*1 Before: GIBBONS and KETHLEDGE, Circuit Judges; DOW, District Judge. [*] _________________
COUNSEL ARGUED: Robert Ukeiley, Berea, Kentucky, for Petitioner. Amy J. Dona, UNITED STATES DEPARTMENT OF JUSTICE, Washington, D.C., for Respondents. Aaron S. Farmer, OFFICE OF THE OHIO ATTORNEY GENERAL, Columbus, Ohio, for Intervenor . ON BRIEF: Robert Ukeiley, Berea, Kentucky, David C. Bender, MCGILLIVRAY WESTERBERG & BENDER LLC, Madison, Wisconsin, for Petitioner. Amy J. Dona, UNITED STATES DEPARTMENT OF JUSTICE, Washington, D.C., for Respondents. Aaron S. Farmer, Elizabeth R. Ewing, OFFICE OF THE OHIO ATTORNEY GENERAL, Columbus, Ohio, for Intervenor State of Ohio. Louis E. Tosi, Michael E. Born, Cheri A. Budzynski, SHUMAKER, LOOP & KENDRICK, LLP, Columbus, Ohio, for Ohio Utility Intervenors. Thomas M. Fisher, OFFICE OF THE INDIANA ATTORNEY GENERAL, Indianapolis, Indiana, for Amicus Curiae.
______________________
AMENDED OPINION
______________________ JULIA SMITH GIBBONS, Circuit Judge. In 2011, the Environmental Protection Agency (“EPA”) determined that the Cincinnati-Hamilton metropolitan area had attained national air quality standards for particulate matter, thanks in no small part to regional cap-and- trade programs that had reduced the flow of interstate pollution. EPA also redesignated the area to “attainment” status even though the three States that administer its pollution controls had never implemented particular provisions, known as “reasonably available control measures,” applicable to nonattainment areas. Sierra Club thought the agency had acted illegally with respect to both actions, and it filed a petition for direct appellate review in this court. The parties dispute both Sierra Club’s standing to challenge the agency action and the correct interpretation of the relevant statute, the Clean Air Act.
We find that the Club has standing, and we agree with its claim that “reasonably available control measures” are a prerequisite to redesignation. Therefore, we vacate EPA’s redesignation of the Ohio and Indiana portions of the Cincinnati area.
I.
A. The Clean Air Act (“CAA”) authorizes EPA to promulgate National Ambient Air Quality Standards (“NAAQS”) for various types of emissions deemed injurious to public health and welfare. 42 U.S.C. § 7409(a)–(b). Once the agency has promulgated a particular NAAQS, the Governor of each State must submit a “state implementation plan” (“SIP”) with particular methods for achieving the NAAQS. § 7410. EPA will then designate portions of each State as “attainment areas” (that attain the standard), “nonattainment areas” (that do not), or as “unclassifiable.” Id. § 7407(d)(1)(B). If an area is designated as nonattainment, the State or States containing that area must revise their SIPs to meet additional requirements located in Part D of Subchapter 1, Chapter 85 of Title 42. See, e.g. , id. § 7502. One such requirement, which we will refer to as “RACM” or “RACT,” is that the state SIP “provide for the implementation of all reasonably available control measures [“RACM”] as expeditiously as practicable (including such reductions in emissions from existing sources in the area as may be obtained through the adoption, at a minimum, of reasonably available control technology [“RACT”]) and shall provide for attainment of the national primary ambient air quality standards.” Id. § 7502(c)(1). Another such provision, termed “New Source Review” or “NSR,” forces the State to set up a permit regime “for the construction and operation of new or modified major stationary sources anywhere in the nonattainment area, in accordance with section 7503 of [Title 42].” Id. § 7502(c)(5).
When a State asks EPA to redesignate a nonattainment area to attainment status (and thus remove these additional requirements from its SIP), the agency may do so only if five conditions are satisfied:
(i) the Administrator determines that the area has attained the national ambient air quality standard;
(ii) the Administrator has fully approved the applicable implementation plan for the area under section 7410(k) of [Title 42];
(iii) the Administrator determines that the improvement in air quality is due to permanent and enforceable reductions in emissions resulting from implementation of the applicable implementation plan and applicable Federal air pollutant control regulations and other permanent and enforceable reductions; (iv) the Administrator has fully approved a maintenance plan for the area as meeting the requirements of section 7505a of [Title 42]; and (v) the State containing such area has met all requirements applicable to the area under section 7410 of this title and part D of [Subchapter 1].
