Petitioners Reply Brief — Chevron USA Inc. v. Natural Resources Defense Council, Inc.
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L . nie Court, US
FILED
Nos. 82-1005, 82-1247, and 82-1591 FEB AY 1964
OCTOBER TERM, 19838
CHEVRON U.S.A., INC., PETITIONER
D.
NATURAL RESOURCES DEFENSE COUNCIL, INC., ET AL.
AMERICAN IRON AND STEEL INSTITUTE, ET AL.,
PETITIONERS
V.
NATURAL RESOURCES DEFENSE COUNCIL, ING., ET AL. 0
WILLIAM D. RUCKELSHAUS, ADMINISTRATOR,
ENVIRONMENTAL PROTECTION AGENCY, PETITIONER
V.
NATURAL RESOURCES DEFENSE COUNCIL, INC., ET AL.
ON WRIT OF CERTIORAL: TO THE
UNITED STATES COURT OF APPEALS
FOR THE DISTRICT OF COLUMBIA CIRCUIT
REPLY BRIEF FOR THE ADMINISTRATOR OF THE
ENVIRONMENTAL PROTECTION AGENCY
(202) 633-2217
TABLE OF AUTHORITIES
Cases: Page
Alabama Power Co. v. Costle, 636 F. 2d 323. 7, 10, 15, 19
ASARCO, Inc. v. EPA, 578 F.2d 31999999 19
Chrysler Corp. v. Brown, 441 U.S. 211111 11
CPSC v. GTE Sylvania, 447 U.S. 102 11
FCC v. National Citizens Committee for Broad-
TD 16
Motor Vehicle Manufacturers Association v. State
Farm Mutual Co., No. 82-854 (June 24, 1983) 16
Pennhurst State School v. Halderman, 451 U.S. 1. 11
Regional Rail Reorganization Act Cases, 419 U.S.
— —— ¶ ˙ — —— messapiune 11
Russello v. United States, No. 82-472 (Nov. 1,
%%% — a ec On 9
Secretary of Interior v. California, No. 82-1326
344 9
United States v. Clark, 445 U.S. 332 11
Statutes and regulations:
Clean Air Act Amendments of 1970, Pub. L. No.
91-604, 84 Stat. 1676 (formerly 42 U.S.C. 1857
et geg.):
§110(a)(2)(D), 42 U.S.C. 1857c-5(a) (2)
(D
OE CE ne 8, 4,5
5110 (a) (4), 42 U.S.C. 1857¢-5 (a) |) Lae 3, 4, 5
D OS {> ie Sees eee 4,5
5111 (a) (8), 42 U.S.C. 1857c-6 (a) 3 3, 18
F111 c), 42 U.S.C. 1876-6 (b) 4
§111(b) C) G), 42 U.S.C. 1887-6 (b) (1)
(A) 20
§111(b)(1)(B), 42 U.S.C. 1857c-6(b) (1)
arne 20
111 c) (2), 42 U.S.C. 1857-6 (b) (2) ......... 20
5112 (a) (8), 42 U.S.C. 1857-7 (a) (3 8
Clean Air Act, as amended by Pub. L. No. 96-95, 91
Stat. 685, 42 U.S.C. (Supp. V) 7410 et geg.:
§ 110(a) (2) (D), 42 U.S.C. 7410 (a) (2) (D). 6
§ 110(a) (4), 42 U.S.C. 7410 (a) (o) 6
§ 111, 42 U.S.C. 7411 7,10
(1)
Statutes and regulations —Continued: Page
§ 111(a) (8), 42 U.S.C. 7411 (a) (8) ................ 3, 18
3111 cb), 42 U.S.C. 7411 (b) 4
§ 111(b) (1) (A), 42 U.S.C. 7411 (b) (1) (A). 20
§ 111(b) (1) ), 42 U.S.C. 7411(b) (1) (B).. 20
§ 111(b) (2), 42 U.S.C. 7411 (b) (2) 20
§ 112(a) (3), 42 U.S.C. 7412 (a) (3) .............. 8
$172, 43 U.S.C. 7% no 13
§ 172(b) (5), 42 U.S.C. 7502 (b) (5) 17
§ 802(j), 42 U.S.C. 7602 () . 7
Energy Supply and Environmental Coordination
Act of 1974, 42 U.S.C. 1857c-10, repealed, Pub.
