Amicus Curiae Brief — Whitman v. American Trucking Assns., Inc.
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Text
Supreme Court, U.S.
No. 99-1257 FILED
In The
Supreme Court of the |Unitét_ Skies
¢
CAROL M. BROWNER, ADMINISTRATOR OF THE
ENVIRONMENTAL PROTECTION AGENCY, ET AL.,
Petitioners,
Vv.
AMERICAN TRUCKING ASSOCIATIONS, INC., ET AL.,
Respondents.
°
On Writ of Certiorari to the United States Court
of Appeals for the District of Columbia Circuit
o
BRIEF OF AMICI CURIAE
ENVIRONMENTAL DEFENSE, ET AL.
ON BEHALF OF PETITIONERS
¢
RicHarp L. Revesz
Counsel of Record
40 Washington Square South
Suite 411-D
New York, N.Y. 10012
212-998-6185
Vickie PATTON
Environmental Defense
1405 Arapahoe Avenue
Boulder, CO 80302
303-440-4901
ANN BrewsTeR WEEKS
Clean Air Task Force
77 Summer Street, 8th Floor
Boston, MA 02110
617-292-0234
Counsel for Amici Curiae Environmental Defense, et al.
July 21, 2000
TABLE OF CONTENTS
Page
TABLE OF AUTHORITIES ................0seeeeee. iii
INTEREST OF AMICI CURIAE...............00005. 1
SUMMARY OF ARGUMENT.................000005 1
REGIE oc ccccccesscessoveentdectcccesvccesees 3
I. THE D.C. CIRCUIT’S REMAND OF THE EPA
REGULATIONS IS BASED UPON A CONSTI-
TUTIONALLY IMPERMISSIBLE APPLICA-
TION OF THE NONDELEGATION
PEPE ccccevcnccsscwiclucdansvabseseuss 3
Il. THE D.C. CIRCUIT’S APPROACH IMPER-
MISSIBLY INTERFERES WITH THE PROPER
FUNCTIONING OF THE DEMOCRATIC
= PPPPVTTTITITIT TTT TT rr ee 7
III. SECTIONS 108 AND 109 OF THE CLEAN AIR
ACT DO NOT RUN AFOUL OF THE NON-
DELEGATION DOCTRINE .................. 9
A. The Clean Air Act gives considerable guid-
ance to EPA on how to set the NAAQS... 9
B. The D.C. Circuit’s suggestion that EPA
was free to set the NAAQS at any level
between zero and the concentration of
London’s Killer Fog stems from a misun-
derstanding of the Clean Air Act........ 14
C. The Court’s jurisprudence establishes that
the Clean Air Act does not violate the
nondelegation doctrine .................. 19
D. The D.C. Circuit’s reliance on Schechter
Poultry is misplaced...............++04+: 21
TABLE OF CONTENTS - Continued
Page
E. The D.C. Circuit also is mistaken in main-
taining that broad delegations are permis-
sible only in special circumstances....... 23
IV. THE D.C. CIRCUIT ERRED IN HOLDING
THAT EPA’S AUTHORITY TO IMPLEMENT
THE 8-HOUR OZONE STANDARD IS CON-
STRAINED BY SECTION 181 OF THE CLEAN
BR BCT ccccccccccccvccccccccccccvccccccess 23
CONCLUSION .......... cece cece cece eee eeeeeeeees 30
TABLE OF AUTHORITIES
Page
Cases:
A.L.A. Schechter Poultry Corp. v. United States, 295
es Gee GED wes cccvcccssasecssncsees 19, 21, 22, 23
Amalgamated Meat Cutters v. Connally, 337 F. Supp.
FE Gs SEWED evcdicccccccdnccdctvcsccesenansecs 5
Baltimore Gas & Elec. Co. v. NRDC, 462 U.S. 87
PEE oS ccntccenececccasusceecuecenoseuseecessennss 5
Chevron, U.S.A., Inc. v. NRDC, 467 U.S. 837 (1984) . .8, 30
Commissioner v. Clark, 489 U.S. 726 (1989) ........... 25
Gustafson v. Alloyd Co., 513 U.S. 561 (1995).......... 29
Industrial Union Dep't, AFL-CIO v. American Petro-
leum Inst., 448 U.S. 607 (1980) .................005- 4
International Union, UAW v. OSHA, 938 F.2d 1310
Se GD GOD bev encenscccsenntesesscccancecuséas 5
].W. Hampton & Co. v. United States, 276 U.S. 394
SUPE eS 06S oc enconcsscenctuccccooncenesscesonceeess 3
Lichter v. United States, 334 U.S. 742 (1948)....... 19, 20
Loving v. United States, 517 U.S. 748 (1996)..... 3, 4, 20
Mistretta v. United States, 488 U.S. 361 (1989)
i ae ae ei eel eee eel oe ed 3, 4, 19, 22, 23
Morales v. Trans World Airlines, Inc., 504 U.S. 374
ia tide tied ine ed etiekeenkeiedsenksanenneel 25
Motor Vehicle Mfrs. Ass'n v. State Farm Mut. Auto.
Cs Se U, 2 OED ccucnncouscoceseees 6, 8, 9
National Broad. Co. v. United States, 319 U.S. 190
Ditch nvédcasndcdoousedheeteubeosenqunsennss 19, 20
Peed caccccevccceccccnsesccceccecscosesceesesss 6, 9
iv
TABI F OF AUTHORITIES - Continued
Page
Panama Ref. Co. v. Ryan, 293 U.S. 388 (1935)..19, 21, 22
Touby v. United States, 500 U.S. 160 (1991) ..3, 4, 19, 20, 23
Yakus v. United States, 321 U.S. 414 (1944)....19, 20, 22
STATUTES:
Administrative Procedure Act, 5 U.S.C. § 551 et seq.
§ 4(a)-(b), 5 U.S.C. § 553(b)-(c).... 2.6 ee eee eee 22
§ 10(e), 5 U.S.C. § 706(2)(A) ...... 66. ee eee eee 5
Clean Air Act, 42 U.S.C. § 7401 et seq.
