Interstate Transport of Fine Particulate Matter: Revision of Federal Implementation Plan Requirements for Texas, 45481-45497 [2017-20832]

Download as PDF Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations 45481 EPA-APPROVED IOWA NONREGULATORY SIP PROVISIONS Name of non-regulatory SIP provision * (49) Sections 110(a)(1) and (2) Infrastructure Requirements 2012 annual PM2.5 NAAQS. Applicable geographic or nonattainment area State submittal date * Statewide ........... [FR Doc. 2017–20829 Filed 9–28–17; 8:45 am] BILLING CODE 6560–50–P ENVIRONMENTAL PROTECTION AGENCY 40 CFR Part 52 [EPA–HQ–OAR–2016–0598; FRL–9968–46– OAR] RIN 2060–AT16 Interstate Transport of Fine Particulate Matter: Revision of Federal Implementation Plan Requirements for Texas Environmental Protection Agency (EPA). ACTION: Final rule. AGENCY: The Environmental Protection Agency (EPA) is finalizing withdrawal of the federal implementation plan (FIP) provisions that require affected electricity generating units (EGUs) in Texas to participate in Phase 2 of the Cross-State Air Pollution Rule (CSAPR) trading programs for annual emissions of sulfur dioxide (SO2) and nitrogen oxides (NOX). Withdrawal of the FIP requirements is intended to address a decision of the U.S. Court of Appeals for the District of Columbia Circuit (D.C. Circuit) remanding the CSAPR Phase 2 SO2 budget for Texas to the EPA for reconsideration. With this action, the EPA is also determining that, following SUMMARY: Category * 12/15/15 EPA approval date * * * * 09/29/17 and [Insert Fed- This action addresses the following CAA elements: eral Register citation]. 110(a)(2)(A), (B), (C), (D)(i)(II) prong 3, (D)(ii), (E), (F), (G), (H), (J), (K), (L), and (M). 110(a)(2)(I) is not applicable. [EPA–R07–OAR– 2017–0517; FRL–XXXX–Region 7.] withdrawal of the FIP requirements, sources in Texas do not contribute significantly to nonattainment in, or interfere with maintenance by, any other state with regard to the 1997 national ambient air quality standard (NAAQS) for fine particulate matter (PM2.5). Accordingly, we are also determining that the EPA has no obligation to issue new FIP requirements for Texas sources to address transported PM2.5 pollution under Clean Air Act (CAA) section 110(a)(2)(D)(i)(I) with regard to that NAAQS. Finally, the EPA is also affirming the continued validity of the Agency’s 2012 determination that participation in CSAPR meets the Regional Haze Rule’s criteria for an alternative to the application of sourcespecific best available retrofit technology (BART). The EPA has determined that changes to CSAPR’s geographic scope resulting from the actions EPA has taken or expects to take in response to the D.C. Circuit’s remand do not affect the continued validity of participation in CSAPR as a BART alternative, because the changes in geographic scope would not have adversely affected the results of the air quality modeling analysis upon which the EPA based the 2012 determination. DATES: This final rule is effective on September 29, 2017. ADDRESSES: The EPA has established a docket for this action under Docket ID NAICS * code Industry .......................... 221112 Explanation No. EPA–HQ–OAR–2016–0598. All documents in the docket are listed and publicly available at https:// www.regulations.gov. FOR FURTHER INFORMATION CONTACT: Questions about the withdrawal of CSAPR FIP requirements for Texas EGUs should be directed to David Lifland, Clean Air Markets Division, Office of Atmospheric Programs, U.S. Environmental Protection Agency, MC 6204M, 1200 Pennsylvania Avenue NW., Washington, DC 20460; telephone number: (202) 343–9151; email address: lifland.david@epa.gov. Questions about the sensitivity analysis regarding CSAPR participation as a BART alternative should be directed to Melinda Beaver, Office of Air Quality Planning and Standards, U.S. Environmental Protection Agency, 109 T.W. Alexander Drive, Mail Code C539– 04, Research Triangle Park, NC 27709; telephone number: (919) 541–1062; email address: beaver.melinda@epa.gov. Regulated Entities. Entities regulated under CSAPR are fossil fuel-fired boilers and stationary combustion turbines that serve generators producing electricity for sale, including combined cycle units and units operating as part of systems that cogenerate electricity and other useful energy output. Regulated categories and entities include: SUPPLEMENTARY INFORMATION: Examples of potentially regulated industries Fossil fuel-fired electric power generation. asabaliauskas on DSKBBXCHB2PROD with RULES * North American Industry Classification System. This table is not intended to be exhaustive, but rather provides a guide for readers regarding entities likely to be regulated. To determine whether your facility is affected by this action, you should carefully examine the applicability provisions in 40 CFR 97.404 and 97.704. If you have questions regarding the applicability of VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 CSAPR to a particular entity, consult the person listed in the FOR FURTHER INFORMATION CONTACT section above. Table of Contents I. Overview II. Background A. History and Summary of CSAPR PO 00000 Frm 00061 Fmt 4700 Sfmt 4700 B. CSAPR Participation as a BART Alternative III. Withdrawal of CSAPR FIP Requirements Related to Texas’ Transport Obligations With Regard to the 1997 Annual PM2.5 NAAQS A. Summary B. Adequacy of Rationale for Finding No Remaining Transport Obligation E:\FR\FM\29SER1.SGM 29SER1 45482 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations asabaliauskas on DSKBBXCHB2PROD with RULES C. Responsiveness to the D.C. Circuit’s Remand Instructions D. Consistency of Responses To Remand Across States E. Consistency of Consideration of D.C. Circuit’s Holding Across States F. Potential Use of Texas FIP Budgets To Address a Different PM2.5 NAAQS IV. Sensitivity Analysis Regarding CSAPR Participation as a BART Alternative A. Summary B. Continued CSAPR Participation by Georgia and South Carolina C. Appropriateness of Continued Reliance on Original CSAPR-Better-than-BART Analysis D. Possible Changes in the Geographic Distribution of Emissions E. Validity of 2012 Analytic Demonstration Prior to CSAPR Changes V. Description of Amendments to Regulatory Text VI. Statutory and Executive Order Reviews A. Executive Order 12866: Regulatory Planning and Review, and Executive Order 13563: Improving Regulation and Regulatory Review B. Executive Order 13771: Reducing Regulations and Controlling Regulatory Costs C. Paperwork Reduction Act D. Regulatory Flexibility Act E. Unfunded Mandates Reform Act F. Executive Order 13132: Federalism G. Executive Order 13175: Consultation and Coordination With Indian Tribal Governments H. Executive Order 13045: Protection of Children from Environmental Health and Safety Risks I. Executive Order 13211: Actions That Significantly Affect Energy Supply, Distribution, or Use J. National Technology Transfer Advancement Act K. Executive Order 12898: Federal Actions To Address Environmental Justice in Minority Populations and Low-Income Populations L. Congressional Review Act M. Judicial Review and Determinations Under CAA Section 307(b)(1) and (d) I. Overview The EPA promulgated CSAPR in 2011 in order to address the obligations of states—and of the EPA when states have not met their obligations—under CAA section 110(a)(2)(D)(i)(I) to prohibit air pollution contributing significantly to nonattainment in, or interfering with maintenance by, any other state with regard to several NAAQS, including the 1997 annual PM2.5 NAAQS.1 To address Texas’ transport obligation under CAA section 110(a)(2)(D)(i)(I) with regard to this NAAQS, CSAPR established FIP requirements for affected EGUs in Texas, including statewide emissions budgets that apply to the EGUs’ 1 Federal Implementation Plans; Interstate Transport of Fine Particulate Matter and Ozone and Correction of SIP Approvals, 76 FR 48208 (August 8, 2011). VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 collective annual emissions of SO2 and NOX. In 2012, the EPA promulgated an amendment to the Regional Haze Rule allowing a state whose EGUs participate in one of the CSAPR trading programs for a given pollutant to rely on its sources’ participation in CSAPR as an alternative to source-specific BART requirements—the so-called CSAPRbetter-than-BART rule, codified at 40 CFR 51.308(e)(4).2 This rule relied on a regional analytic demonstration that included an air quality modeling analysis comparing the projected visibility impacts of CSAPR implementation and BART implementation. To project emissions under CSAPR, the EPA assumed that the geographic scope and state emissions budgets for CSAPR would be implemented as finalized and amended in 2011 and 2012.3 In July 2015, the D.C. Circuit issued a decision on a range of challenges to CSAPR in EME Homer City Generation, L.P. v. EPA (EME Homer City II), denying most claims but remanding several CSAPR emissions budgets to the EPA for reconsideration, including the Phase 2 SO2 budget for Texas.4 Because the remand created the potential for changes in the geographic scope and stringency of CSAPR as evaluated for purposes of the 2012 comparison to BART implementation, the EPA recognizes that how the Agency addresses the remand could raise questions as to whether states and the EPA should continue to rely on the CSAPR-better-than-BART rule. The EPA issued a proposal to address the remand of the Texas Phase 2 SO2 budget and to resolve any questions about continued reliance on the CSAPRbetter-than-BART rule on November 3, 2016, and solicited comment on the proposal.5 Four commenters provided substantive comments, and this final rule takes those comments into consideration. The Agency’s responses to the principal comments are provided below. The remaining comments are addressed in the Response to Comments document available in the docket for this action. In this final action, as proposed, the EPA is withdrawing the FIP provisions requiring Texas EGUs to participate in the CSAPR SO2 Group 2 Trading Program and the CSAPR NOX Annual Trading Program during Phase 2 of these programs, which began with 2017 emissions.6 Removal of Texas EGUs from Phase 2 of these CSAPR trading programs renders it necessary to evaluate whether EPA should use other means to address any remaining transport obligation for Texas under CAA section 110(a)(2)(D)(i)(I) with regard to the 1997 annual PM2.5 NAAQS. However, the EPA is finalizing its proposed determination that Texas does not have any such remaining 1997 annual PM2.5 NAAQS transport obligation as of the beginning of Phase 2 of the CSAPR trading programs for SO2 and annual NOX. Accordingly, the EPA is also determining that the Agency has no obligation to issue new FIP requirements for Texas sources to address transported PM2.5 pollution under CAA section 110(a)(2)(D)(i)(I) with regard to this NAAQS. Also in this action, the EPA is concluding, based on consideration of the sensitivity analysis included in the proposal and additional analysis included in this final action, that the 2012 analytic demonstration supporting the conclusion that CSAPR participation qualifies as a BART alternative is not adversely affected by the actions being taken to respond to the D.C. Circuit’s remand of CSAPR Phase 2 budgets.7 As a result, no revisions are needed to the CSAPR-better-than-BART rule. At the same time, however, because Texas EGUs will no longer participate in a CSAPR SO2 trading program, Texas 2 Regional Haze: Revisions to Provisions Governing Alternatives to Source-Specific Best Available Retrofit Technology (BART) Determinations, Limited SIP Disapprovals, and Federal Implementation Plans, 77 FR 33642 (June 7, 2012). 3 CSAPR was amended three times in 2011 and 2012 to add five states to the seasonal NOX program and to increase certain state budgets. 76 FR 80760 (December 27, 2011); 77 FR 10324 (February 21, 2012); 77 FR 34830 (June 12, 2012). The CSAPRbetter-than-BART final rule reflected consideration of these changes to CSAPR. 4 EME Homer City Generation, L.P. v. EPA (EME Homer City II), 795 F.3d 118, 138 (D.C. Cir. 2015). The court also remanded the Phase 2 SO2 budgets for three other states and the Phase 2 seasonal NOX budgets for eleven states, including Texas. Id. 5 Interstate Transport of Fine Particulate Matter: Revision of Federal Implementation Plan Requirements for Texas, Proposed Rule, 81 FR 78954 (November 10, 2016). 6 With regard to each of the other remanded budgets, the EPA either has already withdrawn or expects to withdraw the FIP provisions requiring the EGUs in the affected states to participate in the corresponding CSAPR federal trading programs in Phase 2 through other actions, as discussed in section III below. 7 In addition to this action, the full set of actions being taken to respond to the remand includes the 2016 CSAPR Update withdrawing the remanded seasonal NOX budgets for eleven states and establishing new seasonal NOX budgets to address a more recent ozone NAAQS for eight of those states, the action approving Alabama’s SIP revision establishing state CSAPR trading programs for SO2 and annual NOX to replace the corresponding federal CSAPR trading programs, and the expected actions to approve proposed SIP revisions for Georgia and South Carolina comparable to Alabama’s SIP revision (see notes 14, 53, and 57 below). These additional actions are described in more detail in sections II.A and III.D below. PO 00000 Frm 00062 Fmt 4700 Sfmt 4700 E:\FR\FM\29SER1.SGM 29SER1 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations will no longer be eligible to rely on CSAPR participation as an alternative to the application of source-specific SO2 BART for its BART-eligible EGUs under 40 CFR 51.308(e)(4). That obligation and any other remaining regional haze obligations for Texas are not addressed in this action and will need to be addressed through other actions as appropriate.8 This final rule is effective immediately upon publication in the Federal Register. As discussed in section VI.L below, the EPA is issuing this rule under CAA section 307(d). While Administrative Procedure Act (APA) section 553(d)9 generally provides that rules may not take effect earlier than 30 days after they are published in the Federal Register, CAA section 307(d)(1) clarifies that ‘‘[t]he provisions of [APA] section 553 . . . shall not, except as expressly provided in this section, apply to actions to which this subsection applies.’’ Thus, APA section 553(d) does not apply to this rule. Nevertheless, in making this rule effective immediately upon publication, the EPA has considered the purposes underlying APA section 553(d). The primary purpose of the prescribed 30-day waiting period is to give affected parties a reasonable time to adjust their behavior and prepare before a final rule takes effect. This rule does not impose any new regulatory requirements and therefore does not necessitate time for affected sources to adjust their behavior or otherwise prepare for implementation. Further, APA section 553(d) expressly allows an effective date less than 30 days after publication for a rule that ‘‘grants or recognizes an exemption or relieves a restriction.’’ This rule relieves Texas EGUs of certain FIP requirements that would otherwise apply. Consequently, making this rule effective immediately upon publication is consistent with the purposes of APA section 553(d). II. Background A. History and Summary of CSAPR asabaliauskas on DSKBBXCHB2PROD with RULES The EPA initially promulgated CSAPR in 2011 to address the obligations of states—and of the EPA when states have not met their 8 The EPA notes that under 40 CFR 51.308(e)(4), CSAPR implementation is available as a NOX BART alternative for a state whose EGUs are subject to CSAPR requirements for either annual NOX or seasonal NOX emissions. See 77 FR at 33652. Texas EGUs continue to participate in a CSAPR trading program for seasonal NOX. In a separate proposed action, the EPA has proposed to address NOX BART for Texas EGUs through reliance on participation in CSAPR as a NOX BART alternative. 82 FR 917 (January 4, 2017). 9 5 U.S.C. 553(d). VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 obligations—under CAA section 110(a)(2)(D)(i)(I), often referred to as the ‘‘good neighbor’’ provision, to prohibit transported air pollution contributing significantly to nonattainment in, or interfering with maintenance by, any other state with regard to the 1997 annual PM2.5 NAAQS, the 2006 24-hour PM2.5 NAAQS, and the 1997 8-hour ozone NAAQS.10 To reduce transported PM2.5 pollution, CSAPR sets limits on annual emissions of NOX and SO2 as precursors to PM2.5. To reduce transported ozone pollution during the May-September ozone season, CSAPR sets limits on seasonal emissions of NOX as a precursor to ozone. The CSAPR requirements were initially established in FIPs, but states can voluntarily replace the CSAPR FIPs with CSAPR state implementation plans (SIPs) that include equally stringent budgets.11 Upon approval of such a CSAPR SIP, the corresponding CSAPR FIP is automatically withdrawn.12 As explained in the proposal, a number of petitioners challenged CSAPR, and in 2015 the D.C. Circuit issued a decision remanding the Phase 2 SO2 emissions budgets for Alabama, Georgia, South Carolina, and Texas and the Phase 2 seasonal NOX budgets for eleven states to the EPA for reconsideration.13 In response to the remand of the Phase 2 SO2 emissions budgets, the EPA has engaged the affected states to determine appropriate next steps to address the decision with regard to each state. As discussed in the proposal and also in section III below, the EPA expects that EGUs in Alabama, Georgia, and South Carolina will continue to participate in CSAPR trading programs for SO2 and annual NOX pursuant to approved SIP revisions (with equally stringent emissions budgets), making Texas the only state whose EGUs will no longer participate in these programs to reduce transported PM2.5 pollution as a result of actions taken to address the remand. Also as explained in the proposal, in the CSAPR Update rule issued in 2016, the EPA responded to the remand of eleven states’ original Phase 2 seasonal NOX budgets (which had been established to address transport obligations with regard to the 1997 8hour ozone NAAQS) by withdrawing the FIP provisions requiring EGUs to comply with those budgets for emissions after 2016.14 The EPA 10 See generally 76 FR 48208. 40 CFR 52.39(i). 40 CFR 52.39(j). 13 EME Homer City II, 795 F.3d at 138. 14 Cross-State Air Pollution Rule Update for the 2008 Ozone NAAQS (CSAPR Update), 81 FR 74504, 74576 (October 26, 2016). 11 E.g., 12 E.g., PO 00000 Frm 00063 Fmt 4700 Sfmt 4700 45483 determined that none of those eleven states has a remaining transport obligation under CAA section 110(a)(2)(D)(i)(I) with regard to the 1997 8-hour ozone NAAQS, but for eight of those states, including Texas, the CSAPR Update rule also established new budgets to address transport obligations with regard to the more stringent 2008 8-hour ozone NAAQS.15 EGUs in the three states with remanded Phase 2 seasonal NOX budgets for which the EPA did not establish new budgets—Florida, North Carolina, and South Carolina—are no longer required to participate in a CSAPR trading program for seasonal NOX emissions to address ozone transport obligations after 2016. However, because EGUs in North Carolina and South Carolina16 are expected to continue to participate in a CSAPR trading program for annual NOX emissions in order to address PM2.5related transport obligations, Florida is expected to be the only state originally covered by CSAPR for NOX emissions for which all such coverage is ending as a result of the EPA’s set of actions to address the remand.17 Prior to this action, Texas EGUs have been subject to CSAPR FIP provisions requiring participation in the CSAPR SO2 Group 2 Trading Program and the CSAPR NOX Annual Trading Program. With this action, the EPA is withdrawing the FIP provisions requiring Texas EGUs to participate in these CSAPR federal trading programs. (Although the court’s decision specifically remanded only Texas’ Phase 2 SO2 budget, the court’s rationale for remanding that budget also implicates Texas’ Phase 2 annual NOX budget because the SO2 and annual NOX budgets were developed through an integrated analysis and were promulgated to meet a common PM2.5 transport obligation under CAA section 110(a)(2)(D)(i)(I).) This action has no effect on the separate CSAPR requirements applicable to Texas EGUs relating to seasonal NOX emissions, which, as discussed in the preceding paragraph, were promulgated in the 15 Id. at 74524. Carolina EGUs remain subject to FIP provisions requiring participation in a CSAPR trading program for annual NOX emissions. The EPA’s expectation that South Carolina EGUs will continue to participate in a CSAPR program for annual NOX emissions is based on South Carolina’s submission of a SIP revision that includes such requirements, as discussed in sections III and V below. 17 For discussion of the EPA’s response to the remand of the Florida seasonal NOX budget, and the assessment of the implications of that response for the CSAPR-better-than-BART analytical demonstration, see 81 FR at 78962. 16 North E:\FR\FM\29SER1.SGM 29SER1 45484 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations CSAPR Update rule and are not subject to the D.C. Circuit’s remand. B. CSAPR Participation as a BART Alternative The proposal provides a detailed explanation of the Regional Haze Rule requirements for best available retrofit technology (BART) and the criteria for demonstrating that an alternative measure achieves greater reasonable progress than source-specific BART.18 In 2012, the EPA amended the Regional Haze Rule to provide that participation by a state’s EGUs in a CSAPR trading program for a given pollutant—either a CSAPR federal trading program implemented through a CSAPR FIP or a CSAPR state trading program implemented through an approved CSAPR SIP revision— qualifies as a BART alternative for those EGUs for that pollutant.19 In promulgating this CSAPR-better-thanBART rule, the EPA relied on an analytic demonstration of the improvement in visibility from CSAPR implementation relative to BART implementation based on an air quality modeling study.20 Since the EPA promulgated this amendment, numerous states covered by CSAPR have come to rely on the provision through either SIPs or FIPs.21 Additionally, many states have submitted or are planning to submit SIPs relying on the CSAPR-better-thanBART rule for BART or visibility transport purposes, or to replace regional haze FIPs with SIPs. As explained in the proposal, the 2012 analytic demonstration that CSAPR provides for greater reasonable progress than BART included Texas EGUs as subject to CSAPR for SO2 and annual NOX (as well as seasonal NOX) 18 81 FR at 78957. CFR 51.308(e)(4); see also generally 77 FR 33642. Legal challenges to the CSAPR-better-thanBART rule from conservation groups and other petitioners are pending. Utility Air Regulatory Group v. EPA, No. 12–1342 (D.C. Cir. filed August 6, 2012). 20 See Technical Support Document for Demonstration of the Transport Rule as a BART Alternative, Docket ID No. EPA–HQ–OAR–2011– 0729–0014 (December 2011) (2011 CSAPR/BART Technical Support Document), and memo entitled ‘‘Sensitivity Analysis Accounting for Increases in Texas and Georgia Transport Rule State Emissions Budgets,’’ Docket ID No. EPA–HQ–OAR–2011– 0729–0323 (May 29, 2012), both available in the docket for this action. 21 The EPA has promulgated FIPs relying on CSAPR participation for BART purposes for Georgia, Indiana, Iowa, Kentucky, Michigan, Missouri, Ohio, Pennsylvania, South Carolina, Tennessee, Virginia, and West Virginia, 77 FR at 33654, and Nebraska, 77 FR 40150, 40151 (July 6, 2012). The EPA has approved SIPs relying on CSAPR participation for BART purposes for Minnesota, 77 FR 34801, 34806 (June 12, 2012), and Wisconsin, 77 FR 46952, 46959 (August 7, 2012). asabaliauskas on DSKBBXCHB2PROD with RULES 19 40 VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 and included Florida EGUs as subject to CSAPR for seasonal NOX. The EPA recognizes that the treatment of these EGUs in the analysis would have been different if the Florida FIP withdrawal finalized in the CSAPR Update rule and the Texas FIP withdrawal finalized in this action had been known at the time of the demonstration. In order to address any potential concern about continuing to rely on CSAPR participation as a BART alternative for EGUs in the remaining CSAPR states, in the proposal for this action the EPA provided a sensitivity analysis explicitly addressing the potential effect on that demonstration of the removal of Texas and Florida EGUs from the relevant CSAPR trading programs in response to the D.C. Circuit’s remand. As discussed in section IV, the sensitivity analysis indicates clearly that the demonstration remains valid despite these changes in CSAPR’s geographic scope, supporting the continued validity of EPA’s 2012 conclusion that CSAPR participation meets the Regional Haze Rule’s criteria for a BART alternative.22 Consequently, in this action the EPA is affirming the current Regional Haze Rule provision at 40 CFR 51.308(e)(4) authorizing the use of CSAPR participation as a BART alternative for BART-eligible EGUs for a given pollutant in states whose EGUs continue to participate in a CSAPR trading program for that pollutant. III. Withdrawal of CSAPR FIP Requirements Related to Texas’ Transport Obligations With Regard to the 1997 Annual PM2.5 NAAQS A. Summary In this action, as proposed, the EPA is responding to the remand of the CSAPR Phase 2 SO2 budget for Texas by withdrawing the FIP provisions requiring Texas EGUs to participate in the CSAPR SO2 Group 2 Trading Program and the CSAPR NOX Annual Trading Program with regard to emissions during Phase 2 of those 22 With respect to each of the remanded budgets, the EPA has responded or expects to respond to the remand by withdrawing the FIP provisions requiring compliance with the remanded budget. Thus, all changes to CSAPR arising directly from the Agency’s response to the remand are changes in CSAPR’s geographic scope rather than changes in the stringency of state budgets. Although the EPA has also promulgated new CSAPR seasonal NOX budgets for 22 states (including eight states with remanded seasonal NOX budgets) in order to address a more stringent NAAQS, see generally 81 FR 74504, for purposes of the sensitivity analysis the EPA has conservatively not considered the generally increased stringency of the new seasonal NOX budgets, but the EPA did consider the changes in CSAPR’s geographic scope—that is, the fact that the remaining three states with remanded seasonal NOX budgets will no longer participate in CSAPR for seasonal NOX. PO 00000 Frm 00064 Fmt 4700 Sfmt 4700 programs, which began in 2017. In EME Homer City II, the court remanded the CSAPR Phase 2 SO2 budget for Texas to the EPA for reconsideration on the grounds that the budget may be more stringent than necessary to address the state’s obligation under CAA section 110(a)(2)(D)(i)(I) to reduce transported pollution with respect to the 1997 annual PM2.5 NAAQS.23 Upon review of options for responding to the remand, the EPA has determined, for the reasons discussed in this section, that withdrawal of the FIP provisions identified above, rather than issuance of revised FIP provisions for Texas with a higher (i.e., less stringent) Phase 2 SO2 budget as advocated by some commenters, is the appropriate response. Withdrawal of the FIP provisions related to the CSAPR SO2 trading program encompasses withdrawal of the requirement for Texas EGUs to comply with the remanded Phase 2 SO2 budget, thereby addressing the specific rule provision remanded by the court. The EPA is withdrawing the FIP provisions related to annual NOX (in addition to the requirements related to SO2) because the CSAPR FIP requirements for SO2 and annual NOX were determined through an integrated analysis and were promulgated in combination to remedy covered states’ PM2.5 transport obligations; the court’s finding that CSAPR’s Phase 2 requirements may be more stringent than necessary to address Texas’ PM2.5 transport obligation therefore implicates the state’s Phase 2 budgets for both SO2 and annual NOX. Withdrawal of the previous CSAPR FIP requirements revives the need to consider Texas’ transport obligation under CAA section 110(a)(2)(D)(i)(I) with regard to the 1997 annual PM2.5 NAAQS and to address any remaining obligation through other means. However, as proposed, the Agency is further determining that Texas has no remaining transport obligation under this CAA provision with regard to this NAAQS following withdrawal of the previous FIP requirements, and consequently is also determining that the EPA has no obligation to issue new FIP requirements as to Texas’s transport obligation under CAA section 110(a)(2)(D)(i)(I) with regard to the 1997 annual PM2.5 NAAQS. In the CSAPR final rule, the EPA determined that 23 states, including Texas, had transport obligations with regard to the 1997 annual PM2.5 23 795 F.3d at 128–29. A more detailed discussion of how the EPA established the CSAPR Phase 2 SO2 budget for Texas and why the court found the budget invalid is included in the proposal for this action. 81 FR at 78958. E:\FR\FM\29SER1.SGM 29SER1 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations asabaliauskas on DSKBBXCHB2PROD with RULES NAAQS, the 2006 24-hour PM2.5 NAAQS, or both, and established SO2 and annual NOX emissions budgets for each of the states.24 The budgets were implemented through FIP provisions requiring the affected EGUs in each covered state to participate in CSAPR allowance trading programs. In the case of Texas, the PM2.5-related FIP requirements were imposed based solely on the state’s transport obligations with regard to the 1997 annual PM2.5 NAAQS.25 Following issuance of the D.C. Circuit’s decision in EME Homer City II remanding the CSAPR Phase 2 SO2 budget for Texas, the EPA reevaluated its earlier conclusions regarding Texas’ PM2.5 transport obligations by reexamining the data in the final CSAPR record in light of the D.C. Circuit’s holdings in the decision, including the holdings regarding the CSAPR Phase 2 seasonal NOX budgets for several states, as explained in the proposal.26 The final CSAPR record contained ‘‘base case’’ modeling projections of air quality at monitoring locations throughout the country both for 2012, the intended start year of Phase 1 of the CSAPR trading programs, and for 2014, the intended start year of Phase 2 of the programs. The base case projections were designed to represent projected air quality at these monitoring locations without any emission reductions from CSAPR. In the CSAPR rulemaking, the EPA used the 2012 base case air quality projections for purposes of identifying ozone receptors projected to have air quality problems and determining states that were linked to those receptors and that therefore might have transport obligations under both Phase 1 and Phase 2 of the CSAPR trading programs. However, in EME Homer City II, the D.C. Circuit agreed with petitioners27 that the EPA should also have considered the 2014 base case air quality projections for these 24 The EPA also determined in CSAPR and a related supplemental rule that 25 states, including Texas, had transport obligations with regard to the 1997 8-hour ozone NAAQS. In all, 28 states were determined to have transport obligations related to either PM2.5, ozone, or both. The EPA’s process for determining states’ emissions limitations under CSAPR and the associated CSAPR FIP requirements is described at length in the preamble to the CSAPR final rule. See generally 77 FR at 48222–71. 25 As noted in the proposal and further discussed below, the modeling for the CSAPR final rule also linked Texas to a downwind air quality problem with regard to the 2006 24-hour PM2.5 NAAQS, but the EPA did not rely on the linkage with regard to that NAAQS as a basis for establishing CSAPR FIP requirements for Texas EGUs. 81 FR at 78960 n.42; see also 76 FR at 48243, 48214. 26 81 FR at 78960. 27 See Opening Brief of Industry and Labor Petitioners on Remand 8, 14, EME Homer City Generation, L.P. v. EPA, No. 11–1302 (D.C. Cir. filed December 10, 2014). VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 purposes, and that in instances of receptors where the 2014 base case projections did not show air quality problems, the EPA lacked authority to require any emission reductions in Phase 2 of the CSAPR trading programs based on linkages to those receptors only occurring in Phase 1 of the programs. On these grounds, the court found that EPA lacked authority to establish Phase 2 seasonal NOX emission limitations for EGUs in ten states linked solely to ozone receptors whose 2014 air quality projections did not show air quality problems.28 While not discussed in the court’s decision, the projections of 2014 air quality for a PM2.5 receptor in Madison County, Illinois (the only PM2.5 receptor with projected air quality problems to which Texas was linked) in the final CSAPR record are analogous to the 2014 air quality projections for the ozone receptors described above, in that the air quality problems at the Madison County receptor were projected to be resolved in 2014 before any emission reductions from CSAPR. In light of the court’s holding as to the legal import of the 2014 base case air quality projections for the ozone receptors described above, the EPA considered the legal import of the analogous 2014 base case air quality projections for the Madison County PM2.5 receptor with respect to Texas’ PM2.5-related obligations under CSAPR. There are three relevant record data elements. First, the record indicates that the only PM2.5 receptor to which Texas is linked for purposes of determining possible obligations under the good neighbor provision is the receptor in Madison County, Illinois.29 Second, the projected maximum design value 30 for annual PM2.5 at the Madison County receptor is 15.02 micrograms per cubic meter (mg/m3) in the 2014 base case.31 28 EME Homer City II, 795 F.3d at 129–30. The court also remanded the Phase 2 seasonal NOX budget for an eleventh state (Texas), but on different grounds. 29 See 76 FR at 48241, tables V.D–2 and V.D–3. 30 The EPA independently considered linkages to ‘‘nonattainment’’ and ‘‘maintenance’’ receptors. If both the projected average design value and the projected maximum design values for a receptor were above the triggering threshold, the receptor was considered a nonattainment receptor. If the projected maximum design value was above the triggering threshold but the projected average design value was not, the receptor was considered a maintenance receptor. Thus, if the projected maximum design value was not above the triggering threshold, the receptor was not considered either a nonattainment receptor or a maintenance receptor. See 76 FR at 48233. 31 See projected 2014 base case maximum annual PM2.5 design value for Madison County, Illinois receptor 171191007 at B–41 of the Air Quality Modeling Final Rule Technical Support Document, Docket ID No. EPA–HQ–OAR–2009–0491–4140 (June 2011) (CSAPR Final Rule Technical Support Document), available in the docket for this action. PO 00000 Frm 00065 Fmt 4700 Sfmt 4700 45485 Finally, the value that the EPA used to determine whether a particular PM2.5 receptor should be identified as having air quality problems that may trigger transport obligations with regard to the 1997 annual PM2.5 NAAQS is 15.05 mg/ m3, which is higher than the Madison County maximum design value in the 2014 base case.32 Thus, the reevaluation of the final CSAPR record in light of the D.C. Circuit’s holding indicates that the record does not support a finding of a transport obligation for Texas under CAA section 110(a)(2)(D)(i)(I) with regard to this NAAQS as of the beginning of Phase 2 of the CSAPR trading programs for SO2 and annual NOX, and the Agency accordingly finds that the state’s obligation is resolved without a need for further emission reductions, including the emission reductions from CSAPR. The finding that Texas’s transport obligation with regard to this NAAQS is resolved as of the start of Phase 2 of the CSAPR trading programs without the need for any emission reductions from CSAPR removes the EPA’s authority to issue new FIP requirements for purposes of responding to the court’s remand of the state’s CSAPR Phase 2 SO2 budget. The finding likewise eliminates any obligation of the EPA to issue new FIP requirements addressing a remaining transport obligation of the state with regard to this NAAQS following withdrawal of the existing CSAPR FIP requirements, because the state has no such remaining transport obligation following the withdrawal. As noted in the proposal, the modeling for the CSAPR final rule also linked Texas to a downwind air quality problem with regard to the 2006 24-hour PM2.5 NAAQS, but the EPA did not rely on the linkage with regard to this NAAQS as a basis for establishing CSAPR FIP requirements for Texas EGUs. In the proposal, the EPA indicated that data in the final CSAPR record, reevaluated in light of EME Homer City II, would show that Texas no longer has a transport obligation with regard to the 2006 24-hour PM2.5 NAAQS as of the beginning of Phase 2 of the CSAPR trading programs for SO2 and annual NOX, but that because Texas was not subject to CSAPR requirements with regard to this NAAQS, the EPA was not proposing to make a determination in this action as to any obligation of Texas with regard to this NAAQS. Nevertheless, because commenters raise the 2006 24-hour PM2.5 NAAQS in their comments, the EPA will explain how the court’s reasoning would apply with respect to 32 76 E:\FR\FM\29SER1.SGM FR at 48233. 29SER1 45486 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations the data for this NAAQS. The analysis for the 2006 24-hour PM2.5 NAAQS is essentially identical to the analysis described above with regard to the 1997 annual PM2.5 NAAQS. Specifically, the Madison County receptor is the only PM2.5 receptor to which Texas was linked for this NAAQS; 33 the projected maximum design value for 24-hour PM2.5 at the Madison County receptor is 35.3 mg/m3 in the 2014 base case; 34 and the value that the EPA used to determine whether a particular PM2.5 receptor should be identified as having air quality problems that may trigger transport obligations with regard to the 2006 24-hour PM2.5 NAAQS is 35.5 mg/ m3, which is higher than the Madison County maximum design value in the 2014 base case.35 Thus, the reevaluation of the final CSAPR record in light of the D.C. Circuit’s holding also indicates that the record would not support a finding of a transport obligation for Texas with regard to the 2006 24-hour PM2.5 NAAQS as of the beginning of Phase 2 of the CSAPR trading programs for SO2 and annual NOX. Overall, on the subject of the proposed withdrawal of the FIP provisions and the proposed finding that Texas will no longer have a transport obligation following withdrawal of the FIP provisions, the EPA received substantive comments from two parties.36 The remainder of this section summarizes these commenters’ principal comments on this topic and provides the Agency’s response. B. Adequacy of Rationale for Finding No Remaining Transport Obligation asabaliauskas on DSKBBXCHB2PROD with RULES The commenters state that the Agency’s explanation for the proposed finding that Texas no longer has a transport obligation under CAA section 110(a)(2)(D)(i)(I) with regard to the 1997 annual PM2.5 NAAQS as of the beginning of Phase 2 of the CSAPR trading programs for SO2 and annual NOX is inadequate or confusing, and that the Agency must provide additional explanation for changing its position on the continued existence of a Texas transport obligation from the contrary position taken by the Agency when promulgating the CSAPR final rule. 33 See 76 FR at 48242–44, tables V.D–5 and V.D– 6. 34 See projected 2014 base case maximum 24hour PM2.5 design value for Madison County, Illinois receptor 171191007 at B–70 of the CSAPR Final Rule Technical Support Document, available in the docket for this action. 35 76 FR at 48234–35. 36 A third commenter states without further elaboration that it does not oppose the FIP withdrawal. VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 The EPA disagrees with these comments. The proposal contained a complete explanation of the Agency’s basis for this finding, including all necessary supporting data and documentation.37 As fully explained in the proposal and reiterated above, the Agency’s change in position as to Texas’ transport obligation between the CSAPR final rule and this action is readily attributable to the D.C. Circuit’s holding in EME Homer City II with regard to the legal import of the 2014 base case air quality projections in the final CSAPR record. The court’s holding clarifies the legal standard the Agency should have used when considering the information in the final CSAPR record, which includes those air quality projections. C. Responsiveness to the D.C. Circuit’s Remand Instructions The commenters assert that withdrawal of the remanded Texas SO2 budget without issuance of a presumably less stringent replacement budget is not responsive to the D.C. Circuit’s remand instructions. According to the commenters, the court directed the EPA to develop a revised CSAPR FIP SO2 budget for Texas EGUs that does not over-control, and the EPA must either do so or, alternatively, must allow Texas to submit a CSAPR SIP with a higher SO2 budget. The commenters’ argument is intended to provide a continued basis for reliance on CSAPR participation as an SO2 BART alternative for Texas EGUs. Underlying the commenters’ arguments is an apparent belief that a revised, higher CSAPR budget, whether issued through a FIP or approved through a SIP, would automatically enable Texas to rely on CSAPR participation as an alternative to source-specific SO2 BART requirements for the State’s EGUs under 40 CFR 51.308(e)(4). The EPA disagrees with these comments. As an initial matter, the D.C. Circuit in fact did not direct the Agency to develop replacement budgets for the Texas SO2 budget or any of the other remanded CSAPR Phase 2 budgets. Rather, the court found that certain budgets were invalid and remanded to the EPA to ‘‘reconsider’’ them,38 a general instruction that encompasses a range of possible Agency actions upon reconsideration. The commenters cite no statement from the court’s opinion that requires the establishment of replacement budgets, but assert that such a requirement must be inferred from the court’s other statements or determinations. For example, the 37 81 FR at 78960. Homer City II, 795 F.3d at 124, 138. 38 EME PO 00000 Frm 00066 Fmt 4700 Sfmt 4700 commenters suggest that because the court remanded the budgets without vacatur instead of vacating the budgets outright, the court must have intended for the Agency to replace rather than simply withdraw the budgets. However, the court actually provided a different rationale for remanding without vacatur, including the statement that ‘‘some good neighbor obligations may be appropriate for some of the relevant states.’’ 