L. No. 95-95, f 112 (b) (1), 91 Stat. 799 8
Steel Industry Compliance Extension Act of 1981,
j— . eee 11
40 C. F. R.:
. 15
eee 15
Miscellaneous:
Comment, The Bubble Concept A Feasible Emis-
sions Reduction Alternative?, 9 Dayton L. Rev.
e LIE ava CT ee 2
123 Cong. Rec. (1977):
D 5
rr 17
„eee 11
C. Duerksen, Environmental Regulation of Indus-
trial Plant Siting (Conservation Foundation
. ̃ Ä ̃⁵dV“9v9 TTT 18
36 Fed. Reg. (1971):
r 12
r 12
1 4 12
38 Fed. Reg. (1978):
S rere 12
, A 12
*
3
Miscellaneaous—Continued : Page
41 Fed. Reg. (1976):
rr 6
p. 55528 a 18
45 Fed. Reg. (1980):
2 Se ee ie 2 15
. — * mis 15
H.R. 10498, 94th Cong., 2d Sess. (1976) 10
H.R. 6161, 95th Cong., Ist Sess. (1977) 10
H.R. Conf. Rep. 95-564, 95th Cong., Ist Sess.
%%% 6, 7, 10, 12, 13, 17
H. I.. Rep. 95-294, 95th Cong., Ist Sess. (1977).... 2, 6,
18, 14, 17
Rhinelander, The Proper Place for the Bubble Con-
cept Under the Clean Air Act, 18 Envtl. L. Rep.
r 2
S. 8219, 94th Cong., 2d Sess. (1976) 9
S. 252, 95th Cong., Ist Sess. (1977) .. 9
S. Rep. 95-127, 95th Cong., Ist Sess. (1977) 6
Staff of Senate Comm. on Environment and Pub-
lie Works, 95th Cong., 2d Sess., A Legislative
History of the Clean Air Act Amendments of
1977 (Comm. Print 1978)....... 4 2
/ —ͤ passim
» eee ö 6, 10, 18, 14, 17
Vol. 6 9
Vol. 7 tin 10
In the Supreme Court of the United States
OCTOBER TERM, 1983
Nos. 82-1005, 82-1247, and 82-1591
CHEVRON U.S.A., INC., PETITIONERS
*.
NATURAL RESOURCES DEFENSE COUNCIL, IN c., ET AL.
ON WRIT OF CERTIORARI TO THE
UNITED STATES COURT OF APPEALS
FOR THE DISTRICT OF COLUMBIA CIRCUIT
REPLY BRIEF FOR THE ADMINISTRATOR OF THE
ENVIRONMENTAL PROTECTION AGENCY
The issue posed by this case is whether the 1977
Amendments to the Clean Air Act—which created the
New Source Review (NSR) program for nonattainment
areas—impose a statutory prohibition precluding the Ad-
ministrator of EPA from adopting a regulation that
allows—but does not require—a state to adopt a plant-
wide (“bubble”) definition of the term “source” for pur-
2
standards. Respondents must further establish that
Congress foreclosed the “bubble” approach in a statute
one of whose “main purposes,” according to Congress
itself, was to allow reasonable economic growth to con-
tinue” during the attainment process (see H.R. Rep.
95-294, 95th Cong., Ist Sess. 211 (1977) (emphasis
added), reprinted in 4 Staff of Senate Comm. on Environ-
ment and Public Works, 95th Cong., 2d Sess., A Legisla-
tive History of the Clean Air Act Amendments of 1977,
at 2678 (Comm. Print 1978) [hereinafter Leg. Hist.] )—
notwithstanding the wide consensus that the “bubble” ap-
proach represents an innovative and creative method pre-
cisely for accommodating the goals of efficient growth and
environmental protection.“ And, finally, they must show
that the Act denies the Administrator discretion to give
the states any flexibility whatever in how to define
“source” for purposes of the NSR program, even though
Congress stated that the second of the two “main pur-
poses” of the nonattainment provisions of the 1977
Amendments was “to allow States greater flexibility” in
achieving reasonable economic growth while making rea-
sonable further progress to assure attainment (ibid.
