010a model. The 2015 interim year emissions were projected using estimates based on the 2009 and 2018 LADCO modeling inventory, using LADCO's growth factors, for all sectors. The 2025 maintenance year inventory is based on emissions estimates from the 2018 LADCO modeling. Table 4 shows the 2008 attainment base year emission estimates and the 2015 and 2025 emission projections for NOX, direct PM2.5 and SO2 for the Canton-Massillon area that Ohio provided in its April 16, 2012 submission.
Table 4—Comparison of 2008, 2015 and 2025 NOX, Direct PM2.5 and SO2 Emission Totals (tpy) for the Canton-Massillon Area
2008 (baseline) 906.79 16,227.26 1,257.11
2015 812.89 11,001.32 1,088.72
2025 795.30 7,822.67 912.92
Change 2008-2025 −111.49 12% decrease −8,404.59 52% decrease −344.19 27% decrease
Table 4 shows that the Canton-Massillon area reduced NOX emissions by 8,404.59 tpy between 2008 and the maintenance projection to 2025, direct PM2.5 emissions by 344.19 tpy, and reduced SO2 emissions by 111.49 tpy between 2008 and 2025.
EPA in this proposal is also considering the effect of the Court's remand of EPA's implementation rule, in particular the remand of presumptions against consideration of VOC and ammonia as PM2.5 precursors, on requirements for the maintenance plan mandated under sections 175A and 107(d)(3)(E)(iv). To begin with, EPA notes that the area has attained the 1997 and 2006 PM2.5 standard and that the state has shown that attainment of those standards is due to permanent and enforceable emission reductions.
EPA proposes to determine that the state's maintenance plan shows continued maintenance of the standard by tracking the levels of the precursors whose control brought about attainment of the 1997 and 2006 PM2.5 standard in the Canton-Massillon area. EPA therefore believes that the only additional consideration related to the maintenance plan requirements that results from the Court's January 4, 2013, decision is that of assessing the potential role of VOC and ammonia in demonstrating continued maintenance in this area. As explained below, based upon documentation provided by the state and supporting information, EPA believes that the maintenance plan for the Canton-Massillon area need not include any additional emission reductions of VOC or ammonia in order to provide for continued maintenance of the standard.
First, as noted above in EPA's discussion of section 189(e), VOC emission levels in this area have historically been well-controlled under SIP requirements related to ozone and other pollutants. Second, total ammonia emissions throughout the Canton-Massillon area are low, estimated to be less than 1,700 tpy. See Table 5 below. This amount of ammonia emissions appears especially small in comparison to the total amounts of NOX, and VOCs from sources in the area. Both VOC and NOX are also well controlled in the Canton-Massillon area and have decreased due to permanent and enforceable measures such as RACT rules controlling stationary sources previously approved (75 FR 65572; OAC 3745-17; OAC 3745-110). Additional significant reductions resulted from Federal mobile source standards discussed above, accounting for 3,536 tpy of the NOX reductions in the area and 665 tpy of PM2.5 reductions between 2005 and 2008. Future compliance with mobile source standards is also projected to reduce NOX by approximately 700 tpy and PM2.5 by approximately 200 tpy between 2008 and 2025.
Ohio's maintenance plan shows a projected reduction of NOX emissions by 8,404.59 tpy between 2008 and the maintenance projection to 2025, direct PM2.5 emissions of 344.19 tpy, and reduced SO2 emissions of 111.49 tpy between 2008 and 2025. See Table 4 above. In addition, emissions inventories used in EPA's regulatory impact analysis (RIA) for the 2012 PM2.5 NAAQS show that VOC emissions are projected to decrease by 720 tpy, respectively between 2007 and 2020. Ammonia emissions are projected to increase slightly between 2007 and 2020 by 8 tpy, which is expected to have minimal air quality impact, an impact that will be more than compensated by the significant emissions reductions projected in direct PM2.5, SO2, and NOX. See Table 5. Given that all emissions except ammonia decrease significantly below attainment year levels, providing a large margin of safety, the minimal increase in ammonia would not be expected to impact the areas ability to attain either the 1997 or 2006 PM2.5 NAAQS.
Table 5—Comparison of 2007 and 2020 VOC and Ammonia Emission Totals by Source Sector (tpy) for the Canton-Massillon Area 1
Point 21.29 20.40 −0.89 919.30 901.40 −17.90
Area 1491.50 1564.69 73.20 4825.67 4846.99 21.32
Nonroad 2.66 3.04 0.38 2723.36 1612.89 −1110.47
On-road 148.98 84.33 −64.65 5199.46 1847.15 −3352.30
Fires 1.69 1.69 0.00 24.28 24.28 0.00
Total 1666.11 1674.16 8.04 13692.06 9232.71 −4459.35
1 These emissions estimates were taken from the emissions inventories developed for the RIA for the 2012 PM2.5 NAAQS which can be found in the docket.