39 The reference to ‘‘some’’ of the states indicates that the court considered it likely that replacement budgets would not be established in every instance, and the use of the word ‘‘may’’ indicates that the court considered it possible that replacement budgets would not be established in any instance. Thus, contrary to the commenters’ claims, the court’s opinion clearly affords the Agency the discretion to determine the appropriate response to the remand and does not prevent the Agency from determining upon reconsideration that the program is no longer needed for a particular state with respect to a particular pollutant and consequently not establishing a replacement budget. The commenters make several additional arguments in support of their contention that the FIP withdrawal is not responsive to the D.C. Circuit’s instructions. One commenter asserts that because the court stated that the Agency could consider new information in responding to the remand, the court must have intended for the Agency’s response to involve the establishment of replacement budgets. This claim is a non sequitur—the court’s acknowledgement that additional information may be considered says nothing about what the Agency may or must conclude from consideration of that information. The same commenter also asserts that the Agency may not rely on lack of FIP authority as the basis for not establishing a revised budget because lack of FIP authority was not the basis cited by the court for remanding the budget. This claim is also a non sequitur—the Agency lacks authority to issue a revised budget and therefore may not do so, regardless of what additional defects the court may have cited in ordering the remand. The other commenter asserts that the FIP withdrawal would disrupt allowance markets, contrary to the concern expressed by the D.C. Circuit that outright vacatur, rather than remand without vacatur, could have that impact. While the EPA agrees with the concern expressed by the court and the commenter regarding the potentially disruptive effects of outright vacatur on 39 Id. E:\FR\FM\29SER1.SGM at 132 (emphasis added). 29SER1 asabaliauskas on DSKBBXCHB2PROD with RULES Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations allowance markets, the Agency does not agree that the court’s concern regarding unintended consequences of a judicial vacatur provides a basis for not taking final action at this time to withdraw the Texas FIP requirements, for two reasons. First, the EPA believes that the court did not intend for its expression of concern to constrain the Agency’s range of possible responses to the remand. As discussed above, it is clear from the opinion that the court anticipated the possibility that upon reconsideration the EPA would determine that some, or even all, of the remanded budgets should be withdrawn and not replaced. Second, in this instance, emissions data reported by the EGUs covered by the CSAPR trading programs for SO2 and annual NOX demonstrate that withdrawal of the FIP provisions requiring Texas EGUs to participate in these programs will not cause allowance market disruption for the programs’ remaining participants. Under both programs, the totals of the emissions reported by participating EGUs for both 2015 and 2016 in states other than Texas were less than the sums of the Phase 2 emissions budgets for these other states.40 Likewise, under both programs the totals of the emissions reported by Texas EGUs for both 2015 and 2016 were less than the Texas Phase 2 budgets.41 The elimination from the programs of Texas EGUs and the allowances allocated to Texas EGUs is therefore not expected to cause either shortages of allowances available for purchase by EGUs in the other states or the loss of an important market for sale of surplus allowances by EGUs in the other states. In these circumstances, the EPA anticipates that the FIP withdrawal will have little impact on the allowance market in either trading program. With regard to the two commenters’ preferred response to the remand—that the EPA establish a revised, less stringent SO2 budget for Texas EGUs and implement that budget through a revised FIP—such an action is infeasible because the Agency lacks the necessary legal authority. In this action, the EPA is finalizing the proposed finding that Texas no longer has a transport obligation under CAA section 110(a)(2)(D)(i)(I) for the 1997 annual PM2.5 NAAQS. That finding addresses the deficiency in the Texas SIP that was the basis for issuance of the withdrawn FIP requirements and, therefore, because there is no longer a deficiency, the Agency no longer has authority to 40 See ‘‘2015–2016 Compliance Summary for CSAPR SO2 Group 2 and NOX Annual Trading Programs,’’ available in the docket for this action. 41 Id. VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 issue revised FIP requirements.42 The reasons for the finding are discussed above and were discussed at length in the proposal.43 With regard to the commenters’ suggested alternative response to the remand—that the EPA allow Texas to submit a CSAPR SIP with a higher SO2 budget in order to allow the state to rely on CSAPR participation as an SO2 BART alternative even if the state’s EGUs are no longer subject to a CSAPR FIP SO2 budget—the comment is not properly directed to the EPA, because Texas has not expressed interest in submitting a CSAPR SIP.44 Moreover, even if consideration of Texas’ BART obligations were relevant for our action on remand, reliance on CSAPR participation with a higher budget would not automatically qualify as an SO2 BART alternative under the terms of the CSAPR-better-than-BART rule. That rule allows a state to rely on its EGUs’ participation in a CSAPR SIP trading program only if the EPA approves the SIP as ‘‘meeting the requirements of’’ the CSAPR regulations at 40 CFR 52.38 and 52.39.45 As relevant here, the CSAPR regulations at § 52.39 expressly preclude a state’s SO2 emissions budget from exceeding the SO2 emissions budget established under the CSAPR FIP trading program that the CSAPR SIP trading program would replace.46 Thus, even if the D.C. Circuit’s remand could serve as a basis for the EPA to approve a SIP revision that does not satisfy § 52.39 on the grounds that the state’s transport obligations can be addressed by a less stringent budget, the CSAPR-betterthan-BART rule at 40 CFR 51.308(e)(4) would not be satisfied. A SIP approved on such a basis could in theory provide a mechanism for Texas EGUs to participate in CSAPR with a higher SO2 budget than the remanded FIP budget despite the Agency’s lack of authority to set a revised SO2 budget through a revised FIP. However, because of the increased SO2 budget, such a SIP would not ‘‘meet[] the requirements of . . . § 52.39’’ and therefore would not allow the state to rely on its EGUs’ participation in the CSAPR SIP trading program as an alternative to sourcespecific BART for SO2.47 42 See CAA section 110(c). FR at 78960. 44 Texas did not submit comments on the proposal for this action. 45 40 CFR 51.308(e)(4). 46 40 CFR 52.39(i)(1)(i). 47 To the extent the commenters are suggesting that the D.C. Circuit’s holdings in EME Homer City II require the Agency to find that a SIP with a revised, higher SO2 budget would somehow satisfy the CSAPR-better-than-BART rule despite its plain 43 81 PO 00000 Frm 00067 Fmt 4700 Sfmt 4700 45487 D. Consistency of Responses to Remand Across States One commenter states that by withdrawing the FIP requirements the EPA is arbitrarily singling Texas out as the only state with a remanded CSAPR budget whose EGUs will lose the ability to rely on CSAPR participation as a BART alternative. The commenter further asserts that the Agency’s ‘‘sole purpose’’ in withdrawing the FIP requirements is to facilitate the imposition of source-specific SO2 BART requirements on Texas EGUs through a different action. The EPA disagrees with these comments, which are entirely contrary to the record. First, on the question of uniform application of the CSAPRbetter-than-BART regulations, no state whose EGUs do not participate in a CSAPR trading program for a given pollutant can rely on CSAPR participation as a BART alternative for that pollutant. In response to the D.C. Circuit’s remand of CSAPR Phase 2 budgets, the EPA has withdrawn or expects to withdraw all fifteen remanded budgets. As explained in the proposal, in thirteen instances, the state will retain eligibility to rely on the CSAPR-better-than-BART rule for the pollutant in question through either the EPA’s establishment of a new CSAPR budget to address a more stringent NAAQS (eight seasonal NOX budgets), the state’s sources’ continued participation in a different CSAPR trading program for the same pollutant (two seasonal NOX budgets), or the state’s voluntary adoption in a SIP revision of a CSAPR state budget as stringent as the remanded CSAPR FIP budget (three SO2 budgets).48 In the remaining two instances where a remanded budget is being withdrawn and none of the three options for preserving eligibility to rely on CSAPRbetter-than-BART applies—Texas’ SO2 budget and Florida’s seasonal NOX budget—the state is losing the language, the Agency disagrees. The court held that the remanded budgets may over-control relative to the states’ transport obligations, but did not determine that the budgets are more stringent than necessary to serve as an alternative to sourcespecific BART. Further, the CSAPR-better-thanBART rule rests on an evaluation of the projected visibility impacts from CSAPR implementation assuming the final CSAPR Phase 2 budget stringencies (including the 2012 CSAPR budget revisions, which were accounted for in the analysis for the final CSAPR-better-than-BART rule). Given this, continuing to enforce the CSAPR-better-thanBART rule’s requirement that a state’s participation in CSAPR through a SIP must ‘‘meet[] the requirements of . . . § 52.39’’—including the requirement for a state budget no less stringent than was analyzed for purposes of promulgating the rule—is entirely reasonable. 48 71 FR at 78956–57. E:\FR\FM\29SER1.SGM 29SER1 45488 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations asabaliauskas on DSKBBXCHB2PROD with RULES opportunity to rely on CSAPR participation as a BART alternative for that pollutant.49 Thus, Texas is being treated the same as every other state with respect to use of the CSAPR-betterthan-BART rule.50 Second, on the question of the EPA’s purpose in withdrawing the FIP requirements, that purpose is to address the court’s remand. As explained in the proposal, before initiating this action, the EPA communicated with officials in all four states with remanded SO2 budgets—Alabama, Georgia, South Carolina, and Texas—regarding the EPA’s intent to respond to the remand of the Phase 2 SO2 budgets by withdrawing the FIP provisions requiring the states’ EGUs to participate in the CSAPR federal trading programs for SO2 and annual NOX.51 The EPA explained that each state would lose its ability to rely on CSAPR participation as a BART alternative for SO2 and/or NOX if its EGUs no longer participated in the CSAPR trading programs, but that the state could preserve that ability, if desired, by submitting a CSAPR SIP revision replacing the CSAPR federal trading programs with CSAPR state trading programs applying stateestablished budgets no less stringent than the remanded federally-established budgets (i.e., budgets consistent with the 2012 CSAPR-better-than-BART analytic demonstration).52 Alabama, Georgia, and South Carolina indicated 49 As noted in the proposal, 81 FR at 78962, n.55, the EPA has already approved the incorporation into Florida’s SIP of determinations regarding source-specific NOX BART. 77 FR 71111, 71113–14 (November 29, 2012); 78 FR 53250, 53267 (August 29, 2013). 50 As a further example of the consistent treatment of Texas, the EPA notes that, despite the withdrawal of the Texas FIP requirements relating to annual NOX emissions, the state will be able to continue to rely on the CSAPR-better-than-BART rule for NOX as long as the state’s EGUs continue to participate in a CSAPR trading program for seasonal NOX emissions. See 81 FR at 78955 n.4 and 78956 n.7. 51 See memo entitled ‘‘The U.S. Environmental Protection Agency’s Plan for Responding to the Remand of the Cross-State Air Pollution Rule Phase 2 SO2 Budgets for Alabama, Georgia, South Carolina and Texas’’ from Janet G. McCabe, EPA Acting Assistant Administrator for Air and Radiation, to EPA Regional Air Division Directors (June 27, 2016), available in the docket for this action. The memo directs the Regional Air Division Directors to share the memo with state officials. The EPA also communicated orally with officials in Alabama, Georgia, South Carolina, and Texas in advance of the memo. 52 Although the D.C. Circuit remanded the states’ Phase 2 SO2 budgets because it determined that the budgets may be more stringent than necessary to address the states’ identified PM2.5 transport obligations, nothing in the court’s decision affects the states’ authority to seek incorporation into their SIPs of state-established budgets as stringent as the remanded federally-established budgets or limits the EPA’s authority to approve such SIP revisions. See CAA sections 116, 110(k)(3). VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 their preference to pursue the SIP revision option. The EPA approved Alabama’s CSAPR SIP revision in 2016 and, accordingly, the FIP provisions requiring its EGUs to participate in the CSAPR federal trading programs for SO2 and annual NOX have been automatically withdrawn.53 Georgia and South Carolina committed to the EPA in 2016 to submit similar CSAPR SIP revisions by deadlines falling in September 2017 and August 2017, respectively.54 Georgia has in fact now submitted its SIP to the EPA for approval,55 South Carolina has submitted its proposed state CSAPR trading program rules and has requested that the EPA begin the SIP approval process under the Agency’s parallel processing procedure,56 and the EPA has proposed to approve both SIP revisions.57 The CSAPR FIP provisions 53 Air Plan Approval; Alabama; Cross-State Air Pollution Rule, 81 FR 59869 (August 31, 2016). 54 See letters to Heather McTeer Toney, Regional Administrator, EPA Region 4, from Judson H. Turner, Director of the Environmental Protection Division, Georgia Department of Natural Resources (May 26, 2016) and from Myra C. Reece, Director of Environmental Affairs, South Carolina Department of Health and Environmental Control (April 19, 2016), available in the docket for this action. The EPA has conditionally approved the CAA section 110(a)(2)(D)(i)(II) prong 4 visibility element for multiple NAAQS in the Georgia and South Carolina SIPs based on each state’s commitment to submit a CSAPR SIP revision. 81 FR 65899, 65900 (September 26, 2016) (Georgia); 81 FR 56512, 56513 (August 22, 2016) (South Carolina). Each state committed to submit its CSAPR SIP revision within one year of the date of the Agency’s final conditional approval of the state’s prong 4 SIP revision. Failure of a state to meet a commitment serving as the basis for a conditional SIP approval results in automatic conversion of the conditional approval to a disapproval. 55 See letter to V. Anne Heard, Acting Regional Administrator, EPA Region 4, from Richard E. Dunn, Director, Environmental Protection Division, Georgia Department of Natural Resources (July 26, 2017), available in the docket for this action. 56 See letter to V. Anne Heard, Acting Regional Administrator, EPA Region 4, from Myra C. Reece, Director of Environmental Affairs, South Carolina Department of Health and Environmental Control (May 26, 2017), available in the docket for this action. Under the parallel processing procedure, the EPA works closely with the state agency during regulatory development, and the state submits a copy of its proposed regulations to the EPA before completion of the state’s public notice and adoption process. The EPA reviews the proposed state action, prepares a notice of proposed EPA action (approval or disapproval) for publication in the Federal Register, and provides public notice concurrently with the state’s process. After the state adopts its final regulations and submits its formal SIP revision request, the EPA reviews the SIP submission for changes from proposal and either prepares a notice of final EPA action or, if the state has made significant changes, may re-propose before taking final EPA action. The public comment period on South Carolina’s proposed regulations ended on June 26, 2017, and the state expects its final regulations to become effective in August 2017. Id. 57 Air Plan Approval; Georgia; Cross-State Air Pollution Rule, 82 FR 38866 (August 16, 2017); Air Plan Approval; South Carolina; Cross-State Air Pollution Rule, 82 FR 37389 (August 10, 2017). PO 00000 Frm 00068 Fmt 4700 Sfmt 4700 remain in place for the time being for EGUs in Georgia and South Carolina, and the EPA is not proposing their withdrawal at this time based on the reasonable expectation that such withdrawal will be automatically accomplished as a result of the Agency’s action on those states’ SIP submittals, just as with Alabama.58 Because Texas has indicated that it will not submit a CSAPR SIP revision, the EPA is proceeding with this action to withdraw the FIP requirements for Texas EGUs, consistent with the intended approach previously communicated to officials for all four states. Texas has had the same set of options available to all four states with remanded SO2 budgets and has selected a different option than the other three states. E. Consistency of Consideration of D.C. Circuit’s Holding Across States One commenter asserts that the EPA has not analyzed whether other states covered by CSAPR are linked only to receptors for which the 2014 base case projections do not show air quality problems, and that ‘‘[b]y not performing that analysis, the EPA is arbitrarily singling Texas out for removal from the CSAPR program.’’ The EPA disagrees with these comments. With respect to the budgets that were not remanded by the court, the Agency has confirmed for each such budget that the state is linked to at least one receptor for which the base case 2014 air quality projections showed air quality problems. The court’s holding as to lack of authority to establish Phase 2 emission reduction requirements for a state in the absence of any linkage to a projected air quality problem in the 2014 base case therefore does not extend to these budgets.59 With respect to the remanded budgets, the EPA again rejects the suggestion that Texas is being treated differently than any other state. As noted in the response above to the comments concerning the consistency of the Agency’s responses to the remand, 58 If the EPA disapproves Georgia’s or South Carolina’s SIP submittal, the EPA will propose to withdraw the FIP provisions requiring that state’s EGUs to participate in the CSAPR federal trading programs for SO2 and annual NOX, consistent with the action taken here for Texas EGUs. 59 See 76 FR at 48241–44, tables V.D–2, V.D–3, V.D–5, and V.D–6 (annual and 24-hour PM2.5 linkages); id. at 48246, tables V.D–8 and V.D–9 (ozone linkages); CSAPR Final Rule Technical Support Document at B–35 to B–92 (2014 base case maximum design values for annual and 24-hour PM2.5); id. at B–4 to B–34 (2014 base case maximum design values for ozone). As discussed above, the relevant triggering values for annual and 24-hour PM2.5 are 15.05 mg/m3 and 35.5 mg/m3, respectively. The relevant triggering value for ozone is 85 parts per billion (ppb). 76 FR at 48236. E:\FR\FM\29SER1.SGM 29SER1 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations the FIP requirements to comply with all the remanded budgets, not just the remanded Texas SO2 budget, have been withdrawn or are expected to be withdrawn. Further, as discussed above, in the cases of ten of the eleven remanded seasonal NOX budgets, the absence of air quality problems at the relevant receptors in the 2014 base case projections was expressly cited by the court as the basis for remanding the budgets. The EPA’s reliance on the court’s holding as applied to those states’ ozone-related transport obligations with regard to the 1997 8hour ozone NAAQS is indistinguishable from the EPA’s reliance on the same holding as applied to Texas’ PM2.5related transport obligations with regard to the 1997 annual PM2.5 NAAQS.60 asabaliauskas on DSKBBXCHB2PROD with RULES F. Potential Use of Texas FIP Budgets To Address a Different PM2.5 NAAQS Finally, the commenters state that the EPA should consider Texas’s obligations to address interstate transport with respect to the 2006 24-hour PM2.5 NAAQS and/or the 2012 annual PM2.5 NAAQS before withdrawing Texas’ FIP obligations. As noted in the proposal and discussed above, in the case of Texas, CSAPR FIP obligations related to PM2.5 pollution were established with respect to the 1997 annual PM2.5 NAAQS only, even though for other states the CSAPR FIPs were based on the states’ transport obligations with respect to both the 1997 annual PM2.5 NAAQS and the 2006 24-hour PM2.5 NAAQS.61 The commenters assert that failure to consider Texas’ potential transport obligations with respect to the 2006 24-hour PM2.5 NAAQS now before withdrawing the FIP obligations would be inconsistent with the manner in which the EPA responded to the D.C. Circuit’s remand of seasonal NOX budgets and inconsistent with data in the CSAPR record that links Texas to downwind air quality problems with respect to the 2006 24-hour PM2.5 NAAQS.62 60 In the case of the last remanded seasonal NO X budget—for Texas—the court remanded the budget on different grounds, and the EPA subsequently determined through further analysis that the state has no remaining transport obligation under CAA section 110(a)(2)(D)(i)(I) with respect to the 1997 8hour ozone NAAQS. See 81 FR at 74524. In the cases of the remanded SO2 budgets for Alabama, Georgia, and South Carolina, the states are adopting equally stringent CSAPR SIP budgets to replace the withdrawn FIP budgets in order to preserve the states’ options to rely on the CSAPR-better-thanBART rule, thereby rendering moot any questions about the states’ remaining transport obligations and EPA’s authority or obligation to issue revised FIP budgets to address such transport obligations. 61 See 81 FR at 78960 n.42; see also 76 FR at 48213, table III–1. 62 One of the commenters asserts that ‘‘under EPA’s own theory,’’ the existence of this data in the VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 The EPA disagrees with this comment for three reasons. First, as noted above, the Agency is responding to the court’s remand of all fifteen CSAPR Phase 2 SO2 and seasonal NOX budgets in the same way, namely by withdrawing the FIP provisions requiring affected EGUs to comply with the remanded budgets.63 The differences noted by the commenters are differences only in the actions that are being coordinated with the responses, not differences in the responses themselves. Second, the differences in the coordinated actions are reasonable given the differences in other regulatory activities being undertaken for the two pollutants. The EPA coordinated the withdrawal of the eleven remanded seasonal NOX budgets addressing the 1997 8-hour ozone NAAQS with the establishment of new budgets for eight of those states addressing the 2008 8-hour ozone NAAQS because a rulemaking to address transported pollution with respect to the 2008 8-hour ozone NAAQS was actively under development at the time of the court’s decision.64 Under this circumstance, such coordination was efficient and fully consistent with the court’s expressed intent to minimize market disruption and to continue to address statutory obligations to reduce transported pollution where appropriate. In contrast, no analogous opportunity is available to coordinate withdrawal of the remanded SO2 budgets with another rulemaking addressing a more recent PM2.5 NAAQS because states’ transport obligations with respect to the 2006 24-hour PM2.5 NAAQS have already been largely addressed through either SIPs or the CSAPR final record mandates that the EPA consider the state’s transport obligations with respect to the 2006 24-hour PM2.5 NAAQS before withdrawing the FIP requirements. Wrongly attributing this ‘‘theory’’ to the Agency, the commenter ignores other factors the Agency must take into account before promulgating FIP requirements, such as whether a statutory condition establishing FIP authority has been satisfied. In any event, for this final action the Agency has expressly considered (and rejected) the option of leaving the Texas FIP requirements in place to address the state’s transport obligations with respect to this NAAQS, as discussed in this section. 63 As discussed in the proposal, addressing the remanded budgets by withdrawing the FIP requirements is also fully consistent with the manner in which EPA has responded to previous judicial remands regarding obligations of individual states under other EPA rules addressing multiple states’ transport obligations. 81 FR at 78959. 64 As noted in the proposal, for three of the eleven states with remanded seasonal NOX budgets addressing the 1997 8-hour ozone NAAQS— Florida, North Carolina, and South Carolina—the EPA found no transport obligations with respect to the 2008 8-hour ozone NAAQS and did not establish seasonal NOX budgets addressing that NAAQS. 81 FR at 78959. PO 00000 Frm 00069 Fmt 4700 Sfmt 4700 45489 CSAPR rulemaking, and the Agency has not identified interstate transport problems with respect to the 2012 annual PM2.5 NAAQS sufficient to justify a new national rulemaking at this time. Third, the EPA lacks authority to rely on a transport obligation for Texas with respect to either the 2006 24-hour PM2.5 NAAQS or the 2012 annual PM2.5 NAAQS as the legal basis to support imposing an SO2 budget for the state via a FIP. Under CAA section 110(c), the Agency’s authority to issue a FIP with respect to a particular state obligation arises either when the Agency finds that a state has failed to submit a required SIP or when the Agency disapproves a submitted SIP. Neither of these predicate events has occurred with regard to Texas’ transport obligations under either the 2006 24-hour PM2.5 NAAQS or the 2012 annual PM2.5 NAAQS.65 Commenters are correct that data in the final CSAPR record, as evaluated by the Agency when CSAPR was promulgated, showed that PM2.5 pollution transported from Texas to downwind states exceeded the minimum threshold level used to establish which states might have transport obligations for the 2006 24hour PM2.5 NAAQS. However, as noted in the proposal 66 and discussed above, the 2014 base case air quality projections in the final CSAPR record, when reevaluated in light of the D.C. Circuit’s holdings in EME Homer City II, would support a finding that as of the beginning of Phase 2 of the CSAPR trading programs for SO2 and annual NOX, Texas does not have an ongoing transport obligation with respect to the 2006 24-hour PM2.5 NAAQS. Thus, even if the EPA had taken final action disapproving Texas’ outstanding SIP submission addressing transported pollution with regard to the 2006 24hour PM2.5 NAAQS, such a disapproval would no longer provide a basis for the Agency to issue a FIP in this instance, because without any remaining transport obligation, there is no remaining SIP deficiency to address through a FIP. 65 Texas has submitted SIPs intended to address its transport obligations under each of these NAAQS. In the case of the 2006 24-hour PM2.5 NAAQS, the EPA has proposed to disapprove the state’s transport SIP submittal, 76 FR 20602 (April 13, 2011), but has yet not taken final action. In the case of the 2012 annual PM2.5 NAAQS, the EPA has not yet taken any action on the state’s transport SIP submittal. 66 81 FR at 78955 n.5. E:\FR\FM\29SER1.SGM 29SER1 45490 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations IV. Sensitivity Analysis Regarding CSAPR Participation as a BART Alternative asabaliauskas on DSKBBXCHB2PROD with RULES A. Summary As explained in the proposal and summarized in section II.B, the EPA amended the Regional Haze Rule in 2012 to authorize states whose EGUs participate in CSAPR trading programs for a given pollutant to rely on CSAPR participation as a BART alternative for that pollutant. The CSAPR-better-thanBART rule rests on an analytic demonstration that implementation of CSAPR as expected to take effect at that time would achieve greater reasonable progress than BART toward the national goal of natural visibility conditions in Class I areas. As part of the proposal for this action, the EPA included a sensitivity analysis to the 2012 analytic demonstration showing that the 2012 analysis would have supported the same conclusion if the actions being taken in response to the D.C. Circuit’s remand of various CSAPR Phase 2 budgets 67 had been reflected in the 2012 analysis. In this action, upon consideration of comments received, the EPA is affirming the sensitivity analysis from the proposal that concluded that the 2012 analytic demonstration is still valid and is consequently affirming that there is no need for revision of the CSAPR-better-than-BART rule as a result of the changes in CSAPR’s geographic scope resulting from the Agency’s set of responses to the EME Homer City II decision. The original 2012 analytic demonstration supporting participation in CSAPR as a BART alternative was based on an air quality modeling analysis comparing projected visibility conditions at relevant locations (referred to in the proposal and here simply as ‘‘Class I areas’’) under three scenarios.68 The first scenario reflected no implementation of either CSAPR or BART, the second scenario reflected implementation of presumptive sourcespecific BART for both SO2 and NOX at BART-eligible EGUs nationwide, and 67 As described in sections II.A and III.D above, in addition to this action, the full set of actions being taken to respond to the remand includes the 2016 CSAPR Update (see note 14 above) withdrawing the remanded seasonal NOX budgets for eleven states and establishing new seasonal NOX budgets to address a more recent ozone NAAQS for eight of those states, the action approving Alabama’s SIP revision establishing state CSAPR trading programs for SO2 and annual NOX to replace the corresponding federal CSAPR trading programs (see note 53 above), and expected actions to approve proposed SIP revisions for Georgia and South Carolina comparable to Alabama’s SIP revision (see note 57 above). 68 This background is set forth in greater detail in the proposal. See 81 FR at 78961–62. VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 the third scenario reflected implementation of CSAPR in covered states and presumptive source-specific BART for each pollutant in states where CSAPR did not apply for that pollutant (the three scenarios are referred to here as the base case scenario, the BART scenario, and the original CSAPR scenario, respectively). The EPA used the results of the three scenarios to compare the projected visibility impacts of CSAPR and BART under a twopronged ‘‘better-than-BART’’ test.69 The first prong—a requirement that visibility must not decline in any Class I area under the proposed BART alternative— was evaluated by comparing the projected visibility conditions under the original CSAPR scenario and the base case scenario. The second prong—a requirement that there must be an overall visibility improvement on average across all affected Class I areas under the proposed BART alternative relative to source-specific BART—was evaluated by comparing the projected visibility conditions under the original CSAPR scenario and the BART scenario. Based on these comparisons, and also taking account of revisions made to CSAPR after the 2011 modeling but before or contemporaneous with the 2012 CSAPR-better-than-BART rule, the EPA concluded that the original CSAPR scenario satisfied both prongs of the test. The EPA’s proposed sensitivity analysis is set forth in detail in the proposal for this action.70 To reiterate briefly, for the sensitivity analysis, the Agency identified a total of five changes in CSAPR’s geographic scope expected to occur as a result of actions responding to the D.C. Circuit’s remand: The removal of Florida, North Carolina, and South Carolina from CSAPR for seasonal NOX; the removal of Texas from CSAPR for annual NOX; and the removal of Texas from CSAPR for SO2.71 With respect to each of the four changes related to NOX, the EPA explained that the change would not have caused a sufficiently large change in the modeled NOX emissions in the original CSAPR scenario to materially alter the visibility impacts comparison. For North Carolina and South Carolina, this assessment was based on the fact that the states’ EGUs 69 As described in the proposal, satisfaction of the two-pronged test based on an air quality modeling analysis is one of three ways that an alternative measure may be demonstrated to be ‘‘better than BART’’ under the Regional Haze Rule. 81 FR at 78957. 70 81 FR at 78961–64. 71 For purposes of the sensitivity analysis, the EPA conservatively did not consider the increased stringency of the CSAPR seasonal NOX budgets established in the CSAPR Update. See generally 81 FR 74504. PO 00000 Frm 00070 Fmt 4700 Sfmt 4700 would, or were expected to, remain subject to CSAPR for annual NOX after the end of their CSAPR obligations for seasonal NOX.72 For Florida and Texas, this assessment was based on the small magnitudes of the differences in projected total NOX emissions from the EGUs in each of those states between the original CSAPR scenario and the relevant other modeled scenarios, combined with the dominance of sulfate impacts compared to nitrate impacts on visibility (especially in the South).73 With respect to the removal of Texas from CSAPR for SO2, the EPA explained that the change would have caused a large reduction in the Texas SO2 emissions as modeled in the original CSAPR scenario,74 thereby causing the visibility impacts comparison to support the Agency’s determination that CSAPR participation met the criteria for a BART alternative even more strongly than the comparison as originally performed in 2012. Thus, because the only material change from the original 2012 analytic demonstration would be the relative visibility improvement in a revised CSAPR scenario resulting from the removal of Texas from CSAPR for SO2, the sensitivity analysis as proposed indicated that the 2012 analytic demonstration remains valid. The EPA received substantive comments from two parties with respect to the proposed sensitivity analysis. One commenter agrees with the EPA’s conclusion and with all but one detail of the EPA’s methodology (which, if changed as suggested by the commenter, would strengthen the Agency’s conclusion). The other commenter does not agree with either the conclusion or 72 81 FR at 78962. at 78962 (Florida), 78963 (Texas). 74 As noted above and discussed in the proposal, the original CSAPR scenario reflected projected implementation of CSAPR in covered states and presumptive source-specific BART in states where CSAPR did not apply for a pollutant. If Texas had not been expected to be covered by CSAPR for SO2, the CSAPR scenario would therefore have reflected SO2 emissions from Texas EGUs consistent with the implementation of presumptive source-specific SO2 BART instead of participation in CSAPR. While EPA projected that the CSAPR region overall would have substantially lower SO2 emissions under CSAPR than under source-specific BART, for some individual states, including Texas, SO2 emissions under source-specific BART were projected to be lower than under CSAPR. Thus, removing Texas from CSAPR for SO2 in the CSAPR-better-thanBART analytic demonstration would have resulted in a decrease in projected SO2 emissions in the CSAPR scenario as modeled for the demonstration. See 81 FR at 78962–63. In the proposal, the EPA identified the minimum amount of the projected decrease in Texas SO2 emissions as 127,300 tons, based on the difference between projected Texas SO2 emissions under the original CSAPR and BART scenarios. Id.; see also ‘‘Projected Changes in Texas Emissions, Fossil Generation, and Fuel Usage Between the Base Case, BART, and Original CSAPR Scenarios,’’ available in the docket for this action. 73 Id. E:\FR\FM\29SER1.SGM 29SER1 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations the methodology, providing several reasons. The remainder of this section summarizes the opposing commenter’s principal comments on this topic and provides the Agency’s response. asabaliauskas on DSKBBXCHB2PROD with RULES B. Continued CSAPR Participation by Georgia and South Carolina The commenter states that in order to analyze the impacts on the CSAPRbetter-than-BART analytic demonstration from changes caused by the remand, in addition to any other changes evaluated, the EPA must also evaluate the removal of Georgia and South Carolina from CSAPR’s SO2 programs, both because the D.C. Circuit remanded their SO2 budgets as invalid and because in the commenter’s view it is impermissible to rely in such a sensitivity analysis on mere commitments from those states to submit CSAPR SIPs in the future. Further, according to the commenter, allowing these states to continue to participate in CSAPR and then rely on such participation as a BART alternative after their SO2 budgets have been remanded would be inconsistent with the EPA’s previous determinations that states could no longer indefinitely rely on participation in the former Clean Air Interstate Rule (CAIR) trading programs as a BART alternative after the D.C. Circuit found CAIR to be an invalid rule that must be replaced.75 The EPA disagrees with the comment that the Agency must consider Georgia and South Carolina ineligible to continue to participate in CSAPR’s SO2 programs as a consequence of the remand of their FIP budgets. The CSAPR regulations expressly provide for approval of CSAPR SIPs that meet certain conditions as replacements for CSAPR FIPs, and Georgia and South Carolina (as well as Alabama) have elected to submit such SIPs. The comparison that the commenter draws to the EPA’s previous findings that states may no longer rely on participation in CAIR as a BART 75 In 2005, the EPA promulgated the Clean Air Interstate Rule (CAIR) addressing certain interstate air pollution reduction obligations, 70 FR 25162 (May 12, 2005), and amended the Regional Haze Rule to allow participation in CAIR to be relied on as a BART alternative (the CAIR-better-than-BART rule), 70 FR 39104 (July 6, 2005). The D.C. Circuit upheld the CAIR-better-than-BART rule, Utility Air Regulatory Group v. EPA, 471 F.3d 1333 (D.C. Cir. 2006), but later found CAIR invalid and remanded that rule to the Agency for replacement, North Carolina v. EPA, 531 F.3d 896 (D.C. Cir. 2008), modified on rehearing, 550 F.3d 1176 (D.C. Cir. 2008). The Agency then replaced CAIR with CSAPR, 76 FR 48208, and replaced the CAIR-betterthan-BART rule with the CSAPR-better-than-BART rule, 77 FR 33642. In addition, following the remand of CAIR, the Agency disapproved SIP submissions for several states seeking to rely on CAIR as a BART alternative, e.g., 77 FR at 33647. VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 45491 alternative is inapt, because the basis for such previous findings was that CAIR itself (including its trading programs) would not exist, not that particular CAIR budgets were invalid. Here, the CSAPR trading program will still exist, making it possible for the states to continue to participate in CSAPR through voluntary SIPs notwithstanding the invalidation of the EPA’s authority to require compliance with the remanded budgets through FIPs addressing the states’ transport obligations. The EPA considers the comment about reliance on mere commitments to submit SIPs to be largely moot because in the interval between submission of the comment and finalization of this action, Georgia has submitted its SIP revision and South Carolina has submitted its proposed state regulations and has requested that EPA begin the SIP approval process under the Agency’s parallel processing procedure.76 Each of the state trading program rules includes a state budget for SO2 or annual NOX emissions equal to that state’s current FIP budget. To the extent the commenter believes that for purposes of a sensitivity analysis the Agency may rely only on a SIP that has been approved and not on a SIP or proposed state rule that has been submitted for EPA approval but not yet approved, the Agency disagrees. Both states’ rules take the approach of incorporating by reference the federal CSAPR trading program rules, including the relevant budget amounts, so there are no substantive differences between the state trading program rules being adopted by the states for inclusion in their SIPs and the federal trading program rules that are being replaced. The Agency has proposed to approve both states’ SIP revisions 77 and at this time is unaware of any reason why the proposed approvals should not be finalized. In these circumstances, the EPA believes it is reasonable to rely on the SIP submittals for purposes of supporting an analytic assumption that Georgia and South Carolina will continue to participate in CSAPR’s SO2 and annual NOX programs at the states’ current budget levels.78 it is based on outdated material, and that instead of evaluating whether the 2012 analytic demonstration remains valid, the EPA must perform an entirely new analytic demonstration based on a new air quality modeling analysis using more current data. The EPA disagrees with this comment. While criticizing aspects of the Agency’s analytic methodology, the commenter does not dispute that the sensitivity analysis as conducted by the EPA using that methodology shows that the 2012 analytic demonstration would have been strengthened rather than weakened by the changes in CSAPR’s geographic scope that are occurring as a result of the D.C. Circuit’s remand. (The methodological criticisms are addressed as the next comment below.) Further, the commenter offers no compelling support for the suggestion that, in the absence of any reason to doubt the conclusion from the 2012 analytic demonstration, the EPA must nevertheless conduct an entirely new demonstration. As an asserted legal rationale for the need for a new analysis, the commenter cites the Regional Haze Rule provisions for approval of BART alternatives, noting that the provision that the EPA followed in approving the CSAPR-better-than-BART rule requires a demonstration based on an air quality modeling analysis.79 The EPA has performed one such air quality modeling analysis and in this action has shown that the analysis already performed would continue to support a conclusion that CSAPR meets the criteria for a BART alternative notwithstanding changes in CSAPR’s geographic scope. Contrary to the commenter’s suggestion, the regulations do not say that the EPA must perform an entirely new analysis. Similarly, the commenter’s assertion that changes in industry data since 2011 necessitate a new analytic demonstration amounts to a call for recurring demonstrations that a BART alternative results in greater reasonable progress than BART as the industry evolves, rather than a one-time demonstration when the alternative is approved. The regulations include no such requirement for recurring demonstrations. C. Appropriateness of Continued Reliance on Original CSAPR-BetterThan-BART Analysis The commenter states that the sensitivity analysis is arbitrary because D. Possible Changes in the Geographic Distribution of Emissions The commenter states that the EPA’s methodology for conducting the sensitivity analysis as set forth in the proposal failed to adequately consider whether changes in a revised CSAPR scenario regarding the geographic distribution of emissions across states or 76 See supra notes 55 and 56. supra note 57. 78 As discussed in section III.D above, both states continue to participate in the CSAPR SO2 and annual NOX programs through FIPs while Agency action on their SIP submittals is pending. 77 See PO 00000 Frm 00071 Fmt 4700 Sfmt 4700 79 See E:\FR\FM\29SER1.SGM 40 CFR 51.308(e)(3). 