(emphasis added) ).
The history of this case consists of a series of at-
tempts to invent new justifications for the foregoing,
1There is no basis whatever for respondents’ assertion (Br.
4, 37, 41, 42) that EPA is seeking to dispense with or waive
the statutory requirements prescribed by Congress. The issue in
implausible, propositions. Respondents’ brief in this
Court is no exception. Respondents have dramatically
abandoned any defense of the artificial “bright-line” test
adopted by the court of appeals—a test which led that
court to the extraordinary conclusion that the term
“source” is to be given a fixed judicial definition not-
withstanding the court’s own conclusion that the text
and legislative history of the Act provide no such defini-
tion. Instead, respondents renew the contention that the
plantwide definition is “prohibited” by the Act itself
because Congress “specifically intended” new source re-
view to apply to every individual piece of equipment
(Br. 6).* The principal vehicle advanced to buttress this
contention is that the definition of “source” provided by
Congress in Section 111 of the Clean Air Act—a defini-
tion applicable by its terms only to the NSPS (new
source performance standards) program (42 U.S.C.
1857c-6(a) (3) and 7411(a) (3) )*—in fact applies to the
NSR (new source review) program as well.
However, the argument that the Section 111 NSPS
definition “applies” to new source review receives an
entirely new twist in respondents’ merits brief. Respond-
ents purport at the eleventh hour to have discovered that
the new source review program created by Congress in
1977 is not a new program at all. It is now asserted
to be simply the continuation of an old “new source re-
view” program, instituted by Congress in the 1970 Act,
and contained in Sections 110 (a (2) (D) and (4) of the
Act, 42 U.S.C. 1857c-5(a)(2)(D) and (4) (App., in-
* “Br.” refers te respondents’ brief in this Court.
:
i
:
1
|
i
1
4
plicit cross-reference to the Section 111 NSPS definition,
the suggested conclusion is that, ever since 1970, the NSR
program has applied to sources as defined in Section 111.
It follows, respondents say, that in perpetuating the new
source review program in 1977, Congress obviously as-
sumed that the program would continue to apply to all
individual pieces of process equipment.
In fact this argument is a concoction presenting an
entirely distorted picture of the architecture of the Clean
Air Act. The program created by Congress in 1970 in
Sections 110(a)(2)(D) and (4)—usually called loca-
tional review—has nothing to do with the new source
review program first created in 1977 in order to deal
with the problem of nonattainment. The cross-reference
to the Section 111 NSPS definition contained in those
sections“ thus does not in any way suggest that the
Section 111 definition was to apply to the nonattainment
program created in 1977.
The 1970 Clean Air Act did not contemplate non-
attainment at all. It envisioned that all areas of the
country would attain National Ambient Air Quality
Standards (NAAQS) by the statutory deadline of 1975.
To achieve this, the 1970 Act relied primarily on two
programs. First, emissions from existing sources were to
be reduced, in accordance with the state implementation
plan, to meet NAAQS (see Gov’t Br. 4). Second, new
“sources” were subject to new source performance stan-
dards to be promulgated by EPA pursuant to Section 111,
42 U.S.C. 1857c-6.
In connection with the process of attaining and main-
taining NAAQS, new “sources” were required to undergo
a locational review process (to be specified in the SIP)
5 In fact, the locational review sections do not simply incorporate
the NSPS definition of “source” or apply to all “sources” within
the NSPS definition. They require locational review for those
sources for which an NSPS standard has in fact been promulgated
by the Administrator. With respect to the NSPS process, see 42
U.S.C. 1857c-6(b) and 7411(b); page 20, infra.
5
pursuant to Sections 110(a)(2)(D) and (4). This was
to be a “procedure” for “review (prior to construction or
modification)” of the “location of new sources” so as to
“prevent the construction or modification of any new
source” that the state determines “will prevent the attain-
ment or maintenance” of NAAQS. See 42 U.S.C. 1857c-
5(a)(2)(D) and (4). The “procedure” was to cover all
new sources to which a “standard” under the NSPS Sec-
tion 111 program “will apply.”
