recognizing agencies’ ability to fashion their procedures within broad constitutional and statutory limits
How later courts described this case
- recognizing agencies’ ability to fashion their procedures within broad constitutional and statutory limits
- explaining that the existence of a citizen-suit provision precludes review of identical claims under the Administrative Procedure Act
- referring to “the standard’s promulgation or last revision”
- discussing the Clean Water Act’s “requirement of a technology-based approach to promulgation and revision of regulations”
Written by the judges who cited it.
The opinion
UNITED STATES DISTRICT COURT
NORTHERN DISTRICT OF CALIFORNIA
CITIZENS FOR PENNSYLVANIA’S Case No. 19-cv-02004-VC
FUTURE, et al.,
Plaintiffs, ORDER RE CROSS-MOTIONS FOR
SUMMARY JUDGMENT
v.
Re: Dkt. Nos. 31, 32
ANDREW R. WHEELER,
Defendant.
This case addresses the provisions of the Clean Air Act that restrict types of air pollution
that are particularly hazardous to human health. The Act requires the Environmental Protection
Agency to regulate the sources of this pollution in two primary ways. First, the agency must
adopt “technology-based standards” to which polluters must adhere. As the name suggests, these
standards are designed to ensure that the polluters are using the best available technology to
mitigate the hazards created by their activities. And the statute requires EPA to revisit
technology-based standards periodically. Second, even after adopting technology-based
standards, the agency must assess the risks created by the polluters to determine whether
additional restrictions should be imposed. Such additional restrictions are referred to as “risk-
based standards.”
This case involves EPA’s failure to fulfill its statutory obligations to regulate pollution
from coke ovens. EPA mostly concedes its failures, so judgment will be entered for the plaintiffs
on most issues presented by this case. But one key legal issue remains in dispute: whether the
Clean Air Act requires EPA to perform a risk assessment every time it revises its technology-
based standards for a hazardous pollution source, or only in connection with its initial adoption
of technology-based standards for that pollution source.
The plaintiffs have a reasonable legal argument (as well as a reasonable policy argument)
that the statute should be read to impose a mandatory duty on the agency to conduct risk
assessments repeatedly rather than merely initially. But having a reasonable argument is not
enough in this context. Courts may not interpret statutes as imposing mandatory duties on
agencies unless the mandate is clear and unequivocal. The Clean Air Act does not clearly speak
to whether repeated risk assessments are mandatory or discretionary; that is to say, the statute
could reasonably be interpreted either way. Therefore, the Court may not interpret the statute as
imposing a mandatory duty on EPA to revisit its risk-based standards for hazardous pollution
sources whenever the agency revises technology-based standards.
I
A
In 1970, Congress amended the Clean Air Act to create a system of national emission
standards for hazardous air pollutants. See Clean Air Amendments of 1970, Pub. L. No. 91-604,
84 Stat. 1676. The cornerstone of that legislative effort was Section 112, which directed the EPA
Administrator to publish and, when appropriate, to revise a list of hazardous air pollutants “for
which he intends to establish an emission standard.” § 112(b)(1)(A), 84 Stat. at 1685. Upon the
listing of a hazardous air pollutant, the EPA Administrator was required to promulgate emission
standards that would provide an “ample margin of safety to protect the public health” from that
pollutant. § 112(b)(1)(B), 84 Stat. at 1685. This margin-of-safety standard was (and is) called a
“risk-based” approach because EPA calibrates emission standards to mitigate risks to human
health. Sierra Club v. EPA, 353 F.3d 976, 979 (D.C. Cir. 2004).
The regime established by the 1970 amendments was—to put it bluntly—a failure. Two
decades later, Congress surveyed EPA’s lack of progress in establishing national emission
standards, compiling a “record of false starts and failed opportunities.” S. Rep. No. 101-228,
p. 132 (1989). Congress, not content merely to blame EPA for the problem, acknowledged the
shortcomings of its own efforts to craft a workable statutory framework.
For one thing, Section 112 conferred a great deal of discretion on EPA in deciding
whether to regulate any particular pollutant. Although that provision required the EPA
Administrator to promulgate emission standards within 360 days of the listing of a hazardous air
pollutant, no provision of the Act forced him to decide in the first instance whether to add a
pollutant to the list. See Clean Air Act § 112(b), 84 Stat. at 1685. The upshot was that the EPA
Administrator didn’t have to assert authority over a pollutant, but if he did list a pollutant, he
then had to finalize emission standards on an “unrealistic” timetable. S. Rep. No. 101-228, at
132. Small wonder that EPA had established standards for only seven hazardous air pollutants in
the prior 20 years. See Sierra Club, 353 F.3d at 979.
Section 112’s risk-based approach to emission standards had also been difficult to
administer in practice. Because people in industrial and urban areas are exposed to higher
quantities of hazardous air pollutants, they suffer from higher rates of adverse health outcomes.
See S. Rep. No. 101-228, at 132. This inequality with respect to exposure created uncertainty
regarding what the appropriate emissions standard should be for a given pollutant. The Senate
Report therefore proposed to shift EPA’s “principal focus” under Section 112 away from directly
regulating pollutants and toward regulating pollution sources to reduce emissions with the “best
available control technology.” Id. at 133. This target, the Senate hoped, would prove an easier
mark for EPA to hit.