29SER1 45492 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations asabaliauskas on DSKBBXCHB2PROD with RULES within individual states might lead to violations of the analytic criteria that the EPA relied on to find that CSAPR qualifies as a BART alternative. In particular, the commenter raises the theoretical possibility that, in a revised CSAPR scenario where Texas EGUs no longer participate in CSAPR for SO2, some individual sources in other CSAPR states could buy additional allowances and increase their emissions, and that such increases in emissions in turn could cause adverse visibility impacts in some individual Class I areas (thereby violating the first prong of the two-pronged test described above). More generally, the commenter asserts that without new modeling the EPA ‘‘has no data’’ and has ‘‘simply assume[d]’’ that the two prongs of the test would be satisfied under such a revised scenario. As an initial matter, the EPA disagrees with the commenter’s summary characterization of the proposed sensitivity analysis as not being grounded in data. To the contrary, the Agency’s proposed conclusions explicitly rely on data drawn from the modeling results in the record for the CSAPR-better-than-BART rule. The EPA explained in the proposal, first, how the data from the earlier rulemaking record showed that a revised CSAPR scenario would reflect a projected reduction in Texas SO2 emissions of 127,300 tons (or more) 80 along with projected increases in Florida and Texas NOX emissions of at most a few thousand tons and, second, why it was logical to conclude from these projected emissions changes that, relative to the modeled BART and base case scenarios, the revised CSAPR scenario would have shown even larger visibility improvements than the original CSAPR scenario.81 The commenter provides no data of any kind, let alone data that might challenge the data presented in the proposal. Turning to the commenter’s more specific methodological criticism—that 80 The 127,300-ton amount was described in the proposal as the minimum reduction in projected Texas SO2 emissions because it did not reflect a 50,500-ton increase in the Texas SO2 budget that occurred after the original CSAPR scenario was modeled. If that budget increase had been reflected in the original CSAPR scenario, modeled Texas EGU SO2 emissions in that scenario would likely have been higher, potentially by the full 50,500-ton amount. The CSAPR budget increase would have had no effect on Texas EGUs’ modeled SO2 emissions under BART. As a consequence, the 127,300-ton minimum estimate of the reduction in projected Texas SO2 emissions caused by removing Texas EGUs from CSAPR for SO2, which are computed as the difference between Texas EGUs’ collective emissions in the original CSAPR scenario and the BART scenario, may be understated by as much as 50,500 tons. 81 81 FR at 78962–64. VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 the Agency has not sufficiently considered whether shifts in the geographic distribution of emissions might lead to violations of the twopronged test—the EPA agrees that the potential for such shifts was not expressly addressed in the sensitivity analysis as proposed. For the final action, the EPA has therefore performed further analysis to address this comment, focusing on the specific circumstance identified by the commenter—shifts associated with the removal of Texas EGUs from CSAPR for SO2—because the Agency agrees that this is the most significant change to CSAPR among the actions that have been or are expected to be taken in response to the D.C. Circuit’s remand.82 The further analysis is based on stateand unit-level data disaggregated from the projections of electricity generation, fuel usage, and emissions developed for the base case, BART, and original CSAPR scenarios that were compared in the 2012 analytic demonstration.83 Based on this additional analysis, the EPA finds that, in addition to the projected SO2 emissions reduction of at least 127,300 tons in Texas identified in the proposal,84 a revised CSAPR scenario without Texas in CSAPR for SO2 could also reflect a projected aggregated increase in SO2 emissions of approximately 22,300 tons in the six other states in the CSAPR SO2 Group 2 trading program (Alabama, Georgia, Kansas, Minnesota, Nebraska, and South Carolina). The reason for this adjustment is that in the original CSAPR 82 As summarized above, the Agency explained in the proposal that the removal of Florida, North Carolina, South Carolina, and Texas EGUs from CSAPR for either seasonal or annual NOX, as applicable, would not have caused sufficient changes in modeled NOX emissions in a revised CSAPR scenario to materially alter the visibility impacts comparison, in some instances because the EGUs would remain subject to another CSAPR NOX program and in some instances because of the small magnitudes of the differences in projected total NOX emissions from the EGUs in each of those states between the original CSAPR scenario and the relevant other modeled scenarios, combined with the dominance of sulfate impacts compared to nitrate impacts on visibility (especially in the South). The EPA believes these same factors likewise indicate that the visibility impacts of any potential shifts in the geographic distribution of NOX emissions related to removal of these states from the CSAPR NOX programs would not be material to either prong of the two-pronged visibility impacts comparison. 83 The state- and plant-level data are derived from the unit-level data in three spreadsheets included in the final CSAPR-better-than-BART rulemaking record and available in the docket for this action: IPM Parsed File for CSAPR Base Case Scenario 2014 (EPA–HQ–OAR–2011–0729–0004), IPM Parsed File for National BART Scenario 2014 (EPA–HQ–OAR– 2011–0729–0008), and IPM Parsed File for CSAPR– BART Scenario 2014 (EPA–HQ–OAR–2011–0729– 0006). 84 See supra note 74. PO 00000 Frm 00072 Fmt 4700 Sfmt 4700 scenario, Texas EGUs were projected to emit 22,300 tons of SO2 in excess of the state’s SO2 budget.85 This would have been possible through the use of allowances purchased from EGUs in other SO2 Group 2 states. Under a revised CSAPR scenario where Texas EGUs are no longer part of the CSAPR trading program, Texas EGUs would no longer purchase the 22,300 allowances from the other states, and the EGUs in those other states could potentially use those allowances to increase their own collective SO2 emissions. Much or all of the total potential increase in emissions in the other states would be projected to occur in Alabama and Georgia, because in the original CSAPR scenario the collective emissions from Kansas EGUs were projected to already be at the state’s ‘‘assurance level’’—the emissions level above which EGUs trigger a CSAPR provision requiring the surrender of three allowances instead of one allowance per ton of emissions— and the collective emissions from Minnesota, Nebraska, and South Carolina EGUs were projected to already be close to their states’ respective assurance levels.86 After accounting for the potential 22,300-ton offsetting adjustment, the net regional SO2 reduction under the revised CSAPR scenario relative to the original CSAPR scenario would be projected to be approximately 105,000 tons (or more) instead of 127,300 tons (or more) as described in the proposed sensitivity analysis.87 For the reasons below, the EPA has considered both the projected decrease in Texas SO2 emissions and the projected aggregated increase in SO2 85 See ‘‘Projected Interstate Trading of CSAPR SO 2 Group 2 Allowances in the Original CSAPR Scenario,’’ available in the docket for this action. 86 Id. 87 It is possible that if the original CSAPR scenario that includes Texas in CSAPR for SO2 had been remodeled to include the 50,500 increase in the Texas SO2 budget described in the proposal and in footnote 80, Texas EGUs would have been projected to purchase either more or less than 22,300 allowances from EGUs in other CSAPR SO2 Group 2 states, and that a revised CSAPR scenario in which Texas was removed from CSAPR for SO2 would therefore have shown the other Group 2 states increasing their SO2 emissions by this different amount. Regardless of the amount or direction of any modeled change in Texas EGUs’ CSAPR allowance purchases, that change would generally have been matched by an equal and opposite change in Texas EGUs’ projected emissions under CSAPR, with the result that the overall net projected reduction in emissions caused by removing Texas from CSAPR for SO2 would continue to be at least 105,000 tons. The maximum amount of CSAPR SO2 allowances that Texas could purchase from other states and use in a given year without incurring 3-for-1 allowance surrender requirements is approximately 53,000 tons, which is the amount of Texas’ SO2 variability limit—the difference between the state’s budget and its assurance level—under the CSAPR regulations. See 40 CFR 97.710(b)(7). E:\FR\FM\29SER1.SGM 29SER1 asabaliauskas on DSKBBXCHB2PROD with RULES Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations emissions in the other states and has concluded that the two-pronged CSAPRbetter-than-BART test described above would continue to be satisfied. As summarized above, the first prong of the two-pronged test requires that visibility conditions must not decline in any Class I area. In the 2012 analytic demonstration, the EPA evaluated this prong by comparing visibility impacts at each affected Class I area under the original CSAPR scenario and the base case scenario. The situation identified by the commenter in which emissions under a revised CSAPR scenario might rise at some individual EGUs sufficiently to cause a decline in visibility at some individual Class I area relative to visibility conditions in the base case scenario—that is, without either CSAPR or BART—would be a very unusual event and likely can be ruled out as impossible, or nearly so, in a scenario such as the revised CSAPR scenario being considered. Under the base case scenario, EGUs incur no cost at all under CSAPR for emitting a ton of SO2. In contrast, under either the original CSAPR scenario or a revised CSAPR scenario, EGUs would incur some cost per ton of SO2 emissions under CSAPR, and where that new cost is the principal change from the base case scenario, EGUs that emit SO2 would generally be projected to either decrease or maintain their emissions relative to the base case scenario where that cost was not present. If in a revised CSAPR scenario, allowances are more plentiful and the cost incurred per ton of SO2 emissions therefore is less than the cost per ton under the original CSAPR scenario, some EGUs that emit SO2 would be projected to reduce their SO2 emissions by a smaller amount than in the original CSAPR scenario, but they generally would not be projected to significantly increase their emissions relative to the base case scenario. An exception to this general principle could occur if some other factor influencing EGUs’ operating decisions, such as electricity demand or relative fuel prices, also changed. The EPA therefore considered whether the removal of Texas from CSAPR could have been projected to result in any material change in demand for generation from other states or relative fuel prices in other states in a revised CSAPR scenario compared to the original CSAPR scenario.88 88 Although the analysis focuses on other CSAPR states, consistent with the concerns raised by the commenter, the EPA notes that absent changes in generation demand or relative fuel prices, removal of Texas from CSAPR would also be expected not to affect the operating decisions of EGUs in nonCSAPR states. VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 With respect to the possibility of changes in electricity demand in other states, record data show that, relative to the original CSAPR scenario, aggregated 2014 generation from fossil-fired Texas EGUs was projected to increase by 0.2% in the BART scenario (which is used here as a proxy representing the operating behavior of Texas EGUs in a revised CSAPR scenario), indicating that removal of Texas EGUs from CSAPR for SO2 and implementation of SO2 BART would not be projected to result in an increase in emissions outside Texas caused by a shift in generation from Texas to other states.89 With respect to changes in relative fuel prices in other states, record data show that, relative to the original CSAPR scenario, in the BART scenario Texas EGUs were projected to decrease their use of subbituminous coal by 68 trillion Btus (TBtu), increase their use of lignite by 66 TBtu, and increase their use of other fossil fuels (predominantly natural gas) by 11 TBtu.90 The changes in projected Texas usage of subbituminous coal and natural gas are less than 1% of the projected total industry usage of those fuels nationwide under the original CSAPR scenario, indicating that there is no reason to expect material impacts on prices or usage of those fuels in other states. Unlike subbituminous coal and natural gas, lignite is an inherently local fuel that is consumed near the point of extraction because the fuel’s low energy content per unit of weight makes shipment over long distances uneconomic. Thus, although the increase in Texas EGUs’ projected usage of lignite is fairly large (8.2% of projected national usage of lignite under the original CSAPR scenario), any resulting increase in the local prices of lignite would not be expected to affect the mix of fuels used in other states. For further confirmation of the applicability here of the general principle discussed above—namely, that in a modeled CSAPR scenario, EGUs that emit SO2 would generally be projected to either decrease or maintain their emissions and not to increase their emissions relative to the base case scenario—the EPA compared the projected unit-level SO2 emissions in 89 See ‘‘Projected Changes in Texas Emissions, Fossil Generation, and Fuel Usage Between the Base Case, BART, and Original CSAPR Scenarios,’’ available in the docket for this action. Because there is little difference in NOX emissions from Texas EGUs between the original CSAPR scenario, the BART scenario, and the base case scenario, id., the EPA considers the BART scenario a reasonable emissions proxy for a revised CSAPR scenario in which Texas EGUs would be subject to BART for SO2 but not for NOX. 90 See id. PO 00000 Frm 00073 Fmt 4700 Sfmt 4700 45493 the original CSAPR and base case scenarios for all coal-fired EGUs in the seven states in the CSAPR SO2 Group 2 trading program. The results of the comparison clearly indicate that the general principle applies in this instance: 77 Units were projected to reduce their SO2 emissions by 1,000 tons or more (in amounts up to 57,000 tons), 106 units were projected to essentially maintain their SO2 emissions (increasing or decreasing by between 0 and 1,000 tons), and 2 units were projected to increase their SO2 emissions by approximately 1,100 tons each.91 A similar comparison at the state level shows that collective SO2 emissions from the sets of EGUs in each of the seven states were also projected to decrease from the base case scenario to the original CSAPR scenario (in amounts ranging from 1,900 tons for Nebraska to 248,800 tons for Alabama).92 In combination with the data above showing that removal of Texas from CSAPR for SO2 would not be expected to cause changes in demand for generation or relative fuel prices in other states, the EPA believes that these data on how EGUs were projected to comply with CSAPR in the original CSAPR scenario indicate that in a revised CSAPR scenario where Texas is removed from CSAPR for SO2 and 22,300 additional allowances (or up to 53,000 allowances, as noted earlier 93) therefore become available to the EGUs in the other SO2 Group 2 states, few if any EGUs would respond to the availability of the additional allowances by increasing their emissions materially above their emissions in the base case scenario. Further, even if some EGUs did increase their emissions above their emissions in the base case scenario, because of the regional nature of sulfate formation from SO2 emissions and the very large decreases in SO2 emissions across the broader region, the EPA believes that any such local increase would be unlikely to cause localized visibility degradation in any Class I area near a CSAPR state affected by the removal of Texas from CSAPR for SO2. In consequence, the Agency finds it reasonable to conclude that in such a revised CSAPR scenario, no such Class I areas would experience declines in visibility conditions relative to the base case scenario. The second prong of the two-pronged test requires the average projected 91 See ‘‘Projected Changes in Unit-Level Emissions Between the Base Case and Original CSAPR Scenarios,’’ available in the docket for this action. 92 See id. 93 See supra note 87. E:\FR\FM\29SER1.SGM 29SER1 45494 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations visibility improvement across all affected Class I areas to be greater under the BART alternative than under BART. In the proposal, the EPA proposed to conclude that this prong would be easily satisfied under the revised CSAPR scenario because Texas EGUs would be modeled in the revised CSAPR scenario as subject to SO2 BART instead of being subject to CSAPR for SO2, and the record data showed that Texas EGUs’ projected SO2 emissions would be at least 127,300 tons lower under BART than under CSAPR. As discussed above, based on further analysis the EPA concludes that the decrease in projected Texas SO2 emissions could potentially be partially offset by an increase in projected SO2 emissions in other CSAPR SO2 Group 2 states, most likely Alabama or Georgia. The EPA believes that such a revised CSAPR scenario would continue to show greater average visibility improvement than the BART scenario (and greater than the original CSAPR scenario), again easily passing the second prong of the two-pronged test. Any reduction in visibility improvement in Class I areas near Alabama, Georgia, or the other Group 2 states relative to the original CSAPR scenario would be more than offset by greater visibility improvement in Class I areas near Texas.94 Due to the regional nature of sulfate particulate matter formation, it is highly likely that, like the original CSAPR scenario, the revised CSAPR scenario would show greater visibility improvement on average across all Class I areas than the BART scenario. The commenters did not present any information to indicate otherwise, and the EPA is not aware of any such information. E. Validity of 2012 Analytic Demonstration Prior to CSAPR Changes Finally, the commenter asserts that regardless of the character of the sensitivity analysis itself, the original 2012 CSAPR-better-than-BART analytic demonstration was arbitrary, rendering any sensitivity analysis performed asabaliauskas on DSKBBXCHB2PROD with RULES 94 The CSAPR-better-than-BART record shows that the Class I areas most impacted by Texas were projected to have greater modeled visibility improvement in the BART scenario (on the 20% best days) than in the CSAPR scenario. This indicates that there would have been additional visibility improvement in a revised CSAPR scenario in which Texas is not in CSAPR for SO2 and is therefore modeled at BART SO2 levels. Note that the average visibility improvements across all affected Class I areas as computed in the original CSAPR and BART scenarios are much closer on the 20% best days than on the 20% worst days. Therefore, in determining whether the second prong of the two-pronged test will be passed under a revised CSAPR scenario, the modeled results on the 20% best days are particularly important. VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 regarding the original demonstration arbitrary. In support of this claim, the commenter incorporates by reference all criticisms of the original analytic demonstration contained in the comments submitted by the commenter in the original CSAPR-better-than-BART rulemaking as well as all criticisms contained in the commenter’s brief in the pending litigation challenging the CSAPR-better-than-BART rule. The EPA rejects these comments as both improperly raised and outside the scope of this proceeding. The EPA appreciates the value of public input in the rulemaking process and seeks to fulfill its legal obligation to consider and respond to all substantive comments that are ‘‘raised with reasonable specificity,’’ 95 but catch-all references to whatever statements may have been made in another proceeding do not meet this standard. Moreover, even if they had been properly raised, comments concerning the legal validity of the original 2012 analytic demonstration are beyond the scope of this rulemaking, which concerns only the sensitivity analysis addressing the effect on the 2012 analytic demonstration of changes in CSAPR’s geographic scope resulting from the D.C. Circuit’s remand (as well as the withdrawal of Texas CSAPR FIP requirements for SO2 and annual NOX and the finding as to Texas’ remaining transport obligation under CAA section 110(a)(2)(D)(i)(I) regarding the 1997 annual PM2.5 NAAQS). Arguments concerning the original 2012 analytic demonstration should be, and have been, raised in the original CSAPRbetter-than-BART rulemaking and in the pending litigation over that rule. V. Description of Amendments to Regulatory Text In order to implement the withdrawal of the FIP provisions requiring Texas EGUs to participate in the CSAPR NOX Annual Trading Program and the CSAPR SO2 Group 2 Trading Program with regard to emissions occurring in Phase 2 of those programs, the EPA is amending the regulatory text at 40 CFR 52.38(a)(2), 52.39(c), 52.2283(c), and 52.2284(c) to provide that Texas EGUs are subject to requirements under these two programs with regard to emissions occurring in 2015 and 2016 only. Conforming amendments to crossreferences are being made at § 52.38(a)(3), (a)(4), (a)(5), (a)(6), and (a)(8)(iii) and § 52.39(g), (h), (i), (j), and (m)(3). The EPA is also clarifying the CSAPR regulations by adding the introductory 95 CAA PO 00000 section 307(d)(7)(B). Frm 00074 Fmt 4700 Sfmt 4700 headings ‘‘Annual emissions’’ and ‘‘Ozone season emissions’’ to § 52.38(a) and (b), respectively, and by amending the wording of the regulatory text at §§ 52.38(b)(2)(i) and 52.39(b) to parallel the wording of the newly amended regulatory text at §§ 52.38(a)(2)(i) and 52.39(c)(1). These editorial clarifications do not alter any existing regulatory requirements. Finally, the EPA is correcting the CSAPR regulations applicable to South Carolina EGUs by amending the regulatory text at § 52.2141(b) to reference CSAPR SO2 Group 2 allowances and 40 CFR part 97, subpart DDDDD instead of CSAPR SO2 Group 1 allowances and 40 CFR part 97, subpart CCCCC. The corrections make the text at § 52.2141(b) consistent with the existing text at § 52.2141(a), and the two paragraphs together now correctly reflect the existing regulatory requirements applicable to South Carolina EGUs as already set forth at § 52.39(c) and (k). VI. Statutory and Executive Order Reviews Additional information about these statutes and Executive Orders can be found at https://www2.epa.gov/lawsregulations/laws-and-executive-orders. A. Executive Order 12866: Regulatory Planning and Review, and Executive Order 13563: Improving Regulation and Regulatory Review This action is not a significant regulatory action and therefore was not submitted to the Office of Management and Budget (OMB) for review. B. Executive Order 13771: Reducing Regulations and Controlling Regulatory Costs This action is not expected to be an Executive Order 13771 regulatory action because this action is not significant under Executive Order 12866. C. Paperwork Reduction Act This action does not impose any new information collection burden under the Paperwork Reduction Act. The OMB has previously approved the information collection activities contained in the existing regulations and has assigned OMB control number 2060–0667. The withdrawal of the FIP provisions in this action will eliminate the obligations of Texas sources to comply with the existing monitoring, recordkeeping, and reporting requirements under the CSAPR SO2 Group 2 Trading Program and the CSAPR NOX Annual Trading Program. E:\FR\FM\29SER1.SGM 29SER1 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations D. Regulatory Flexibility Act I certify that this action will not have a significant economic impact on a substantial number of small entities under the Regulatory Flexibility Act. In making this determination, the impact of concern is any significant adverse economic impact on small entities. An agency may certify that a rule will not have a significant economic impact on a substantial number of small entities if the rule relieves regulatory burden, has no net burden, or otherwise has a positive economic effect on the small entities subject to the rule. This action withdraws existing regulatory requirements for some entities and does not impose new requirements on any entity. We have therefore concluded that this action will either relieve or have no net regulatory burden for all directly regulated small entities. while developing CSAPR. A summary of that consultation is provided in the preamble for CSAPR, 76 FR 48208, 48346 (August 8, 2011). E. Unfunded Mandates Reform Act This action does not contain any unfunded mandate as described in the Unfunded Mandates Reform Act, 2 U.S.C. 1531–1538, and does not significantly or uniquely affect small governments. The action imposes no enforceable duty on any state, local, or tribal governments or the private sector. This action simply eliminates certain federal regulatory requirements that the D.C. Circuit has held invalid. I. Executive Order 13211: Actions That Significantly Affect Energy Supply, Distribution, or Use asabaliauskas on DSKBBXCHB2PROD with RULES F. Executive Order 13132: Federalism This action does not have federalism implications. It will not have substantial direct effects on the states, on the relationship between the national government and the states, or on the distribution of power and responsibilities among the various levels of government. This action simply eliminates certain federal regulatory requirements that the D.C. Circuit has held invalid. G. Executive Order 13175: Consultation and Coordination With Indian Tribal Governments This action does not have tribal implications as specified in Executive Order 13175. It will not have substantial direct effects on tribal governments, on the relationship between the federal government and Indian tribes, or on the distribution of power and responsibilities between the federal government and Indian tribes. This action simply eliminates certain federal regulatory requirements that the D.C. Circuit has held invalid. Thus, Executive Order 13175 does not apply to this action. Consistent with the EPA Policy on Consultation and Coordination with Indian Tribes, the EPA consulted with tribal officials VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 H. Executive Order 13045: Protection of Children From Environmental Health and Safety Risks The EPA interprets Executive Order 13045 as applying only to those regulatory actions that concern environmental health or safety risks that the EPA has reason to believe may disproportionately affect children, per the definition of ‘‘covered regulatory action’’ in section 2–202 of the Executive Order. This action is not subject to Executive Order 13045 because it simply eliminates certain federal regulatory requirements that the D.C. Circuit has held invalid. This action is not subject to Executive Order 13211, because it is not a significant regulatory action under Executive Order 12866. J. National Technology Transfer Advancement Act This rulemaking does not involve technical standards. K. Executive Order 12898: Federal Actions To Address Environmental Justice in Minority Populations and Low-Income Populations The EPA believes that this action is not subject to Executive Order 12898 because it does not establish an environmental health or safety standard. This action simply eliminates certain federal regulatory requirements that the D.C. Circuit has held invalid. Consistent with Executive Order 12898 and the EPA’s environmental justice policies, the EPA considered effects on lowincome populations, minority populations, and indigenous peoples while developing CSAPR. The process and results of that consideration are described in the preamble for CSAPR, 76 FR 48208, 48347–52 (August 8, 2011). L. Congressional Review Act This action is subject to the Congressional Review Act, and the EPA will submit a rule report to each House of the Congress and to the Comptroller General of the United States. This action is not a ‘‘major rule’’ as defined by 5 U.S.C. 804(2). PO 00000 Frm 00075 Fmt 4700 Sfmt 4700 45495 M. Judicial Review and Determinations Under CAA Section 307(b)(1) and (d) CAA section 307(b)(1) indicates which federal appellate courts have venue for petitions of review of final actions by the EPA. This section provides, in part, that petitions for review must be filed in the D.C. Circuit Court of Appeals if (i) the agency action consists of ‘‘nationally applicable regulations promulgated, or final action taken, by the Administrator,’’ or (ii) such action is locally or regionally applicable, if ‘‘such action is based on a determination of nationwide scope or effect and if in taking such action the Administrator finds and publishes that such action is based on such a determination.’’ This final action is ‘‘nationally applicable.’’ In addition, the EPA finds that all aspects of this action are based on a determination of ‘‘nationwide scope and effect’’ within the meaning of section 307(b)(1). First, the EPA’s withdrawal of FIP requirements under the CSAPR program for Texas is being undertaken in response to a remand by the D.C. Circuit in litigation that challenged numerous aspects of CSAPR with implications for multiple states and resulted in the remand of fifteen budgets for thirteen states. Retaining review in the D.C. Circuit is appropriate and avoids the potential that another court is forced to interpret the remand order of a sister circuit. Also, the finding that, after the FIP withdrawal, Texas has no remaining obligation to address interstate transport with respect to the 1997 annual PM2.5 NAAQS is based on a common core of factual findings and analyses concerning the transport of pollutants between the different states subject to CSAPR, which is a nationally applicable program. Further, this action is based on a determination that modifies the scope and effect of CSAPR; thus, any judicial review of this action will necessarily implicate the national-level policies, technical analyses, or interpretations that undergird this nationwide program. Second, in express consideration of the effect of the withdrawal of Texas FIP requirements accomplished through this final action, the EPA is affirming the continued validity of 40 CFR 51.308(e)(4), a regulatory provision available to each of the 27 States whose sources currently participate in one or more CSAPR trading programs. This determination affects the rights and interests of regulated parties and other stakeholders throughout the eastern United States relying on or otherwise affected by that regulatory provision. For these reasons, this final action is nationally applicable and, in addition, E:\FR\FM\29SER1.SGM 29SER1 45496 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations the Administrator finds that this final action is based on a determination of nationwide scope and effect for purposes of section 307(b)(1). Thus, pursuant to section 307(b) any petitions for review of this action must be filed in the D.C. Circuit within 60 days from the date of publication of this action in the Federal Register. In addition, pursuant to CAA sections 307(d)(1)(B), 307(d)(1)(J), and 307(d)(1)(V), the Administrator determines that this action is subject to the provisions of section 307(d). CAA section 307(d)(1)(B) provides that section 307(d) applies to, among other things, ‘‘the promulgation or revision of an implementation plan by the Administrator under [CAA section 110(c)].’’ 42 U.S.C. 7607(d)(1)(B). Under section 307(d)(1)(J), the provisions of section 307(d) apply to the ‘‘promulgation or revision of regulations . . . relating to . . . protection of visibility.’’ 42 U.S.C. 7607(d)(1)(J). Under section 307(d)(1)(V), the provisions of section 307(d) also apply to ‘‘such other actions as the Administrator may determine.’’ 42 U.S.C. 7607(d)(1)(V). The agency has complied with the procedural requirements of CAA section 307(d) during the course of this rulemaking. CAA section 307(b)(1) also provides that filing a petition for reconsideration by the Administrator of this rule does not affect the finality of the rule for the purposes of judicial review, does not extend the time within which a petition for judicial review may be filed, and does not postpone the effectiveness of the rule. Under CAA section 307(b)(2), the requirements established by this rule may not be challenged separately in any civil or criminal proceedings brought by the EPA to enforce these requirements. List of Subjects in 40 CFR Part 52 asabaliauskas on DSKBBXCHB2PROD with RULES Environmental protection, Administrative practice and procedure, Air pollution control, Incorporation by reference, Intergovernmental relations, Nitrogen oxides, Ozone, Particulate matter, Regional haze, Reporting and recordkeeping requirements, Sulfur dioxide. Dated: September 21, 2017. E. Scott Pruitt, Administrator. For the reasons stated in the preamble, part 52 of chapter I of title 40 of the Code of Federal Regulations is amended as follows: VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 PART 52—APPROVAL AND PROMULGATION OF IMPLEMENTATION PLANS 1. The authority citation for part 52 continues to read as follows: ■ Authority: 42 U.S.C. 7401 et seq. Subpart A—General Provisions 2. Section 52.38 is amended by: a. Adding a paragraph (a) heading; b. Revising paragraph (a)(2); c. In paragraph (a)(3) introductory text, removing the text ‘‘(a)(2)’’ and in its place adding the text ‘‘(a)(2)(i) or (ii)’’; ■ d. In paragraph (a)(4) introductory text, removing the text ‘‘(a)(2)’’ and in its place adding the text ‘‘(a)(2)(i)’’; ■ e. In paragraphs (a)(5) introductory text and (a)(6), removing the text ‘‘(a)(2)’’ and in its place adding the text ‘‘(a)(2)(i)’’, and removing the text ‘‘(a)(1) through (4)’’ and in its place adding the text ‘‘(a)(1), (a)(2)(i), and (a)(3) and (4)’’; ■ f. In paragraph (a)(8)(iii), removing the text ‘‘(a)(1) through (4)’’ and in its place adding the text ‘‘(a)(1), (a)(2)(i), and (a)(3) and (4)’’; ■ g. Adding a paragraph (b) heading; and ■ h. In paragraph (b)(2)(i), after the word ‘‘emissions’’ adding the word ‘‘occurring’’. The additions and revisions read as follows: ■ ■ ■ ■ § 52.38 What are the requirements of the Federal Implementation Plans (FIPs) for the Cross-State Air Pollution Rule (CSAPR) relating to emissions of nitrogen oxides? (a) Annual emissions. * * * (2)(i) The provisions of subpart AAAAA of part 97 of this chapter apply to sources in each of the following States and Indian country located within the borders of such States with regard to emissions occurring in 2015 and each subsequent year: Alabama, Georgia, Illinois, Indiana, Iowa, Kansas, Kentucky, Maryland, Michigan, Minnesota, Missouri, Nebraska, New Jersey, New York, North Carolina, Ohio, Pennsylvania, South Carolina, Tennessee, Virginia, West Virginia, and Wisconsin. (ii) The provisions of subpart AAAAA of part 97 of this chapter apply to sources in each of the following States and Indian country located within the borders of such States with regard to emissions occurring in 2015 and 2016 only: Texas. * * * * * (b) Ozone season emissions. * * * ■ 3. Section 52.39 is amended by: ■ a. In paragraph (b), before the colon, adding the text ‘‘with regard to PO 00000 Frm 00076 Fmt 4700 Sfmt 4700 emissions occurring in 2015 and each subsequent year’’; ■ b. Revising paragraph (c); ■ c. In paragraph (g) introductory text, removing the text ‘‘(c)’’ and in its place adding the text ‘‘(c)(1) or (2)’’; ■ d. In paragraph (h) introductory text, removing the text ‘‘(c)’’ and in its place adding the text ‘‘(c)(1)’’; ■ e. In paragraphs (i) introductory text and (j), removing the text ‘‘(c)’’ two times and in its place adding the text ‘‘(c)(1)’’; and ■ f. In paragraph (m)(3), removing the text ‘‘(c)’’ and in its place adding the text ‘‘(c)(1)’’. The revision reads as follows: § 52.39 What are the requirements of the Federal Implementation Plans (FIPs) for the Cross-State Air Pollution Rule (CSAPR) relating to emissions of sulfur dioxide? * * * * * (c)(1) The provisions of subpart DDDDD of part 97 of this chapter apply to sources in each of the following States and Indian country located within the borders of such States with regard to emissions occurring in 2015 and each subsequent year: Alabama, Georgia, Kansas, Minnesota, Nebraska, and South Carolina. (2) The provisions of subpart DDDDD of part 97 of this chapter apply to sources in each of the following States and Indian country located within the borders of such States with regard to emissions occurring in 2015 and 2016 only: Texas. * * * * * Subpart PP—South Carolina § 52.2141 [Amended] 4. Section 52.2141, paragraph (b) is amended by removing the text ‘‘Group 1’’ two times and in its place adding the text ‘‘Group 2’’, and removing the text ‘‘CCCCC’’ two times and in its place adding the text ‘‘DDDDD’’. ■ Subpart SS—Texas 5. Section 52.2283 is amended by revising paragraph (c)(1) and removing and reserving paragraph (c)(2). The revision reads as follows: ■ § 52.2283 Interstate pollutant transport provisions; What are the FIP requirements for decreases in emissions of nitrogen oxides? * * * * * (c)(1) The owner and operator of each source and each unit located in the State of Texas and Indian country within the borders of the State and for which requirements are set forth under the CSAPR NOX Annual Trading Program in subpart AAAAA of part 97 of this E:\FR\FM\29SER1.SGM 29SER1 Federal Register / Vol. 82, No. 188 / Friday, September 29, 2017 / Rules and Regulations chapter must comply with such requirements with regard to emissions occurring in 2015 and 2016. * * * * * ■ 6. Section 52.2284 is amended by revising paragraph (c)(1) and removing and reserving paragraph (c)(2). The revision reads as follows: § 52.2284 Interstate pollutant transport provisions; What are the FIP requirements for decreases in emissions of sulfur dioxide? * * * * * (c)(1) The owner and operator of each source and each unit located in the State of Texas and Indian country within the borders of the State and for which requirements are set forth under the CSAPR SO2 Group 2 Trading Program in subpart DDDDD of part 97 of this chapter must comply with such requirements with regard to emissions occurring in 2015 and 2016. * * * * * [FR Doc. 2017–20832 Filed 9–28–17; 8:45 am] BILLING CODE 6560–50–P ENVIRONMENTAL PROTECTION AGENCY 40 CFR Part 52 [EPA–R07–OAR–2017–0267; FRL–9968–62– Region 7] Approval of Implementation Plans; State of Iowa; Elements of the Infrastructure SIP Requirements for the 2010 Sulfur Dioxide National Ambient Air Quality Standard (NAAQS) Environmental Protection Agency (EPA). ACTION: Direct final rule. AGENCY: The Environmental Protection Agency (EPA) is taking direct final action to approve elements of a State Implementation Plan (SIP) submission, and an amended SIP submission from the State of Iowa for the 2010 Sulfur Dioxide (SO2) National Ambient Air Quality Standard (NAAQS). Infrastructure SIPs address the applicable requirements of Clean Air Act (CAA) section 110, which requires that each state adopt and submit a SIP for the implementation, maintenance, and enforcement of each new or revised NAAQS promulgated by the EPA. These SIPs are commonly referred to as ‘‘infrastructure’’ SIPs. The infrastructure requirements are designed to ensure that the structural components of each state’s air quality management program are adequate to meet the state’s responsibilities under the CAA. asabaliauskas on DSKBBXCHB2PROD with RULES SUMMARY: VerDate Sep<11>2014 16:55 Sep 28, 2017 Jkt 241001 This direct final rule will be effective November 28, 2017, without further notice, unless EPA receives adverse comment by October 30, 2017. If EPA receives adverse comment, we will publish a timely withdrawal of the direct final rule in the Federal Register informing the public that the rule will not take effect. ADDRESSES: Submit your comments, identified by Docket ID No. EPA–R07– OAR–2017–0267, to https:// www.regulations.gov. Follow the online instructions for submitting comments. Once submitted, comments cannot be edited or removed from Regulations.gov. The EPA may publish any comment received to its public docket. Do not submit electronically any information you consider to be Confidential Business Information (CBI) or other information whose disclosure is restricted by statute. Multimedia submissions (audio, video, etc.) must be accompanied by a written comment. The written comment is considered the official comment and should include discussion of all points you wish to make. The EPA will generally not consider comments or comment contents located outside of the primary submission (i.e., on the web, cloud, or other file sharing system). For additional submission methods, the full EPA public comment policy, information about CBI or multimedia submissions, and general guidance on making effective comments, please visit https://www2.epa.gov/dockets/ commenting-epa-dockets. FOR FURTHER INFORMATION CONTACT: Heather Hamilton, Air Planning and Development Branch, U.S. Environmental Protection Agency, Region 7, 11201 Renner Boulevard, Lenexa, KS 66219 at (913) 551–7039, or by email at hamilton.heather@epa.gov. SUPPLEMENTARY INFORMATION: Throughout this document ‘‘we,’’ ‘‘us,’’ and ‘‘our’’ refer to EPA. This section provides additional information by addressing the following: DATES: I. What is being addressed in this document? II. Have the requirements for approval of a SIP revision been met? III. What action is EPA taking? IV. Statutory and Executive Order Reviews I. What is being addressed in this document? EPA is approving elements of the 2010 SO2 NAAQS infrastructure SIP submission from the State of Iowa received on July 29, 2013. Specifically, EPA is approving the following elements of section 110(a)(2): (A),(B),(C),(D)(i)(II)—prevent of PO 00000 Frm 00077 Fmt 4700 Sfmt 4700 45497 significant deterioration of air quality (prong 3), and (D)(ii), (E) through (H), and (J) through (M). A Technical Support Document (TSD) is included as part of the docket to discuss the details of this action, including analysis of how the SIP meets the applicable 110 requirements for infrastructure SIPs. II. Have the requirements for approval of a SIP revision been met? The state submission has met the public notice requirements for SIP submissions in accordance with 40 CFR 51.102. The state initiated public comment from April 6, 2013, to May 8, 2013. One comment was received and adequately addressed in the final SIP submission. This submission also satisfied the completeness criteria of 40 CFR part 51, appendix V. In addition, as explained in above preamble and in more detail in the TSD which is part of this docket, the revision meets the substantive SIP requirements of the CAA, including section 110 and implementing regulations. III. What action is EPA taking? EPA is approving elements of the July 23, 2013, infrastructure SIP submission from the State of Iowa, which addresses the requirements of CAA sections 110(a)(1) and (2) as applicable to the 2010 SO2 NAAQS. As stated above, EPA is approving the following elements of section 110(a)(2): (A),(B),(C),(D)(i)(II)— prevent of significant deterioration of air quality (prong 3), and (D)(ii), (E) through (H), and (J) through (M). Details of the submission are addressed in the TSD, included as part of the docket, and discuss this approval action. EPA is not taking action on section 110(a)(2)(I). Section 110(a)(2)(I) requires that in the case of a plan or plan revision for areas designated as nonattainment areas, states must meet applicable requirements of part D of the CAA, relating to SIP requirements for designated nonattainment areas. EPA does not expect infrastructure SIP submissions to address element (I). The specific SIP submissions for designated nonattainment areas, as required under CAA title I, part D, are subject to different submission schedules than those for section 110 infrastructure elements. EPA will take action on part D attainment plan SIP submissions through a separate rulemaking governed by the requirements for nonattainment areas, as described in part D. EPA is not taking action on section 110(a)(2)(D)(i)(I) prongs 1 and 2, and section 110(a)(2)(D)(i)(II) prong 4. We are publishing this direct final rule without a prior proposed rule because we view this as a E:\FR\FM\29SER1.SGM 29SER1