The purpose of locational review was to create a re-
view process—applicable in “clean” and “dirty” air areas
alike—to make sure that the installation of new plant
and equipment would not prejudice either the attainment
or the continuing maintenance of national air quality
standards.* It looked to the net effect on air quality of
a new or modified “source.” For this reason, its refer-
ence to the NSPS definition of “source” has no independ-
ent functional signific:. ce. The only substantive question
in connection with locational review is whether construc-
tion or modification of a new source“ however defined
—should be prevented because it will adversely affect net
air quality. “Netting” is implicit in the only substantive
judgment called for in locational review: whether the
addition or modification should be vetoed because it will
lead to air quality that does not satisfy NAAQS. If the
addition or modification produces no net increase in emis-
sions, locational review has, by hypothesis, no bite. In
contrast, the whole point of respondents’ submission
about NSR is to impose elaborate requirements (e. g.,
LAER technology, see Gov’t Br. 7) on individual pieces
of machinery even if there is no net effect on air quality.
Importing the NSPS definition into the 1977 NSR pro-
|
*In practice locational review did not turn out to be a program
of great significance; [ flor the first 4 years after the 1970
amendments, States and EPA conducted rather spotty review of new
sources in dirty air areas.” 123 Cong. Rec. 18017 (1977) (remarks
of Senator Muskie), 8 Leg. Hist. 718.
6
gram would thus have a radically different substantive re-
sult than is created by the cross-reference to that defini-
tion in the 1970 locational review provisions.
Beyond this, the fact is that the 1977 Amendments
marked a major change in the over-all architecture of the
Clean Air Act. In contrast to the 1970 Act, which had
assumed that air quality standards would be timely at-
tained, the 1977 Act was established in response to the
failure of a number of regions to attain air quality
standards by 1975. A major concern was that existing
law might completely prohibit the construction or modifi-
cation of facilities in such areas.“ Following EPA’s prom-
ulgation of an administrative solution to this problem
in its “Emissions Offset Ruling” (41 Fed. Reg. 55524
(1976)), Congress passed the NSR program specifically
to deal with the issue of accommodating industrial
growth to the problem of nonattainment. The NSR stat-
ute was intended to be a “comprehensive scheme.”* It
was designed “to reconcile the[] conflicting concerns“ be-
tween air quality attainment and continued economic
growth.“ Congress made clear that it was adopting new
legislation to address new problems not foreseen in 1970.
There exists no support for the novel assertion that the
elaborate NSR provisions considered at length in 1977
are nothing more than an extension of the locational re-
view requirements. Indeed, NSR and locational review
both continue to exist in the current version of the Act
(see 42 U.S.C. 7410(a)(2)(D) and (4)); such co-
existence would hardly be expected if NSR were simply
the current version of locational review.
See Gov't Br. 4-5; H.R. Conf. Rep. 95-564, 95th Cong., Ist Sess.
155-158 (1977), 3 Leg. Hist. 535-538; S. Rep. 95-127, 95th Cong.,
Ist Sess. 55 (1977), 3 Leg. Hist. 1429; H.R. Rep. 95-294, 95th Cong.,
Ist Sess. 207-211 (1977), 4 Leg. Hist. 2674-2678.
8. Rep. 95-127, supra, at 55, 3 Leg. Hist. 1429.
H.R. Rep. 95-294, supra, at 210, 4 Leg. Hist. 2677.
7
At the same time Congress passed the nonattainment
provisions in Part D of the 1977 Amendments, it also
adopted Part C. This dealt with a converse problem:
preventing the significant deterioration of air quality in
areas where the air was cleaner than required by federal
standards. This program—called the “Prevention of Sig-
nificant Deterioration” (PSD) program—was considered
by Congress together with the NSR program in 1977.
See, e.g., H.R. Conf. Rep. 95-564, supra, at 128, 3 Leg.
Hist. 508. The test for what is to be considered “major”
in connection with the NSR term “major stationary
source” and the PSD term “major emitting facility” is
provided in the same section of the Act (42 U.S.C.