With these findings in hand, Congress substantially restructured Section 112. See Clean
Air Act Amendments of 1990, Pub. L. No. 101-549, § 301, 104 Stat. 2399, 2531–74.
Section 112, as amended, is codified at 42 U.S.C. § 7412. For simplicity’s sake, this ruling will
refer to the provision by its U.S. Code location—that is, “section 7412”—from this point
forward.
The 1990 amendments altered the original 1970 design in several important ways. Rather
than wait for EPA to take the initiative, Congress itself identified 189 hazardous air pollutants
and directed EPA to revise that initial list on a regular basis. 42 U.S.C. § 7412(b). Congress then
reoriented EPA’s attention, as the Senate Report suggested, to “sources” of pollution, specifying
two categories: “major sources” and “area sources.” § 7412(c). The former are defined as having
the potential to emit many tons of pollutants, while the latter are defined as “any building,
structure, facility, or installation [other than a vehicle] which emits or may emit any air
pollutant” at an amount below a major source. §§ 7411(a)(3), 7412(a)(1)–(3). To remedy the
perceived failings of the risk-based approach, Congress adopted the Senate Report’s proposal of
technology-based standards. § 7412(d). And to give teeth to this alternative regime, Congress set
a strict statutory timeline for EPA to promulgate technology-based standards for each source
category. § 7412(e)(1). Congress nonetheless preserved the risk-based approach to protect
against residual risks to public health that might linger after the adoption of technology-based
standards. § 7412(f). Taken together, these changes “eliminate[d] much of EPA’s discretion” in
setting national emission standards. New Jersey v. EPA, 517 F.3d 574, 578 (D.C. Cir. 2008).
The Clean Air Act thus now establishes a “two-phase approach” to emission standards
for hazardous air pollutants. Sierra Club, 353 F.3d at 980. At the first phase, EPA promulgates
technology-based emission standards requiring the “maximum achievable control technology”
for the source category. Id.; see 42 U.S.C. § 7412(d)(2) (discussing “measures, processes,
methods, systems or techniques” that reduce, eliminate, or capture emissions). Section 7412(d)—
once you muddle through its jargon—simply means that polluting businesses must adopt the
technology, techniques, and practices that their best-performing peers use (or that the source
category could practically adopt if the industry as a whole has not installed cost-effective control
technology). § 7412(d)(3). Every eight years, EPA must assess whether the technology-based
standards should be updated to reflect advances in control technology. § 7412(d)(6).
At the second phase, EPA performs a “risk-based analysis” to assess “whether residual
risks remain that warrant more stringent standards” to supplement the technology-based
standards. Sierra Club, 353 F.3d at 980; see 42 U.S.C. § 7412(f). This backstop—commonly
called a “residual risk review”—reflects Congress’ concern about “lingering public health risk”
not eliminated by “the initial standard” mandating the adoption of maximum achievable control
technology. National Association for Surface Finishing v. EPA, 795 F.3d 1, 5 (D.C. Cir. 2015).
Congress chose a very specific type and amount of risk that would force EPA to act: If “lifetime
excess cancer risks to the individual most exposed to emissions from a source” exceed one in one
million, EPA must promulgate risk-based standards that “provide an ample margin of safety to
protect public health.” 42 U.S.C. § 7412(f)(2)(A). Although the margin of safety must be
“ample,” EPA need not lower cancer risks below the one-in-one-million threshold. See Natural
Resource Defense Council v. EPA, 529 F.3d 1077, 1081–82 (D.C. Cir. 2008). The agency may
consider, in addition to health outcomes, other relevant factors like cost, feasibility, and
environmental impacts. See Surface Finishing, 795 F.3d at 5.
B
This dispute involves coke ovens, which convert coal into coke, a component in steel
production. Coke ovens emit multiple substances, including benzene and lead, that are harmful to
human health, and coke oven emissions are accordingly listed as a hazardous air pollutant by the
Clean Air Act. See 42 U.S.C. § 7412(b)(1). Indeed, the 1990 amendments, perhaps due to the
outsized health risks posed by coke oven emissions, prescribed a fixed statutory deadline for the
promulgation of technology-based standards for coke oven batteries (which are groups of ovens
connected by common walls) and enumerated a series of considerations that EPA must evaluate
for this particular source of pollution. 42 U.S.C. § 7412(d)(8), (e)(1)(B). Nor does the Act stop at
coke oven batteries. In fact, coke ovens give rise to multiple “source categories”—that is,
multiple types of polluting infrastructure regulated under the Clean Air Act.
The two source categories in this case are “Coke Oven Batteries” and “Coke Ovens:
Pushing, Quenching, and Battery Stacks.” The initial technology-based standards for coke oven
batteries were promulgated in 1993. 58 Fed. Reg. 57,898 (Oct. 27, 1993); see generally 40
C.F.R. Part 63, Subpart L. Then, in 2005, EPA revised the technology-based standards for this
category following its technology review under section 7412(d)(6); the agency also issued risk-
based standards following its residual risk review under section 7412(f)(2). 70 Fed. Reg. 19,992
(Apr. 15, 2005). As for the category of pushing, quenching, and battery stacks, EPA established
technology-based standards in 2003. 68 Fed. Reg. 18,008 (Apr. 14, 2003); see generally 40
C.F.R. Part 63, Subpart CCCCC. Two years later, these standards were amended pursuant to a
litigation settlement. 70 Fed. Reg. 44,285 (Aug. 2, 2005).