Agencies

ENVIRONMENTAL PROTECTION AGENCY

[Federal Register Volume 82, Number 188 (Friday, September 29, 2017)]
[Rules and Regulations]
[Pages 45481-45497]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-20832]


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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 52

[EPA-HQ-OAR-2016-0598; FRL-9968-46-OAR]
RIN 2060-AT16


Interstate Transport of Fine Particulate Matter: Revision of 
Federal Implementation Plan Requirements for Texas

AGENCY: Environmental Protection Agency (EPA).

ACTION: Final rule.

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SUMMARY: The Environmental Protection Agency (EPA) is finalizing 
withdrawal of the federal implementation plan (FIP) provisions that 
require affected electricity generating units (EGUs) in Texas to 
participate in Phase 2 of the Cross-State Air Pollution Rule (CSAPR) 
trading programs for annual emissions of sulfur dioxide 
(SO2) and nitrogen oxides (NOX). Withdrawal of 
the FIP requirements is intended to address a decision of the U.S. 
Court of Appeals for the District of Columbia Circuit (D.C. Circuit) 
remanding the CSAPR Phase 2 SO2 budget for Texas to the EPA 
for reconsideration. With this action, the EPA is also determining 
that, following withdrawal of the FIP requirements, sources in Texas do 
not contribute significantly to nonattainment in, or interfere with 
maintenance by, any other state with regard to the 1997 national 
ambient air quality standard (NAAQS) for fine particulate matter 
(PM2.5). Accordingly, we are also determining that the EPA 
has no obligation to issue new FIP requirements for Texas sources to 
address transported PM2.5 pollution under Clean Air Act 
(CAA) section 110(a)(2)(D)(i)(I) with regard to that NAAQS. Finally, 
the EPA is also affirming the continued validity of the Agency's 2012 
determination that participation in CSAPR meets the Regional Haze 
Rule's criteria for an alternative to the application of source-
specific best available retrofit technology (BART). The EPA has 
determined that changes to CSAPR's geographic scope resulting from the 
actions EPA has taken or expects to take in response to the D.C. 
Circuit's remand do not affect the continued validity of participation 
in CSAPR as a BART alternative, because the changes in geographic scope 
would not have adversely affected the results of the air quality 
modeling analysis upon which the EPA based the 2012 determination.