Id. § 7407(d)(3)(E).
In 1997, EPA promulgated a NAAQS concerning fine particulate matter (referred to as PM 2.5 to distinguish it from coarse particulate matter, PM [10] ), motivated largely by concerns of health impacts. National Ambient Air Quality Standards for Particulate Matter, 62 Fed. Reg. 38,652, 38,652 (July 18, 1997).
B.
To combat the flow of air pollutants across state lines, EPA has also created so-called “cap-and-trade” programs. In this sort of scheme, the agency first “caps” the total emissions allowable from a particular facility, state, or region, and then requires any source that pollutes too much either to invest in cleaner technology or to purchase emission reduction credits from other, more environmentally friendly sources (the “trade” part). Three cap-and-trade programs are pertinent to this case.
The first is the NO x SIP Call, which covered 22 States plus the District of Columbia and
targeted known precursor emissions to ozone and particulate matter.
See
Finding of Significant
Contribution and Rulemaking for Certain States in the Ozone Transport Assessment Group
Region for Purposes of Reducing Regional Transport of Ozone, 63 Fed. Reg. 57,356, 57,477
(Oct. 27, 1998). EPA promulgated another cap-and-trade program with the Clean Air Interstate
Rule (“CAIR”) in 2005; this was also partly aimed at reducing fine particulate matter in the
atmosphere.
See
Rule To Reduce Interstate Transport of Fine Particulate Matter and Ozone
(Clean Air Interstate Rule); Revisions to Acid Rain Program; Revisions to the NO x SIP Call, 70
Fed. Reg. 25,162, 25,162 (May 12, 2005). After the D.C. Circuit ruled CAIR illegal,
see North
Carolina v. EPA
, 531 F.3d 896, 901 (D.C. Cir. 2008) (per curiam), EPA promulgated a third
program called the Cross-State Air Pollution Rule (“CSAPR”),
see
Federal Implementation
Plans: Interstate Transport of Fine Particulate Matter and Ozone and Correction of SIP
Approvals, 76 Fed. Reg. 48,208, 48,208 (Aug. 8, 2011). The Supreme Court recently upheld this
program.
See EPA v. EME Homer City Generation, L.P.
,
C.
In 2011, EPA issued Direct Final Rules approving requests from Ohio, Indiana, and
Kentucky to redesignate each of their respective portions of the Cincinnati-Hamilton area from
nonattainment to attainment status under the 1997 fine particulate matter NAAQS.
See
76 Fed.
Reg. 64,825, 64,825 (Oct. 19, 2011) [hereinafter “Direct Final Rule (Ohio/Indiana)”] (approving
the redesignation requests of Ohio and Indiana); 76 Fed. Reg. 77,903, 77,903 (Dec. 15, 2011)
(approving Kentucky’s redesignation request). Notably, the agency determined that the local
atmosphere had reached attainment status in significant part thanks to EPA’s three cap-and-trade
programs, which had reduced inflows of particulate matter from regional sources.
See
Direct
Final Rule (Ohio/Indiana),
In those comments Sierra Club made two arguments of particular relevance to this appeal. First, it contended that improvements in the area’s air quality attributable to the cap-and- trade programs were not “permanent and enforcement reductions in emissions” required under 42 U.S.C. § 7407(d)(3)(E)(iii), and that the Cincinnati area could therefore not be redesignated. Second, Sierra Club argued that the existing nonattainment SIPs had never implemented RACM/RACT rules under § 7502(c)(1), and that therefore EPA could not have “fully approved the applicable implementation plan” for purposes of § 7407(d)(3)(E)(ii). EPA rejected these comments in its Final Rule and redesignated the area to attainment status. 76 Fed. Reg. 80,253, 80,255–56, 80,258 (Dec. 23, 2011) [hereinafter “Final Rule (Ohio/Indiana)”]. Sierra Club then filed timely petitions asking this court to vacate the redesignation. The State of Ohio and a group of utilities operating in the Cincinnati area (the “Utilities Group”) intervened in support of EPA’s position.
II.
A.
At the outset, we must address a jurisdictional question. “Before bringing a case in
federal court, a plaintiff must establish standing to do so.”
Klein v. Dep’t of Energy
, 753 F.3d
576, 579 (6th Cir. 2014). An organization like Sierra Club can establish standing through two
routes: on behalf of its members, in what we have called “representational standing,” or on its
own behalf if directly injured.