But EPA has taken no further action on either category in the last 15 years. This
rulemaking hiatus for coke ovens is no oversight or fluke. The agency has struggled mightily to
meet the statutory deadlines created by the 1990 amendments. In just the past few years, district
courts have determined that the EPA Administrator violated the deadlines in section 7412 for
more than 40 source categories. See Community In-Power & Development Ass’n, Inc. v. Pruitt,
304 F. Supp. 3d 212, 217 (D.D.C. 2018); Blue Ridge Environmental Defense League v. Pruitt,
261 F. Supp. 3d 53, 57 (D.D.C. 2017); California Communities Against Toxics v. Pruitt, 241
F. Supp. 3d 199, 202 (D.D.C. 2017); Sierra Club v. McCarthy, No. 15-cv-01165-HSG, 2016 WL
1055120, at *3 (N.D. Cal. Mar. 15, 2016).
The Clean Air Act contains an external enforcement mechanism—the citizen suit—to
keep EPA in compliance with its statutory and regulatory obligations. The Act’s citizen-suit
provision vests subject-matter jurisdiction in the federal district courts over actions brought by
“any person” who alleges “a failure of the Administrator to perform any act or duty under this
chapter which is not discretionary with the Administrator.” 42 U.S.C. § 7604(a)(2). Taking up
that charge, four environmental groups—Citizens for Pennsylvania’s Future, Gasp, Louisiana
Bucket Brigade, and Sierra Club—filed this citizen suit to compel EPA Administrator Andrew
Wheeler to complete both a technology review and a residual risk review for each of the two
source categories at issue in this case, Coke Oven Batteries and Coke Ovens: Pushing,
Quenching, and Battery Stacks. The lawsuit’s theory is that these duties (four in total) are non-
discretionary under section 7412(d)(6) and (f)(2). The parties have filed cross-motions for
summary judgment on these four claims.
EPA concedes three of the four claims. As it relates to pushing, quenching, and battery
stacks, EPA has neither performed a technology review of its initial technology-based standards
nor its first residual risk review. Accordingly, the parties agree that the Court should order EPA
to comply with its statutory duties by conducting both a technology review (because that type of
review is long overdue) and a residual risk review (because that type of review has never been
done). The only dispute is over the appropriate deadline for EPA to complete these tasks.
As it relates to coke oven batteries, EPA performed both a technology review and a
residual risk review in 2005. EPA concedes that a follow-up technology review is long overdue
under the recurring eight-year deadline, and thus that the plaintiffs should win on this claim as
well. But the plaintiffs also contend that EPA must perform a second residual risk review
because EPA revised the technology-based standards during its 2005 technology review.
Resisting this duty, EPA contends that a follow-up residual risk review is not required by the
statute because this type of review is mandatory only in connection with the initial technology
review. This dispute is the only substantive legal issue left in the case.
Section II of this ruling addresses this key substantive question: whether EPA violated a
non-discretionary duty by failing to perform a second risk review for the source category of coke
oven batteries. Section III determines the appropriate remedy for EPA’s conceded failure to
perform the three undisputed mandatory duties: the technology and risk reviews for pushing,
quenching, and battery stacks, and the technology review for coke oven batteries.
II
As detailed above, the Clean Air Act regulates hazardous air pollutants through a
combination of technology-based emission standards and risk-based emission standards. Those
technology-based standards, all agree, must be reviewed for potential revision every eight years.
42 U.S.C. § 7412(d)(6). But the plaintiffs contend that EPA must perform another residual risk
analysis within eight years of the revision of a technology-based standard—a recurring duty that
EPA allegedly triggered with its 2005 revisions to the technology-based standards for coke oven
batteries. In contrast, EPA argues that the residual risk review is a one-time obligation performed
within eight years of the date that the initial technology-based standards are established for a
given source category—a duty that EPA discharged in 2005 by conducting a risk review for coke
oven batteries. Both sides ground their conflicting positions in the language of section 7412(f).
That densely worded statute provides in relevant part:
If Congress does not act on any recommendation submitted under
paragraph (1), the Administrator shall, within 8 years after
promulgation of standards for each category or subcategory of
sources pursuant to subsection (d), promulgate standards for such
category or subcategory if promulgation of such standards is
required in order to provide an ample margin of safety to protect
public health in accordance with this section (as in effect before
November 15, 1990) or to prevent, taking into consideration costs,
energy, safety, and other relevant factors, an adverse environmental
effect. Emission standards promulgated under this subsection shall
provide an ample margin of safety to protect public health in
accordance with this section (as in effect before November 15,
1990), unless the Administrator determines that a more stringent
standard is necessary to prevent, taking into consideration costs,
energy, safety, and other relevant factors, an adverse environmental
effect. If standards promulgated pursuant to subsection (d) and
applicable to a category or subcategory of sources emitting a
pollutant (or pollutants) classified as a known, probable or possible
human carcinogen do not reduce lifetime excess cancer risks to the
individual most exposed to emissions from a source in the category
or subcategory to less than one in one million, the Administrator
shall promulgate standards under this subsection for such source
category.
§ 7412(f)(2)(A) (emphasis added).
To reemphasize the key portion of the statute, section 7412(f) mandates that EPA address
residual risks “within 8 years after promulgation of standards for each category or subcategory of
sources pursuant to subsection (d).” The parties offer competing interpretations of this language.