DATES: This final rule is effective on September 29, 2017.

ADDRESSES: The EPA has established a docket for this action under 
Docket ID No. EPA-HQ-OAR-2016-0598. All documents in the docket are 
listed and publicly available at https://www.regulations.gov.

FOR FURTHER INFORMATION CONTACT: Questions about the withdrawal of 
CSAPR FIP requirements for Texas EGUs should be directed to David 
Lifland, Clean Air Markets Division, Office of Atmospheric Programs, 
U.S. Environmental Protection Agency, MC 6204M, 1200 Pennsylvania 
Avenue NW., Washington, DC 20460; telephone number: (202) 343-9151; 
email address: lifland.david@epa.gov. Questions about the sensitivity 
analysis regarding CSAPR participation as a BART alternative should be 
directed to Melinda Beaver, Office of Air Quality Planning and 
Standards, U.S. Environmental Protection Agency, 109 T.W. Alexander 
Drive, Mail Code C539-04, Research Triangle Park, NC 27709; telephone 
number: (919) 541-1062; email address: beaver.melinda@epa.gov.

SUPPLEMENTARY INFORMATION: Regulated Entities. Entities regulated under 
CSAPR are fossil fuel-fired boilers and stationary combustion turbines 
that serve generators producing electricity for sale, including 
combined cycle units and units operating as part of systems that 
cogenerate electricity and other useful energy output. Regulated 
categories and entities include:

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                                                 Examples of potentially
            Category              NAICS * code     regulated industries
------------------------------------------------------------------------
Industry.......................          221112  Fossil fuel-fired
                                                  electric power
                                                  generation.
------------------------------------------------------------------------
* North American Industry Classification System.

    This table is not intended to be exhaustive, but rather provides a 
guide for readers regarding entities likely to be regulated. To 
determine whether your facility is affected by this action, you should 
carefully examine the applicability provisions in 40 CFR 97.404 and 
97.704. If you have questions regarding the applicability of CSAPR to a 
particular entity, consult the person listed in the FOR FURTHER 
INFORMATION CONTACT section above.

Table of Contents

I. Overview
II. Background
    A. History and Summary of CSAPR
    B. CSAPR Participation as a BART Alternative
III. Withdrawal of CSAPR FIP Requirements Related to Texas' 
Transport Obligations With Regard to the 1997 Annual 
PM2.5 NAAQS
    A. Summary
    B. Adequacy of Rationale for Finding No Remaining Transport 
Obligation

[[Page 45482]]

    C. Responsiveness to the D.C. Circuit's Remand Instructions
    D. Consistency of Responses To Remand Across States
    E. Consistency of Consideration of D.C. Circuit's Holding Across 
States
    F. Potential Use of Texas FIP Budgets To Address a Different 
PM2.5 NAAQS
IV. Sensitivity Analysis Regarding CSAPR Participation as a BART 
Alternative
    A. Summary
    B. Continued CSAPR Participation by Georgia and South Carolina
    C. Appropriateness of Continued Reliance on Original CSAPR-
Better-than-BART Analysis
    D. Possible Changes in the Geographic Distribution of Emissions
    E. Validity of 2012 Analytic Demonstration Prior to CSAPR 
Changes
V. Description of Amendments to Regulatory Text
VI. Statutory and Executive Order Reviews
    A. Executive Order 12866: Regulatory Planning and Review, and 
Executive Order 13563: Improving Regulation and Regulatory Review
    B. Executive Order 13771: Reducing Regulations and Controlling 
Regulatory Costs
    C. Paperwork Reduction Act
    D. Regulatory Flexibility Act
    E. Unfunded Mandates Reform Act
    F. Executive Order 13132: Federalism
    G. Executive Order 13175: Consultation and Coordination With 
Indian Tribal Governments
    H. Executive Order 13045: Protection of Children from 
Environmental Health and Safety Risks
    I. Executive Order 13211: Actions That Significantly Affect 
Energy Supply, Distribution, or Use
    J. National Technology Transfer Advancement Act
    K. Executive Order 12898: Federal Actions To Address 
Environmental Justice in Minority Populations and Low-Income 
Populations
    L. Congressional Review Act
    M. Judicial Review and Determinations Under CAA Section 
307(b)(1) and (d)

I. Overview

    The EPA promulgated CSAPR in 2011 in order to address the 
obligations of states--and of the EPA when states have not met their 
obligations--under CAA section 110(a)(2)(D)(i)(I) to prohibit air 
pollution contributing significantly to nonattainment in, or 
interfering with maintenance by, any other state with regard to several 
NAAQS, including the 1997 annual PM2.5 NAAQS.\1\ To address 
Texas' transport obligation under CAA section 110(a)(2)(D)(i)(I) with 
regard to this NAAQS, CSAPR established FIP requirements for affected 
EGUs in Texas, including statewide emissions budgets that apply to the 
EGUs' collective annual emissions of SO2 and NOX.
---------------------------------------------------------------------------

    \1\ Federal Implementation Plans; Interstate Transport of Fine 
Particulate Matter and Ozone and Correction of SIP Approvals, 76 FR 
48208 (August 8, 2011).
---------------------------------------------------------------------------

    In 2012, the EPA promulgated an amendment to the Regional Haze Rule 
allowing a state whose EGUs participate in one of the CSAPR trading 
programs for a given pollutant to rely on its sources' participation in 
CSAPR as an alternative to source-specific BART requirements--the so-
called CSAPR-better-than-BART rule, codified at 40 CFR 51.308(e)(4).\2\ 
This rule relied on a regional analytic demonstration that included an 
air quality modeling analysis comparing the projected visibility 
impacts of CSAPR implementation and BART implementation. To project 
emissions under CSAPR, the EPA assumed that the geographic scope and 
state emissions budgets for CSAPR would be implemented as finalized and 
amended in 2011 and 2012.\3\
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    \2\ Regional Haze: Revisions to Provisions Governing 
Alternatives to Source-Specific Best Available Retrofit Technology 
(BART) Determinations, Limited SIP Disapprovals, and Federal 
Implementation Plans, 77 FR 33642 (June 7, 2012).
    \3\ CSAPR was amended three times in 2011 and 2012 to add five 
states to the seasonal NOX program and to increase 
certain state budgets. 76 FR 80760 (December 27, 2011); 77 FR 10324 
(February 21, 2012); 77 FR 34830 (June 12, 2012). The CSAPR-better-
than-BART final rule reflected consideration of these changes to 
CSAPR.
---------------------------------------------------------------------------

    In July 2015, the D.C. Circuit issued a decision on a range of 
challenges to CSAPR in EME Homer City Generation, L.P. v. EPA (EME 
Homer City II), denying most claims but remanding several CSAPR 
emissions budgets to the EPA for reconsideration, including the Phase 2 
SO2 budget for Texas.\4\ Because the remand created the 
potential for changes in the geographic scope and stringency of CSAPR 
as evaluated for purposes of the 2012 comparison to BART 
implementation, the EPA recognizes that how the Agency addresses the 
remand could raise questions as to whether states and the EPA should 
continue to rely on the CSAPR-better-than-BART rule.
---------------------------------------------------------------------------

    \4\ EME Homer City Generation, L.P. v. EPA (EME Homer City II), 
795 F.3d 118, 138 (D.C. Cir. 2015). The court also remanded the 
Phase 2 SO2 budgets for three other states and the Phase 
2 seasonal NOX budgets for eleven states, including 
Texas. Id.
---------------------------------------------------------------------------

    The EPA issued a proposal to address the remand of the Texas Phase 
2 SO2 budget and to resolve any questions about continued 
reliance on the CSAPR-better-than-BART rule on November 3, 2016, and 
solicited comment on the proposal.\5\ Four commenters provided 
substantive comments, and this final rule takes those comments into 
consideration. The Agency's responses to the principal comments are 
provided below. The remaining comments are addressed in the Response to 
Comments document available in the docket for this action.
---------------------------------------------------------------------------

    \5\ Interstate Transport of Fine Particulate Matter: Revision of 
Federal Implementation Plan Requirements for Texas, Proposed Rule, 
81 FR 78954 (November 10, 2016).
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    In this final action, as proposed, the EPA is withdrawing the FIP 
provisions requiring Texas EGUs to participate in the CSAPR 
SO2 Group 2 Trading Program and the CSAPR NOX 
Annual Trading Program during Phase 2 of these programs, which began 
with 2017 emissions.\6\ Removal of Texas EGUs from Phase 2 of these 
CSAPR trading programs renders it necessary to evaluate whether EPA 
should use other means to address any remaining transport obligation 
for Texas under CAA section 110(a)(2)(D)(i)(I) with regard to the 1997 
annual PM2.5 NAAQS. However, the EPA is finalizing its 
proposed determination that Texas does not have any such remaining 1997 
annual PM2.5 NAAQS transport obligation as of the beginning 
of Phase 2 of the CSAPR trading programs for SO2 and annual 
NOX. Accordingly, the EPA is also determining that the 
Agency has no obligation to issue new FIP requirements for Texas 
sources to address transported PM2.5 pollution under CAA 
section 110(a)(2)(D)(i)(I) with regard to this NAAQS.
---------------------------------------------------------------------------

    \6\ With regard to each of the other remanded budgets, the EPA 
either has already withdrawn or expects to withdraw the FIP 
provisions requiring the EGUs in the affected states to participate 
in the corresponding CSAPR federal trading programs in Phase 2 
through other actions, as discussed in section III below.
---------------------------------------------------------------------------

    Also in this action, the EPA is concluding, based on consideration 
of the sensitivity analysis included in the proposal and additional 
analysis included in this final action, that the 2012 analytic 
demonstration supporting the conclusion that CSAPR participation 
qualifies as a BART alternative is not adversely affected by the 
actions being taken to respond to the D.C. Circuit's remand of CSAPR 
Phase 2 budgets.\7\ As a result, no revisions are needed to the CSAPR-
better-than-BART rule.
---------------------------------------------------------------------------

    \7\ In addition to this action, the full set of actions being 
taken to respond to the remand includes the 2016 CSAPR Update 
withdrawing the remanded seasonal NOX budgets for eleven 
states and establishing new seasonal NOX budgets to 
address a more recent ozone NAAQS for eight of those states, the 
action approving Alabama's SIP revision establishing state CSAPR 
trading programs for SO2 and annual NOX to 
replace the corresponding federal CSAPR trading programs, and the 
expected actions to approve proposed SIP revisions for Georgia and 
South Carolina comparable to Alabama's SIP revision (see notes 14, 
53, and 57 below). These additional actions are described in more 
detail in sections II.A and III.D below.
---------------------------------------------------------------------------

    At the same time, however, because Texas EGUs will no longer 
participate in a CSAPR SO2 trading program, Texas

[[Page 45483]]

will no longer be eligible to rely on CSAPR participation as an 
alternative to the application of source-specific SO2 BART 
for its BART-eligible EGUs under 40 CFR 51.308(e)(4). That obligation 
and any other remaining regional haze obligations for Texas are not 
addressed in this action and will need to be addressed through other 
actions as appropriate.\8\
---------------------------------------------------------------------------

    \8\ The EPA notes that under 40 CFR 51.308(e)(4), CSAPR 
implementation is available as a NOX BART alternative for 
a state whose EGUs are subject to CSAPR requirements for either 
annual NOX or seasonal NOX emissions. See 77 
FR at 33652. Texas EGUs continue to participate in a CSAPR trading 
program for seasonal NOX. In a separate proposed action, 
the EPA has proposed to address NOX BART for Texas EGUs 
through reliance on participation in CSAPR as a NOX BART 
alternative. 82 FR 917 (January 4, 2017).
---------------------------------------------------------------------------

    This final rule is effective immediately upon publication in the 
Federal Register. As discussed in section VI.L below, the EPA is 
issuing this rule under CAA section 307(d). While Administrative 
Procedure Act (APA) section 553(d)\9\ generally provides that rules may 
not take effect earlier than 30 days after they are published in the 
Federal Register, CAA section 307(d)(1) clarifies that ``[t]he 
provisions of [APA] section 553 . . . shall not, except as expressly 
provided in this section, apply to actions to which this subsection 
applies.'' Thus, APA section 553(d) does not apply to this rule. 
Nevertheless, in making this rule effective immediately upon 
publication, the EPA has considered the purposes underlying APA section 
553(d). The primary purpose of the prescribed 30-day waiting period is 
to give affected parties a reasonable time to adjust their behavior and 
prepare before a final rule takes effect. This rule does not impose any 
new regulatory requirements and therefore does not necessitate time for 
affected sources to adjust their behavior or otherwise prepare for 
implementation. Further, APA section 553(d) expressly allows an 
effective date less than 30 days after publication for a rule that 
``grants or recognizes an exemption or relieves a restriction.'' This 
rule relieves Texas EGUs of certain FIP requirements that would 
otherwise apply. Consequently, making this rule effective immediately 
upon publication is consistent with the purposes of APA section 553(d).
---------------------------------------------------------------------------

    \9\ 5 U.S.C. 553(d).
---------------------------------------------------------------------------

II. Background

A. History and Summary of CSAPR

    The EPA initially promulgated CSAPR in 2011 to address the 
obligations of states--and of the EPA when states have not met their 
obligations--under CAA section 110(a)(2)(D)(i)(I), often referred to as 
the ``good neighbor'' provision, to prohibit transported air pollution 
contributing significantly to nonattainment in, or interfering with 
maintenance by, any other state with regard to the 1997 annual 
PM2.5 NAAQS, the 2006 24-hour PM2.5 NAAQS, and 
the 1997 8-hour ozone NAAQS.\10\ To reduce transported PM2.5 
pollution, CSAPR sets limits on annual emissions of NOX and 
SO2 as precursors to PM2.5. To reduce transported 
ozone pollution during the May-September ozone season, CSAPR sets 
limits on seasonal emissions of NOX as a precursor to ozone. 
The CSAPR requirements were initially established in FIPs, but states 
can voluntarily replace the CSAPR FIPs with CSAPR state implementation 
plans (SIPs) that include equally stringent budgets.\11\ Upon approval 
of such a CSAPR SIP, the corresponding CSAPR FIP is automatically 
withdrawn.\12\
---------------------------------------------------------------------------

    \10\ See generally 76 FR 48208.
    \11\ E.g., 40 CFR 52.39(i).
    \12\ E.g., 40 CFR 52.39(j).
---------------------------------------------------------------------------

    As explained in the proposal, a number of petitioners challenged 
CSAPR, and in 2015 the D.C. Circuit issued a decision remanding the 
Phase 2 SO2 emissions budgets for Alabama, Georgia, South 
Carolina, and Texas and the Phase 2 seasonal NOX budgets for 
eleven states to the EPA for reconsideration.\13\ In response to the 
remand of the Phase 2 SO2 emissions budgets, the EPA has 
engaged the affected states to determine appropriate next steps to 
address the decision with regard to each state. As discussed in the 
proposal and also in section III below, the EPA expects that EGUs in 
Alabama, Georgia, and South Carolina will continue to participate in 
CSAPR trading programs for SO2 and annual NOX 
pursuant to approved SIP revisions (with equally stringent emissions 
budgets), making Texas the only state whose EGUs will no longer 
participate in these programs to reduce transported PM2.5 
pollution as a result of actions taken to address the remand.
---------------------------------------------------------------------------

    \13\ EME Homer City II, 795 F.3d at 138.
---------------------------------------------------------------------------

    Also as explained in the proposal, in the CSAPR Update rule issued 
in 2016, the EPA responded to the remand of eleven states' original 
Phase 2 seasonal NOX budgets (which had been established to 
address transport obligations with regard to the 1997 8-hour ozone 
NAAQS) by withdrawing the FIP provisions requiring EGUs to comply with 
those budgets for emissions after 2016.\14\ The EPA determined that 
none of those eleven states has a remaining transport obligation under 
CAA section 110(a)(2)(D)(i)(I) with regard to the 1997 8-hour ozone 
NAAQS, but for eight of those states, including Texas, the CSAPR Update 
rule also established new budgets to address transport obligations with 
regard to the more stringent 2008 8-hour ozone NAAQS.\15\ EGUs in the 
three states with remanded Phase 2 seasonal NOX budgets for 
which the EPA did not establish new budgets--Florida, North Carolina, 
and South Carolina--are no longer required to participate in a CSAPR 
trading program for seasonal NOX emissions to address ozone 
transport obligations after 2016. However, because EGUs in North 
Carolina and South Carolina\16\ are expected to continue to participate 
in a CSAPR trading program for annual NOX emissions in order 
to address PM2.5-related transport obligations, Florida is 
expected to be the only state originally covered by CSAPR for 
NOX emissions for which all such coverage is ending as a 
result of the EPA's set of actions to address the remand.\17\
---------------------------------------------------------------------------

    \14\ Cross-State Air Pollution Rule Update for the 2008 Ozone 
NAAQS (CSAPR Update), 81 FR 74504, 74576 (October 26, 2016).
    \15\ Id. at 74524.
    \16\ North Carolina EGUs remain subject to FIP provisions 
requiring participation in a CSAPR trading program for annual 
NOX emissions. The EPA's expectation that South Carolina 
EGUs will continue to participate in a CSAPR program for annual 
NOX emissions is based on South Carolina's submission of 
a SIP revision that includes such requirements, as discussed in 
sections III and V below.
    \17\ For discussion of the EPA's response to the remand of the 
Florida seasonal NOX budget, and the assessment of the 
implications of that response for the CSAPR-better-than-BART 
analytical demonstration, see 81 FR at 78962.
---------------------------------------------------------------------------

    Prior to this action, Texas EGUs have been subject to CSAPR FIP 
provisions requiring participation in the CSAPR SO2 Group 2 
Trading Program and the CSAPR NOX Annual Trading Program. 
With this action, the EPA is withdrawing the FIP provisions requiring 
Texas EGUs to participate in these CSAPR federal trading programs. 
(Although the court's decision specifically remanded only Texas' Phase 
2 SO2 budget, the court's rationale for remanding that 
budget also implicates Texas' Phase 2 annual NOX budget 
because the SO2 and annual NOX budgets were 
developed through an integrated analysis and were promulgated to meet a 
common PM2.5 transport obligation under CAA section 
110(a)(2)(D)(i)(I).) This action has no effect on the separate CSAPR 
requirements applicable to Texas EGUs relating to seasonal 
NOX emissions, which, as discussed in the preceding 
paragraph, were promulgated in the

[[Page 45484]]

CSAPR Update rule and are not subject to the D.C. Circuit's remand.

B. CSAPR Participation as a BART Alternative

    The proposal provides a detailed explanation of the Regional Haze 
Rule requirements for best available retrofit technology (BART) and the 
criteria for demonstrating that an alternative measure achieves greater 
reasonable progress than source-specific BART.\18\
---------------------------------------------------------------------------

    \18\ 81 FR at 78957.
---------------------------------------------------------------------------

    In 2012, the EPA amended the Regional Haze Rule to provide that 
participation by a state's EGUs in a CSAPR trading program for a given 
pollutant--either a CSAPR federal trading program implemented through a 
CSAPR FIP or a CSAPR state trading program implemented through an 
approved CSAPR SIP revision--qualifies as a BART alternative for those 
EGUs for that pollutant.\19\ In promulgating this CSAPR-better-than-
BART rule, the EPA relied on an analytic demonstration of the 
improvement in visibility from CSAPR implementation relative to BART 
implementation based on an air quality modeling study.\20\ Since the 
EPA promulgated this amendment, numerous states covered by CSAPR have 
come to rely on the provision through either SIPs or FIPs.\21\ 
Additionally, many states have submitted or are planning to submit SIPs 
relying on the CSAPR-better-than-BART rule for BART or visibility 
transport purposes, or to replace regional haze FIPs with SIPs.
---------------------------------------------------------------------------

    \19\ 40 CFR 51.308(e)(4); see also generally 77 FR 33642. Legal 
challenges to the CSAPR-better-than-BART rule from conservation 
groups and other petitioners are pending. Utility Air Regulatory 
Group v. EPA, No. 12-1342 (D.C. Cir. filed August 6, 2012).
    \20\ See Technical Support Document for Demonstration of the 
Transport Rule as a BART Alternative, Docket ID No. EPA-HQ-OAR-2011-
0729-0014 (December 2011) (2011 CSAPR/BART Technical Support 
Document), and memo entitled ``Sensitivity Analysis Accounting for 
Increases in Texas and Georgia Transport Rule State Emissions 
Budgets,'' Docket ID No. EPA-HQ-OAR-2011-0729-0323 (May 29, 2012), 
both available in the docket for this action.
    \21\ The EPA has promulgated FIPs relying on CSAPR participation 
for BART purposes for Georgia, Indiana, Iowa, Kentucky, Michigan, 
Missouri, Ohio, Pennsylvania, South Carolina, Tennessee, Virginia, 
and West Virginia, 77 FR at 33654, and Nebraska, 77 FR 40150, 40151 
(July 6, 2012). The EPA has approved SIPs relying on CSAPR 
participation for BART purposes for Minnesota, 77 FR 34801, 34806 
(June 12, 2012), and Wisconsin, 77 FR 46952, 46959 (August 7, 2012).
---------------------------------------------------------------------------

    As explained in the proposal, the 2012 analytic demonstration that 
CSAPR provides for greater reasonable progress than BART included Texas 
EGUs as subject to CSAPR for SO2 and annual NOX 
(as well as seasonal NOX) and included Florida EGUs as 
subject to CSAPR for seasonal NOX. The EPA recognizes that 
the treatment of these EGUs in the analysis would have been different 
if the Florida FIP withdrawal finalized in the CSAPR Update rule and 
the Texas FIP withdrawal finalized in this action had been known at the 
time of the demonstration. In order to address any potential concern 
about continuing to rely on CSAPR participation as a BART alternative 
for EGUs in the remaining CSAPR states, in the proposal for this action 
the EPA provided a sensitivity analysis explicitly addressing the 
potential effect on that demonstration of the removal of Texas and 
Florida EGUs from the relevant CSAPR trading programs in response to 
the D.C. Circuit's remand. As discussed in section IV, the sensitivity 
analysis indicates clearly that the demonstration remains valid despite 
these changes in CSAPR's geographic scope, supporting the continued 
validity of EPA's 2012 conclusion that CSAPR participation meets the 
Regional Haze Rule's criteria for a BART alternative.\22\ Consequently, 
in this action the EPA is affirming the current Regional Haze Rule 
provision at 40 CFR 51.308(e)(4) authorizing the use of CSAPR 
participation as a BART alternative for BART-eligible EGUs for a given 
pollutant in states whose EGUs continue to participate in a CSAPR 
trading program for that pollutant.
---------------------------------------------------------------------------

    \22\ With respect to each of the remanded budgets, the EPA has 
responded or expects to respond to the remand by withdrawing the FIP 
provisions requiring compliance with the remanded budget. Thus, all 
changes to CSAPR arising directly from the Agency's response to the 
remand are changes in CSAPR's geographic scope rather than changes 
in the stringency of state budgets. Although the EPA has also 
promulgated new CSAPR seasonal NOX budgets for 22 states 
(including eight states with remanded seasonal NOX 
budgets) in order to address a more stringent NAAQS, see generally 
81 FR 74504, for purposes of the sensitivity analysis the EPA has 
conservatively not considered the generally increased stringency of 
the new seasonal NOX budgets, but the EPA did consider 
the changes in CSAPR's geographic scope--that is, the fact that the 
remaining three states with remanded seasonal NOX budgets 
will no longer participate in CSAPR for seasonal NOX.
---------------------------------------------------------------------------

III. Withdrawal of CSAPR FIP Requirements Related to Texas' Transport 
Obligations With Regard to the 1997 Annual PM2.5 NAAQS

A. Summary

    In this action, as proposed, the EPA is responding to the remand of 
the CSAPR Phase 2 SO2 budget for Texas by withdrawing the 
FIP provisions requiring Texas EGUs to participate in the CSAPR 
SO2 Group 2 Trading Program and the CSAPR NOX 
Annual Trading Program with regard to emissions during Phase 2 of those 
programs, which began in 2017. In EME Homer City II, the court remanded 
the CSAPR Phase 2 SO2 budget for Texas to the EPA for 
reconsideration on the grounds that the budget may be more stringent 
than necessary to address the state's obligation under CAA section 
110(a)(2)(D)(i)(I) to reduce transported pollution with respect to the 
1997 annual PM2.5 NAAQS.\23\ Upon review of options for 
responding to the remand, the EPA has determined, for the reasons 
discussed in this section, that withdrawal of the FIP provisions 
identified above, rather than issuance of revised FIP provisions for 
Texas with a higher (i.e., less stringent) Phase 2 SO2 
budget as advocated by some commenters, is the appropriate response. 
Withdrawal of the FIP provisions related to the CSAPR SO2 
trading program encompasses withdrawal of the requirement for Texas 
EGUs to comply with the remanded Phase 2 SO2 budget, thereby 
addressing the specific rule provision remanded by the court. The EPA 
is withdrawing the FIP provisions related to annual NOX (in 
addition to the requirements related to SO2) because the 
CSAPR FIP requirements for SO2 and annual NOX 
were determined through an integrated analysis and were promulgated in 
combination to remedy covered states' PM2.5 transport 
obligations; the court's finding that CSAPR's Phase 2 requirements may 
be more stringent than necessary to address Texas' PM2.5 
transport obligation therefore implicates the state's Phase 2 budgets 
for both SO2 and annual NOX.
---------------------------------------------------------------------------

    \23\ 795 F.3d at 128-29. A more detailed discussion of how the 
EPA established the CSAPR Phase 2 SO2 budget for Texas 
and why the court found the budget invalid is included in the 
proposal for this action. 81 FR at 78958.
---------------------------------------------------------------------------

    Withdrawal of the previous CSAPR FIP requirements revives the need 
to consider Texas' transport obligation under CAA section 
110(a)(2)(D)(i)(I) with regard to the 1997 annual PM2.5 
NAAQS and to address any remaining obligation through other means. 
However, as proposed, the Agency is further determining that Texas has 
no remaining transport obligation under this CAA provision with regard 
to this NAAQS following withdrawal of the previous FIP requirements, 
and consequently is also determining that the EPA has no obligation to 
issue new FIP requirements as to Texas's transport obligation under CAA 
section 110(a)(2)(D)(i)(I) with regard to the 1997 annual 
PM2.5 NAAQS.
    In the CSAPR final rule, the EPA determined that 23 states, 
including Texas, had transport obligations with regard to the 1997 
annual PM2.5

[[Page 45485]]

NAAQS, the 2006 24-hour PM2.5 NAAQS, or both, and 
established SO2 and annual NOX emissions budgets 
for each of the states.\24\ The budgets were implemented through FIP 
provisions requiring the affected EGUs in each covered state to 
participate in CSAPR allowance trading programs. In the case of Texas, 
the PM2.5-related FIP requirements were imposed based solely 
on the state's transport obligations with regard to the 1997 annual 
PM2.5 NAAQS.\25\
---------------------------------------------------------------------------

    \24\ The EPA also determined in CSAPR and a related supplemental 
rule that 25 states, including Texas, had transport obligations with 
regard to the 1997 8-hour ozone NAAQS. In all, 28 states were 
determined to have transport obligations related to either 
PM2.5, ozone, or both. The EPA's process for determining 
states' emissions limitations under CSAPR and the associated CSAPR 
FIP requirements is described at length in the preamble to the CSAPR 
final rule. See generally 77 FR at 48222-71.
    \25\ As noted in the proposal and further discussed below, the 
modeling for the CSAPR final rule also linked Texas to a downwind 
air quality problem with regard to the 2006 24-hour PM2.5 
NAAQS, but the EPA did not rely on the linkage with regard to that 
NAAQS as a basis for establishing CSAPR FIP requirements for Texas 
EGUs. 81 FR at 78960 n.42; see also 76 FR at 48243, 48214.
---------------------------------------------------------------------------