The current air quality design values for the area are 13.0 and 29 μg/m3 (based on 2010-2012 air quality data), which are well below the 1997 annual and 2006 24-hour PM2.5 NAAQS of 15 and 35 μg/m3. In addition, available air quality modeling analyses show continued maintenance of the standard during the maintenance period. The modeling analysis conducted for the RIA for the 2012 PM2.5 NAAQS indicates that the design value for this area is expected to continue to decline through 2020. In the RIA analysis, the highest 2020 modeled design value for the Canton-Massillon area is 10.8 μg/m3. Given that NOX, SO2, PM2.5, and VOC emissions are projected to decrease through 2025, and given that ammonia emissions are expected to remain relatively constant, it is reasonable to conclude that monitored PM2.5 levels in this area will continue to decrease through 2025.
Thus, EPA believes that there is ample justification to conclude that the Canton-Massillon area will continue to maintain the standard, even taking into consideration the emissions of other precursors potentially relevant to PM2.5. After consideration of the DC Circuit's January 4, 2013, decision, and for the reasons set forth in this notice, EPA proposes to approve the state's maintenance plan and its request to redesignate the Canton-Massillon area to attainment for the PM2.5 1997 annual and 2006 24-hour NAAQS.
As described in section V.3.b of this action, the result of Federal rules and consent decree actions, demonstrate that the reductions in emissions from point, area, and mobile sources in the Canton-Massillon area have occurred and are mandated to continue to occur through Start Printed Page 481002025 and beyond. Thus the emissions inventories set forth in Table 4 show that the area will continue to maintain the annual PM2.5 standard during the maintenance period at least through 2025.
Ohio's plan includes a commitment to continue working with West Virginia to operate its EPA-approved monitoring network, as necessary to demonstrate ongoing compliance with the NAAQS. Ohio currently operates three PM2.5 monitors in the Canton-Massillon area. West Virginia currently operates three monitors in their portion of the Canton-Massillon area.
Ohio remains obligated to continue to quality-assure monitoring data and enter all data into AQS in accordance with Federal guidelines. Ohio will use these data, supplemented with additional information as necessary, to assure that the area continues to attain the standard. Ohio 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. Both of these actions will help to verify continued attainment in accordance with 40 CFR part 58.
Ohio's contingency measures include a Warning Level Response and an Action Level Response. An initial Warning Level Response is triggered when the average weighted annual mean for one year exceeds 15.5 μg/m3. A warning level response for the 2006 24-hour standard shall be prompted whenever the 98th percentile 24-hour PM2.5 concentration of 35.5 μg/m3 occurs in a single calendar year within the maintenance area. In that case, a study will be conducted to determine if the emissions trends show increases; if action is necessary to reverse emissions increases, Ohio will follow the same procedures for control selection and implementation as for an Action Level Response.
As required by section 175A(b) of the CAA, Ohio commits to submit to the EPA an updated PM2.5 maintenance plan eight years after redesignation of the Canton-Massillon area to cover an additional ten year period beyond the initial ten year maintenance period. As required by section 175A of the CAA, Ohio has also committed to retain the PM2.5 control measures contained in the SIP prior to redesignation.
For all of the reasons set forth above, EPA is proposing to approve Ohio's 1997 annual and 2006 24-hour PM2.5 maintenance plan for the Canton-Massillon area as meeting the requirements of CAA section 175A.
When reviewing SIP revisions containing MVEBs, including attainment strategies, rate-of-progress plans, and maintenance plans, EPA must affirmatively find adequate and/or approve the MVEBs for use in determining transportation conformity before the MVEBs can be used. Once EPA affirmatively approves and/or 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 plans and TIPs 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). Additionally, to approve a motor vehicle emissions budget EPA must complete a thorough review of the SIP, in this case the PM2.5 maintenance plans, and conclude that the SIP will achieve its overall purpose, in this case providing for maintenance of the 1997 annual PM2.5 standard the Canton-Massillon area.