§ 107(d), 42 U.S.C. § 7407(d)........... 24, 27, 28, 29
§ 107(d)(1)(A), (B), 42 U.S.C. § 7407(d)(1)(A), (B) .... 29
§ 107(d)(1)(C), 42 U.S.C. § 7407(d)(1)(C)........ 28, 29
§ 107(d)(3), 42 U.S.C. § 7407(d)(3)............----- 29
§ 107(d)(4), 42 U.S.C. § 7407(d)(4).............. 28, 29
§ 108, 42 U.S.C. § 7408........... 2, 9, 11, 12, 19, 20
§ 108(a)(1), 42 U.S.C. § 7408(a)(1) ...........---6-- 10
§ 108(a)(1)(A), 42 U.S.C. § 7408(a)(1)(A).......---- 22
§ 108(a)(2), 42 U.S.C. § 7408(a)(2) ...........--. 10, 11
B 269, 2 USL. & POBD .. cc ccccsccccccccccces passim
§ 109%(b), 42 U.S.C. § 7409%(b)............... 16, 17, 18
§ 109%(b)(1), 42 U.S.C. § 7409(b)(1).......... 11, 14, 22
§ 109(b)(2), 42 U.S.C. § 7409(b)(2)........- eee eee 11
§ 10%(d), 42 U.S.C. § 7409(d)....... 2... eee ees 15, 28
Vv
TABLE OF AUTHORITIES - Continued
Page
§ 109(d)(1), 42 U.S.C. § 7409(d)(1)................. 12
§ 109(d)(2), 42 U.S.C. § 7409(d)(2).........0....... 23
§ 109(d)(2)(A), 42 U.S.C. § 7409(d)(2)(A) .......... 12
§ 109(d)(2)(B), 42 U.S.C. § 7409(d)(2)(B) ........... 12
§ 110(a)(2)(D)(i), 42 U.S.C. § 7410(a)(2)(D)(i(]) ... . . 28
§§ 171-179B, 42 U.S.C. §§ 7501-7509a.............. 24
Brey Se ie OO Pec ccccccecccccesncectocs 25, 29
§ 172(a)(1)(A), 42 U.S.C. § 7502(a)(1)(A)........... 29
§ 172(a)(2), 42 U.S.C. § 7502(a)(2).............. 24, 25
§ 172(a)(2)(A), 42 U.S.C. § 7502(a)(2)(A)........ 24, 29
§ 172(a)(2)(B), 42 U.S.C. § 7502(a)(2)(B)............ 24
§ 172(a)(2)(C), 42 U.S.C. § 7502(a)(2)(C) ........... 24
§ 172(a)(2)(D), 42 U.S.C. § 7502(a)(2)(D)........... 25
fF Sf ee passim
§ 181(a)(1), 42 U.S.C. § 7511(a)(1)...... 25, 26, 27, 28
§§ 181-185B, 42 U.S.C. §§ 7511-7511f.............. 24
. §§ 181-192, 42 U.S.C. §§ 7511-7514a............... 24
§ 302(h), 42 U.S.C. § 7602(h)............... 11, 12, 21
5 SONG), 42 USC. § PEGA)... nc cccccccccccces 22
§ 307(d)(2), (4)(A), 4(B)(ii), (5), 42 U.S.C.
§ 7607(d)(2), (4)(A), 4(B)(ii), (5) ...........0000.. 22
§ 307(d)(2)-(7), 42 U.S.C. § 7607(d)(2)-(7) .......... 22
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vi | vii
TABLE OF AUTHORITIES - Continued TABLE OF AUTHORITIES - Continued
Page Page
§ 307(d)(3), 42 U.S.C. § 7607(d)(3)..........-+-- 12, 23 ) i, DEED ssietnenuteddecebeenddscbacdscedsacens 27
§ 307(d)(9)(A), 42 U.S.C. § 7607(d)(9)(A) .......-.-. 5 | ih SE Sade Niebbecedabncdotundesdesdddecnedsaeds 16
DP, RTO cc csvecvscdcccncccseséeccesséecesscees 17
MISCELLANEOUS: i PEEP RKbd cabdenedécedeesoncteendevedesecekeeda 17
44 Fed. Reg. (1979) eS eee 30
P- 8202 ..... 2... eee eeeeeeeeeeeseeeesnererneecenes 26 i aid dedtacdecciscopstsnediensovens 26
D. GRID... cccccccccccccccccccccccccccevececceseees 27 | Be Sh See Sy Gb cncdsdccedcckacsdenedeess 13
61 Fed. Reg. (1996) Kenneth Culp Davis, A New Approach to Delega-
edna 18 tion, 36 U. Chi. L. Rev. 713 (1969) ...............-. 6
PP. 65,641-44 . 2... e eee eens 18
D. GEOG 2... ccc ccccccccccccccccccscccceseccccess 17
DP. 65,721-22 .... ccccccccccccccccscccccsecccccess 15
BD. GBT22 2. wocccccccccccccccccccccsesecesessccvees 15
BD. GBTTS 2. cccccccccccccccscccccccscscccsccevccess 16
DB. GATED .ccccccccccccccccceccccessccscccescees 15, 16
B. GATE 2c ccccccccccccccccccccccccccscccscoseses 16
BD. GB,T2D 2. cc ccccccccccccccccccccccccececccssceses 16
62 Fed. Reg. (1997) : aes
B. GRGTD .ccccccccccccccccccccocceseosevesceccees 18 :
BD. TBBIG 2... cccccccccccccccccccceseccscccesccess 18
BD. SOTO onc ccccccccccccccccsscccscscccccssecvess 15
BD. SBBED 2... nc cccccccccccccccccveccccccvevcceceees 15
BD. SBBGI 2... ccccccccccccccvcvesscssccccveveceers 16
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1
INTEREST OF AMICI CURIAE
Amici curiae Environmental Defense (formerly Envi-
ronmental Defense Fund), Clean Air Council, East Michi-
gan Environmental Action Council, Environmental Law
and Policy Center of the Midwest, Hoosier Environmen-
tal Council, Inc., Illinois Environmental Council, The
Izaak Walton League of America, Inc., Legal Environmen-
tal Assistance Foundation, Inc., Michigan Environmental
Council, Ohio Citizen Action, The Ohio Environmental
Council, Southern Environmental Law Center, Tennessee
Environmental Council, and Valley Watch, Inc., are four-
teen not-for-profit organizations working to improve
public health and environmental quality throughout the
United States. Environmental Defense, et al. seek health-
ier air quality on behalf of their many thousands of
members who live and raise families in communities
across the country that have air pollution concentrations
in excess of the ozone and particulate matter standards
under review in this case.!
SUMMARY OF ARGUMENT
The D.C. Circuit followed a constitutionally imper-
missible path in remanding, on nondelegation grounds,
the regulations challenged in this case. Instead of deter-
mining whether the Clean Air Act provided an “intellig-
ible principle” to guide the agency’s exercise of its
discretion, the D.C. Circuit scrutinized the agency’s
explanation for how it chose to set the National Ambient
Air Quality Standards (NAAQS) for ozone and particu-
late matter. The D.C. Circuit’s approach does not promote
1 No counsel for any party authored this brief in whole or
in part, and 1:0 person or entity other than the amici and their
counsel made any monetary contribution to the preparation or
submission of this brief. This brief is being filed with the written
consent of the parties, and the corresponding documentation is
simultaneously being filed with the Court.
2
the key purpose of the nondeleg ation doctrine — that core
political decisions be made by Congress —- and improperly
constitutionalizes the requirement in the Administrative
Procedure Act (APA) that an agency adequately explain
its actions.
Moreover, the D.C. Circuit’s insistence that EPA con-
strain its discretion in a manner that is binding on future
Administrations places impermissible limits on how the
democratic process functions. Its approach threatens the
connection of administrative agencies to the political
process, which legitimates administrative action.
Because it dispensed with any analysis of the statute,
the D.C. Circuit overlooked the considerable guidance
that sections 108 and 109 of the Clean Air Act give EPA
on how to set the NAAQS. This guidance easily is more
extensive and no less determinate than the guidance at
issue in several cases in which the Court rejected non-
delegation challenges, and clearly meets the Court’s
“intelligible principle” standard.
Finally, the D.C. Circuit was mistaken in holding that
the nonattainment provisions of the Clean Air Act con-
strain EPA’s authority to implement the challenged
NAAQS for ozone. The D.C. Circuit believed that this
conclusion was necessary to accord the same meaning to
the same words used in different parts of the statute. In
fact, however, this objective can be achieved only by
concluding that the Clean Air Act does not constrain
EPA’s implementation authority. More generally, the
structure of the nonattainment provisions compels the
conclusion that EPA’s authority to implement the chal-
lenged standard is not constrained. At the very least,
EPA’s interpretation to that effect is permissible and is
not inconsistent with the clear intent of Congress.