    Following issuance of the D.C. Circuit's decision in EME Homer City 
II remanding the CSAPR Phase 2 SO2 budget for Texas, the EPA 
reevaluated its earlier conclusions regarding Texas' PM2.5 
transport obligations by reexamining the data in the final CSAPR record 
in light of the D.C. Circuit's holdings in the decision, including the 
holdings regarding the CSAPR Phase 2 seasonal NOX budgets 
for several states, as explained in the proposal.\26\ The final CSAPR 
record contained ``base case'' modeling projections of air quality at 
monitoring locations throughout the country both for 2012, the intended 
start year of Phase 1 of the CSAPR trading programs, and for 2014, the 
intended start year of Phase 2 of the programs. The base case 
projections were designed to represent projected air quality at these 
monitoring locations without any emission reductions from CSAPR. In the 
CSAPR rulemaking, the EPA used the 2012 base case air quality 
projections for purposes of identifying ozone receptors projected to 
have air quality problems and determining states that were linked to 
those receptors and that therefore might have transport obligations 
under both Phase 1 and Phase 2 of the CSAPR trading programs. However, 
in EME Homer City II, the D.C. Circuit agreed with petitioners\27\ that 
the EPA should also have considered the 2014 base case air quality 
projections for these purposes, and that in instances of receptors 
where the 2014 base case projections did not show air quality problems, 
the EPA lacked authority to require any emission reductions in Phase 2 
of the CSAPR trading programs based on linkages to those receptors only 
occurring in Phase 1 of the programs. On these grounds, the court found 
that EPA lacked authority to establish Phase 2 seasonal NOX 
emission limitations for EGUs in ten states linked solely to ozone 
receptors whose 2014 air quality projections did not show air quality 
problems.\28\
---------------------------------------------------------------------------

    \26\ 81 FR at 78960.
    \27\ See Opening Brief of Industry and Labor Petitioners on 
Remand 8, 14, EME Homer City Generation, L.P. v. EPA, No. 11-1302 
(D.C. Cir. filed December 10, 2014).
    \28\ EME Homer City II, 795 F.3d at 129-30. The court also 
remanded the Phase 2 seasonal NOX budget for an eleventh 
state (Texas), but on different grounds.
---------------------------------------------------------------------------

    While not discussed in the court's decision, the projections of 
2014 air quality for a PM2.5 receptor in Madison County, 
Illinois (the only PM2.5 receptor with projected air quality 
problems to which Texas was linked) in the final CSAPR record are 
analogous to the 2014 air quality projections for the ozone receptors 
described above, in that the air quality problems at the Madison County 
receptor were projected to be resolved in 2014 before any emission 
reductions from CSAPR. In light of the court's holding as to the legal 
import of the 2014 base case air quality projections for the ozone 
receptors described above, the EPA considered the legal import of the 
analogous 2014 base case air quality projections for the Madison County 
PM2.5 receptor with respect to Texas' PM2.5-
related obligations under CSAPR. There are three relevant record data 
elements. First, the record indicates that the only PM2.5 
receptor to which Texas is linked for purposes of determining possible 
obligations under the good neighbor provision is the receptor in 
Madison County, Illinois.\29\ Second, the projected maximum design 
value \30\ for annual PM2.5 at the Madison County receptor 
is 15.02 micrograms per cubic meter ([micro]g/m\3\) in the 2014 base 
case.\31\ Finally, the value that the EPA used to determine whether a 
particular PM2.5 receptor should be identified as having air 
quality problems that may trigger transport obligations with regard to 
the 1997 annual PM2.5 NAAQS is 15.05 [micro]g/m\3\, which is 
higher than the Madison County maximum design value in the 2014 base 
case.\32\ Thus, the reevaluation of the final CSAPR record in light of 
the D.C. Circuit's holding indicates that the record does not support a 
finding of a transport obligation for Texas under CAA section 
110(a)(2)(D)(i)(I) with regard to this NAAQS as of the beginning of 
Phase 2 of the CSAPR trading programs for SO2 and annual 
NOX, and the Agency accordingly finds that the state's 
obligation is resolved without a need for further emission reductions, 
including the emission reductions from CSAPR. The finding that Texas's 
transport obligation with regard to this NAAQS is resolved as of the 
start of Phase 2 of the CSAPR trading programs without the need for any 
emission reductions from CSAPR removes the EPA's authority to issue new 
FIP requirements for purposes of responding to the court's remand of 
the state's CSAPR Phase 2 SO2 budget. The finding likewise 
eliminates any obligation of the EPA to issue new FIP requirements 
addressing a remaining transport obligation of the state with regard to 
this NAAQS following withdrawal of the existing CSAPR FIP requirements, 
because the state has no such remaining transport obligation following 
the withdrawal.
---------------------------------------------------------------------------

    \29\ See 76 FR at 48241, tables V.D-2 and V.D-3.
    \30\ The EPA independently considered linkages to 
``nonattainment'' and ``maintenance'' receptors. If both the 
projected average design value and the projected maximum design 
values for a receptor were above the triggering threshold, the 
receptor was considered a nonattainment receptor. If the projected 
maximum design value was above the triggering threshold but the 
projected average design value was not, the receptor was considered 
a maintenance receptor. Thus, if the projected maximum design value 
was not above the triggering threshold, the receptor was not 
considered either a nonattainment receptor or a maintenance 
receptor. See 76 FR at 48233.
    \31\ See projected 2014 base case maximum annual 
PM2.5 design value for Madison County, Illinois receptor 
171191007 at B-41 of the Air Quality Modeling Final Rule Technical 
Support Document, Docket ID No. EPA-HQ-OAR-2009-0491-4140 (June 
2011) (CSAPR Final Rule Technical Support Document), available in 
the docket for this action.
    \32\ 76 FR at 48233.
---------------------------------------------------------------------------

    As noted in the proposal, the modeling for the CSAPR final rule 
also linked Texas to a downwind air quality problem with regard to the 
2006 24-hour PM2.5 NAAQS, but the EPA did not rely on the 
linkage with regard to this NAAQS as a basis for establishing CSAPR FIP 
requirements for Texas EGUs. In the proposal, the EPA indicated that 
data in the final CSAPR record, reevaluated in light of EME Homer City 
II, would show that Texas no longer has a transport obligation with 
regard to the 2006 24-hour PM2.5 NAAQS as of the beginning 
of Phase 2 of the CSAPR trading programs for SO2 and annual 
NOX, but that because Texas was not subject to CSAPR 
requirements with regard to this NAAQS, the EPA was not proposing to 
make a determination in this action as to any obligation of Texas with 
regard to this NAAQS. Nevertheless, because commenters raise the 2006 
24-hour PM2.5 NAAQS in their comments, the EPA will explain 
how the court's reasoning would apply with respect to

[[Page 45486]]

the data for this NAAQS. The analysis for the 2006 24-hour 
PM2.5 NAAQS is essentially identical to the analysis 
described above with regard to the 1997 annual PM2.5 NAAQS. 
Specifically, the Madison County receptor is the only PM2.5 
receptor to which Texas was linked for this NAAQS; \33\ the projected 
maximum design value for 24-hour PM2.5 at the Madison County 
receptor is 35.3 [micro]g/m\3\ in the 2014 base case; \34\ and the 
value that the EPA used to determine whether a particular 
PM2.5 receptor should be identified as having air quality 
problems that may trigger transport obligations with regard to the 2006 
24-hour PM2.5 NAAQS is 35.5 [micro]g/m\3\, which is higher 
than the Madison County maximum design value in the 2014 base case.\35\ 
Thus, the reevaluation of the final CSAPR record in light of the D.C. 
Circuit's holding also indicates that the record would not support a 
finding of a transport obligation for Texas with regard to the 2006 24-
hour PM2.5 NAAQS as of the beginning of Phase 2 of the CSAPR 
trading programs for SO2 and annual NOX.
---------------------------------------------------------------------------

    \33\ See 76 FR at 48242-44, tables V.D-5 and V.D-6.
    \34\ See projected 2014 base case maximum 24-hour 
PM2.5 design value for Madison County, Illinois receptor 
171191007 at B-70 of the CSAPR Final Rule Technical Support 
Document, available in the docket for this action.
    \35\ 76 FR at 48234-35.
---------------------------------------------------------------------------

    Overall, on the subject of the proposed withdrawal of the FIP 
provisions and the proposed finding that Texas will no longer have a 
transport obligation following withdrawal of the FIP provisions, the 
EPA received substantive comments from two parties.\36\ The remainder 
of this section summarizes these commenters' principal comments on this 
topic and provides the Agency's response.
---------------------------------------------------------------------------

    \36\ A third commenter states without further elaboration that 
it does not oppose the FIP withdrawal.
---------------------------------------------------------------------------

B. Adequacy of Rationale for Finding No Remaining Transport Obligation

    The commenters state that the Agency's explanation for the proposed 
finding that Texas no longer has a transport obligation under CAA 
section 110(a)(2)(D)(i)(I) with regard to the 1997 annual 
PM2.5 NAAQS as of the beginning of Phase 2 of the CSAPR 
trading programs for SO2 and annual NOX is 
inadequate or confusing, and that the Agency must provide additional 
explanation for changing its position on the continued existence of a 
Texas transport obligation from the contrary position taken by the 
Agency when promulgating the CSAPR final rule.
    The EPA disagrees with these comments. The proposal contained a 
complete explanation of the Agency's basis for this finding, including 
all necessary supporting data and documentation.\37\ As fully explained 
in the proposal and reiterated above, the Agency's change in position 
as to Texas' transport obligation between the CSAPR final rule and this 
action is readily attributable to the D.C. Circuit's holding in EME 
Homer City II with regard to the legal import of the 2014 base case air 
quality projections in the final CSAPR record. The court's holding 
clarifies the legal standard the Agency should have used when 
considering the information in the final CSAPR record, which includes 
those air quality projections.
---------------------------------------------------------------------------

    \37\ 81 FR at 78960.
---------------------------------------------------------------------------

C. Responsiveness to the D.C. Circuit's Remand Instructions

    The commenters assert that withdrawal of the remanded Texas 
SO2 budget without issuance of a presumably less stringent 
replacement budget is not responsive to the D.C. Circuit's remand 
instructions. According to the commenters, the court directed the EPA 
to develop a revised CSAPR FIP SO2 budget for Texas EGUs 
that does not over-control, and the EPA must either do so or, 
alternatively, must allow Texas to submit a CSAPR SIP with a higher 
SO2 budget. The commenters' argument is intended to provide 
a continued basis for reliance on CSAPR participation as an 
SO2 BART alternative for Texas EGUs. Underlying the 
commenters' arguments is an apparent belief that a revised, higher 
CSAPR budget, whether issued through a FIP or approved through a SIP, 
would automatically enable Texas to rely on CSAPR participation as an 
alternative to source-specific SO2 BART requirements for the 
State's EGUs under 40 CFR 51.308(e)(4).
    The EPA disagrees with these comments. As an initial matter, the 
D.C. Circuit in fact did not direct the Agency to develop replacement 
budgets for the Texas SO2 budget or any of the other 
remanded CSAPR Phase 2 budgets. Rather, the court found that certain 
budgets were invalid and remanded to the EPA to ``reconsider'' 
them,\38\ a general instruction that encompasses a range of possible 
Agency actions upon reconsideration. The commenters cite no statement 
from the court's opinion that requires the establishment of replacement 
budgets, but assert that such a requirement must be inferred from the 
court's other statements or determinations. For example, the commenters 
suggest that because the court remanded the budgets without vacatur 
instead of vacating the budgets outright, the court must have intended 
for the Agency to replace rather than simply withdraw the budgets. 
However, the court actually provided a different rationale for 
remanding without vacatur, including the statement that ``some good 
neighbor obligations may be appropriate for some of the relevant 
states.'' \39\ The reference to ``some'' of the states indicates that 
the court considered it likely that replacement budgets would not be 
established in every instance, and the use of the word ``may'' 
indicates that the court considered it possible that replacement 
budgets would not be established in any instance. Thus, contrary to the 
commenters' claims, the court's opinion clearly affords the Agency the 
discretion to determine the appropriate response to the remand and does 
not prevent the Agency from determining upon reconsideration that the 
program is no longer needed for a particular state with respect to a 
particular pollutant and consequently not establishing a replacement 
budget.
---------------------------------------------------------------------------

    \38\ EME Homer City II, 795 F.3d at 124, 138.
    \39\ Id. at 132 (emphasis added).
---------------------------------------------------------------------------

    The commenters make several additional arguments in support of 
their contention that the FIP withdrawal is not responsive to the D.C. 
Circuit's instructions. One commenter asserts that because the court 
stated that the Agency could consider new information in responding to 
the remand, the court must have intended for the Agency's response to 
involve the establishment of replacement budgets. This claim is a non 
sequitur--the court's acknowledgement that additional information may 
be considered says nothing about what the Agency may or must conclude 
from consideration of that information. The same commenter also asserts 
that the Agency may not rely on lack of FIP authority as the basis for 
not establishing a revised budget because lack of FIP authority was not 
the basis cited by the court for remanding the budget. This claim is 
also a non sequitur--the Agency lacks authority to issue a revised 
budget and therefore may not do so, regardless of what additional 
defects the court may have cited in ordering the remand.
    The other commenter asserts that the FIP withdrawal would disrupt 
allowance markets, contrary to the concern expressed by the D.C. 
Circuit that outright vacatur, rather than remand without vacatur, 
could have that impact. While the EPA agrees with the concern expressed 
by the court and the commenter regarding the potentially disruptive 
effects of outright vacatur on

[[Page 45487]]

allowance markets, the Agency does not agree that the court's concern 
regarding unintended consequences of a judicial vacatur provides a 
basis for not taking final action at this time to withdraw the Texas 
FIP requirements, for two reasons. First, the EPA believes that the 
court did not intend for its expression of concern to constrain the 
Agency's range of possible responses to the remand. As discussed above, 
it is clear from the opinion that the court anticipated the possibility 
that upon reconsideration the EPA would determine that some, or even 
all, of the remanded budgets should be withdrawn and not replaced. 
Second, in this instance, emissions data reported by the EGUs covered 
by the CSAPR trading programs for SO2 and annual 
NOX demonstrate that withdrawal of the FIP provisions 
requiring Texas EGUs to participate in these programs will not cause 
allowance market disruption for the programs' remaining participants. 
Under both programs, the totals of the emissions reported by 
participating EGUs for both 2015 and 2016 in states other than Texas 
were less than the sums of the Phase 2 emissions budgets for these 
other states.\40\ Likewise, under both programs the totals of the 
emissions reported by Texas EGUs for both 2015 and 2016 were less than 
the Texas Phase 2 budgets.\41\ The elimination from the programs of 
Texas EGUs and the allowances allocated to Texas EGUs is therefore not 
expected to cause either shortages of allowances available for purchase 
by EGUs in the other states or the loss of an important market for sale 
of surplus allowances by EGUs in the other states. In these 
circumstances, the EPA anticipates that the FIP withdrawal will have 
little impact on the allowance market in either trading program.
---------------------------------------------------------------------------

    \40\ See ``2015-2016 Compliance Summary for CSAPR SO2 
Group 2 and NOX Annual Trading Programs,'' available in 
the docket for this action.
    \41\ Id.
---------------------------------------------------------------------------

    With regard to the two commenters' preferred response to the 
remand--that the EPA establish a revised, less stringent SO2 
budget for Texas EGUs and implement that budget through a revised FIP--
such an action is infeasible because the Agency lacks the necessary 
legal authority. In this action, the EPA is finalizing the proposed 
finding that Texas no longer has a transport obligation under CAA 
section 110(a)(2)(D)(i)(I) for the 1997 annual PM2.5 NAAQS. 
That finding addresses the deficiency in the Texas SIP that was the 
basis for issuance of the withdrawn FIP requirements and, therefore, 
because there is no longer a deficiency, the Agency no longer has 
authority to issue revised FIP requirements.\42\ The reasons for the 
finding are discussed above and were discussed at length in the 
proposal.\43\
---------------------------------------------------------------------------

    \42\ See CAA section 110(c).
    \43\ 81 FR at 78960.
---------------------------------------------------------------------------

    With regard to the commenters' suggested alternative response to 
the remand--that the EPA allow Texas to submit a CSAPR SIP with a 
higher SO2 budget in order to allow the state to rely on 
CSAPR participation as an SO2 BART alternative even if the 
state's EGUs are no longer subject to a CSAPR FIP SO2 
budget--the comment is not properly directed to the EPA, because Texas 
has not expressed interest in submitting a CSAPR SIP.\44\ Moreover, 
even if consideration of Texas' BART obligations were relevant for our 
action on remand, reliance on CSAPR participation with a higher budget 
would not automatically qualify as an SO2 BART alternative 
under the terms of the CSAPR-better-than-BART rule. That rule allows a 
state to rely on its EGUs' participation in a CSAPR SIP trading program 
only if the EPA approves the SIP as ``meeting the requirements of'' the 
CSAPR regulations at 40 CFR 52.38 and 52.39.\45\ As relevant here, the 
CSAPR regulations at Sec.  52.39 expressly preclude a state's 
SO2 emissions budget from exceeding the SO2 
emissions budget established under the CSAPR FIP trading program that 
the CSAPR SIP trading program would replace.\46\ Thus, even if the D.C. 
Circuit's remand could serve as a basis for the EPA to approve a SIP 
revision that does not satisfy Sec.  52.39 on the grounds that the 
state's transport obligations can be addressed by a less stringent 
budget, the CSAPR-better-than-BART rule at 40 CFR 51.308(e)(4) would 
not be satisfied. A SIP approved on such a basis could in theory 
provide a mechanism for Texas EGUs to participate in CSAPR with a 
higher SO2 budget than the remanded FIP budget despite the 
Agency's lack of authority to set a revised SO2 budget 
through a revised FIP. However, because of the increased SO2 
budget, such a SIP would not ``meet[] the requirements of . . . Sec.  
52.39'' and therefore would not allow the state to rely on its EGUs' 
participation in the CSAPR SIP trading program as an alternative to 
source-specific BART for SO2.\47\
---------------------------------------------------------------------------

    \44\ Texas did not submit comments on the proposal for this 
action.
    \45\ 40 CFR 51.308(e)(4).
    \46\ 40 CFR 52.39(i)(1)(i).
    \47\ To the extent the commenters are suggesting that the D.C. 
Circuit's holdings in EME Homer City II require the Agency to find 
that a SIP with a revised, higher SO2 budget would 
somehow satisfy the CSAPR-better-than-BART rule despite its plain 
language, the Agency disagrees. The court held that the remanded 
budgets may over-control relative to the states' transport 
obligations, but did not determine that the budgets are more 
stringent than necessary to serve as an alternative to source-
specific BART. Further, the CSAPR-better-than-BART rule rests on an 
evaluation of the projected visibility impacts from CSAPR 
implementation assuming the final CSAPR Phase 2 budget stringencies 
(including the 2012 CSAPR budget revisions, which were accounted for 
in the analysis for the final CSAPR-better-than-BART rule). Given 
this, continuing to enforce the CSAPR-better-than-BART rule's 
requirement that a state's participation in CSAPR through a SIP must 
``meet[] the requirements of . . . Sec.  52.39''--including the 
requirement for a state budget no less stringent than was analyzed 
for purposes of promulgating the rule--is entirely reasonable.
---------------------------------------------------------------------------

D. Consistency of Responses to Remand Across States

    One commenter states that by withdrawing the FIP requirements the 
EPA is arbitrarily singling Texas out as the only state with a remanded 
CSAPR budget whose EGUs will lose the ability to rely on CSAPR 
participation as a BART alternative. The commenter further asserts that 
the Agency's ``sole purpose'' in withdrawing the FIP requirements is to 
facilitate the imposition of source-specific SO2 BART 
requirements on Texas EGUs through a different action.
    The EPA disagrees with these comments, which are entirely contrary 
to the record. First, on the question of uniform application of the 
CSAPR-better-than-BART regulations, no state whose EGUs do not 
participate in a CSAPR trading program for a given pollutant can rely 
on CSAPR participation as a BART alternative for that pollutant. In 
response to the D.C. Circuit's remand of CSAPR Phase 2 budgets, the EPA 
has withdrawn or expects to withdraw all fifteen remanded budgets. As 
explained in the proposal, in thirteen instances, the state will retain 
eligibility to rely on the CSAPR-better-than-BART rule for the 
pollutant in question through either the EPA's establishment of a new 
CSAPR budget to address a more stringent NAAQS (eight seasonal 
NOX budgets), the state's sources' continued participation 
in a different CSAPR trading program for the same pollutant (two 
seasonal NOX budgets), or the state's voluntary adoption in 
a SIP revision of a CSAPR state budget as stringent as the remanded 
CSAPR FIP budget (three SO2 budgets).\48\ In the remaining 
two instances where a remanded budget is being withdrawn and none of 
the three options for preserving eligibility to rely on CSAPR-better-
than-BART applies--Texas' SO2 budget and Florida's seasonal 
NOX budget--the state is losing the

[[Page 45488]]

opportunity to rely on CSAPR participation as a BART alternative for 
that pollutant.\49\ Thus, Texas is being treated the same as every 
other state with respect to use of the CSAPR-better-than-BART rule.\50\
---------------------------------------------------------------------------

    \48\ 71 FR at 78956-57.
    \49\ As noted in the proposal, 81 FR at 78962, n.55, the EPA has 
already approved the incorporation into Florida's SIP of 
determinations regarding source-specific NOX BART. 77 FR 
71111, 71113-14 (November 29, 2012); 78 FR 53250, 53267 (August 29, 
2013).
    \50\ As a further example of the consistent treatment of Texas, 
the EPA notes that, despite the withdrawal of the Texas FIP 
requirements relating to annual NOX emissions, the state 
will be able to continue to rely on the CSAPR-better-than-BART rule 
for NOX as long as the state's EGUs continue to 
participate in a CSAPR trading program for seasonal NOX 
emissions. See 81 FR at 78955 n.4 and 78956 n.7.
---------------------------------------------------------------------------

    Second, on the question of the EPA's purpose in withdrawing the FIP 
requirements, that purpose is to address the court's remand. As 
explained in the proposal, before initiating this action, the EPA 
communicated with officials in all four states with remanded 
SO2 budgets--Alabama, Georgia, South Carolina, and Texas--
regarding the EPA's intent to respond to the remand of the Phase 2 
SO2 budgets by withdrawing the FIP provisions requiring the 
states' EGUs to participate in the CSAPR federal trading programs for 
SO2 and annual NOX.\51\ The EPA explained that 
each state would lose its ability to rely on CSAPR participation as a 
BART alternative for SO2 and/or NOX if its EGUs 
no longer participated in the CSAPR trading programs, but that the 
state could preserve that ability, if desired, by submitting a CSAPR 
SIP revision replacing the CSAPR federal trading programs with CSAPR 
state trading programs applying state-established budgets no less 
stringent than the remanded federally-established budgets (i.e., 
budgets consistent with the 2012 CSAPR-better-than-BART analytic 
demonstration).\52\ Alabama, Georgia, and South Carolina indicated 
their preference to pursue the SIP revision option. The EPA approved 
Alabama's CSAPR SIP revision in 2016 and, accordingly, the FIP 
provisions requiring its EGUs to participate in the CSAPR federal 
trading programs for SO2 and annual NOX have been 
automatically withdrawn.\53\ Georgia and South Carolina committed to 
the EPA in 2016 to submit similar CSAPR SIP revisions by deadlines 
falling in September 2017 and August 2017, respectively.\54\ Georgia 
has in fact now submitted its SIP to the EPA for approval,\55\ South 
Carolina has submitted its proposed state CSAPR trading program rules 
and has requested that the EPA begin the SIP approval process under the 
Agency's parallel processing procedure,\56\ and the EPA has proposed to 
approve both SIP revisions.\57\ The CSAPR FIP provisions remain in 
place for the time being for EGUs in Georgia and South Carolina, and 
the EPA is not proposing their withdrawal at this time based on the 
reasonable expectation that such withdrawal will be automatically 
accomplished as a result of the Agency's action on those states' SIP 
submittals, just as with Alabama.\58\ Because Texas has indicated that 
it will not submit a CSAPR SIP revision, the EPA is proceeding with 
this action to withdraw the FIP requirements for Texas EGUs, consistent 
with the intended approach previously communicated to officials for all 
four states. Texas has had the same set of options available to all 
four states with remanded SO2 budgets and has selected a 
different option than the other three states.
---------------------------------------------------------------------------

    \51\ See memo entitled ``The U.S. Environmental Protection 
Agency's Plan for Responding to the Remand of the Cross-State Air 
Pollution Rule Phase 2 SO2 Budgets for Alabama, Georgia, 
South Carolina and Texas'' from Janet G. McCabe, EPA Acting 
Assistant Administrator for Air and Radiation, to EPA Regional Air 
Division Directors (June 27, 2016), available in the docket for this 
action. The memo directs the Regional Air Division Directors to 
share the memo with state officials. The EPA also communicated 
orally with officials in Alabama, Georgia, South Carolina, and Texas 
in advance of the memo.
    \52\ Although the D.C. Circuit remanded the states' Phase 2 
SO2 budgets because it determined that the budgets may be 
more stringent than necessary to address the states' identified 
PM2.5 transport obligations, nothing in the court's 
decision affects the states' authority to seek incorporation into 
their SIPs of state-established budgets as stringent as the remanded 
federally-established budgets or limits the EPA's authority to 
approve such SIP revisions. See CAA sections 116, 110(k)(3).
    \53\ Air Plan Approval; Alabama; Cross-State Air Pollution Rule, 
81 FR 59869 (August 31, 2016).
    \54\ See letters to Heather McTeer Toney, Regional 
Administrator, EPA Region 4, from Judson H. Turner, Director of the 
Environmental Protection Division, Georgia Department of Natural 
Resources (May 26, 2016) and from Myra C. Reece, Director of 
Environmental Affairs, South Carolina Department of Health and 
Environmental Control (April 19, 2016), available in the docket for 
this action. The EPA has conditionally approved the CAA section 
110(a)(2)(D)(i)(II) prong 4 visibility element for multiple NAAQS in 
the Georgia and South Carolina SIPs based on each state's commitment 
to submit a CSAPR SIP revision. 81 FR 65899, 65900 (September 26, 
2016) (Georgia); 81 FR 56512, 56513 (August 22, 2016) (South 
Carolina). Each state committed to submit its CSAPR SIP revision 
within one year of the date of the Agency's final conditional 
approval of the state's prong 4 SIP revision. Failure of a state to 
meet a commitment serving as the basis for a conditional SIP 
approval results in automatic conversion of the conditional approval 
to a disapproval.
    \55\ See letter to V. Anne Heard, Acting Regional Administrator, 
EPA Region 4, from Richard E. Dunn, Director, Environmental 
Protection Division, Georgia Department of Natural Resources (July 
26, 2017), available in the docket for this action.
    \56\ See letter to V. Anne Heard, Acting Regional Administrator, 
EPA Region 4, from Myra C. Reece, Director of Environmental Affairs, 
South Carolina Department of Health and Environmental Control (May 
26, 2017), available in the docket for this action. Under the 
parallel processing procedure, the EPA works closely with the state 
agency during regulatory development, and the state submits a copy 
of its proposed regulations to the EPA before completion of the 
state's public notice and adoption process. The EPA reviews the 
proposed state action, prepares a notice of proposed EPA action 
(approval or disapproval) for publication in the Federal Register, 
and provides public notice concurrently with the state's process. 
After the state adopts its final regulations and submits its formal 
SIP revision request, the EPA reviews the SIP submission for changes 
from proposal and either prepares a notice of final EPA action or, 
if the state has made significant changes, may re-propose before 
taking final EPA action. The public comment period on South 
Carolina's proposed regulations ended on June 26, 2017, and the 
state expects its final regulations to become effective in August 
2017. Id.
    \57\ Air Plan Approval; Georgia; Cross-State Air Pollution Rule, 
82 FR 38866 (August 16, 2017); Air Plan Approval; South Carolina; 
Cross-State Air Pollution Rule, 82 FR 37389 (August 10, 2017).
    \58\ If the EPA disapproves Georgia's or South Carolina's SIP 
submittal, the EPA will propose to withdraw the FIP provisions 
requiring that state's EGUs to participate in the CSAPR federal 
trading programs for SO2 and annual NOX, 
consistent with the action taken here for Texas EGUs.
---------------------------------------------------------------------------

E. Consistency of Consideration of D.C. Circuit's Holding Across States

    One commenter asserts that the EPA has not analyzed whether other 
states covered by CSAPR are linked only to receptors for which the 2014 
base case projections do not show air quality problems, and that ``[b]y 
not performing that analysis, the EPA is arbitrarily singling Texas out 
for removal from the CSAPR program.''
    The EPA disagrees with these comments. With respect to the budgets 
that were not remanded by the court, the Agency has confirmed for each 
such budget that the state is linked to at least one receptor for which 
the base case 2014 air quality projections showed air quality problems. 
The court's holding as to lack of authority to establish Phase 2 
emission reduction requirements for a state in the absence of any 
linkage to a projected air quality problem in the 2014 base case 
therefore does not extend to these budgets.\59\
---------------------------------------------------------------------------

    \59\ See 76 FR at 48241-44, tables V.D-2, V.D-3, V.D-5, and V.D-
6 (annual and 24-hour PM2.5 linkages); id. at 48246, 
tables V.D-8 and V.D-9 (ozone linkages); CSAPR Final Rule Technical 
Support Document at B-35 to B-92 (2014 base case maximum design 
values for annual and 24-hour PM2.5); id. at B-4 to B-34 
(2014 base case maximum design values for ozone). As discussed 
above, the relevant triggering values for annual and 24-hour 
PM2.5 are 15.05 [micro]g/m\3\ and 35.5 [micro]g/m\3\, 
respectively. The relevant triggering value for ozone is 85 parts 
per billion (ppb). 76 FR at 48236.
---------------------------------------------------------------------------

    With respect to the remanded budgets, the EPA again rejects the 
suggestion that Texas is being treated differently than any other 
state. As noted in the response above to the comments concerning the 
consistency of the Agency's responses to the remand,