Am. Canoe Ass’n v. City of Louisa Water & Sewer Comm’n
,
“The party invoking federal jurisdiction bears the burden of establishing these elements.”
Lujan v. Defenders of Wildlife
,
Here, we have a form of litigation not directly addressed by the Supreme Court in Lujan or subsequent cases: a petition for direct appellate review of final agency action. Surprisingly, more than two decades after Lujan , our circuit has not decided the “manner and degree of evidence” necessary to prove standing upon direct review, id. , so we must consider an issue of first impression. We now hold, like several of our sister circuits, that the petitioner carries a burden of production similar to that required at summary judgment.
The D.C. Circuit first took up the question of a petitioner’s burden in, fittingly, Sierra Club v. Environmental Protection Agency . 292 F.3d 895 (D.C. Cir. 2002). The D.C. Circuit thought a direct petition more analogous to summary judgment than a motion to dismiss. Id. at 899. Because “a petitioner seeking review in the court of appeals does not ask the court merely to assess the sufficiency of its legal theory[,]” but instead seeks “a final judgment on the merits, based upon the application of its legal theory to facts established by evidence in the record[,]” that party “must either identify in that record evidence sufficient to support its standing . . . [or] submit additional evidence to the court of appeals.” Id. The D.C. Circuit also thought this requirement “the most fair and orderly” means to adjudicate standing because petitioners are often best situated to produce evidence of their injuries. Id. at 901. The court therefore required the petitioner to present specific facts supporting standing through citations to the administrative record or “affidavits or other evidence” attached to its opening brief, unless standing is self- evident. at 900.
The Seventh, Eighth, and Tenth Circuits each found this reasoning persuasive.
N.
Laramie Range Alliance v. FERC
,
B.
An injury in fact must be “concrete and particularized” to the petitioner, and also “actual
or imminent, not conjectural or hypothetical.”
Lujan
,
We first note that many courts have apparently found it so obvious that redesignation
would lead to higher emissions that they did not even need to discuss the standing of
environmental litigants,
see, e.g.
,
BCCA Appeal Grp. v. EPA
, 355 F.3d 817, 847–48 (5th Cir.
2003) (assuming Sierra Club’s standing to force implementation of RACM/RACT), and we
ourselves have done so in a challenge by the Club concerning some of these very same rules,
see
Wall v. EPA
, 265 F.3d 426 (6th Cir. 2001). Yet the Clean Air Act addresses PM 2.5 pollution
through a wide variety of mechanisms, some of which might not present an “actual or imminent”
threat of increased exposure if relaxed after redesignation. The Kanfer Declaration primarily
addresses the structure and purposes of the Club and is entirely unhelpful on this issue. And
while the Wall Declaration broadly asserts that redesignation will increase fine particulate matter
in the area, it does not explain precisely how. Wall Decl. ¶ 12 (“I understand that areas
designated nonattainment . . . must take certain steps to remedy that pollution. If an area is
improperly redesignated, that results in more air pollution emitted and breathed by nonattainment
area residents such as myself.”). The Club’s standing therefore turns on what reasonable
inferences we can draw about redesignation’s impact on PM 2.5 .
Cf. Klein
,
Sierra Club more clearly identifies an impact on PM 2.5 emissions through the
RACM/RACT requirements under § 7502(c)(1), which, again, state that SIPs for nonattainment
areas “shall provide for the implementation of all reasonably available control measures . . .
including such reductions from
existing sources
in the area as may be obtained through the
adoption, at a minimum, of reasonably available control technology[.]” 42 U.S.C. § 7502(c)(1)
(emphasis added). Taking as true its claim that Ohio and Indiana did not have legally sufficient
RACM/RACT measures for fine particulate matter at the time of redesignation, we find it highly
likely that imposition of RACM/RACT would have some marginal effect on area emissions. Or
at least as likely as an environmental litigant could ever hope to establish.
See Monsanto Co. v.
Geertson Seed Farms
, 561 U.S. 139, 153 n.3 (2010) (finding an injury in fact where
“deregulation . . . pose[d] a significant risk of contamination to respondents’ crops”);
Sierra Club
v. EPA
,
Having found injury in fact, we can easily dispose of the redressability and causation
requirements, which often run together.
Allen v. Wright
,
III.