7602(j)). And, as noted in our opening brief (at 11
n.19), it is not unusual for a given plant to be subject
to NSR review for one pollutant and PSD review for an-
other. All these considerations suggest that “source”
should have the same meaning in both the NSR and PSD
programs. And it has of course been held that the plant-
wide definition of “source” is the proper one for purposes
of the PSD program. See Alabama Power Co. v. Costle,
636 F.2d 323 (D.C. Cir. 1979).
In sum, the assertion that the Section 111 definition of
“source” applies to the 1977 NSR program because that
program simply continues the requirements of the 1970
locational review sections—which do refer to the Section
111 definition—is a last-minute invention that ignores
the Act’s history and twists it into an unrecognizable
shape.
II.
Respondents’ remaining arguments concerning the ap-
plicability of the Section 111 NSPS definition to the
1977 NSR program were generally anticipated in our
principal brief and can be dealt with summarily. As
pointed out in that brief (at 42-43), Section 111 ex-
plicitly provides that its definition is [for purposes of
this section” (emphasis added). Respondents object that
8
the specification does not provide that it is“ for the
[sic] purposes of this section only’” (Br. 30 n. 57). But
why should Congress, in enacting the NSPS definition in
1970, add the (redundant) word “only” to exclude the
possibility of its applying to the NSR program not created
until 1977? * In fact, Congress took affirmative steps to
avoid tying the new source review program to the NSPS
definition of “source”: as discussed in our opening brief
(at 48-44), it deleted from the 1977 Act a provision
expressly adopting the NSPS definition for the NSR pro-
gram, while at the same time incorporating by reference
other NSPS terms.
Finally, the NSR and NSPS programs are entirely
different in function and structure (see Gov’t Br. 13
n.24, 42-43 n.55). There is therefore no substantive rea-
son to import the NSPS definition into the NSR program.
III.
Respondents' further argument is that the legislative
history of the 1977 Act shows that Congress intended the
NSR program to apply to every individual piece of
process equipment. Respondents misconceive that history.
9
for purposes of the NSR program; in addition, as re-
spondents emphasize (Br. 10, 33), its NSR section re-
ferred to “a facility proposed for construction or modifi-
cation at an existing site or plant,” * thereby suggesting
a difference between “facilities,” on the one hand, and
“sites” and “plants,” on the other. As previously dis-
cussed (Gov’t Br. 45-46 & nn.58, 60), however, both of
these provisions were deleted from the 1977 NSR statute
enacted by Congress.“
Respondents’ contention is that, nevertheless, the Senate
assumed that the NSPS definition would apply to NSR
and that this assumption persisted throughout the con-
sideration and ultimate enactment of the NSR provisions.
Not a shred of evidence supports this argument. Indeed,
it ignores the critical fact that the NSR program eventu-
ally enacted was based principally on the House rather
than the Senate bill.“ The Conference Report plainly
states: 2
All implementation plan revisions must contain a
permit program for new or modified major facilities
similar to the program required in the House bill.
11 8. 8219, 94th Cong., 2d Sess. § 802 (m), at 79 (1976), 6 Leg.
Hist. 4688, 4918.
12 8. 3219, supra, § 118 (g) (1), at 48, 6 Leg. Hist. 4652, 4869.
sumed that the limitation was not intended” (Russello v. United
States, No. 82-472 (Nov. 1, 1988), slip op. 7), and [it is
10
H.R. Conf. Rep. 95-564, 95th Cong., Ist Sess. 157
(1977), 3 Leg. Hist. 537.“ Most significantly, neither
the House bill nor the NSR statute incorporated the
NSPS definition of “source” or referred to a “facility
* * * at an existing site or plant” as the entity subject to
new source review; both applied new source review to a
“new or modified major stationary source” and left the
term “source” undefined.
Respondents argue—in a confusing paragraph—that
the 1977 House bill did not need to adopt the Section 111
definition of “source” because the “plain reading” of
“source” is the Section 111 definition (“ ‘building, struc-
ture, facility, or installation'“) (Br. 31). But this is
nothing more than ipse dixit. The question is whether the
15In fact an examination of the House bill will show that its
permit program was largely the same as the one ultimately adopted.
See Gov't Br. 5-7, and H.R. 6161, 95th Cong., Ist Sess. § 127, at 847-
353 (1977), 4 Leg. Hist. 2332-2338, 2854-2857.