[[Page 45489]]

the FIP requirements to comply with all the remanded budgets, not just 
the remanded Texas SO2 budget, have been withdrawn or are 
expected to be withdrawn. Further, as discussed above, in the cases of 
ten of the eleven remanded seasonal NOX budgets, the absence 
of air quality problems at the relevant receptors in the 2014 base case 
projections was expressly cited by the court as the basis for remanding 
the budgets. The EPA's reliance on the court's holding as applied to 
those states' ozone-related transport obligations with regard to the 
1997 8-hour ozone NAAQS is indistinguishable from the EPA's reliance on 
the same holding as applied to Texas' PM2.5-related 
transport obligations with regard to the 1997 annual PM2.5 
NAAQS.\60\
---------------------------------------------------------------------------

    \60\ In the case of the last remanded seasonal NOX 
budget--for Texas--the court remanded the budget on different 
grounds, and the EPA subsequently determined through further 
analysis that the state has no remaining transport obligation under 
CAA section 110(a)(2)(D)(i)(I) with respect to the 1997 8-hour ozone 
NAAQS. See 81 FR at 74524. In the cases of the remanded 
SO2 budgets for Alabama, Georgia, and South Carolina, the 
states are adopting equally stringent CSAPR SIP budgets to replace 
the withdrawn FIP budgets in order to preserve the states' options 
to rely on the CSAPR-better-than-BART rule, thereby rendering moot 
any questions about the states' remaining transport obligations and 
EPA's authority or obligation to issue revised FIP budgets to 
address such transport obligations.
---------------------------------------------------------------------------

F. Potential Use of Texas FIP Budgets To Address a Different PM2.5 
NAAQS

    Finally, the commenters state that the EPA should consider Texas's 
obligations to address interstate transport with respect to the 2006 
24-hour PM2.5 NAAQS and/or the 2012 annual PM2.5 
NAAQS before withdrawing Texas' FIP obligations. As noted in the 
proposal and discussed above, in the case of Texas, CSAPR FIP 
obligations related to PM2.5 pollution were established with 
respect to the 1997 annual PM2.5 NAAQS only, even though for 
other states the CSAPR FIPs were based on the states' transport 
obligations with respect to both the 1997 annual PM2.5 NAAQS 
and the 2006 24-hour PM2.5 NAAQS.\61\ The commenters assert 
that failure to consider Texas' potential transport obligations with 
respect to the 2006 24-hour PM2.5 NAAQS now before 
withdrawing the FIP obligations would be inconsistent with the manner 
in which the EPA responded to the D.C. Circuit's remand of seasonal 
NOX budgets and inconsistent with data in the CSAPR record 
that links Texas to downwind air quality problems with respect to the 
2006 24-hour PM2.5 NAAQS.\62\
---------------------------------------------------------------------------

    \61\ See 81 FR at 78960 n.42; see also 76 FR at 48213, table 
III-1.
    \62\ One of the commenters asserts that ``under EPA's own 
theory,'' the existence of this data in the CSAPR final record 
mandates that the EPA consider the state's transport obligations 
with respect to the 2006 24-hour PM2.5 NAAQS before 
withdrawing the FIP requirements. Wrongly attributing this 
``theory'' to the Agency, the commenter ignores other factors the 
Agency must take into account before promulgating FIP requirements, 
such as whether a statutory condition establishing FIP authority has 
been satisfied. In any event, for this final action the Agency has 
expressly considered (and rejected) the option of leaving the Texas 
FIP requirements in place to address the state's transport 
obligations with respect to this NAAQS, as discussed in this 
section.
---------------------------------------------------------------------------

    The EPA disagrees with this comment for three reasons. First, as 
noted above, the Agency is responding to the court's remand of all 
fifteen CSAPR Phase 2 SO2 and seasonal NOX 
budgets in the same way, namely by withdrawing the FIP provisions 
requiring affected EGUs to comply with the remanded budgets.\63\ The 
differences noted by the commenters are differences only in the actions 
that are being coordinated with the responses, not differences in the 
responses themselves.
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    \63\ As discussed in the proposal, addressing the remanded 
budgets by withdrawing the FIP requirements is also fully consistent 
with the manner in which EPA has responded to previous judicial 
remands regarding obligations of individual states under other EPA 
rules addressing multiple states' transport obligations. 81 FR at 
78959.
---------------------------------------------------------------------------

    Second, the differences in the coordinated actions are reasonable 
given the differences in other regulatory activities being undertaken 
for the two pollutants. The EPA coordinated the withdrawal of the 
eleven remanded seasonal NOX budgets addressing the 1997 8-
hour ozone NAAQS with the establishment of new budgets for eight of 
those states addressing the 2008 8-hour ozone NAAQS because a 
rulemaking to address transported pollution with respect to the 2008 8-
hour ozone NAAQS was actively under development at the time of the 
court's decision.\64\ Under this circumstance, such coordination was 
efficient and fully consistent with the court's expressed intent to 
minimize market disruption and to continue to address statutory 
obligations to reduce transported pollution where appropriate. In 
contrast, no analogous opportunity is available to coordinate 
withdrawal of the remanded SO2 budgets with another 
rulemaking addressing a more recent PM2.5 NAAQS because 
states' transport obligations with respect to the 2006 24-hour 
PM2.5 NAAQS have already been largely addressed through 
either SIPs or the CSAPR rulemaking, and the Agency has not identified 
interstate transport problems with respect to the 2012 annual 
PM2.5 NAAQS sufficient to justify a new national rulemaking 
at this time.
---------------------------------------------------------------------------

    \64\ As noted in the proposal, for three of the eleven states 
with remanded seasonal NOX budgets addressing the 1997 8-
hour ozone NAAQS--Florida, North Carolina, and South Carolina--the 
EPA found no transport obligations with respect to the 2008 8-hour 
ozone NAAQS and did not establish seasonal NOX budgets 
addressing that NAAQS. 81 FR at 78959.
---------------------------------------------------------------------------

    Third, the EPA lacks authority to rely on a transport obligation 
for Texas with respect to either the 2006 24-hour PM2.5 
NAAQS or the 2012 annual PM2.5 NAAQS as the legal basis to 
support imposing an SO2 budget for the state via a FIP. 
Under CAA section 110(c), the Agency's authority to issue a FIP with 
respect to a particular state obligation arises either when the Agency 
finds that a state has failed to submit a required SIP or when the 
Agency disapproves a submitted SIP. Neither of these predicate events 
has occurred with regard to Texas' transport obligations under either 
the 2006 24-hour PM2.5 NAAQS or the 2012 annual 
PM2.5 NAAQS.\65\ Commenters are correct that data in the 
final CSAPR record, as evaluated by the Agency when CSAPR was 
promulgated, showed that PM2.5 pollution transported from 
Texas to downwind states exceeded the minimum threshold level used to 
establish which states might have transport obligations for the 2006 
24-hour PM2.5 NAAQS. However, as noted in the proposal \66\ 
and discussed above, the 2014 base case air quality projections in the 
final CSAPR record, when reevaluated in light of the D.C. Circuit's 
holdings in EME Homer City II, would support a finding that as of the 
beginning of Phase 2 of the CSAPR trading programs for SO2 
and annual NOX, Texas does not have an ongoing transport 
obligation with respect to the 2006 24-hour PM2.5 NAAQS. 
Thus, even if the EPA had taken final action disapproving Texas' 
outstanding SIP submission addressing transported pollution with regard 
to the 2006 24-hour PM2.5 NAAQS, such a disapproval would no 
longer provide a basis for the Agency to issue a FIP in this instance, 
because without any remaining transport obligation, there is no 
remaining SIP deficiency to address through a FIP.
---------------------------------------------------------------------------

    \65\ Texas has submitted SIPs intended to address its transport 
obligations under each of these NAAQS. In the case of the 2006 24-
hour PM2.5 NAAQS, the EPA has proposed to disapprove the 
state's transport SIP submittal, 76 FR 20602 (April 13, 2011), but 
has yet not taken final action. In the case of the 2012 annual 
PM2.5 NAAQS, the EPA has not yet taken any action on the 
state's transport SIP submittal.
    \66\ 81 FR at 78955 n.5.

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[[Page 45490]]

IV. Sensitivity Analysis Regarding CSAPR Participation as a BART 
Alternative

A. Summary

    As explained in the proposal and summarized in section II.B, the 
EPA amended the Regional Haze Rule in 2012 to authorize states whose 
EGUs participate in CSAPR trading programs for a given pollutant to 
rely on CSAPR participation as a BART alternative for that pollutant. 
The CSAPR-better-than-BART rule rests on an analytic demonstration that 
implementation of CSAPR as expected to take effect at that time would 
achieve greater reasonable progress than BART toward the national goal 
of natural visibility conditions in Class I areas. As part of the 
proposal for this action, the EPA included a sensitivity analysis to 
the 2012 analytic demonstration showing that the 2012 analysis would 
have supported the same conclusion if the actions being taken in 
response to the D.C. Circuit's remand of various CSAPR Phase 2 budgets 
\67\ had been reflected in the 2012 analysis. In this action, upon 
consideration of comments received, the EPA is affirming the 
sensitivity analysis from the proposal that concluded that the 2012 
analytic demonstration is still valid and is consequently affirming 
that there is no need for revision of the CSAPR-better-than-BART rule 
as a result of the changes in CSAPR's geographic scope resulting from 
the Agency's set of responses to the EME Homer City II decision.
---------------------------------------------------------------------------

    \67\ As described in sections II.A and III.D above, in addition 
to this action, the full set of actions being taken to respond to 
the remand includes the 2016 CSAPR Update (see note 14 above) 
withdrawing the remanded seasonal NOX budgets for eleven 
states and establishing new seasonal NOX budgets to 
address a more recent ozone NAAQS for eight of those states, the 
action approving Alabama's SIP revision establishing state CSAPR 
trading programs for SO2 and annual NOX to 
replace the corresponding federal CSAPR trading programs (see note 
53 above), and expected actions to approve proposed SIP revisions 
for Georgia and South Carolina comparable to Alabama's SIP revision 
(see note 57 above).
---------------------------------------------------------------------------

    The original 2012 analytic demonstration supporting participation 
in CSAPR as a BART alternative was based on an air quality modeling 
analysis comparing projected visibility conditions at relevant 
locations (referred to in the proposal and here simply as ``Class I 
areas'') under three scenarios.\68\ The first scenario reflected no 
implementation of either CSAPR or BART, the second scenario reflected 
implementation of presumptive source-specific BART for both 
SO2 and NOX at BART-eligible EGUs nationwide, and 
the third scenario reflected implementation of CSAPR in covered states 
and presumptive source-specific BART for each pollutant in states where 
CSAPR did not apply for that pollutant (the three scenarios are 
referred to here as the base case scenario, the BART scenario, and the 
original CSAPR scenario, respectively). The EPA used the results of the 
three scenarios to compare the projected visibility impacts of CSAPR 
and BART under a two-pronged ``better-than-BART'' test.\69\ The first 
prong--a requirement that visibility must not decline in any Class I 
area under the proposed BART alternative--was evaluated by comparing 
the projected visibility conditions under the original CSAPR scenario 
and the base case scenario. The second prong--a requirement that there 
must be an overall visibility improvement on average across all 
affected Class I areas under the proposed BART alternative relative to 
source-specific BART--was evaluated by comparing the projected 
visibility conditions under the original CSAPR scenario and the BART 
scenario. Based on these comparisons, and also taking account of 
revisions made to CSAPR after the 2011 modeling but before or 
contemporaneous with the 2012 CSAPR-better-than-BART rule, the EPA 
concluded that the original CSAPR scenario satisfied both prongs of the 
test.
---------------------------------------------------------------------------

    \68\ This background is set forth in greater detail in the 
proposal. See 81 FR at 78961-62.
    \69\ As described in the proposal, satisfaction of the two-
pronged test based on an air quality modeling analysis is one of 
three ways that an alternative measure may be demonstrated to be 
``better than BART'' under the Regional Haze Rule. 81 FR at 78957.
---------------------------------------------------------------------------

    The EPA's proposed sensitivity analysis is set forth in detail in 
the proposal for this action.\70\ To reiterate briefly, for the 
sensitivity analysis, the Agency identified a total of five changes in 
CSAPR's geographic scope expected to occur as a result of actions 
responding to the D.C. Circuit's remand: The removal of Florida, North 
Carolina, and South Carolina from CSAPR for seasonal NOX; 
the removal of Texas from CSAPR for annual NOX; and the 
removal of Texas from CSAPR for SO2.\71\ With respect to 
each of the four changes related to NOX, the EPA explained 
that the change would not have caused a sufficiently large change in 
the modeled NOX emissions in the original CSAPR scenario to 
materially alter the visibility impacts comparison. For North Carolina 
and South Carolina, this assessment was based on the fact that the 
states' EGUs would, or were expected to, remain subject to CSAPR for 
annual NOX after the end of their CSAPR obligations for 
seasonal NOX.\72\ For Florida and Texas, this assessment was 
based on the small magnitudes of the differences in projected total 
NOX emissions from the EGUs in each of those states between 
the original CSAPR scenario and the relevant other modeled scenarios, 
combined with the dominance of sulfate impacts compared to nitrate 
impacts on visibility (especially in the South).\73\ With respect to 
the removal of Texas from CSAPR for SO2, the EPA explained 
that the change would have caused a large reduction in the Texas 
SO2 emissions as modeled in the original CSAPR scenario,\74\ 
thereby causing the visibility impacts comparison to support the 
Agency's determination that CSAPR participation met the criteria for a 
BART alternative even more strongly than the comparison as originally 
performed in 2012. Thus, because the only material change from the 
original 2012 analytic demonstration would be the relative visibility 
improvement in a revised CSAPR scenario resulting from the removal of 
Texas from CSAPR for SO2, the sensitivity analysis as 
proposed indicated that the 2012 analytic demonstration remains valid.
---------------------------------------------------------------------------

    \70\ 81 FR at 78961-64.
    \71\ For purposes of the sensitivity analysis, the EPA 
conservatively did not consider the increased stringency of the 
CSAPR seasonal NOX budgets established in the CSAPR 
Update. See generally 81 FR 74504.
    \72\ 81 FR at 78962.
    \73\ Id. at 78962 (Florida), 78963 (Texas).
    \74\ As noted above and discussed in the proposal, the original 
CSAPR scenario reflected projected implementation of CSAPR in 
covered states and presumptive source-specific BART in states where 
CSAPR did not apply for a pollutant. If Texas had not been expected 
to be covered by CSAPR for SO2, the CSAPR scenario would 
therefore have reflected SO2 emissions from Texas EGUs 
consistent with the implementation of presumptive source-specific 
SO2 BART instead of participation in CSAPR. While EPA 
projected that the CSAPR region overall would have substantially 
lower SO2 emissions under CSAPR than under source-
specific BART, for some individual states, including Texas, 
SO2 emissions under source-specific BART were projected 
to be lower than under CSAPR. Thus, removing Texas from CSAPR for 
SO2 in the CSAPR-better-than-BART analytic demonstration 
would have resulted in a decrease in projected SO2 
emissions in the CSAPR scenario as modeled for the demonstration. 
See 81 FR at 78962-63. In the proposal, the EPA identified the 
minimum amount of the projected decrease in Texas SO2 
emissions as 127,300 tons, based on the difference between projected 
Texas SO2 emissions under the original CSAPR and BART 
scenarios. Id.; see also ``Projected Changes in Texas Emissions, 
Fossil Generation, and Fuel Usage Between the Base Case, BART, and 
Original CSAPR Scenarios,'' available in the docket for this action.
---------------------------------------------------------------------------

    The EPA received substantive comments from two parties with respect 
to the proposed sensitivity analysis. One commenter agrees with the 
EPA's conclusion and with all but one detail of the EPA's methodology 
(which, if changed as suggested by the commenter, would strengthen the 
Agency's conclusion). The other commenter does not agree with either 
the conclusion or

[[Page 45491]]

the methodology, providing several reasons. The remainder of this 
section summarizes the opposing commenter's principal comments on this 
topic and provides the Agency's response.

B. Continued CSAPR Participation by Georgia and South Carolina

    The commenter states that in order to analyze the impacts on the 
CSAPR-better-than-BART analytic demonstration from changes caused by 
the remand, in addition to any other changes evaluated, the EPA must 
also evaluate the removal of Georgia and South Carolina from CSAPR's 
SO2 programs, both because the D.C. Circuit remanded their 
SO2 budgets as invalid and because in the commenter's view 
it is impermissible to rely in such a sensitivity analysis on mere 
commitments from those states to submit CSAPR SIPs in the future. 
Further, according to the commenter, allowing these states to continue 
to participate in CSAPR and then rely on such participation as a BART 
alternative after their SO2 budgets have been remanded would 
be inconsistent with the EPA's previous determinations that states 
could no longer indefinitely rely on participation in the former Clean 
Air Interstate Rule (CAIR) trading programs as a BART alternative after 
the D.C. Circuit found CAIR to be an invalid rule that must be 
replaced.\75\
---------------------------------------------------------------------------

    \75\ In 2005, the EPA promulgated the Clean Air Interstate Rule 
(CAIR) addressing certain interstate air pollution reduction 
obligations, 70 FR 25162 (May 12, 2005), and amended the Regional 
Haze Rule to allow participation in CAIR to be relied on as a BART 
alternative (the CAIR-better-than-BART rule), 70 FR 39104 (July 6, 
2005). The D.C. Circuit upheld the CAIR-better-than-BART rule, 
Utility Air Regulatory Group v. EPA, 471 F.3d 1333 (D.C. Cir. 2006), 
but later found CAIR invalid and remanded that rule to the Agency 
for replacement, North Carolina v. EPA, 531 F.3d 896 (D.C. Cir. 
2008), modified on rehearing, 550 F.3d 1176 (D.C. Cir. 2008). The 
Agency then replaced CAIR with CSAPR, 76 FR 48208, and replaced the 
CAIR-better-than-BART rule with the CSAPR-better-than-BART rule, 77 
FR 33642. In addition, following the remand of CAIR, the Agency 
disapproved SIP submissions for several states seeking to rely on 
CAIR as a BART alternative, e.g., 77 FR at 33647.
---------------------------------------------------------------------------

    The EPA disagrees with the comment that the Agency must consider 
Georgia and South Carolina ineligible to continue to participate in 
CSAPR's SO2 programs as a consequence of the remand of their 
FIP budgets. The CSAPR regulations expressly provide for approval of 
CSAPR SIPs that meet certain conditions as replacements for CSAPR FIPs, 
and Georgia and South Carolina (as well as Alabama) have elected to 
submit such SIPs. The comparison that the commenter draws to the EPA's 
previous findings that states may no longer rely on participation in 
CAIR as a BART alternative is inapt, because the basis for such 
previous findings was that CAIR itself (including its trading programs) 
would not exist, not that particular CAIR budgets were invalid. Here, 
the CSAPR trading program will still exist, making it possible for the 
states to continue to participate in CSAPR through voluntary SIPs 
notwithstanding the invalidation of the EPA's authority to require 
compliance with the remanded budgets through FIPs addressing the 
states' transport obligations.
    The EPA considers the comment about reliance on mere commitments to 
submit SIPs to be largely moot because in the interval between 
submission of the comment and finalization of this action, Georgia has 
submitted its SIP revision and South Carolina has submitted its 
proposed state regulations and has requested that EPA begin the SIP 
approval process under the Agency's parallel processing procedure.\76\ 
Each of the state trading program rules includes a state budget for 
SO2 or annual NOX emissions equal to that state's 
current FIP budget. To the extent the commenter believes that for 
purposes of a sensitivity analysis the Agency may rely only on a SIP 
that has been approved and not on a SIP or proposed state rule that has 
been submitted for EPA approval but not yet approved, the Agency 
disagrees. Both states' rules take the approach of incorporating by 
reference the federal CSAPR trading program rules, including the 
relevant budget amounts, so there are no substantive differences 
between the state trading program rules being adopted by the states for 
inclusion in their SIPs and the federal trading program rules that are 
being replaced. The Agency has proposed to approve both states' SIP 
revisions \77\ and at this time is unaware of any reason why the 
proposed approvals should not be finalized. In these circumstances, the 
EPA believes it is reasonable to rely on the SIP submittals for 
purposes of supporting an analytic assumption that Georgia and South 
Carolina will continue to participate in CSAPR's SO2 and 
annual NOX programs at the states' current budget 
levels.\78\
---------------------------------------------------------------------------

    \76\ See supra notes 55 and 56.
    \77\ See supra note 57.
    \78\ As discussed in section III.D above, both states continue 
to participate in the CSAPR SO2 and annual NOX 
programs through FIPs while Agency action on their SIP submittals is 
pending.
---------------------------------------------------------------------------

C. Appropriateness of Continued Reliance on Original CSAPR-Better-Than-
BART Analysis

    The commenter states that the sensitivity analysis is arbitrary 
because it is based on outdated material, and that instead of 
evaluating whether the 2012 analytic demonstration remains valid, the 
EPA must perform an entirely new analytic demonstration based on a new 
air quality modeling analysis using more current data.
    The EPA disagrees with this comment. While criticizing aspects of 
the Agency's analytic methodology, the commenter does not dispute that 
the sensitivity analysis as conducted by the EPA using that methodology 
shows that the 2012 analytic demonstration would have been strengthened 
rather than weakened by the changes in CSAPR's geographic scope that 
are occurring as a result of the D.C. Circuit's remand. (The 
methodological criticisms are addressed as the next comment below.) 
Further, the commenter offers no compelling support for the suggestion 
that, in the absence of any reason to doubt the conclusion from the 
2012 analytic demonstration, the EPA must nevertheless conduct an 
entirely new demonstration. As an asserted legal rationale for the need 
for a new analysis, the commenter cites the Regional Haze Rule 
provisions for approval of BART alternatives, noting that the provision 
that the EPA followed in approving the CSAPR-better-than-BART rule 
requires a demonstration based on an air quality modeling analysis.\79\ 
The EPA has performed one such air quality modeling analysis and in 
this action has shown that the analysis already performed would 
continue to support a conclusion that CSAPR meets the criteria for a 
BART alternative notwithstanding changes in CSAPR's geographic scope. 
Contrary to the commenter's suggestion, the regulations do not say that 
the EPA must perform an entirely new analysis. Similarly, the 
commenter's assertion that changes in industry data since 2011 
necessitate a new analytic demonstration amounts to a call for 
recurring demonstrations that a BART alternative results in greater 
reasonable progress than BART as the industry evolves, rather than a 
one-time demonstration when the alternative is approved. The 
regulations include no such requirement for recurring demonstrations.
---------------------------------------------------------------------------

    \79\ See 40 CFR 51.308(e)(3).
---------------------------------------------------------------------------

D. Possible Changes in the Geographic Distribution of Emissions

    The commenter states that the EPA's methodology for conducting the 
sensitivity analysis as set forth in the proposal failed to adequately 
consider whether changes in a revised CSAPR scenario regarding the 
geographic distribution of emissions across states or

[[Page 45492]]

within individual states might lead to violations of the analytic 
criteria that the EPA relied on to find that CSAPR qualifies as a BART 
alternative. In particular, the commenter raises the theoretical 
possibility that, in a revised CSAPR scenario where Texas EGUs no 
longer participate in CSAPR for SO2, some individual sources 
in other CSAPR states could buy additional allowances and increase 
their emissions, and that such increases in emissions in turn could 
cause adverse visibility impacts in some individual Class I areas 
(thereby violating the first prong of the two-pronged test described 
above). More generally, the commenter asserts that without new modeling 
the EPA ``has no data'' and has ``simply assume[d]'' that the two 
prongs of the test would be satisfied under such a revised scenario.
    As an initial matter, the EPA disagrees with the commenter's 
summary characterization of the proposed sensitivity analysis as not 
being grounded in data. To the contrary, the Agency's proposed 
conclusions explicitly rely on data drawn from the modeling results in 
the record for the CSAPR-better-than-BART rule. The EPA explained in 
the proposal, first, how the data from the earlier rulemaking record 
showed that a revised CSAPR scenario would reflect a projected 
reduction in Texas SO2 emissions of 127,300 tons (or more) 
\80\ along with projected increases in Florida and Texas NOX 
emissions of at most a few thousand tons and, second, why it was 
logical to conclude from these projected emissions changes that, 
relative to the modeled BART and base case scenarios, the revised CSAPR 
scenario would have shown even larger visibility improvements than the 
original CSAPR scenario.\81\ The commenter provides no data of any 
kind, let alone data that might challenge the data presented in the 
proposal.
---------------------------------------------------------------------------

    \80\ The 127,300-ton amount was described in the proposal as the 
minimum reduction in projected Texas SO2 emissions 
because it did not reflect a 50,500-ton increase in the Texas 
SO2 budget that occurred after the original CSAPR 
scenario was modeled. If that budget increase had been reflected in 
the original CSAPR scenario, modeled Texas EGU SO2 
emissions in that scenario would likely have been higher, 
potentially by the full 50,500-ton amount. The CSAPR budget increase 
would have had no effect on Texas EGUs' modeled SO2 
emissions under BART. As a consequence, the 127,300-ton minimum 
estimate of the reduction in projected Texas SO2 
emissions caused by removing Texas EGUs from CSAPR for 
SO2, which are computed as the difference between Texas 
EGUs' collective emissions in the original CSAPR scenario and the 
BART scenario, may be understated by as much as 50,500 tons.
    \81\ 81 FR at 78962-64.
---------------------------------------------------------------------------

    Turning to the commenter's more specific methodological criticism--
that the Agency has not sufficiently considered whether shifts in the 
geographic distribution of emissions might lead to violations of the 
two-pronged test--the EPA agrees that the potential for such shifts was 
not expressly addressed in the sensitivity analysis as proposed. For 
the final action, the EPA has therefore performed further analysis to 
address this comment, focusing on the specific circumstance identified 
by the commenter--shifts associated with the removal of Texas EGUs from 
CSAPR for SO2--because the Agency agrees that this is the 
most significant change to CSAPR among the actions that have been or 
are expected to be taken in response to the D.C. Circuit's remand.\82\ 
The further analysis is based on state- and unit-level data 
disaggregated from the projections of electricity generation, fuel 
usage, and emissions developed for the base case, BART, and original 
CSAPR scenarios that were compared in the 2012 analytic 
demonstration.\83\
---------------------------------------------------------------------------

    \82\ As summarized above, the Agency explained in the proposal 
that the removal of Florida, North Carolina, South Carolina, and 
Texas EGUs from CSAPR for either seasonal or annual NOX, 
as applicable, would not have caused sufficient changes in modeled 
NOX emissions in a revised CSAPR scenario to materially 
alter the visibility impacts comparison, in some instances because 
the EGUs would remain subject to another CSAPR NOX 
program and in some instances because of the small magnitudes of the 
differences in projected total NOX emissions from the 
EGUs in each of those states between the original CSAPR scenario and 
the relevant other modeled scenarios, combined with the dominance of 
sulfate impacts compared to nitrate impacts on visibility 
(especially in the South). The EPA believes these same factors 
likewise indicate that the visibility impacts of any potential 
shifts in the geographic distribution of NOX emissions 
related to removal of these states from the CSAPR NOX 
programs would not be material to either prong of the two-pronged 
visibility impacts comparison.
    \83\ The state- and plant-level data are derived from the unit-
level data in three spreadsheets included in the final CSAPR-better-
than-BART rulemaking record and available in the docket for this 
action: IPM Parsed File for CSAPR Base Case Scenario 2014 (EPA-HQ-
OAR-2011-0729-0004), IPM Parsed File for National BART Scenario 2014 
(EPA-HQ-OAR-2011-0729-0008), and IPM Parsed File for CSAPR-BART 
Scenario 2014 (EPA-HQ-OAR-2011-0729-0006).
---------------------------------------------------------------------------

    Based on this additional analysis, the EPA finds that, in addition 
to the projected SO2 emissions reduction of at least 127,300 
tons in Texas identified in the proposal,\84\ a revised CSAPR scenario 
without Texas in CSAPR for SO2 could also reflect a 
projected aggregated increase in SO2 emissions of 
approximately 22,300 tons in the six other states in the CSAPR 
SO2 Group 2 trading program (Alabama, Georgia, Kansas, 
Minnesota, Nebraska, and South Carolina). The reason for this 
adjustment is that in the original CSAPR scenario, Texas EGUs were 
projected to emit 22,300 tons of SO2 in excess of the 
state's SO2 budget.\85\ This would have been possible 
through the use of allowances purchased from EGUs in other 
SO2 Group 2 states. Under a revised CSAPR scenario where 
Texas EGUs are no longer part of the CSAPR trading program, Texas EGUs 
would no longer purchase the 22,300 allowances from the other states, 
and the EGUs in those other states could potentially use those 
allowances to increase their own collective SO2 emissions. 
Much or all of the total potential increase in emissions in the other 
states would be projected to occur in Alabama and Georgia, because in 
the original CSAPR scenario the collective emissions from Kansas EGUs 
were projected to already be at the state's ``assurance level''--the 
emissions level above which EGUs trigger a CSAPR provision requiring 
the surrender of three allowances instead of one allowance per ton of 
emissions--and the collective emissions from Minnesota, Nebraska, and 
South Carolina EGUs were projected to already be close to their states' 
respective assurance levels.\86\ After accounting for the potential 
22,300-ton offsetting adjustment, the net regional SO2 
reduction under the revised CSAPR scenario relative to the original 
CSAPR scenario would be projected to be approximately 105,000 tons (or 
more) instead of 127,300 tons (or more) as described in the proposed 
sensitivity analysis.\87\ For the reasons below, the EPA has considered 
both the projected decrease in Texas SO2 emissions and the 
projected aggregated increase in SO2