The maintenance plan submitted by Ohio for the Canton-Massillon area contains new primary PM2.5 and NOX MVEBs for the area for the years 2015 and 2025. The motor vehicle emissions budgets were calculated using MOVES2010(a). After the adequacy finding and approval of the budgets become effective, the budgets will have to be used in future conformity determinations and regional emissions analyses prepared by the SCATS, will have to be based on the use of MOVES2010a or the most recent version of MOVES required to be used in transportation conformity determinations.[12] The state has determined the 2015 MVEBs for the Canton-Massillon area to be 204.33 tpy for primary PM2.5 and 7,782.84 tpy for NOX. Ohio has determined the 2025 MVEBs for the Canton-Massillon area to be 101.50 tpy for primary PM2.5 and 4,673.83 tpy for NOX. These MVEBs exceed the on-road mobile source primary PM2.5 and NOX emissions projected by the states for 2015 and 2025. Ohio has decided to include “safety margins” as provided for in 40 CFR 93.124(a) (described below) of 26.65 tpy and 13.24 tpy for primary PM2.5 and 1,015.15 tpy and 609.63 tpy for NOX in the 2015 and 2025 MVEBs, respectively, to provide for on-road mobile source growth. Ohio did not provide emission budgets for SO2, VOCs, and ammonia because it concluded, that emissions of these precursors from on-road motor vehicles are not significant contributors to the area's PM2.5 air quality problem.
EPA issued conformity regulations to implement the 1997 PM2.5 NAAQS in July 2004 and May 2005 (69 FR 40004, July 1, 2004 and 70 FR 24280, May 6, 2005, respectively). Those actions were not part of the final rule recently remanded to EPA by the Court of Appeals for the District of Columbia in NRDC v. EPA, No. 08-1250 (Jan. 4, 2013), in which the Court remanded to EPA the implementation rule for the PM2.5 NAAQS because it concluded that EPA must implement that NAAQS pursuant to the PM-specific implementation provisions of subpart 4 of part D of title I of the CAA, rather than solely under the general provisions of subpart 1. That decision does not affect EPA's proposed approval of the Canton-Massillon area MVEBs.
In the Canton-Massillon area, the motor vehicle budgets including the safety margins and motor vehicle emission projections for both NOX and PM2.5 are lower than the levels in the attainment year.
EPA has reviewed the submitted budgets for 2015 and 2025 including the added safety margins using the conformity rule's adequacy criteria found at 40 CFR 93.118(e)(4) and the conformity rule's requirements for safety margins found at 40 CFR 93.124(a). EPA has also completed a thorough review of the maintenance plan for the Canton-Massillon area. Based on the results of this review of the budgets and the maintenance plans, EPA is approving the 2015 and 2025 direct PM2.5 and NOX budgets including the requested safety margins for the Canton-Massillon area. Additionally, EPA, through this rulemaking, has found the submitted budgets to be adequate for use to determine transportation conformity in the Canton-Massillon area, because EPA has determined that the area can maintain the 1997 annual PM2.5 NAAQS for the relevant maintenance period with on-road mobile source emissions at the levels of the MVEBs including the requested safety margins. These budgets must be used in conformity determinations made on or after the effective date of this direct final rulemaking (40 CFR 93.118(f)(iii)). Additionally, transportation conformity determinations made after the effective date of this notice must be based on regional emissions analyses using MOVES2010a or a more recent version of MOVES that has been approved for use in conformity determinations.[13]
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 shown in Table 4, the Canton-Massillon area is projected to have safety margins for NOX and direct PM2.5 of 8,404.59 tpy and 344.19 tpy in 2025 (the difference between the attainment year, 2008, emissions and the projected year of 2025 emissions for all sources in the Canton-Massillon area). The transportation conformity rule allows areas to allocate all or a portion of a “safety margin” to the area's motor Start Printed Page 48102vehicle emissions budgets (40 CFR 92.124(a)). The MVEBs requested by Ohio contain NOX safety margins for mobile sources in 2015 and 2025 and PM2.5 safety margins for mobile sources in 2015 and 2025 are much smaller than the allowable safety margins reflected in the total emissions for the Canton-Massillon area. The state is not requesting allocation to the MVEBs of the entire available safety margins reflected in the demonstration of maintenance. Therefore, even though the state is requesting MVEBs that exceed the projected on-road mobile source emissions for 2015 and 2025 contained in the demonstration of maintenance, the increase in on-road mobile source emissions that can be considered for transportation conformity purposes is well within the safety margins of the overall PM2.5 maintenance demonstration.
EPA, through this rulemaking, has found adequate and is proposing to approve the MVEBs for use to determine transportation conformity in the Canton-Massillon area, because EPA has determined that the area can maintain attainment of the 1997 annual PM2.5 NAAQS for the relevant maintenance period with mobile source emissions at the levels of the MVEBs including the requested safety margins. These budgets must be used in conformity determinations if this rulemaking goes final. (40 CFR 93.118(f)(iii)) Additionally, the determinations must be based on regional emissions analyses using MOVES2010b or a more recent version of MOVES that has been approved for use in conformity determinations.[14]
As discussed above, section 172(c)(3) of the CAA requires areas to submit a comprehensive emissions inventory. Ohio submitted a 2005 inventory and a 2008 base year emissions inventory that meets this requirement. Emissions contained in the submittals cover the general source categories of point sources, area sources, on-road mobile sources, and nonroad mobile sources. Further discussion on the methodology of compiling the emissions inventories can be found in section V.3.b above, and in the docket. Ohio's supplemental submittal of base year emission inventories of VOCs and ammonia are also found in the docket and summarized in Table 6, below.