_— A — i ee Ml
3
ARGUMENT
I. THE D.C. CIRCUIT’S REMAND OF THE EPA REG-
ULATIONS IS BASED UPON A CONSTITU-
TIONALLY IMPERMISSIBLE APPLICATION OF
THE NONDELEGATION DOCTRINE
The D.C. Circuit’s justification for remanding the
challenged NAAQS bears no resemblance to any accepted
application of the constitutional doctrine of nondelega-
tion. The Court repeatedly has held that the most impor-
tant purpose of the nondelegation doctrine is to ensure
that core political decisions are made by Congress, and
that where Congress delegates authority to an adminis-
trative agency it provides an “intelligible principle” to
guide the exercise of the agency’s discretion. See Loving v.
United States, 517 U.S. 748, 771 (1996); Touby v. United
States, 500 U.S. 160, 165 (1991); Mistretta v. United States,
488 U.S. 361, 372 (1989); ].W. Hampton & Co. v. United
States, 276 U.S. 394, 409 (1928).
Despite the Court's clear articulation of these central
concerns of the nondelegation doctrine, the D.C. Circuit
did not even attempt to analyze the nature of the con-
straints Congress placed on the agency’s exercise of dis-
cretion. Instead, it delved immediately into the agency’s
explanations for the choice it made pursuant to that dis-
cretion. The opinion states explicitly: “We begin with the
criteria EPA has announced for assessing health effects in
setting the NAAQS for non-threshold pollutants.” Pet.
App. 6a. The D.C. Circuit’s holding similarly focused on
EPA’s exercise of its discretion: “We find that the con-
struction of the Clean Air Act on which EPA relied in
promulgating the NAAQS at issue here «<tects an uncon-
stitutional delegation of legislative power.” Pei. App. 4a
(emphasis added).
4
The D.C. Circuit’s preoccupation with the agency
rather than Congress - the institution that is the focus of
the nondelegation doctrine’s concern - is particularly
problematic given the circuit’s own admission that the
approach it took does not serve “the third key function of
non-delegation doctrine [sic]”, which is to ensure ” ‘that
important choices of social policy are made by Congress.’ ”
Pet. App. 14a. (quoting Industrial Union Dep't, AFL-CIO v.
American Petroleum Inst., 448 U.S. 607, 685 (1980) (Benzene)
(Rehnquist, J., concurring)). This “third” function, which
the D.C. Circuit chose to leave unfulfilled, is the only
rationale for the nondelegation doctrine on which the
Court has consistently relied. See, e.g., Loving, 517 U.S. at
771-72; Touby, 500 U.S. at 164-66; Mistretta, 488 U.S. at
371-73; see also Pet. App. 95a n.2 (“It is . . . only this so-
called ‘third’ purpose . . . that has any connection to the
doctrine’s constitutional source.”) (Silberman, J., dissent-
ing from the denial of rehearing en banc).
In explaining why it was choosing a remedy that did
not serve the key function of the nondelegation doctrine,
the panel noted, citing Mistretta: “[W]e do not read cur-
rent Supreme Court cases as applying the strong form of
the nondelegation doctrine voiced in Justice Rehnquist's
concurrence [in the Benzene case].” Pet. App. 14a. But the
nondelegation doctrine simply does not have a “weak”
version that is served by setting aside regulations as well
as a “strong” version that compels declaring statutes
unconstitutional. There is only one nondelegation doc-
trine, and its focus is on the actions of Congress.
The D.C. Circuit advanced two rationales for order-
ing the agency to constrain its discretion: to discourage
the agency from “exercis[ing] the delegated authority
arbitrarily” and to promote “meaningful judicial review.”
5
Pet. App. 14a. But both these goals are served by “arbi-
trary and capricious” review under the APA. See 5 U.S.C.
§ 706(2)(A); Baltimore Gas & Elec. Co. v. NRDC, 462 U.S.
87, 97-98 (1983).2 Given the broad oversight exercised by
the courts pursuant to this APA provision, a further con-
stitutionally based requirement designed to serve essen-
tially the same purposes is wholly unnecessary.
Not only is the D.C. Circuit’s approach to the non-
delegation doctrine analytically unsound, but it is vir-
tually unsupported by precedent. The D.C. Circuit
repeatedly cited a prior decision, International Union,
UAW v. OSHA, 938 F.2d 1310, 1316-18 (D.C. Cir. 1991)
(Lockout-Tagout I), in which it similarly misapplied the
nondelegation doctrine to invalidate a regulation. See Pet.
App. 1la-15a.
The only other case on which the D.C. Circuit relied,
Amalgamated Meat Cutters v. Connally, 337 F. Supp. 737
(D.D.C. 1971) (Leventhal, J., for a three-judge court), is
inapposite. See Pet. App. 14a. Unlike the opinion below,
Judge Leventhal’s analysis began, as is appropriate under
the nondelegation doctrine, with an exhaustive analysis
of the legislative materials. See Amalgamated Meat Cutters,
337 F. Supp. at 747-58. Following this review, Judge
Leventhal stated that administrative discretion also is
confined by “the requirement that any action taken by the
Executive under the law . . . must be in accordance with
further standards as developed by the Executive.” Id. at
758. Judge Leventhal viewed this requirement as one of
“intelligible administrative policy that is corollary to and
implementing of the legislature’s ultimate standard and
objective.” Id. at 759. Nowhere does the opinion state that
2 The Clean Air Act’s judicial review provisions call for
“arbitrary and capricious” review. See 42 U.S.C. § 7607(d)(9)(A).
6
the requirement of administrative explanation derives
from the Constitution’s nondelegation doctrine.
In fact, subsequent cases make clear that the require-
ment that agencies provide detailed explanations for their
regulations is an integral part of “arbitrary and capri-
cious” review under the APA, and, in particular, of the
“hard look” doctrine. See Motor Vehicle Mfrs. Ass’n v. State
Farm Mut. Auto. Ins. Co., 463 U.S. 29, 41-43 (1983);
National Lime Ass'n v. EPA, 627 F.2d 416, 451 & n.126 (D.C.
Cir. 1980).
The intellectual foundation for the D.C. Circuit's
approach appears to come from Kenneth Culp Davis, A
New Approach to Delegation, 36 U. Chi. L. Rev. 713 (1969).%
Davis urged courts to “acknowledge that the nondelega-
tion doctrine is unsatisfactory and to invent better ways
to protect against arbitrary administrative power.” Id. at
713 (emphasis added). Davis added that the purpose of
the nondelegation doctrine “should no longer be either to
prevent delegations of legislative power or to require
meaningful statutory standards.” Id.; see also id. at 725.
Instead, he proposed shifting “[t]he focus of judicial
inquiries . . . from statutory standards to administrative
safeguards and administrative standards.” Id. Like Davis,
the D.C. Circuit freely acknowledged that under its
approach, “[t]he agency will make the fundamental pol-
icy choices.” Pet. App. 14a.
Davis’ position had no doctrinal grounding at the
time that it was made; his use of the term “invent” is
revealing on this score. Moreover, the Court has never
3 Although the only time that the D.C. Circuit cited the
Davis article it gave it a “but see” signal, Pet. App. 76a, the
approach of the court below bears a strong resemblance to
Davis’.
7
accepted his invitation to reconceptualize the nondelega-
tion doctrine, and has continued to view this doctrine as
a constraint on congressional - not administrative -
action.
In summary, as Judge Silberman stated, the D.C.
Circuit’s approach is “fundamentally unsound.” Pet.
App. 92a (Silberman, J., dissenting from the denial of
rehearing en banc). The nondelegation doctrine cannot
“be employed to force an agency to narrow a broad
legislative delegation from Congress.” Id.