The question presented by the cross-motions—apparently one of first impression in any court—
is whether that duty is triggered only by the initial technology-based standards for a given source
category (as EPA argues) or also by each successive revision to the technology-based standards
(as the plaintiffs argue). Put differently, does the phrase “promulgation of standards” include
revisions to existing standards?
To prevail, the plaintiffs’ position must be more than merely plausible, because a “clear
statement rule” applies to citizen suits brought against the EPA Administrator under the Clean
Air Act. WildEarth Guardians v. McCarthy, 772 F.3d 1179, 1182 (9th Cir. 2014). That clear-
statement rule recognizes a duty as non-discretionary only when the duty takes the form of a
“‘specific, unequivocal command’ from the text of the statute at issue using traditional tools of
statutory interpretation.” Id. Here, the standard interpretive toolkit doesn’t eliminate the
ambiguity in the term “promulgation of standards” as applied to revisions. Section 7412(f)
therefore does not create a non-discretionary duty to review risk-based standards when existing
technology-based standards are revised.
To begin with, the text does not supply a readymade answer to the parties’ dispute. The
statute requires EPA to perform a residual risk review “within 8 years after promulgation of
standards for each category or subcategory of sources pursuant to subsection (d).” 42 U.S.C.
§ 7412(f)(2)(A). The triggering event for a mandatory risk review is the “promulgation of
standards . . . pursuant to subsection (d)”—a phrase that, at first glance, seems broad enough to
sweep in the revisions to the technology-based standards. That broad interpretation can be
distilled into three steps. First, a revision to an existing standard can itself be a “standard,”
meaning a requirement that “limits the quantity, rate, or concentration of emissions of air
pollutants on a continuous basis.” 42 U.S.C. § 7602(k). Second, a revision to a technology-based
standard is, technically speaking, “promulgated” in the Federal Register. See Ass’n of Battery
Recyclers, Inc. v. EPA, 716 F.3d 667, 673 (D.C. Cir. 2013) (per curiam). And third, the revision
is “pursuant to” (that is, under the authority of) section 7412(d)(6). See Kucana v. Holder, 558
U.S. 233, 244 (2010). So at least in some sense, each element of the text is present: (1) a
promulgation (the publication), (2) a standard (the revised emissions requirement), and (3) the
exercise of authority pursuant to subsection (d). But this is not the only reasonable interpretation
of the disputed statutory language, especially when the term “promulgation” is viewed in its
larger statutory context.
The word “promulgation” has no plain, ordinary meaning of universal application, nor is
“promulgation of standards” a term of art with a well-settled meaning. At times, you might say
“promulgation” when you intend to describe any “publication in the Federal Register.”
Horsehead Resource Development Co. v. EPA, 130 F.3d 1090, 1093 (D.C. Cir. 1997); see, e.g.,
Chase Bank USA, N.A. v. McCoy, 562 U.S. 195, 199 (2011). The plaintiffs advance that
technical, procedural meaning here. But you wouldn’t be taken aback if you heard an agency say
“promulgation of standards” when referring only to the establishment of a new standard, as
opposed to a revision to an existing standard. That definition, no less than the one favored by the
plaintiffs, is firmly within the ballpark of permissible meanings. See “Promulgation,” Black’s
Law Dictionary (11th ed. 2019) (“The official publication of a new law or regulation, by which it
is put into effect.”) (emphasis added). Because both definitions are commonplace, the text of
section 7412(f) can’t settle the debate on its own.
Nor can a uniform definition of “promulgation” be sensibly applied across the Clean Air
Act. Although “[a] term appearing in several places in a statutory text is generally read the same
way each time it appears,” Ratzlaf v. United States, 510 U.S. 135, 143 (1994), this interpretive
principle “readily yields to context, especially when a statutory term is used throughout a statute
and takes on distinct characters in distinct statutory provisions,” Return Mail, Inc. v. U.S. Postal
Service, 139 S. Ct. 1853, 1863 (2019) (internal quotation marks omitted). The plaintiffs
observe—quite correctly—that the Act sometimes uses the term “promulgation” in a way that
indisputably covers revisions to a standard. For example, technology-based standards are
“effective upon promulgation,” a phrase that surely includes revisions to such standards, lest the
revisions never take effect. 42 U.S.C. § 7412(d)(10). Yet the Act’s rulemaking procedures refer
to “the promulgation or revision” of 20 types of regulations. § 7607(d)(1)(A)–(M), (O)–(U)
(emphasis added). That promulgation-revision distinction applies to the technology-based
standards at issue here: “the promulgation or revision of any . . . emission standard or limitation
under section 7412(d).” § 7607(d)(1)(C).
By linking “promulgation” and “revision” with the disjunctive “or,” these provisions
indicate that the promulgation of a revision to a standard (in the technical sense of publication in
the Federal Register) is not itself a “promulgation of standards” (as the Clean Air Act uses that
phrase). See Encino Motorcars, LLC v. Navarro, 138 S. Ct. 1134, 1141 (2018). Perhaps
Congress wanted to make doubly clear that these statutes apply to revisions of standards as an
important subset of promulgations of standards. See Ali v. Federal Bureau of Prisons, 552 U.S.