[[Page 45493]]

emissions in the other states and has concluded that the two-pronged 
CSAPR-better-than-BART test described above would continue to be 
satisfied.
---------------------------------------------------------------------------

    \84\ See supra note 74.
    \85\ See ``Projected Interstate Trading of CSAPR SO2 
Group 2 Allowances in the Original CSAPR Scenario,'' available in 
the docket for this action.
    \86\ Id.
    \87\ It is possible that if the original CSAPR scenario that 
includes Texas in CSAPR for SO2 had been remodeled to 
include the 50,500 increase in the Texas SO2 budget 
described in the proposal and in footnote 80, Texas EGUs would have 
been projected to purchase either more or less than 22,300 
allowances from EGUs in other CSAPR SO2 Group 2 states, 
and that a revised CSAPR scenario in which Texas was removed from 
CSAPR for SO2 would therefore have shown the other Group 
2 states increasing their SO2 emissions by this different 
amount. Regardless of the amount or direction of any modeled change 
in Texas EGUs' CSAPR allowance purchases, that change would 
generally have been matched by an equal and opposite change in Texas 
EGUs' projected emissions under CSAPR, with the result that the 
overall net projected reduction in emissions caused by removing 
Texas from CSAPR for SO2 would continue to be at least 
105,000 tons. The maximum amount of CSAPR SO2 allowances 
that Texas could purchase from other states and use in a given year 
without incurring 3-for-1 allowance surrender requirements is 
approximately 53,000 tons, which is the amount of Texas' 
SO2 variability limit--the difference between the state's 
budget and its assurance level--under the CSAPR regulations. See 40 
CFR 97.710(b)(7).
---------------------------------------------------------------------------

    As summarized above, the first prong of the two-pronged test 
requires that visibility conditions must not decline in any Class I 
area. In the 2012 analytic demonstration, the EPA evaluated this prong 
by comparing visibility impacts at each affected Class I area under the 
original CSAPR scenario and the base case scenario. The situation 
identified by the commenter in which emissions under a revised CSAPR 
scenario might rise at some individual EGUs sufficiently to cause a 
decline in visibility at some individual Class I area relative to 
visibility conditions in the base case scenario--that is, without 
either CSAPR or BART--would be a very unusual event and likely can be 
ruled out as impossible, or nearly so, in a scenario such as the 
revised CSAPR scenario being considered. Under the base case scenario, 
EGUs incur no cost at all under CSAPR for emitting a ton of 
SO2. In contrast, under either the original CSAPR scenario 
or a revised CSAPR scenario, EGUs would incur some cost per ton of 
SO2 emissions under CSAPR, and where that new cost is the 
principal change from the base case scenario, EGUs that emit 
SO2 would generally be projected to either decrease or 
maintain their emissions relative to the base case scenario where that 
cost was not present. If in a revised CSAPR scenario, allowances are 
more plentiful and the cost incurred per ton of SO2 
emissions therefore is less than the cost per ton under the original 
CSAPR scenario, some EGUs that emit SO2 would be projected 
to reduce their SO2 emissions by a smaller amount than in 
the original CSAPR scenario, but they generally would not be projected 
to significantly increase their emissions relative to the base case 
scenario. An exception to this general principle could occur if some 
other factor influencing EGUs' operating decisions, such as electricity 
demand or relative fuel prices, also changed. The EPA therefore 
considered whether the removal of Texas from CSAPR could have been 
projected to result in any material change in demand for generation 
from other states or relative fuel prices in other states in a revised 
CSAPR scenario compared to the original CSAPR scenario.\88\
---------------------------------------------------------------------------

    \88\ Although the analysis focuses on other CSAPR states, 
consistent with the concerns raised by the commenter, the EPA notes 
that absent changes in generation demand or relative fuel prices, 
removal of Texas from CSAPR would also be expected not to affect the 
operating decisions of EGUs in non-CSAPR states.
---------------------------------------------------------------------------

    With respect to the possibility of changes in electricity demand in 
other states, record data show that, relative to the original CSAPR 
scenario, aggregated 2014 generation from fossil-fired Texas EGUs was 
projected to increase by 0.2% in the BART scenario (which is used here 
as a proxy representing the operating behavior of Texas EGUs in a 
revised CSAPR scenario), indicating that removal of Texas EGUs from 
CSAPR for SO2 and implementation of SO2 BART 
would not be projected to result in an increase in emissions outside 
Texas caused by a shift in generation from Texas to other states.\89\
---------------------------------------------------------------------------

    \89\ See ``Projected Changes in Texas Emissions, Fossil 
Generation, and Fuel Usage Between the Base Case, BART, and Original 
CSAPR Scenarios,'' available in the docket for this action. Because 
there is little difference in NOX emissions from Texas 
EGUs between the original CSAPR scenario, the BART scenario, and the 
base case scenario, id., the EPA considers the BART scenario a 
reasonable emissions proxy for a revised CSAPR scenario in which 
Texas EGUs would be subject to BART for SO2 but not for 
NOX.
---------------------------------------------------------------------------

    With respect to changes in relative fuel prices in other states, 
record data show that, relative to the original CSAPR scenario, in the 
BART scenario Texas EGUs were projected to decrease their use of 
subbituminous coal by 68 trillion Btus (TBtu), increase their use of 
lignite by 66 TBtu, and increase their use of other fossil fuels 
(predominantly natural gas) by 11 TBtu.\90\ The changes in projected 
Texas usage of subbituminous coal and natural gas are less than 1% of 
the projected total industry usage of those fuels nationwide under the 
original CSAPR scenario, indicating that there is no reason to expect 
material impacts on prices or usage of those fuels in other states. 
Unlike subbituminous coal and natural gas, lignite is an inherently 
local fuel that is consumed near the point of extraction because the 
fuel's low energy content per unit of weight makes shipment over long 
distances uneconomic. Thus, although the increase in Texas EGUs' 
projected usage of lignite is fairly large (8.2% of projected national 
usage of lignite under the original CSAPR scenario), any resulting 
increase in the local prices of lignite would not be expected to affect 
the mix of fuels used in other states.
---------------------------------------------------------------------------

    \90\ See id.
---------------------------------------------------------------------------

    For further confirmation of the applicability here of the general 
principle discussed above--namely, that in a modeled CSAPR scenario, 
EGUs that emit SO2 would generally be projected to either 
decrease or maintain their emissions and not to increase their 
emissions relative to the base case scenario--the EPA compared the 
projected unit-level SO2 emissions in the original CSAPR and 
base case scenarios for all coal-fired EGUs in the seven states in the 
CSAPR SO2 Group 2 trading program. The results of the 
comparison clearly indicate that the general principle applies in this 
instance: 77 Units were projected to reduce their SO2 
emissions by 1,000 tons or more (in amounts up to 57,000 tons), 106 
units were projected to essentially maintain their SO2 
emissions (increasing or decreasing by between 0 and 1,000 tons), and 2 
units were projected to increase their SO2 emissions by 
approximately 1,100 tons each.\91\ A similar comparison at the state 
level shows that collective SO2 emissions from the sets of 
EGUs in each of the seven states were also projected to decrease from 
the base case scenario to the original CSAPR scenario (in amounts 
ranging from 1,900 tons for Nebraska to 248,800 tons for Alabama).\92\ 
In combination with the data above showing that removal of Texas from 
CSAPR for SO2 would not be expected to cause changes in 
demand for generation or relative fuel prices in other states, the EPA 
believes that these data on how EGUs were projected to comply with 
CSAPR in the original CSAPR scenario indicate that in a revised CSAPR 
scenario where Texas is removed from CSAPR for SO2 and 
22,300 additional allowances (or up to 53,000 allowances, as noted 
earlier \93\) therefore become available to the EGUs in the other 
SO2 Group 2 states, few if any EGUs would respond to the 
availability of the additional allowances by increasing their emissions 
materially above their emissions in the base case scenario. Further, 
even if some EGUs did increase their emissions above their emissions in 
the base case scenario, because of the regional nature of sulfate 
formation from SO2 emissions and the very large decreases in 
SO2 emissions across the broader region, the EPA believes 
that any such local increase would be unlikely to cause localized 
visibility degradation in any Class I area near a CSAPR state affected 
by the removal of Texas from CSAPR for SO2. In consequence, 
the Agency finds it reasonable to conclude that in such a revised CSAPR 
scenario, no such Class I areas would experience declines in visibility 
conditions relative to the base case scenario.
---------------------------------------------------------------------------

    \91\ See ``Projected Changes in Unit-Level Emissions Between the 
Base Case and Original CSAPR Scenarios,'' available in the docket 
for this action.
    \92\ See id.
    \93\ See supra note 87.
---------------------------------------------------------------------------

    The second prong of the two-pronged test requires the average 
projected

[[Page 45494]]

visibility improvement across all affected Class I areas to be greater 
under the BART alternative than under BART. In the proposal, the EPA 
proposed to conclude that this prong would be easily satisfied under 
the revised CSAPR scenario because Texas EGUs would be modeled in the 
revised CSAPR scenario as subject to SO2 BART instead of 
being subject to CSAPR for SO2, and the record data showed 
that Texas EGUs' projected SO2 emissions would be at least 
127,300 tons lower under BART than under CSAPR. As discussed above, 
based on further analysis the EPA concludes that the decrease in 
projected Texas SO2 emissions could potentially be partially 
offset by an increase in projected SO2 emissions in other 
CSAPR SO2 Group 2 states, most likely Alabama or Georgia. 
The EPA believes that such a revised CSAPR scenario would continue to 
show greater average visibility improvement than the BART scenario (and 
greater than the original CSAPR scenario), again easily passing the 
second prong of the two-pronged test. Any reduction in visibility 
improvement in Class I areas near Alabama, Georgia, or the other Group 
2 states relative to the original CSAPR scenario would be more than 
offset by greater visibility improvement in Class I areas near 
Texas.\94\ Due to the regional nature of sulfate particulate matter 
formation, it is highly likely that, like the original CSAPR scenario, 
the revised CSAPR scenario would show greater visibility improvement on 
average across all Class I areas than the BART scenario. The commenters 
did not present any information to indicate otherwise, and the EPA is 
not aware of any such information.
---------------------------------------------------------------------------

    \94\ The CSAPR-better-than-BART record shows that the Class I 
areas most impacted by Texas were projected to have greater modeled 
visibility improvement in the BART scenario (on the 20% best days) 
than in the CSAPR scenario. This indicates that there would have 
been additional visibility improvement in a revised CSAPR scenario 
in which Texas is not in CSAPR for SO2 and is therefore 
modeled at BART SO2 levels. Note that the average 
visibility improvements across all affected Class I areas as 
computed in the original CSAPR and BART scenarios are much closer on 
the 20% best days than on the 20% worst days. Therefore, in 
determining whether the second prong of the two-pronged test will be 
passed under a revised CSAPR scenario, the modeled results on the 
20% best days are particularly important.
---------------------------------------------------------------------------

E. Validity of 2012 Analytic Demonstration Prior to CSAPR Changes

    Finally, the commenter asserts that regardless of the character of 
the sensitivity analysis itself, the original 2012 CSAPR-better-than-
BART analytic demonstration was arbitrary, rendering any sensitivity 
analysis performed regarding the original demonstration arbitrary. In 
support of this claim, the commenter incorporates by reference all 
criticisms of the original analytic demonstration contained in the 
comments submitted by the commenter in the original CSAPR-better-than-
BART rulemaking as well as all criticisms contained in the commenter's 
brief in the pending litigation challenging the CSAPR-better-than-BART 
rule.
    The EPA rejects these comments as both improperly raised and 
outside the scope of this proceeding. The EPA appreciates the value of 
public input in the rulemaking process and seeks to fulfill its legal 
obligation to consider and respond to all substantive comments that are 
``raised with reasonable specificity,'' \95\ but catch-all references 
to whatever statements may have been made in another proceeding do not 
meet this standard. Moreover, even if they had been properly raised, 
comments concerning the legal validity of the original 2012 analytic 
demonstration are beyond the scope of this rulemaking, which concerns 
only the sensitivity analysis addressing the effect on the 2012 
analytic demonstration of changes in CSAPR's geographic scope resulting 
from the D.C. Circuit's remand (as well as the withdrawal of Texas 
CSAPR FIP requirements for SO2 and annual NOX and 
the finding as to Texas' remaining transport obligation under CAA 
section 110(a)(2)(D)(i)(I) regarding the 1997 annual PM2.5 
NAAQS). Arguments concerning the original 2012 analytic demonstration 
should be, and have been, raised in the original CSAPR-better-than-BART 
rulemaking and in the pending litigation over that rule.
---------------------------------------------------------------------------

    \95\ CAA section 307(d)(7)(B).
---------------------------------------------------------------------------

V. Description of Amendments to Regulatory Text

    In order to implement the withdrawal of the FIP provisions 
requiring Texas EGUs to participate in the CSAPR NOX Annual 
Trading Program and the CSAPR SO2 Group 2 Trading Program 
with regard to emissions occurring in Phase 2 of those programs, the 
EPA is amending the regulatory text at 40 CFR 52.38(a)(2), 52.39(c), 
52.2283(c), and 52.2284(c) to provide that Texas EGUs are subject to 
requirements under these two programs with regard to emissions 
occurring in 2015 and 2016 only. Conforming amendments to cross-
references are being made at Sec.  52.38(a)(3), (a)(4), (a)(5), (a)(6), 
and (a)(8)(iii) and Sec.  52.39(g), (h), (i), (j), and (m)(3).
    The EPA is also clarifying the CSAPR regulations by adding the 
introductory headings ``Annual emissions'' and ``Ozone season 
emissions'' to Sec.  52.38(a) and (b), respectively, and by amending 
the wording of the regulatory text at Sec. Sec.  52.38(b)(2)(i) and 
52.39(b) to parallel the wording of the newly amended regulatory text 
at Sec. Sec.  52.38(a)(2)(i) and 52.39(c)(1). These editorial 
clarifications do not alter any existing regulatory requirements.
    Finally, the EPA is correcting the CSAPR regulations applicable to 
South Carolina EGUs by amending the regulatory text at Sec.  52.2141(b) 
to reference CSAPR SO2 Group 2 allowances and 40 CFR part 
97, subpart DDDDD instead of CSAPR SO2 Group 1 allowances 
and 40 CFR part 97, subpart CCCCC. The corrections make the text at 
Sec.  52.2141(b) consistent with the existing text at Sec.  52.2141(a), 
and the two paragraphs together now correctly reflect the existing 
regulatory requirements applicable to South Carolina EGUs as already 
set forth at Sec.  52.39(c) and (k).

VI. Statutory and Executive Order Reviews

    Additional information about these statutes and Executive Orders 
can be found at https://www2.epa.gov/laws-regulations/laws-and-executive-orders.

A. Executive Order 12866: Regulatory Planning and Review, and Executive 
Order 13563: Improving Regulation and Regulatory Review

    This action is not a significant regulatory action and therefore 
was not submitted to the Office of Management and Budget (OMB) for 
review.

B. Executive Order 13771: Reducing Regulations and Controlling 
Regulatory Costs

    This action is not expected to be an Executive Order 13771 
regulatory action because this action is not significant under 
Executive Order 12866.

C. Paperwork Reduction Act

    This action does not impose any new information collection burden 
under the Paperwork Reduction Act. The OMB has previously approved the 
information collection activities contained in the existing regulations 
and has assigned OMB control number 2060-0667. The withdrawal of the 
FIP provisions in this action will eliminate the obligations of Texas 
sources to comply with the existing monitoring, recordkeeping, and 
reporting requirements under the CSAPR SO2 Group 2 Trading 
Program and the CSAPR NOX Annual Trading Program.

[[Page 45495]]

D. Regulatory Flexibility Act

    I certify that this action will not have a significant economic 
impact on a substantial number of small entities under the Regulatory 
Flexibility Act. In making this determination, the impact of concern is 
any significant adverse economic impact on small entities. An agency 
may certify that a rule will not have a significant economic impact on 
a substantial number of small entities if the rule relieves regulatory 
burden, has no net burden, or otherwise has a positive economic effect 
on the small entities subject to the rule. This action withdraws 
existing regulatory requirements for some entities and does not impose 
new requirements on any entity. We have therefore concluded that this 
action will either relieve or have no net regulatory burden for all 
directly regulated small entities.

E. Unfunded Mandates Reform Act

    This action does not contain any unfunded mandate as described in 
the Unfunded Mandates Reform Act, 2 U.S.C. 1531-1538, and does not 
significantly or uniquely affect small governments. The action imposes 
no enforceable duty on any state, local, or tribal governments or the 
private sector. This action simply eliminates certain federal 
regulatory requirements that the D.C. Circuit has held invalid.

F. Executive Order 13132: Federalism

    This action does not have federalism implications. It will not have 
substantial direct effects on the states, on the relationship between 
the national government and the states, or on the distribution of power 
and responsibilities among the various levels of government. This 
action simply eliminates certain federal regulatory requirements that 
the D.C. Circuit has held invalid.

G. Executive Order 13175: Consultation and Coordination With Indian 
Tribal Governments

    This action does not have tribal implications as specified in 
Executive Order 13175. It will not have substantial direct effects on 
tribal governments, on the relationship between the federal government 
and Indian tribes, or on the distribution of power and responsibilities 
between the federal government and Indian tribes. This action simply 
eliminates certain federal regulatory requirements that the D.C. 
Circuit has held invalid. Thus, Executive Order 13175 does not apply to 
this action. Consistent with the EPA Policy on Consultation and 
Coordination with Indian Tribes, the EPA consulted with tribal 
officials while developing CSAPR. A summary of that consultation is 
provided in the preamble for CSAPR, 76 FR 48208, 48346 (August 8, 
2011).

H. Executive Order 13045: Protection of Children From Environmental 
Health and Safety Risks

    The EPA interprets Executive Order 13045 as applying only to those 
regulatory actions that concern environmental health or safety risks 
that the EPA has reason to believe may disproportionately affect 
children, per the definition of ``covered regulatory action'' in 
section 2-202 of the Executive Order. This action is not subject to 
Executive Order 13045 because it simply eliminates certain federal 
regulatory requirements that the D.C. Circuit has held invalid.

I. Executive Order 13211: Actions That Significantly Affect Energy 
Supply, Distribution, or Use

    This action is not subject to Executive Order 13211, because it is 
not a significant regulatory action under Executive Order 12866.

J. National Technology Transfer Advancement Act

    This rulemaking does not involve technical standards.

K. Executive Order 12898: Federal Actions To Address Environmental 
Justice in Minority Populations and Low-Income Populations

    The EPA believes that this action is not subject to Executive Order 
12898 because it does not establish an environmental health or safety 
standard. This action simply eliminates certain federal regulatory 
requirements that the D.C. Circuit has held invalid. Consistent with 
Executive Order 12898 and the EPA's environmental justice policies, the 
EPA considered effects on low-income populations, minority populations, 
and indigenous peoples while developing CSAPR. The process and results 
of that consideration are described in the preamble for CSAPR, 76 FR 
48208, 48347-52 (August 8, 2011).

L. Congressional Review Act

    This action is subject to the Congressional Review Act, and the EPA 
will submit a rule report to each House of the Congress and to the 
Comptroller General of the United States. This action is not a ``major 
rule'' as defined by 5 U.S.C. 804(2).

M. Judicial Review and Determinations Under CAA Section 307(b)(1) and 
(d)

    CAA section 307(b)(1) indicates which federal appellate courts have 
venue for petitions of review of final actions by the EPA. This section 
provides, in part, that petitions for review must be filed in the D.C. 
Circuit Court of Appeals if (i) the agency action consists of 
``nationally applicable regulations promulgated, or final action taken, 
by the Administrator,'' or (ii) such action is locally or regionally 
applicable, if ``such action is based on a determination of nationwide 
scope or effect and if in taking such action the Administrator finds 
and publishes that such action is based on such a determination.'' This 
final action is ``nationally applicable.'' In addition, the EPA finds 
that all aspects of this action are based on a determination of 
``nationwide scope and effect'' within the meaning of section 
307(b)(1).
    First, the EPA's withdrawal of FIP requirements under the CSAPR 
program for Texas is being undertaken in response to a remand by the 
D.C. Circuit in litigation that challenged numerous aspects of CSAPR 
with implications for multiple states and resulted in the remand of 
fifteen budgets for thirteen states. Retaining review in the D.C. 
Circuit is appropriate and avoids the potential that another court is 
forced to interpret the remand order of a sister circuit. Also, the 
finding that, after the FIP withdrawal, Texas has no remaining 
obligation to address interstate transport with respect to the 1997 
annual PM2.5 NAAQS is based on a common core of factual 
findings and analyses concerning the transport of pollutants between 
the different states subject to CSAPR, which is a nationally applicable 
program. Further, this action is based on a determination that modifies 
the scope and effect of CSAPR; thus, any judicial review of this action 
will necessarily implicate the national-level policies, technical 
analyses, or interpretations that undergird this nationwide program.
    Second, in express consideration of the effect of the withdrawal of 
Texas FIP requirements accomplished through this final action, the EPA 
is affirming the continued validity of 40 CFR 51.308(e)(4), a 
regulatory provision available to each of the 27 States whose sources 
currently participate in one or more CSAPR trading programs. This 
determination affects the rights and interests of regulated parties and 
other stakeholders throughout the eastern United States relying on or 
otherwise affected by that regulatory provision.
    For these reasons, this final action is nationally applicable and, 
in addition,

[[Page 45496]]

the Administrator finds that this final action is based on a 
determination of nationwide scope and effect for purposes of section 
307(b)(1). Thus, pursuant to section 307(b) any petitions for review of 
this action must be filed in the D.C. Circuit within 60 days from the 
date of publication of this action in the Federal Register.
    In addition, pursuant to CAA sections 307(d)(1)(B), 307(d)(1)(J), 
and 307(d)(1)(V), the Administrator determines that this action is 
subject to the provisions of section 307(d). CAA section 307(d)(1)(B) 
provides that section 307(d) applies to, among other things, ``the 
promulgation or revision of an implementation plan by the Administrator 
under [CAA section 110(c)].'' 42 U.S.C. 7607(d)(1)(B). Under section 
307(d)(1)(J), the provisions of section 307(d) apply to the 
``promulgation or revision of regulations . . . relating to . . . 
protection of visibility.'' 42 U.S.C. 7607(d)(1)(J). Under section 
307(d)(1)(V), the provisions of section 307(d) also apply to ``such 
other actions as the Administrator may determine.'' 42 U.S.C. 
7607(d)(1)(V). The agency has complied with the procedural requirements 
of CAA section 307(d) during the course of this rulemaking.
    CAA section 307(b)(1) also provides that filing a petition for 
reconsideration by the Administrator of this rule does not affect the 
finality of the rule for the purposes of judicial review, does not 
extend the time within which a petition for judicial review may be 
filed, and does not postpone the effectiveness of the rule. Under CAA 
section 307(b)(2), the requirements established by this rule may not be 
challenged separately in any civil or criminal proceedings brought by 
the EPA to enforce these requirements.

List of Subjects in 40 CFR Part 52

    Environmental protection, Administrative practice and procedure, 
Air pollution control, Incorporation by reference, Intergovernmental 
relations, Nitrogen oxides, Ozone, Particulate matter, Regional haze, 
Reporting and recordkeeping requirements, Sulfur dioxide.

    Dated: September 21, 2017.
E. Scott Pruitt,
Administrator.

    For the reasons stated in the preamble, part 52 of chapter I of 
title 40 of the Code of Federal Regulations is amended as follows:

PART 52--APPROVAL AND PROMULGATION OF IMPLEMENTATION PLANS

0
1. The authority citation for part 52 continues to read as follows:

    Authority: 42 U.S.C. 7401 et seq.

Subpart A--General Provisions

0
2. Section 52.38 is amended by:
0
a. Adding a paragraph (a) heading;
0
b. Revising paragraph (a)(2);
0
c. In paragraph (a)(3) introductory text, removing the text ``(a)(2)'' 
and in its place adding the text ``(a)(2)(i) or (ii)'';
0
d. In paragraph (a)(4) introductory text, removing the text ``(a)(2)'' 
and in its place adding the text ``(a)(2)(i)'';
0
e. In paragraphs (a)(5) introductory text and (a)(6), removing the text 
``(a)(2)'' and in its place adding the text ``(a)(2)(i)'', and removing 
the text ``(a)(1) through (4)'' and in its place adding the text 
``(a)(1), (a)(2)(i), and (a)(3) and (4)'';
0
f. In paragraph (a)(8)(iii), removing the text ``(a)(1) through (4)'' 
and in its place adding the text ``(a)(1), (a)(2)(i), and (a)(3) and 
(4)'';
0
g. Adding a paragraph (b) heading; and
0
h. In paragraph (b)(2)(i), after the word ``emissions'' adding the word 
``occurring''.
    The additions and revisions read as follows:


Sec.  52.38  What are the requirements of the Federal Implementation 
Plans (FIPs) for the Cross-State Air Pollution Rule (CSAPR) relating to 
emissions of nitrogen oxides?

    (a) Annual emissions. * * *
    (2)(i) The provisions of subpart AAAAA of part 97 of this chapter 
apply to sources in each of the following States and Indian country 
located within the borders of such States with regard to emissions 
occurring in 2015 and each subsequent year: Alabama, Georgia, Illinois, 
Indiana, Iowa, Kansas, Kentucky, Maryland, Michigan, Minnesota, 
Missouri, Nebraska, New Jersey, New York, North Carolina, Ohio, 
Pennsylvania, South Carolina, Tennessee, Virginia, West Virginia, and 
Wisconsin.
    (ii) The provisions of subpart AAAAA of part 97 of this chapter 
apply to sources in each of the following States and Indian country 
located within the borders of such States with regard to emissions 
occurring in 2015 and 2016 only: Texas.
* * * * *
    (b) Ozone season emissions. * * *

0
3. Section 52.39 is amended by:
0
a. In paragraph (b), before the colon, adding the text ``with regard to 
emissions occurring in 2015 and each subsequent year'';
0
b. Revising paragraph (c);
0
c. In paragraph (g) introductory text, removing the text ``(c)'' and in 
its place adding the text ``(c)(1) or (2)'';
0
d. In paragraph (h) introductory text, removing the text ``(c)'' and in 
its place adding the text ``(c)(1)'';
0
e. In paragraphs (i) introductory text and (j), removing the text 
``(c)'' two times and in its place adding the text ``(c)(1)''; and
0
f. In paragraph (m)(3), removing the text ``(c)'' and in its place 
adding the text ``(c)(1)''.
    The revision reads as follows:


Sec.  52.39  What are the requirements of the Federal Implementation 
Plans (FIPs) for the Cross-State Air Pollution Rule (CSAPR) relating to 
emissions of sulfur dioxide?

* * * * *
    (c)(1) The provisions of subpart DDDDD of part 97 of this chapter 
apply to sources in each of the following States and Indian country 
located within the borders of such States with regard to emissions 
occurring in 2015 and each subsequent year: Alabama, Georgia, Kansas, 
Minnesota, Nebraska, and South Carolina.
    (2) The provisions of subpart DDDDD of part 97 of this chapter 
apply to sources in each of the following States and Indian country 
located within the borders of such States with regard to emissions 
occurring in 2015 and 2016 only: Texas.
* * * * *

Subpart PP--South Carolina


Sec.  52.2141  [Amended]

0
4. Section 52.2141, paragraph (b) is amended by removing the text 
``Group 1'' two times and in its place adding the text ``Group 2'', and 
removing the text ``CCCCC'' two times and in its place adding the text 
``DDDDD''.

Subpart SS--Texas

0
5. Section 52.2283 is amended by revising paragraph (c)(1) and removing 
and reserving paragraph (c)(2).
    The revision reads as follows:


Sec.  52.2283  Interstate pollutant transport provisions; What are the 
FIP requirements for decreases in emissions of nitrogen oxides?

* * * * *
    (c)(1) The owner and operator of each source and each unit located 
in the State of Texas and Indian country within the borders of the 
State and for which requirements are set forth under the CSAPR 
NOX Annual Trading Program in subpart AAAAA of part 97 of 
this

[[Page 45497]]

chapter must comply with such requirements with regard to emissions 
occurring in 2015 and 2016.
* * * * *

0
6. Section 52.2284 is amended by revising paragraph (c)(1) and removing 
and reserving paragraph (c)(2).
    The revision reads as follows:


Sec.  52.2284  Interstate pollutant transport provisions; What are the 
FIP requirements for decreases in emissions of sulfur dioxide?

* * * * *
    (c)(1) The owner and operator of each source and each unit located 
in the State of Texas and Indian country within the borders of the 
State and for which requirements are set forth under the CSAPR 
SO2 Group 2 Trading Program in subpart DDDDD of part 97 of 
this chapter must comply with such requirements with regard to 
emissions occurring in 2015 and 2016.
* * * * *
[FR Doc. 2017-20832 Filed 9-28-17; 8:45 am]
 BILLING CODE 6560-50-P

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