II. THE D.C. CIRCUIT’S APPROACH IMPERMISSI-
BLY INTERFERES WITH THE PROPER FUNC-
TIONING OF THE DEMOCRATIC PROCESS
The D.C. Circuit’s approach also places impermissi-
ble constraints on the democratic process. In its opinion
on the petitions for rehearing, the panel majority made
clear that no administrative explanation - no matter how
well-reasoned or detailed - would satisfy its approach to
the nondelegation doctrine unless it contained an express
constraint on the agency’s future discretion. For example,
EPA had explained in the regulatory materials that it had
set the annual standard for particulate matter on the basis
of evidence of adverse health effects that was statistically
significant at the 95th confidence level, and that it had set
the ozone standards to protect against adverse health
effects that were not transient. Pet. App. 73a & nn. 1-2;
see infra Part III.B. The D.C. Circuit reacted to this argu-
ment as follows:
To be sure, in the rulemakings that set the
NAAQS, the EPA mentioned the corollary prop-
Ositions its counsel now claim served as intellig-
ible limiting principles, but the agency did not
identify either as a limit upon its discretion; the
EPA never suggested that it could not (or in a
8
later rulemaking would not) base a NAAQS
upon evidence that did not meet the 95 percent
confidence level or that revealed adverse but
transient effects.
Pet. App. 73a. Thus, the D.C. Circuit insisted that EPA’s
approach to these matters be frozen not only with respect
to future NAAQS for ozone and particulate matter — the
contaminants at issue in this case — but also for NAAQS
for all other contaminants.
The D.C. Circuit’s approach threatens an important
source of the legitimacy of agency action: the connection
of administrative agencies to the political process. As the
Court has observed:
While agencies are not directly accountable to
the people, the Chief Executive is, and it is
entirely appropriate for this political branch of
Government to make such policy choices -
resolving the competing interests which Con-
gress itself either inadvertently did not resolve,
or intentionally left to be resolved by the agency
charged with the administration of the statute in
light of everyday realities.
Chevron, U.S.A., Inc. v. NRDC, 467 U.S. 837, 865-66 (1984).
It is inconsistent with long-established norms con-
cerning the role of administrative agencies to hold, as the
D.C. Circuit did, that where Congress vests regulatory
discretion in an agency, the first Administration that exer-
cises this discretion is required to bind all future Adminis-
trations. Instead, if a statute does not prescribe a
particular outcome, different Administrations should be
able to exercise congressionally delegated discretion in
different ways. See Chevron, 467 U.S. at 863-64 (“An initial
agency interpretation is not instantly carved in stone. On
the contrary, the agency . . . must consider . . . the wisdom
of its policy on a continuing basis.”); State Farm, 463 U.S.
-_ - “~o os
9
at 42 (“[RJegulatory agencies do not establish rules of
conduct to last forever and . . . must be given ample
latitude to adapt their rules and policies to the demands
of changing circumstances.”) (citations omitted).
The Court has held that the APA requires an agency
that changes a prior policy to explain the reasons for this
change. See State Farm, 463 U.S. at 41-42. It has never
held, however, that the Constitution prevents an agency
from changing its policy altogether. Given the nature of
the policy dispute in this case, such a position would be
particularly destructive of the connection between agency
action and political legitimacy. Should a future Adminis-
tration that favors more stringent environmental regula-
tion be precluded from regulating on the basis of a lower
confidence level —- say 90% instead of 95%? Cf. National
Lime, 627 F.2d at 454 n.139 (“Agencies are not limited to
scientific fact, to 95% certainties.”). Or should such an
Administration be barred from concluding that transient
effects can be adverse? The D.C. Circuit’s approach
would compel affirmative answers to both these ques-
tions, contrary to the key reason why our constitutional
scheme has periodic presidential elections: so that the
voters can put in place Administrations that are respon-
sive to their views.
Ill. SECTIONS 108 AND 109 OF THE CLEAN AIR
ACT DO NOT RUN AFOUL OF THE NON-
DELEGATION DOCTRINE
A. The Clean Air Act gives considerable guidance
to EPA on how to set the NAAQS
The congressional delegation relevant to this case is
primarily contained in sections 108 and 109 of the Clean
Air Act. 42 U.S.C. §§ 7408, 7409. Section 108 — which the
D.C. Circuit’s panel majority overlooked altogether -
10
requires EPA to establish air quality criteria that will
serve as the basis for the agency to then set the NAAQS
under section 109.
Section 108(a)(1) requires the EPA Administrator to
list the pollutants for which NAAQS will eventually be
set. The Administrator must place on this list each air
pollutant that meets two principal requirements:
(A) [the] emissions of [the pollutant], in
his judgment, cause or contribute to air pollu-
tion which may reasonably be anticipated to
endanger public health or welfare; [and]
(B) the presence of [the pollutant] in the
ambient air results from numerous or diverse
mobile or stationary sources.
42 U.S.C. § 7408(a)(1). Thus, only pollutants “which may
reasonably be anticipated to endanger public health or
welfare” can be regulated. Moreover, such pollutants can
be regulated only if they have an effect on the “ambient
air” — as opposed to, for example, on indoor air. Even
pollutants that do have an effect on ambient air can be
regulated only if they are produced by “numerous or
diverse mobile or stationary sources.” (emphasis added).
Following the listing of a pollutant, the Administra-
tor must prepare air quality criteria. 42 U.S.C.
§ 7408(a)(2). The statute provides:
Air quality criteria for an air pollutant shall
accurately reflect the latest scientific knowledge
useful in indicating the kind and extent of all
identifiable effects on public health or welfare
which may be expected from the presence of
such pollutant in the ambient air, in varying
quantities. The criteria for an air pollutant, to
the extent practicable, shall include information
on -
(A) those variable factors (including atmo-
spheric conditions) which of themselves or in
11
combination with other factors may alter the
effects on public health or welfare of such air
pollutant; |
(B) the types of air pollutants which, when
present in the atmosphere, may interact with
such pollutant to produce an adverse effect on
public health or welfare; and
(C) any known or anticipated adverse
effects on welfare.
42 U.S.C. § 7408(a)(2). Thus, such criteria must be based
on “the latest scientific knowledge,” and must indicate
“all identifiable effects on public health and welfare.” The
statute also requires the consideration of interactions
among pollutants.
Section 109(b)(1) prescribes the level at which pri-
mary NAAQS must be set:
National primary ambient air quality stan-
dards . . . shall be ambient air quality standards
the attainment and maintenance of which in the
judgment of the Administrator, based on such
criteria and allowing an adequate margin of
safety, are requisite to protect the public health.
42 U.S.C. § 7409(b)(1). The statute therefore provides that
the primary NAAQS must meet three requirements: they
must be “based on” the air quality criteria developed
under section 108, they must be “requisite to protect the
public health,” and they must provide “an adequate mar-
gin of safety.”
In turn, section 109(b)(2) prescribes that the second-
ary standards must also be “based on” the air quality
criteria and must be “requisite to protect the public wel-
fare.” Id. § 7409(b)(2). For the latter inquiry, both “known
or anticipated” adverse effects must be taken into
account. Section 302(h), moreover, contains a statutory
definition of the term “public welfare,” which requires
12
EPA to take account of an extensive set of factors in
fashioning the secondary standards. See 42 U.S.C.
§ 7602(h).
Section 109 further requires the Administrator to
review, at least at five-year intervals, the air quality crite-
ria as well as both the health-based primary standards
and the welfare-based secondary standards. In undertak-
ing this review, the Administrator must “make such revi-
sions in such criteria and standards and promulgate such
new standards as may be appropriate in accordance with
section 7408 . . . and subsection (b) of . . . section [7409]”.