214, 226 (2008). But that interpretation “effectively reads ‘or’ to mean ‘including’”—a feat of
linguistic gymnastics that invites a healthy dose of skepticism. Loughrin v. United States, 573
U.S. 351, 357 (2014). The phrase “promulgation or revision” therefore suggests (and courts have
likewise reiterated) that the revision of a standard is treated as a separate process from its
promulgation. See Surface Finishing, 795 F.3d at 5 (referring to “the standard’s promulgation or
last revision”); see also Our Children’s Earth Foundation v. EPA, 527 F.3d 842, 849 (9th Cir.
2008) (discussing the Clean Water Act’s “requirement of a technology-based approach to
promulgation and revision of regulations”).
The belt-and-suspenders explanation for “promulgation or revision” also clashes with the
principle that statutes should be interpreted, when possible, such that “no clause, sentence, or
word shall be superfluous, void, or insignificant.” TRW Inc. v. Andrews, 534 U.S. 19, 31 (2001).
Redundancy, standing alone, is no reason to ignore the best reading of the statute. See Barton v.
Barr, 140 S. Ct. 1442, 1453 (2020). But the plaintiffs’ interpretation is undermined by the
number of times Congress distinguished between promulgation and revision in the Clean Air
Act. Consider, for instance, the statute’s reference to “the promulgation of a national primary
ambient air quality standard (or any revision thereof).” 42 U.S.C. § 7410(a)(1). Or the allowance
that EPA “may promulgate (and from time to time revise) regulations establishing” fees for the
motor vehicle compliance program. § 7552(a). Or the Act’s command that EPA designate air
quality control regions “[u]pon promulgation or revision of a national ambient air quality
standard.” § 7407(d)(1)(B)(i). Congress thus knew how to make non-discretionary duties
explicitly contingent on both promulgations and revisions, but it did not take this path in
section 7412(f). Indeed, the Clean Air Act’s repeated distinction between promulgation and
revision makes Congress’ selection of only one of the two terms here “seem quite deliberate.”
DHS v. MacLean, 574 U.S. 383, 392 (2015); see, e.g., 42 U.S.C. §§ 7409(b)(1), 7410(n)(2)(A),
7617(a), 7620(d). The Act’s structure thus supports the conclusion “that Congress differentiated
duties stemming from a ‘promulgation’ versus a ‘revision.’” WildEarth Guardians v. Jackson,
870 F. Supp. 2d 847, 854 (N.D. Cal. 2012).
Precedent confirms that a revision to an existing standard does not necessarily qualify
under the Clean Air Act as a “promulgation of standards.” In WildEarth Guardians, the Ninth
Circuit interpreted a statute that requires EPA to promulgate Prevention of Significant
Deterioration (PSD) regulations “not more than 2 years after the date of promulgation of such
standards” setting national ambient air quality standards (NAAQS). 42 U.S.C. § 7476(a). There,
like here, the plaintiffs sued the EPA Administrator for her failure to revise one set of regulations
upon the revision of a related standard. EPA, the plaintiffs argued, must “promulgate PSD
regulations not only when NAAQS are first issued for a newly regulated pollutant, but also when
NAAQS are revised for any pollutant.” WildEarth Guardians, 772 F.3d at 1181. But the
plaintiffs’ claim could not overcome the clear-statement rule for citizen suits brought under the
Clean Air Act. The Ninth Circuit explained that the statutory language—“promulgation of such
standards”—could plausibly be read to require PSD regulations only upon the initial NAAQS for
a pollutant, and that Congress could sensibly leave “to the agency’s discretion the responsibility
for making whatever revisions to those regulations might be warranted when the corresponding
NAAQS were revised.” Id. at 1182.
The plaintiffs protest the relevance of WildEarth Guardians to section 7412(f). The Ninth
Circuit, as they read the court’s opinion, found ambiguity only as to which pollutants are covered
by the statute. To be sure, the statute in WildEarth Guardians draws a distinction between those
pollutants for which Congress itself had established NAAQS and the pollutants for which EPA
would establish the initial NAAQS. See 42 U.S.C. § 7476(a). But the court didn’t rely solely on
that point. To the contrary, the Ninth Circuit also recognized the plausibility of EPA’s argument
that “Congress could have been content to kick-start the PSD program” with “a one-time duty of
limited scope: to promulgate PSD regulations within two years after NAAQS are first issued for
a newly regulated pollutant.” WildEarth Guardians, 772 F.3d at 1181–82 (first emphasis added).
So too here.
The plaintiffs’ interpretation also runs contrary to the guidepost that “Congress generally
acts intentionally when it uses particular language in one section of a statute but omits it in
another.” Republic of Sudan v. Harrison, 139 S. Ct. 1048, 1058 (2019) (internal quotation marks
omitted). While section 7412(f) says nothing explicit about revising risk-based standards,
neighboring subsections direct EPA in no uncertain terms to “revise” four other types of
regulations: the list of hazardous air pollutants, the list of source categories, technology-based
emission standards, and certain emissions limitations. 42 U.S.C. § 7412(b)(2), (c)(1), (d)(6),
(i)(8)(C). EPA, for example, must “review, and revise as necessary (taking into account
developments in practices, and control technologies), emissions standards promulgated under
this section no less often than every 8 years.” § 7412(d)(6). Thus, where Congress wanted to
establish a recurring obligation in section 7412, the statute appears to accomplish that goal by
express language, not by latent implication. See Limelight Networks, Inc. v. Akamai
Technologies, Inc., 572 U.S. 915, 922–23 (2014). The absence of parallel language in
section 7412(f) is yet another reason to be skeptical that the statute clearly commands the
plaintiffs’ interpretation.1
Prior interpretations of the statute further reinforce the plausibility of EPA’s position.