Table 6—Summary of 2007 Base Year Emissions of Ammonia and VOCs for the Canton-Massillon Area by Source Type
Point 21.29 919.30
Area 1491.50 4825.67
Nonroad 2.66 2723.36
On-road 148.98 5199.46
Total 1666.11 13692.06
All emissions discussed in Tables 2, 3, and 6 above were documented in the docket and the appendices of Ohio's redesignation request and supplemental submittals. EPA has reviewed Ohio's documentation of the emissions inventory techniques and data sources used for the derivation of the 2005, 2007, and 2008 emissions estimates, and has found that Ohio has thoroughly documented the derivation of these emissions inventories. The submittal from the state shows that the 2008 emissions inventory is currently the most complete emissions inventories for PM2.5 and PM2.5 precursors in the Canton-Massillon area. Based upon EPA's review, we propose to find that the 2005 and 2007/2008 emissions inventories are as complete and accurate as possible given the input data available to Ohio, and we are proposing to approve them under CAA section 172(c)(3).
EPA has previously determined that the Canton-Massillon area has attained the 1997 annual and 2006 24-hour PM2.5 NAAQS. EPA is proposing to determine that the Canton-Massillon area continues to attain the 1997 annual and 2006 24-hour PM2.5 standard using the latest three years of certified, quality-assured data, and that the area has met the requirements for redesignation under section 107(d)(3)(E) of the CAA. EPA is proposing to approve the request from Ohio to change the legal designation of the Canton-Massillon area from nonattainment to attainment for the 1997 annual and 2006 24-hour PM2.5 NAAQS. EPA is proposing to approve Ohio's PM2.5 maintenance plan for the Canton-Massillon area as a revision to the Ohio SIP because the plan meets the requirements of section 175A of the CAA. EPA is proposing to approve the 2005 and 2008 emissions inventories for primary PM2.5, NOX, and SO2, documented in Ohio's April 16, 2012, submittal as satisfying the requirement in section 172(c)(3) of the CAA for a comprehensive, current emission inventory. Finally, EPA finds adequate and is approving 2015 and 2025 primary PM2.5 and NOX MVEBs for the Canton-Massillon area. These MVEBs will be used in future transportation conformity analyses for the area.
If finalized, approval of the redesignation request would change the official designation of the Canton-Massillon area for the 1997 annual and 2006 24-hour PM2.5 NAAQS, found at 40 CFR part 81, from nonattainment to attainment. If EPA's proposal is finalized, this action would approve the maintenance plan for the 1997 annual and 2006 24-hour PM2.5 standards for the Canton-Massillon area, as well as the 2005 and 2008 emissions inventories included with the redesignation request, as revisions to the Ohio SIP.
Under the CAA, redesignation of an area to attainment and the accompanying approval of a maintenance plan under section 107(d)(3)(E) are actions that affect the status of a geographical area and do not impose any additional regulatory requirements on sources beyond those imposed by state law. A redesignation to attainment does not in and of itself create any new requirements, but rather results in the applicability of requirements contained in the CAA for areas that have been redesignated to attainment. Moreover, the Administrator is required to approve a SIP submission that complies with the provisions of the Act and applicable Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in reviewing SIP submissions, EPA's role is to approve state choices, provided that they meet the criteria of the CAA. Accordingly, this action merely approves state law as meeting Federal requirements and does not Start Printed Page 48103impose additional requirements beyond those imposed by state law. For that reason, these actions:
8. The Canton-Massillon area has reduced VOC emissions through the implementation of various SIP approved VOC control programs and various on-road and nonroad motor vehicle control programs.
12. EPA described the circumstances under which an area would be required to use MOVES in transportation conformity determinations in its March 2, 2010, Federal Register notice officially releasing MOVES2010 for use in SIPs and transportation conformity determinations. (75 FR 9413)
13. EPA described the circumstances under which an area would be required to use MOVES in transportation conformity determinations in its March 2, 2010 Federal Register notice officially releasing MOVES2010 for use in SIPs and transportation conformity determinations. (75 FR 9413)
[FR Doc. 2013-18951 Filed 8-6-13; 8:45 am]