Id. § 7409(d)(1). Thus, the statutory requirements that
govern the initial promulgation of the standards apply
also to their revision.
The statute also prescribes an institutional structure
to aid the Administrator in revising the criteria and stan-
dards. For this purpose, the Administrator must “appoint
an independent scientific review committee composed of
seven members including at least one member of the
National Academy of Sciences, one physician, and one
person representing State air pollution control agencies.”
Id. § 7409(d)(2)(A). This committee “shall recommend to
the Administrator any new national ambient air quality
standards and revisions of existing criteria and standards
as may be appropriate.” Id. § 7409(d)(2)(B). If the regula-
tions establishing the NAAQS depart in any important
respect from the recommendations of this group, EPA
must explain the reasons for such a departure. Id.
§ 7607(d)(3).
The Clean Air Act's legislative history provides fur-
ther guidance on the level at which the NAAQS should
be set. The report of the Senate Committee on Public
Works stresses that concern with health effects must
extend to particularly sensitive populations: “[I]ncluded
—— ee
13
among those persons whose health should be protected
by the ambient standard are particularly sensitive citizens
such as bronchial asthmatics and emphysematics who in
the normal course of daily activity are exposed to the
ambient environment.” S. Rep. No. 91-1196, at 10 (1970).
The report states, however, that the NAAQS “will not
necessarily provide for the quality of air required to
protect those individuals who are otherwise dependent
on a controlled internal environment.” Id.
The report makes clear that the purpose of the
NAAQS is to protect particularly sensitive populations,
not particularly sensitive individuals. Under this
approach, ambient air quality sufficiently protects sensi-
tive populations if there is an “absence of adverse effect
on the health of a statistically related sample of persons
in sensitive groups.” Id. The report further specifies that
“a statistically related sample is the number of persons
necessary to test in order to detect a deviation in the
health of any person within such sensitive group which is
attributable to the condition of the ambient air.” Id.
Thus, the legislative history explains that the deter-
mination of adverse health effects must be made with
respect to certain groups in the general population. It also
explains what counts as a group for this purpose.
In summary, Congress gave considerable guidance to
EPA on how to set the NAAQS. In failing to examine the
nature of the legislative direction, the D.C. Circuit missed
the central point of the nondelegation doctrine.
14
B. The D.C. Circuit’s suggestion that EPA was free
to set the NAAQS at any level between zero
and the concentration of London’s Killer Fog
stems from a misunderstanding of the Clean
Air Act
The preceding analysis of the legislative guidance
shows that the D.C. Circuit was simply mistaken when it
stated, with rhetorical flourish, that EPA is “free to pick
any point between zero and a hair below the concentra-
tions yielding London’s Killer Fog.” Pet. App. 13a. The
D.C. Circuit’s characterization stems from an erroneous
understanding of the statutory scheme, and in particular,
of the trigger for revisions of the NAAQS, the manner in
which adverse effects on public health are determined,
and the types of sensitive populations that the standards
are designed to protect.
The D.C. Circuit recognized that the London Killer
Fog “led to 4,000 excess deaths in a week.” Pet. App. 11a.
It is difficult to imagine any plausible interpretation of
the statutory command that would allow such a calamity.
See 42 U.S.C. § 7409(b)(1) (NAAQS must be set at levels
that “allowing an adequate margin of safety, are requisite
to protect the public health”).
Similarly, the Administrator would be able to set a
standard of zero only if such a standard is “requisite to
protect the public health,” “allowing an adequate margin
of safety.” Id. The Clean Air Act's legislative history,
discussed in Part III.A, supra, makes clear that even if
some individual's health would be promoted by a stan-
dard of zero, the Administrator is precluded from pro-
mulgating such a standard if at this level there is no
statistically significant evidence of an adverse health
effect in a population.
ci ee eee
15
An examination of the administrative record illus-
trates the nature of these constraints on EPA’s discretion.
In the case of ozone, EPA began, consistent with the
legislative command, by defining the sensitive popula-
tions - the populations that experience adverse health
effects at the lowest concentrations. EPA determined that
three populations were particularly sensitive: active chil-
dren, outdoor workers, and individuals with preexisting
respiratory disease (for example, asthma or chronic
obstructive lung disease). 61 Fed. Reg. 65,716, 65,721-22
(1996).
The agency then considered what should count as an
“adverse health effect” for these sensitive populations. To
make this determinatior, EPA looked to guidelines pub-
_lished by the American Thoracic Society, which used the
following definition:
[M]edically significant physiologic or pathologic
changes generally evidenced by one or more of
the following: (1) Interference with the normal
activity of the affected person or persons, (2)
episodic respiratory illness, (3) incapacitating
illness, (4) permanent respiratory injury, and/or
(S) progressive respiratory dysfunction.
Id. at 65,722; see 62 Fed. Reg. 38,856, 38,860 (1997).
In justifying a need for a revision of the existing
standard pursuant to section 109(d), see Part III.A, supra,
EPA noted that “a significant body of information” that
became available after the promulgation of the ozone
NAAQS then in effect provided “clear evidence from
human clinical studies” of adverse health effects at con-
centrations permitted by the then-existing standard. 61
Fed. Reg. at 65,727; see 62 Fed. Reg. at 38,859.
One of the ways in which EPA revised the NAAQS
for ozone was to extend the averaging period from 1 hour
to 8 hours on the ground that “[t]he 8-hour averaging
16
time is more directly associated with health effects of
concern at lower [ozone] concentrations than is the
1-hour averaging time.” 61 Fed. Reg. at 65,727; 62 Fed.
Reg. at 38,861. This change reflects the conclusion that a
high concentration during one hour might not cause
adverse health effects if it is followed by sufficiently
lower concentrations in subsequent hours.
Because under an 8-hour averaging period a high
concentration during one hour can be offset by a suffi-
ciently lower concentration in other portions of the
8-hour period, EPA determined that the 1-hour 0.12 parts
per million (ppm) standard then in effect was essentially
equivalent to a 0.09 ppm standard with an 8-hour averag-
ing period. See 61 Fed. Reg. at 65,729; see also id. at
65,725, 65,728; 62 Fed. Reg. at 38,864.
EPA then determined that a standard of 0.08 ppm
was preferable to one of 0.09 ppm in light of the statutory
mandate of section 109(b). First, children active outdoors
would experience significantly higher decreases in lung
function and pain on deep inspiration under a standard
of 0.09 ppm as compared to a standard of 0.08 ppm.
Under a standard of 0.09 ppm between 40 and 65 percent
more children would experience such effects, and there
would be 120 percent more yearly occurrences of such
effects. These percentages would translate into tens oj
thousands of more affected children and hundreds of
thousands more yearly occurrences. Second, a risk assess-
ment revealed that a 0.09 ppm standard would result in
40 more yearly hospital admissions for respiratory causes
of asthmatics in New York City alone (a 40 percent
increase). Third, a standard of 0.09 ppm would allow
more than three times as many children to experience
exposures of concern. Fourth, EPA determined that these
17
examples were indicators of public health impacts in the
broader population. See 62 Fed. Reg. at 38,867-68.