A reviewing court will set aside agency action that is “arbitrary, capricious, an abuse of
discretion, or otherwise not in accordance with law[.]” 5 U.S.C. § 706(2)(A). Where a petitioner
challenges an agency’s interpretation of a statute promulgated after notice-and-comment
rulemaking, we assess the lawfulness of the interpretation under the familiar two-step
Chevron
framework.
See United States v. Mead Corp.
,
But “[i]f the intent of Congress on a matter of statutory meaning is ambiguous, however,
the court is to proceed to ‘step two’ of the
Chevron
inquiry: whether the agency’s interpretation
is a ‘permissible construction of the statute.’”
Mid-America Care Found. v. NLRB
, 148 F.3d
638, 642 (6th Cir. 1998) (quoting
Chevron
,
A.
Sierra Club aims its first challenge at EPA’s compliance with 42 U.S.C. § 7407(d)(3)(E)(iii), which bars redesignation to attainment unless “the Administrator determines that the improvement in air quality is due to permanent and enforceable reductions in emissions resulting from implementation of the applicable implementation plan and applicable Federal air pollutant control regulations and other permanent and enforceable reductions[.]” More specifically, Sierra Club claims that EPA improperly included emissions reductions from cap-and-trade programs (including the NO x SIP Call, CAIR, and CSAPR) as “permanent and enforceable.” The plain meaning of this phrase, in the Club’s view, cannot accommodate a situation in which an individual emissions source can reduce its emissions one year but increase emissions in the next year through purchase of credits from other sources or from “spending” stored reduction credits from previous years.
The heart of this dispute is really where the sources that reduce their emissions must be located. Sierra Club implicitly asks this court to read § 7407(d)(3)(E)(iii) as requiring “permanent and enforceable reductions in emissions from sources in the nonattainment area .” Under this interpretation, EPA would need to determine that the Cincinnati area has achieved attainment status solely because sources within the confines of the nonattainment area have sufficiently reduced their emissions; improvements in Cincinnati air quality due to emissions reductions from anywhere else would be ignored. EPA and the Intervenors respond that the statutory text is silent on the location of the reductions and that a regional focus is necessary to address a fundamentally regional pollution problem. In other words, the States can show an improvement in Cincinnati air quality due to less inflow of particulate matter from sources outside the nonattainment area.
We think that the statutory context alone is sufficiently ambiguous for EPA to clear the
first step of
Chevron
.
Cf. Nat’l Ass’n of Home Builders v. Defenders of Wildlife
,
Here, EPA’s interpretation seems eminently reasonable. In its direct final rule, the
agency indicated that emissions from other “upwind” States significantly influence particulate
matter concentrations in the Cincinnati area. Final Rule (Ohio/Indiana), 76 Fed. Reg. at
80,256 (noting the “regional nature of particulate matter”); Direct Final Rule (Ohio/Indiana),
Moreover, even if EPA can count improvements in air quality attributable to reductions
from extra-area sources, Sierra Club contends that these reductions are not “permanent and
enforceable.” 42 U.S.C. § 7407(d)(3)(E)(iii). In its view, the plain meaning of “permanent”
requires that each and every source reducing its emissions “will never increase [its] emissions”
again. We, however, do not think it so obvious from this one word alone that the statute
forecloses inclusion of cap-and-trade programs. For one thing, Sierra Club assumes that
emissions “reductions” must be evaluated at the level of individual sources. But the statute does
not explicitly state whether the net “reductions” may be calculated for a wider area (like the state
or region). And for substantially the same reasons that § 7407(d)(3)(E)(iii) does not necessarily
limit the inquiry to reductions in the nonattainment area, EPA can plausibly and rationally
interpret the statute to allow a wider purview than individual sources. Under such an
interpretation, the “cap” in each of the cap-and-trade programs would ensure that the relevant
“reductions” are not foreseeably reversed, at least at the level of the entire cap-and-trade region.
See
Final Rule (Ohio/Indiana),
And we cannot say that this interpretation of “permanent” is impermissible. Sierra Club
asserts that anything other than an interpretation forbidding even temporary upticks in emissions
could, in the aggregate, completely undermine the NAAQS, but it overlooks that
§ 7407(d)(3)(E)(i) independently requires attainment of the standard as a condition of
redesignation. Furthermore, the threat of future designations of nonattainment (perhaps under
future particulate matter NAAQS) helps to mitigate any runaway increases in emissions after this
initial redesignation.
See
42 U.S.C. § 7407(d)(1)(B). Attainment status aside, the net benefits of
forbidding
any
source to
ever
increase emissions post-redesignation, a patently harsh standard, is
a policy judgment best left to the agency.