While no court has addressed this question head-on, the D.C. Circuit characterized
section 7412(f) as a “one-time risk review.” Surface Finishing, 795 F.3d at 5. The court’s
1 Speaking of section 7412(d)(6), that statute arguably requires EPA to review risk-based
standards for potential revision. Risk-based standards, like technology-based standards, fit the
description in the phrase “review, and revise as necessary . . . , emission standards promulgated
under this section”—that is, standards authorized by section 7412. 42 U.S.C. § 7412(d)(6); see
§ 7412(f)(2) (titled “Emission standards”). “But when read in context, with a view to its place in
the overall statutory scheme,” section 7412(d)(6)—despite its textual overbreadth—likely applies
only to standards promulgated under section 7412(d). King v. Burwell, 135 S. Ct. 2480, 2490
(2015) (internal quotation marks and brackets omitted). The strongest clue that Congress
intended a narrower reach is that the provision is nestled within a subsection that pertains only to
technology-based standards. At a bare minimum, section 7412(d)(6) is ambiguous on this point,
and EPA has concluded, in a notice-and-comment rulemaking, that “section 112(d)(6) should be
interpreted as applying only to standards adopted under section 112(d).” 70 Fed. Reg. at 20,008.
So while section 7412(d)(6) is no model of careful draftsmanship, not even the plaintiffs contend
that this provision is an unequivocal command to review risk-based standards promulgated under
section 7412(f).
passing remark was dictum, but its description matches EPA’s nearly decade-long position that
section 7412(f) is a “one-time review.” 81 Fed. Reg. 97,046, 97,048 (Dec. 30, 2016); 77 Fed.
Reg. 55,698, 55,699 (Sept. 11, 2012). As the plaintiffs note, the D.C. Circuit’s interpretation is
not binding in this (or any) case, and EPA’s interpretations—although far from a “convenient
litigating position” or “post hoc rationalization”—are too conclusory to merit any form of
deference. Christopher v. SmithKline Beecham Corp., 567 U.S. 142, 155 (2012) (internal
quotation marks and brackets omitted). Yet the fact that judges and agency officials have both
articulated an interpretation of section 7412(f) contrary to the plaintiffs’ only underscores the
absence of a clear statement.
As the plaintiffs point out, the original Senate bill would have unambiguously dictated
the interpretation urged by EPA by conditioning residual risk reviews on “the initial
promulgation of emissions standards for a category or subcategory of sources pursuant to
subsection (d).” S. 1630, 101st Cong. § 301 (1989) (emphasis added) (proposing Clean Air Act
§ 112(e)(7)(A)). The word “initial” is not present in the provision eventually passed by Congress.
See 42 U.S.C. § 7412(f)(2)(A). Relying on this absence, the plaintiffs intone the familiar maxim
that when “Congress includes limiting language in an earlier version of a bill but deletes it prior
to enactment, it may be presumed that the limitation was not intended.” Russello v. United
States, 464 U.S. 16, 23–24 (1983). To the extent that drafting history can substitute for (or more
charitably put, elucidate) a “‘specific, unequivocal command’ from the text of the statute,”
WildEarth Guardians, 772 F.3d at 1182, the inference that Congress intended “promulgation” to
include revisions is surely debatable here. Congress did not merely strike the word “initial” with
red pen when marking up the Senate bill; instead, Congress “entirely rewrote” subsections (e)
and (f) during the legislative process, and the adjective “initial” may have been “simply lost in
the shuffle.” United States v. Wilson, 503 U.S. 329, 336 (1992); compare 42 U.S.C. § 7412(e),
(f) with S. 1630 § 301. But even assuming (somewhat doubtfully) that the drafters intentionally
omitted the word “initial,” and even assuming (yet more doubtfully) that the legislators who
voted on the bill considered this issue, it’s equally plausible that Congress decided that the
adjective would be superfluous because “promulgation” already excludes revisions of existing
standards. See Murphy v. Smith, 138 S. Ct. 784, 790 n.2 (2018).
The plaintiffs, moving to the frontier of policy, contend that EPA’s interpretive
arguments from text, context, and precedent (however reasonable in the abstract) threaten to
severely undermine the Clean Air Act’s framework for the regulation of hazardous air pollutants.
Cf. County of Maui v. Hawaii Wildlife Fund, 140 S. Ct. 1462, 1474 (2020). Their main objection
is that EPA is never forced to perform an additional residual risk review, no matter what new
risks emerge in the future. For example, the plaintiffs observe that EPA, under its interpretation,
would not be required to perform a risk review after listing a new hazardous air pollutant emitted
by a source for which standards already exist. The listing of a new pollutant might call into
question whether the risk-based standards for that source truly “provide an ample margin of
safety to protect public health,” since the particular risks posed by the new pollutant have never
been considered as part of a risk review for the source category. 42 U.S.C. § 7412(f)(2)(A). But
nothing in the text or legislative history suggests that anyone in Congress considered whether the
risk-review process should be repeated. In any event, the plaintiffs’ interpretation does not
guarantee another residual risk review at all, let alone a prompt response to a new listing,
because the duty would be triggered only if the corresponding technology-based standards are
later revised.