Moreover, as Judge Tatel discussed at length in his
dissent, EPA determined that setting the standard at a
more stringent level — 0.07 ppm - was unwarranted under
section 109(b). Pet. App. 64a (Tatel, J., dissenting). He
observed that no single member of EPA’s scientific review
committee had recommended setting the standard below
0.08 ppm. Id. He also pointed to EPA’s explanation that
the adverse health effects below 0.08 ppm were quali-
tatively different. Id.; see 62 Fed. Reg. at 38,868 (at a level
of 0.07 ppm, the most serious adverse health effects of
ozone “are less certain, both as to percentage of individ-
uals exposed to various concentrations who are likely to
experience such effects and as to the long-term medical
significance of these effects”); see also Pet. App. 64a-65a
(Tatel, J., dissenting) (referring to EPA’s additional techni-
cal explanation for its decision).
EPA followed a comparable approach in revising the
NAAQS for particulate matter (PM). It defined five cate-
gories of sensitive populations: (1) individuals with respi-
ratory and cardiovascular disease, who are at greater risk
of premature mortality and hospitalization; (2) individ-
uals with infectious respiratory disease, who are at
greater risk of premature mortality and morbidity; (3)
elderly individuals, who are at greater risk of premature
mortality and hospitalization for cardiopulmonary
causes; (4) children, who are at greater risk of increased
respiratory symptoms and decreased lung function; and
(5) asthmatic children and adults, who are at risk of more
serious symptoms. See 61 Fed. Reg. 65,638, 65,644 (1996).
18
EPA justified the need for revising the NAAQS for
particulate matter as follows:
[S]ince the last review of the PM criteria and
standards, the most significant new evidence on
the health effects of PM is the greatly expanded
body of community epidemiological studies.
The Criteria Document stated that these recent
studies provide “evidence that serious health
effects (mortality, exacerbation of chronic dis-
ease, increased hospital admissions, etc.) are
associated with exposures to ambient levels of
PM found in contemporary U.S. urban airsheds
even at concentrations below current U.S. PM
standards.”
61 Fed. Reg. at 65,641; see 62 Fed. Reg. 38,652, 38,655
(1997).
EPA paid considerable attention to how the standard
should be derived from the epidemiological studies. The
Administrator based the annual standard on the level at
which the concentration of particulate matter was linked
to statistically significant increases, at a 95% confidence
level, see Part II, supra, in the risk of adverse health
effects across a number of study locations. See 62 Fed.
Reg. at 38,676; 61 Fed. Reg. at 65,641-44.
In summary, EPA’s discretion was constrained by the
legislative direction of the Clean Air Act. The agency
followed the congressional direction in finding a need for
revising the existing standards and for determining that
more stringent standards were necessary to fulfill the
statutory mandate in section 109(b). EPA was also con-
strained by the legislative command to protect popula-
tions rather than individuals. The preceding analysis thus
clearly establishes that the D.C. Circuit erred in suggest-
ing that the Clean Air Act permits EPA to set the NAAQS
—
19
at any level between a concentration of zero and the
concentration present during the London Killer Fog.
C. The Court’s jurisprudence establishes that the
Clean Air Act does not violate the nondelega-
tion doctrine
In the over 200 years of its history, the Court has
struck down a statute on nondelegation grounds in only
two cases. See Mistretta, 488 U.S. at 373. These cases,
Panama Refining Co. v. Ryan, 293 U.S. 388 (1935) and
A.L.A. Schechter Poultry Corp. v. United States, 295 U.S. 495
(1935), were both decided in 1935 and both involved
challenges to the National Industrial Recovery Act
(NIRA) - one of the economic recovery statutes of the
New Deal. Both are inapposite for reasons discussed in
Part III.D, infra.
Since 1935 the Court has validated broad delegations
in a variety of areas. See, e.g., Lichter v. United States, 334
U.S. 742, 746, 785-86 (1948) (recovery of “excessive
profits” under the Renegotiation Act); Yakus v. United
States, 321 U.S. 414, 420, 426-27 (1944) (establishment of
“fair and equitable prices” under the Emergency Price
Control Act); National Broad. Co. v. United States, 319 U.S.
190, 215, 225-26 (1943) (regulation pursuant to a “public
interest, convenience, or necessity” standard under the
Communications Act). In each of those cases, Congress
provided guidance that was less extensive and no more
determinate than that provided by sections 108 and 109 of
the Clean Air Act, as described in Part III.A, supra.
In one of the more recent nondelegation cases, Touby
v. United States, 500 U.S. at 160, the Court unanimously
upheld a delegation that employed guidance similar to
that at issue here. Touby involved a delegation to the
Attorney General under the Controlled Substances Act to
20
establish categories or “schedules” of controlled sub-
stances that are to be regulated by the Act. The statute
authorized the Attorney General to schedule a substance
through an expedited procedure when doing so is “neces-
sary to avoid an imminent hazard to the public safety.”
Touby, 500 U.S. at 163 (quoting section 201(h) of the Act).
Citing Lichter, Yakus, and National Broadcasting, the
Court stated that in light of its nondelegation precedents
“one cannot plausibly argue that [the] ‘imminent hazard to
the public safety’ standard is not an intelligible principle.”
Id. at 165. By comparison, the terms “endanger public
health or welfare” in section 108 of the Clean Air Act, and
“requisite to protect the public health” and “requisite to
protect the public welfare” in section 109 are no broader
than the “imminent hazard to the public safety” standard
upheld in Touby. Moreover, the other forms of congres-
sional guidance contained in the Clean Air Act and dis-
cussed in Part III.A, supra, were absent in Touby.
Furthermore, the Court held that the delegation at
stake in Touby “passes muster even if greater congres-
sional specificity is required in the criminal context.” Id.
at 166. In contrast, under sections 108 and 109 of the
Clean Air Act, which do not give rise to risks to individ-
ual liberty, such heightened congressional guidance is not
required.
Only four years ago, in Loving v. United States, 517
U.S. 748 (1996), the Court unanimously reemphasized the
breadth of permissible delegations: “Though in 1935 we
struck down two delegations for lack of an intelligible
principle, we have since upheld, without exception, dele-
gations under standards phrased in sweeping terms.” Id.
at 771.
The Clean Air Act’s guidance — the constraints on the
reach of agency authority in section 108, the statutory
21
standards in section 109, the required consultation with
expert scientists, the definition of public welfare in sec-
tion 302(h), and the legislative history’s determination of
what groups should be protected by the NAAQS - is
considerable. Certainly, the grant of legislative authority
in the Clean Air Act provides no warrant for departing
from more than half a century of consistent practice
upholding congressional delegations.
D. The D.C. Circuit’s reliance on Schechter Poultry
is misplaced
The panel majority’s arguments casting doubt on the
constitutionality of the congressional delegation rely pri-
marily on Schechter Poultry. See Pet. App. 12a. None of
these arguments, however, has any merit.
The D.C. Circuit stated that “[t]he standards in ques-
tion affect the whole economy, requiring a ‘more precise’
delegation than would otherwise be the case.” Pet. App.
12a. Like almost all regulations, the NAAQS “affect the
whole economy” in the sense that they affect the price of
certain goods, which in an interrelated economy, may
affect the prices of other goods and services. But the
NAAQS regulate only the concentration of air pollution,
and as discussed in Part III.A, supra, apply only to a
subset of air pollutants, only to pollutants in ambient air,
and only to pollutants emitted by certain types of
sources. That is a far cry from the all-encompassing,
multifaceted delegation of the NIRA, which gave the
President the authority to establish “codes of fair compe-
tition” governing a broad set of issues, including wages
and hours as well as marketing and competitive practices
for a broad set of industries. See Schechter Poultry, 295
U.S. at 521-24; Panama Refining, 293 U.S. at 405-10.