See Chevron
,
This leaves Sierra Club with only one remaining argument: that reductions attributable to cap-and-trade programs are not “enforceable.” 42 U.S.C. § 7407(d)(3)(E)(iii). Congress did not directly define “enforceable” in the Clean Air Act. id. § 7602. Nor does Sierra Club attempt to provide a fully inclusive definition of the term. Instead, it proffers other uses of the term “enforceable” as evidence that Congress did not think cap-and-trade programs create enforceable reductions. As noted earlier, § 7410(a)(2)(A) requires SIPs to “include enforceable emission limitations and other control measures , means, or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights) . . . .” (emphasis added). Sierra Club argues that Congress set “enforceable emission limitations” apart from “other control measures” (including tradeable permits) because the latter were not “enforceable.” But it seems at least as plausible that “other control measures” shares some meaning with the earlier phrase. At the very least, this possible inference from § 7410(a)(2)(A) leaves some doubt that Congress meant to exclude cap-and-trade reductions by inserting the word “enforceable.” Nor is there any reason to think an interpretation of reductions attributable to regional cap-and-trade schemes as “enforceable” any less rational than considering such reductions as “permanent.”
Ultimately, then, EPA has permissibly interpreted § 7407(d)(3)(E)(iii) to allow for a showing of “improvement in air quality” at least partially due to regional cap-and-trade schemes.
B.
Sierra Club next challenges EPA’s approval of the States’ respective SIPs without
RACM/RACT provisions specifically tailored towards fine particulate matter. Here, Sierra Club
alleges non-compliance with 42 U.S.C. § 7407(d)(3)(E)(ii), which prevents redesignation unless
“the Administrator has fully approved the applicable implementation plan for the area under
section 7410(k).” The Club argues that this section mandates implementation of the Clean Air
Act’s general RACM/RACT provision, which states that all SIPs for nonattainment areas “shall
provide for the implementation of all reasonably available control measures [RACM] as
expeditiously as practicable (including such reductions in emissions from existing sources in the
area as may be obtained through the adoption, at a minimum, of reasonably available control
technology [RACT]) . . . .” 42 U.S.C. § 7502(c)(1). In approving the redesignation requests of
Ohio and Indiana despite their lack of RACM/RACT,
[4]
EPA interpreted these provisions to
mandate these measures only if needed to attain the air quality standard for PM 2.5 . Final
Rule (Ohio/Indiana),
We have already addressed, and accepted, a similar challenge by the Club in
Wall v.
EPA
,
Sierra Club leans heavily on this court’s opinion in Wall for the proposition that the phrase “shall provide” in § 7502(c)(1) unambiguously means that RACM and RACT provisions “must be contained be contained in SIPs submitted with respect to redesignation requests” under the PM 2.5 NAAQS. We agree with the Club, despite the fact that Wall interpreted RACT requirements for ozone nonattainment areas, see 42 U.S.C. § 7511a(b)(2) (“The State shall submit a revision to the applicable implementation plan to include provisions to require the implementation of reasonably available control technology under section 7502(c)(1) of this title . . . .”) (emphasis added), because the statutory language at issue in that case is functionally identical to—and directly references—§ 7502(c)(1). We therefore reject EPA’s attempt to distinguish Wall on the grounds that that case is confined to the particulars of the ozone provisions. See Final Rule (Ohio/Indiana), 76 Fed. Reg. at 80,258 (“The Wall decision addressed entirely different statutory provisions for ozone RACT under CAA Part D subpart 2, which do not apply or pertain to the subpart 1 RACT requirements for [PM 2.5 ].”).
EPA raises two final arguments that we also find unconvincing. Relying mostly on a
decision from the Seventh Circuit,
Sierra Club v. EPA
,
But Wall forecloses either of these readings. Again, we held in that case that the Act unambiguously requires RACT in the area’s SIP as a prerequisite to redesignation—despite use of the phrase “applicable implementation plan” in the ozone RACT provision. See Wall , 265 F.3d at 440. Clearly, we did not read this phrase as an implicit delegation to the EPA to require ozone RACT only if necessary to attainment, and we do not now read that phrase in § 7407(d)(3)(E)(ii) as a similar delegation with respect to the general RACM/RACT provisions for all types of emissions. So we must respectfully disagree with the Seventh Circuit that “applicable implementation plan” is sufficiently vague to trigger Chevron deference.