Finally, the plaintiffs argue that their claim does not implicate “whether the EPA’s duty is
clear-cut, but whether the duty is triggered at all” by revisions, a proposition they support by
citing Natural Resources Defense Council v. McCarthy, 231 F. Supp. 3d 491, 502 n.10 (N.D.
Cal. 2017). But in that case, EPA possessed a clear-cut duty to act upon a State’s submission of
any “revised or new standard,” and the parties disputed only whether certain state orders as a
factual matter constituted revisions. 33 U.S.C. § 1313(c)(2)(A); see McCarthy, 231 F. Supp. 3d
at 498. In contrast, as the foregoing analysis shows, whether a revision to an existing technology-
based standard counts as a “promulgation of standards” under section 7412(f) is a purely legal
question of statutory interpretation, not a mixed question of applying a statute to the real-world
facts on the ground. See U.S. Bank N.A. v. Village at Lakeridge, LLC, 138 S. Ct. 960, 965–66
(2018). Here, as in WildEarth Guardians, the scope of the statute—and thus the scope of EPA’s
duty—is unclear.
Both parties have put forward plausible interpretations of the statute, and when the statute
could reasonably be read either way, the clear-statement rule dictates the outcome of the case. To
acknowledge that risk-based standards may or even should be revised does not answer whether
and when they must be revised. Indeed, the Clean Air Act expressly contemplates that EPA
might revise its risk-based standards. See 42 U.S.C. § 7607(d)(1)(C) (referring to “the
promulgation or revision of . . . any standard under section 7412(f)”). But Congress—wisely or
foolishly, by compromise or by oversight—did not establish a clear-cut duty to review risk-based
standards for potential revision when technology-based standards are revised.2
The only remaining question is whether the absence of a clear-cut duty means that this
claim should be dismissed for lack of subject-matter jurisdiction or denied on the merits. The
most on-point precedent (once again) is WildEarth Guardians, which dismissed a claim for lack
of jurisdiction under similar circumstances. See 772 F.3d at 1182. To rebut this conclusion, the
plaintiffs insist that they need make only a “colorable claim” that the revisions qualify as
promulgations of standards to get to the merits of the claim. Leeson v. Transamerica Disability
Income Plan, 671 F.3d 969, 979 (9th Cir. 2012). Leeson addressed the burden of establishing
subject-matter jurisdiction when material facts are disputed, but as just explained, this case turns
on a “pure question of statutory construction.” Bolivarian Republic of Venezuela v. Helmerich &
Payne Int’l Drilling Co., 137 S. Ct. 1312, 1318 (2017) (internal quotation marks omitted). At
least “[w]here, as here, the facts are not in dispute,” the colorable-claim standard is inconsistent
with the Supreme Court’s recent admonition that plaintiffs must “show (and not just arguably
show)” that the jurisdictional prerequisites are met. Id. at 1324. That means that “[s]imply
2 That said, the plaintiffs are not left entirely without recourse. Out-of-date risk-based standards
can be challenged by a petition for rulemaking under the Clean Air Act, and EPA’s action on any
such petition would be subject to judicial review. 42 U.S.C. § 7607(b)(1); cf. Massachusetts v.
EPA, 549 U.S. 497, 533 (2007).
making a nonfrivolous argument” in support of jurisdiction under 42 U.S.C. § 7604(a)—as the
plaintiffs have done here—“is not sufficient.” Id. Although Helmerich interpreted a statute
related to foreign sovereign immunity, citizen-suit provisions operate in the analogous context of
federal sovereign immunity. See Department of Energy v. Ohio, 503 U.S. 607, 615 (1992).
Accordingly, this claim is dismissed for lack of subject-matter jurisdiction. See Coos County
Board of County Commissioners v. Kempthorne, 531 F.3d 792, 802–03, 810 (9th Cir. 2008)
(explaining that the existence of a citizen-suit provision precludes review of identical claims
under the Administrative Procedure Act).
III
EPA concedes liability on the plaintiffs’ three remaining claims, admitting its failure to
perform: (i) an initial technology review for the “Pushing, Quenching, and Battery Stacks”
category; (ii) any risk review at all for the “Pushing, Quenching, and Battery Stacks” category;
and (iii) a follow-up technology review for the “Coke Oven Batteries” category. Summary
judgment is therefore granted to the plaintiffs on these three claims.
When a failure-to-act violation is proved by citizen suit, the Clean Air Act authorizes the
district court “to order the Administrator to perform such act or duty.” 42 U.S.C. § 7604(a). The
parties have proposed dueling timelines for completing these non-discretionary tasks. The
plaintiffs ask for an injunction requiring EPA to publish a notice of proposed action within 12
months and to finalize each action within 16 months; EPA counters that 24 and 36 months,
respectively, are necessary for each task. EPA also argues that no intermediate deadlines for
notices of proposed action are warranted here.
In this context, the courts have applied an “impossibility” standard for remedying
violations of statutory deadlines. Natural Resources Defense Council, Inc. v. Train, 510 F.2d
692, 713 (D.C. Cir. 1975); Sierra Club v. Thomas, 658 F. Supp. 165, 171 (N.D. Cal. 1987).