22
Furthermore, the delegation under the Clean Air Act
does not exhibit the features that were problematic in
Schechter Poultry. First, there is no delegation to private
individuals. See Mistretta, 488 U.S. at 373 n.7; Yakus, 321
U.S. at 424; Schechter Poultry, 295 U.S. at 537.
Second, the D.C. Circuit itself acknowledged that
EPA’s interpretation of the terms “endanger public
health” in section 108(a)(1)(A) and “requisite to protect
the public health” in section 109(b)(1) is informed by the
meaning these terms have in the medical community. See
Pet. App. 15a-16a. In contrast, in Schechter Poultry, the
concept of “fair competition” had no meaning that could
be ascertained from external sources. See Schechter Poul-
try, 295 U.S. at 531-33.
A third problem with the NIRA was the absence of
administrative procedures, which made it difficult for the
courts to assess how the President had carried out his
delegated discretion. See Schechter Poultry, 295 U.S. at
533-34; Panama Refining, 293 U.S. at 431-32. The Clean Air
Act, in contrast, contains extensive procedural protec-
tions. Section 307(d) requires the Administrator to follow
notice-and-comment rulemaking procedures that are
more extensive than those prescribed in the APA. Com-
pare 42 U.S.C. § 7607(d)(2)-(7) with 5 U.S.C. § 553(b)-(c).
For example, section 307(d) requires EPA to establish a
“rulemaking docket” open to the public; to place in this
docket communications with the Office of Management
and Budget pursuant to any interagency review process;
and to provide interested persons with an opportunity
for “oral presentation of data, views, or arguments.” 42
U.S.C. § 7607(d)(2), (4)(A), 4(B)(ii), (5). Moreover, as dis-
cussed in Part III.A, supra, the Administrator must
appoint an independent scientific committee to review
and recommend revisions to the criteria documents and
"ee? ear wee
ee ie
23
the NAAQS, and must explain her reasons for departing
from the committee’s recommendations. See 42 U.S.C.
§§ 7409(d)(2), 7607(d)(3).
In summary, the Clean Air Act does not present any
of the problems that led the Court to declare unconstitu-
tional the delegation at issue in Schechter Poultry.
E. The D.C. Circuit also is mistaken in maintain-
ing that broad delegations are permissible only
in special circumstances
The D.C. Circuit also suggested that this case is
unlike ones in which broad delegations were upheld
because it does not involve ” ‘special theories’ justifying
vague delegations such as the war powers of the Presi-
dent or the sovereign attributes of the delegatee.” Pet.
App. 12a. But, as discussed in Part III.C, supra, in recent
years, the Court has upheld broad delegations in cases
that do not implicate such “special theories.” See, ¢.g.,
Touby, 500 U.S. at 165-67 (delegation to the Attorney
General to designate controlled substances); Mistretta, 488
U.S. at 371-79 (delegation to the U.S. Sentencing Commis-
sion to promulgate sentencing guidelines).
IV. THE D.C. CIRCUIT ERRED IN HOLDING THAT
EPA’S AUTHORITY TO IMPLEMENT THE
8-HOUR OZONE STANDARD IS CONSTRAINED
BY SECTION 181 OF THE CLEAN AIR ACT
A brief review of the structure of the nonattainment
provisions of the Clean Air Act reveals why the D.C.
Circuit was mistaken in holding that section 181 con-
strains EPA’s authority to implement the 8-hour ozone
24
standard of 0.08 ppm promulgated in 1997.4 The Clean
Air Act’s nonattainment provisions govern the regulation
of areas that do not meet the NAAQS. Subpart 1, entitled
“Nonattainment Provisions in General,” applies to all of
the pollutants for which EPA has promulgated NAAQS.
See 42 U.S.C. §§ 7501-7509a. Subparts 2 through 5 deal
with additional pollutant-specific provisions. See id.
§§ 7511-7514a. In particular, Subpart 2, entitled “Addi-
tional Provisions for Ozone Nonattainment Areas,”
applies to ozone. See id. §§ 7511-7511f.
Both the general provisions of Subpart 1 and the
specific provisions of Subpart 2 prescribe dates by which
the NAAQS must be attained. In Subpart 1, section
172(a)(2) provides, in language added by the 1990 amend-
ments, that primary standards must be met
as expeditiously as practicable, but no later than
5 years from the date such area was designated
nonattainment under section 7407(d) of this
title, except that the Administrator may extend
the attainment date to the extent the Adminis-
trator determines appropriate, for a period no
greater than 10 years from the date of designa-
tion of nonattainment .. .
Id. § 7502(a)(2)(A). (Two additional one-year extensions
are also possible. Id. § 7502(a)(2)(C).) Section 172(a)(2)
also requires that secondary standards be met “as expe-
ditiously as practicable” but imposes no outside limit on
that time. Id. § 7502(a)(2)(B).
4 This brief focuses on the merits rather than the
justiciability of the implementation issues. Amicus
Environmental Defense has argued before the lower courts that
EPA did not resolve important implementation issues in the
NAAQS rulemaking with finality. See Environmental Defense
Fund v. Browner, No. 98-1363 (D.C. Cir.); Idaho Clean Air Force v.
EPA, Nos. 99-70289 & 99-70576 (9th Cir.).
25
In addition, section 172(a)(2) defines when the attain-
ment dates in Subpart 1 are inapplicable: “This paragraph
shall not apply with respect to nonattainment areas for
which attainment dates are specifically provided under
other provisions of this part.” Id. § 7502(a)(2)(D)
(emphasis added). As exceptions to the general rule of
section 172, provisions containing such attainment dates
must be construed narrowly. See Commissioner v. Clark,
489 U.S. 726, 739 (1989).5
Section 181 in Subpart 2, which was also added by
the 1990 amendments, contains such “specifically pro-
vided” attainment dates: “[T]he primary standard attain-
ment date for ozone shall be as expeditiously as
practicable but not later than the date provided in table
1.” Id. § 7511(a)(1). The outside time limits for attainment
contained in table 1 range from 3 years after November
15, 1990, in the case of areas in which the level of nonat-
tainment is “marginal” to 20 years after November 15,
1990, in the case of areas in which the level of nonattain-
ment is “extreme.” Id.
Section 181(a)(1), however, provides only “the pri-
mary standard attainment date.” 42 U.S.C. § 7£11(a)(1)
(emphasis added). Because attainment dates for the sec-
ondary standards are not “specifically provided” in sec-
tion 181 or elsewhere in Subpart 2, the attainment of such
standards is governed by the general provisions of sec-
tion 172(a)(2) in Subpart 1. Thus, nothing in section 181
can constrain EPA’s authority to require attainment of the
secondary standards “as expeditiously as practicable.” In
5 Thus, this is not a situation in which the statute contains a
general provision and a specific provision but does not specify
how they interrelate. The canon that “the specific governs the
general” is therefore inapplicable. See Morales v. Trans World
Airlines, Inc., 504 U.S. 374, 384 (1992).
26
granting in part the petition for rehearing, the D.C. Cir-
cuit recognized as much, retracting an inconsistent con-
clusion in the original panel opinion: “Therefore, we
conclude that Subpart 2 erects no bar to the EPA’s requir-
ing compliance with a revised secondary ozone NAAQS
‘as expeditiously as practicable.’ ” Pet. App. 80a-81a.