As to EPA’s “applicable requirements” argument, we did note in
Wall
that this language
could be read to “limit[] the number of actual requirements within [§ 7410] and Part D that apply
to a given area.” 265 F.3d at 439. In
Wall
, in fact, we deferred to the agency’s view that
separate nonattainment provisions,
transportation conformity requirements, were not
“requirements applicable to the area” for the purposes of a
separate
redesignation requirement
located in § 7407(d)(3)(e)(v). at 438–39. But EPA cannot rely on that language to avoid
implementation of RACT provisions under the statutory sections at issue in this case—a
§ 7407(d)(3)(E)(ii) or in § 7502(c)(1)—which do not contain similar language. So our past
deference to the agency on the meaning of § 7407(d)(3)(E)(v) does not dispose of the Club’s
petition. Instead, as noted above, we look to
Wall’s
teachings on the type of language that does
occur in the provisions directly under review, and that type of language unambiguously requires
implementation of RACM/RACT prior to redesignation. Congress did not remain silent on this
issue.
Chevron
,
In sum, a State seeking redesignation “shall provide for the implementation” of RACM/RACT, even if those measures are not strictly necessary to demonstrate attainment with the PM 2.5 NAAQS. See 42 U.S.C. § 7502(c)(1). If the State has not done so, EPA cannot “fully approve[]” the area’s SIP, and redesignation to attainment status is improper. See id. § 7407(d)(3)(E)(ii). Because the Ohio and Indiana SIPs for their respective portions of the Cincinnati-Hamilton area did not provide for RACM/RACT, [5] the EPA acted in violation of the Clean Air Act when it approved those redesignation requests.
IV.
The petitions are granted in part and denied in part. We vacate the redesignations of the Ohio and Indiana portions of the Cincinnati-Hamilton area but leave the redesignation of the Kentucky portion undisturbed.
Notes
[*] The Honorable Robert M. Dow, Jr., United States District Judge for the Northern District of Illinois, sitting by designation. 1
[1] Sierra Club’s organizational purposes are germane to air pollution regulation, s ee Kanfer Decl. ¶ 2 (“The Sierra Club’s purposes are to explore, enjoy, and protect the wild places of the Earth; to practice and promote the responsible use of the Earth’s ecosystems and resources; . . . and to use all lawful means to carry out these objectives.”), and there is no reason to think that its members need to participate individually in the claim or relief requested.
[2] The parties do not meaningfully dispute that additional particulate matter in the atmosphere presents a greater risk to human health and may reduce visibility. See Am. Farm Bureau Fed’n v. EPA , 559 F.3d 512, 515 (D.C. Cir. 2009) (“Studies have demonstrated that both fine and coarse PM can have negative effects on public health and welfare. For example, each is associated with increased mortality (premature death) rates and morbidity (illness) effects such as cardiovascular disease and decreased lung function. . . . [H]igh levels of fine PM in the air can impair visibility . . . .”). See also Clean Air Fine Particle Implementation Rule, 72 Fed. Reg. 20,586, 20,586 (Apr. 25, 2007) (codified at 40 C.F.R. pt. 51) (“The EPA established air quality standards for PM 2.5 based on evidence from numerous health studies demonstrating that serious health effects are associated with exposures to elevated levels of PM 2.5 .”).
[3] We note that our characterization of the petitioner’s injury in this case might overlap with the causation element of standing. Under either label, our essential task is to determine how the redesignation influences the air quality of the Cincinnati area.
[4]
Like those of Ohio and Indiana, Kentucky’s redesignation request did not contain provisions for the
implementation of RACM/RACT for fine particulate matter. But as Sierra Club candidly acknowledges, the
petitioner has waived any objection to redesignation of the Kentucky area because it failed to comment on this
oversight during the rulemaking process.
See, e.g.
,
Natural Res. Def. Council v. Thomas
,
[5] Intervenor Utilities Group argues that Ohio’s SIP in fact includes RACT for PM 2.5 because it has general RACT provisions covering all types of emissions. This is not, however, the interpretation advocated by EPA as the justification for its rulemaking on redesignation. Recall that EPA took the position when approving redesignation that RACT requirements as a category only apply if needed to reach attainment. Final Rule (Ohio/Indiana), 76 Fed. Reg. at 80,255 (“[N]o RACT is required because the areas is attaining the standard.”); see id. at 80,258 (“[A] determination that an area has attained the PM 2.5 standard suspends the requirements to submit RACT and RACM requirements.”).