Congress already prescribed a timeline, and its “deadlines are not aspirational.” Natural
Resources Defense Council, Inc. v. EPA, 966 F.2d 1292, 1300 (9th Cir. 1992). Respect for
congressional prerogatives means that once the agency violates a statutory deadline, the judiciary
should not balance the costs and benefits of further delaying Congress’ objectives. The remedial
question is instead one of parsimony. Courts should grant no more—but also no less—time than
necessary for EPA to perform its non-discretionary duties.
The impossibility standard is tempered somewhat by the recognition that the agency’s
speed in completing a rulemaking is subject to multiple constraints. Most prominently, the court
must consider “budgetary commitments and manpower demands” because EPA can expend only
those resources appropriated by Congress. Train, 510 F.2d at 712; cf. 31 U.S.C. § 1341. Nor
would a more stringent deadline benefit anyone—not Congress, the plaintiffs, or people exposed
to hazardous air pollutants—unless EPA can adequately compare the “relative merits” of
different regulatory paths. Train, 510 F.2d at 712. In addition, a lengthier schedule “may well
ensure earlier, not later, implementation of any eventual regulatory scheme,” because a hasty
rulemaking process risks “later judicial invalidation and remand to the agency.” Sierra Club v.
Thomas, 828 F.2d 783, 798–99 (D.C. Cir. 1987). The remedial question, notwithstanding the
“impossibility” label, is really about feasibility given the agency’s existing constraints. Still,
EPA shoulders a “heavy burden” to demonstrate that its proposal is the shortest feasible
schedule. Blue Ridge, 261 F. Supp. 3d at 61.
The plaintiffs contend that EPA could complete the two technology reviews and the
single risk review within 16 months. There is reason to doubt that this schedule would be
feasible. No court has ordered a risk or technology rulemaking to take place in so short a period,
and the plaintiffs have not adequately explained how EPA could complete each crucial step of
the rulemaking process during their timeframe. Nor do the plaintiffs dispute EPA’s
representation that coke ovens are among the most complex of the nearly 200 source categories.
Finally, the plaintiffs have not supported their contested (and contestable) assertions that because
the source categories cover different emission points in a single type of facility, and because
EPA has already completed a technology review for coke oven batteries, these rulemakings can
be completed faster than normal.
EPA, for its part, submitted a declaration from Penny Lassiter, the Director of the Sector
Policies and Programs Division, which is responsible for EPA’s risk and technology reviews.
She estimated the time necessary to complete each of the remaining seven phases in the
rulemaking process, concluding that these rulemakings could not be completed in under 36
months. Yet her schedule builds in extra steps beyond those necessary to produce an
environmentally sound and legally defensible rule. Most glaringly, her schedule allots six months
total for two separate pre-publication reviews by the Office of Management and Budget (OMB).
But EPA has blown through its statutory deadlines, and additional rulemaking procedures
beyond those required by law are a luxury that people exposed to hazardous coke oven emissions
can ill afford. See Community In-Power, 304 F. Supp. 3d at 223. Whatever the ideal practices
might be, it is not impossible or infeasible to direct the agency to adopt the most expeditious
procedures to remedy a statutory violation. Cf. Vermont Yankee Nuclear Power Corp. v. Natural
Resources Defense Council, Inc., 435 U.S. 519, 543 (1978) (recognizing agencies’ ability to
fashion their procedures within broad constitutional and statutory limits). And EPA can—indeed,
must—reallocate resources to the extent possible to satisfy its court-ordered deadlines. See
Community In-Power, 304 F. Supp. 3d at 222–23.
Courts have also considered the agency’s diligence when crafting the appropriate remedy.
Here, the Administrator has not exercised “the utmost diligence in discharging his statutory
responsibilities.” Train, 510 F.2d at 713. Recent district court decisions have confirmed that EPA
regularly violates its statutory deadlines and waits for a citizen suit to concede liability before
beginning the technology and risk reviews required by section 7412. That is to say, EPA has
effectively swapped out concrete congressional deadlines for later-in-time, ad hoc judicial
deadlines; meanwhile, the Sector Policy and Programs Division has expended resources on
discretionary tasks. See Community In-Power, 304 F. Supp. 3d at 221–22. This factor weighs
against EPA’s proposed schedule.
The Court is not bound to pick between the parties’ proposals when neither adheres to the
impossibility standard. See id. at 224. Although the Lassiter declaration is a useful starting point,
its phase-by-phase breakdown of the rulemaking process allots six of the 36 months to optional
OMB review. Moreover, it appears that rulemakings in the mine-run of source categories can be
completed in 18 to 21 months, see, e.g., Blue Ridge, 261 F. Supp. 3d at 61, and another court
deemed a “2.5-year timeframe to be a useful benchmark” in this context, California
Communities Against Toxics, 241 F. Supp. 3d at 205. Taking account of the complexity of the
coke oven source categories, the Court determines that EPA could feasibly take final action in
these two categories within 30 months of this ruling. The employees in the Sector Policy and
Programs Division should be able to turn to these rulemakings as many of the court-ordered
deadlines mentioned earlier come off the books. And the 30-month deadline runs from this
ruling, rather than February’s hearing on the cross-motions, in light of the strain on resources
created by the current global pandemic. The Court declines to impose any intermediate deadlines
here, so EPA can distribute the 30 months across the various rulemaking phases as it deems
appropriate.
IT IS SO ORDERED.
Dated: June 26, 2020 z=
VINCE CHHABRIA
United States District Judge