Moreover, the attainment dates in section 181 apply
to only one primary standard for ozone: the 1-hour pri-
mary standard of 0.12 ppm, which was the only ozone
NAAQS in effect in 1990 at the time section 181 was
added to the Clean Air Act. See 44 Fed. Reg. 8202 (1979)
(codified at 40 C.F.R. § 50.9(a)). Indeed, the outside time
limits for attainment contained in table 1 classify nonat-
tainment areas by reference to the amount by which their
ambient air quality levels - referred to as “design
value[s]” in the statute - exceed the 0.12 ppm standard.
See 42 U.S.C. § 7511(a)(1). So, for example, if EPA were to
revise the 1-hour standard to 0.10 ppm, the outside time
limits for areas with design values between 0.10 ppm and
0.12 ppm simply could not be determined on the basis of
table 1, since the table does not provide such time limits -
“specifically” or otherwise — for areas with concentration
below 0.12 ppm.
Even with respect to areas with design values higher
than 0.12 ppm, the congressional balancing between envi-
ronmental protection and economic growth reflected in
the outside time limits for attainment in table 1 would no
longer be applicable. This balancing was performed for a
standard of 0.12 ppm and would not necessarily be the
same if subsequent information, giving rise to the pro-
mulgation of the more stringent standard of 0.10 ppm,
revealed that the environmental problem was more
serious than was known at the time of the adoption of the
0.12 ppm standard.
27
There is another reason why the scheme in section
181 cannot apply to the standard under review. The 0.12
ppm standard in effect at the time of the 1990 amend-
ments used a 1-hour averaging period. 44 Fed. Reg. at
8218. (For this reason, it is referred to as the 1-hour
standard.) In contrast, the NAAQS under review uses an
8-hour averaging period. 62 Fed. Reg. at 38,861-63. The
ambient air quality levels computed under these different
averaging periods are not directly comparable.
As indicated in Part III.B, supra, if two ambient stan-
dards prescribe the same maximum permissible concen-
tration but have different averaging periods, the stai.dard
with the longer averaging period is the less stringent one.
Lower concentrations during part of the longer period
can offset higher concentrations during another part of
that period in a way that would not be possible if the
averaging period were shorter. If after section 181 was
enacted, EPA had retained the 0.12 ppm level but
extended the averaging period to 8 hours, there is no
reason to believe that Congress would have wanted to
apply the outside time limits set forth in section 181 to
these less stringent standards. It might, for example, have
believed that the less stringent standards should be
attained in shorter time periods.
The D.C. Circuit’s principal argument in support of
its conclusion that section 181 in Subpart 2 constrains
EPA’s authority to implement the 8-hour standard of 0.08
ppm is wholly without merit. According to the D.C.
Circuit, great weight must be placed on the fact that
section 181(a)(i) in Subpart 2 makes a reference to section
107(d), 42 U.S.C. § 7407(d): “Each area designated nonat-
tainment for ozone pursuant to section 7407(d) of this
title shall be classified at the time of such designation,
under table 1, by operation of law, . . . based on the
28
design value for the area.” 42 U.S.C. § 7511(a)(1); see Pet.
App. 37a-43a, 79a-80a. The D.C. Circuit reasoned that if
section 181 was intended to apply only to the NAAQS for
ozone in effect at the time of the 1990 amendments, the
reference in section 181 would have been, instead, to
section 107(d)(1)(C) and (d)(4). See Pet. App. 38a-42a,
79a-80a. Both section 107(d)(1)(C) and (d)(4) deal with the
designation of nonattainment areas immediately follow-
ing the 1990 amendments: section 107(d)(1)(C) applies
generally whereas section 107(d)(4) specifically covers
ozone. See 42 U.S.C. § 7407(d)(1)(C), (d)(4).
The argument conerning the reference to section
107(d) is far from convincing because it would strain
neither logic nor the English language to read the refer-
ence to section 107(d) as applying only to the portions of
section 107(d) that are relevant to the setting of the attain-
ment dates under section 181. For example, it would not
be unnatural to say that section 110 of the Clean Air Act
constrains interstate pollution that contributes to the non-
attainment of the NAAQS when in fact this requirement
is to be found in section 110(a)(2)(D)(i)(1). See 42 U.S.C.
§ 7410(a)(2)(D)(i)(I).
Moreover, as the preceding discussion shows, the
application of section 181 to ozone NAAQS other than the
1-hour 0.12 ppm standard in effect at the time of the 1990
amendments would give rise to a number of illogical
results. The reference to section 107(d) cannot trump the
analysis showing why section 181(a)(1) does not “speci-
fically provide[]” attainment dates for other ozone
NAAQS, particularly since there is a plausible interpreta-
tion of this reference that avoids such illogical results.
Neither should this reference be read to stand in the way
of EPA’s authority to implement standards that it revises,
pursuant to congressional direction, under section 109(d).
29
Finally, a more searching statutory inquiry wholly
disposes of the D.C. Circuit’s core argument. Section 172,
like section 181, refers to the “designation of an area as a
nonattainment area pursuant to section 7407(d).” 42
U.S.C. § 7502(a)(1)(A); see id. § 7502(a)(2)(A). But, the
references to section 107(d) designations in section 172
cannot possibly refer to section 107(d)(1)(C) and (d)(4),
which apply to the designations for the 1-hour ozone
standard in effect at the time of the 1990 amendments.
Unquestionably, the classifications and corresponding
attainment dates for the pre-existing 1-hour 0.12 ppm
ozone NAAQS are “specifically provided” for these areas
in section 181 of Subpart 2.
Therefore, the reference to section 107(d) contained
in section 172 cannot refer to all of section 107(d). Instead,
it must refer only to those portions of section 107(d) that
are relevant to the establishment of attainment dates
under section 172: section 107(d)(1)(A), (B) and (d)(3). See
42 U.S.C. § 7407(d)(1)(A), (B), (d)(3). It follows that the
reference to section 107(d) contained in section 181
should be interpreted, in the same way, to mean only the
portions of section 107(d) - namely, subsections (d)(1)(C)
and (d)(4) — that are relevant to the establishment of
attainment dates under section 181.
The D.C. Circuit correctly invoked the standard
canon of statutory construction that ” ‘identical words
used in different parts of the same act are intended to
have the same meaning.’ ” Pet. App. 80a (citing Gustafson
v. Alloyd Co., 513 U.S. 561, 570 (1995)). But the D.C.
Circuit erred in applying the canon: the only way that the
references to section 107(d) in section 172 and 181 can be
given the same meaning is by interpreting these refer-
ences to apply only to the portions of section 107(d) that
30
are relevant for the establishment of the attainment dates
under the respective provisions.
In summary, an understanding of the structure of the
nonattainment provisions of the Clean Air Act compels
the conclusion that section 181 does not constrain EPA’s
authority to implement the 8-hour standard of 0.08 ppm
promulgated in 1997. At the very least, it follows that
EPA’s interpretation to that effect is permissible and not
inconsistent with the clear intent of Congress. See 62 Fed.
Reg. at 38,884-85. Thus, Chevron, 467 U.S. at 842-43,
requires courts to accord deference to this interpretation.
CONCLUSION
For the foregoing reasons the judgment of the D.C.
Circuit should be reversed. The promulgation of the
NAAQS for ozone and particulate matter did not give
rise to any nondelegation problems and nothing in sec-
tion 181 constrains EPA’s authority to implement the
ozone standard.
Respectfully submitted.
RicHarpD L. Revesz
Counsel of Record
Vickie PATTON
ANN BrewsTER WEEKS
Counsel for Amici Curiae
Environmental Defense, et al.
July 21, 2000
This is a copy of a public record, reproduced as it was published. It is not legal advice, and it may not be the version a court would rely on. Check the official source before you cite it.