16 The confusion is caused, in part, by the use of the word “an-
other” in the sentence: “In the House bill, there was simply no need
for another provision to define ‘major stationary source’” (Br. 31
(emphasis added)). This suggests what is not the case—that the
just quoted Section 111 definition is made applicable to the NSR
program by some other provision.
In this connection, respondents refer (Br. 31 n.59) to the fact
that the 1976 House bill—unlike the 1977 bill—included a definition
of “major stationary source” that refers to the NSPS definition
of “source.” See H.R. 10498, 94th Cong., 2d Sess. §§ 121(a) (8) and
127(c) (3), at 159, 236 (1976), 7 Leg. Hist. 6896 and 5972, 6880 and
11
House intended, in the absence of an explicit eross-
reference, to import the NSPS definition of “source” into
the NSR program. It begs that question simply to assert
that such an explicit cross-reference was unnecessary, in
the absence of some independent evidence that the lan-
guage or structure or functional purposes of the statute
suggest such a cross-reference."”
The sole “evidence” in fact adduced by respondents is
their quotation (Br. 31-32) (footnote omitted) from the
17 Respondents rely (Br. 86) on part of a statement made by
Senator Muskie during the debates over the Conference Report.
Even assuming that great weight can be accorded to a single floor
remark (see, e. g., Pennhurst State School v. Halderman, 451 U.S. 1,
20 (1981); Chrysler Corp. v. Brown, 441 U.S. 281, 311 (1979)),
this statement does not carry respondents’ argument. Fairly read
in its entirety, it appears to do no more than explain the difference
between “new” and “modified” sources—both subject to new source
review—and makes clear that a “new” source does not escape review
simply because it replaces an older facility that had higher emis-
sions. See 123 Cong. Rec. 26847 (1977), 3 Leg. Hist. 355-356.
In addition, respondents (Br. 38) and amicus United Steelwork-
ers of America cite to the history of the Steel Industry Compliance
Extension Act of 19810 42 U.S.C. 7418) to show that Congress con-
templated a process-unit definition of “source.” The purpose of the
Steel Extension Act was to afford assistance to the steel industry by
extending certain compliance dates. Neither the Act nor its legisla-
tive history focused on the quite unrelated issue of the definition of
“source” under existing law. When the Steel Extension Act was
under consideration in May and June of 1981, the EPA regulations
then in force provided for a dual definition (see Gov’t Br. 11-14) ;
12
Conference Report of the sentence, “The bill [dl efines
major stationary source and major emitting facility as
defined in the Senate bill.“ But the quoted sentence has
nothing to do with the question whether “source” means
a plant or an individual piece of machinery. As a glance
at the context will make clear, it refers exclusively to the
fact that the House and Senate bills differed in their defi-
nitions of the term “major.” The House bill was based on
“design capacity to emit 100 tons annually,” while the
Senate bill referred to “an annual potential to emit 100
tons.” The Conference adopted the Senate’s definition of
“major.” H.R. Conf. Rep. 95-564, supra, at 172, 3 Leg.
Hist. 552. The quoted sentence, referring to this action
on the quantitative standard for measuring “major”
emissions, in no way suggests that the Conference also
intended—at the same time that it deleted the Senate’s
explicit definition of source“ —to endorse the Senate's
understanding of the industrial unit that, if “major,”
would be covered by the NSR program.
IV
Respondents next argue that EPA has, since 1971,
applied the NSPS definition of “source” to new source
review (Br. 4, 6, 7, 15-19, 42) and that Congress
ratified that approach in enacting the NSR program in
1977 (Br. 11, 38, 42, 43). This argument is without
merit.
It is EPA’s Emissions Offset Ruling of 1976 that con-
stitutes the proper point of departure for analyzing
EPA’s approach to the issue in this case (see Gov't Br.
5). There is no quarrel over respondents’ contention
18 Respondents’ reference to EPA's practice back to 1971 is based
on the 1970 locational review provisions, which (as we have shown)
have no bearing on the question presented here. Furthermore, since
those provisions expressly referred to the NSPS section, the fact
that EPA in 1971 and 1973 construed or applied the locational re-
view program in light of NSPS is without significance. In fact,
EPA's pre-1977 regulations recognized state flexibility to determine
the “sources” subject to such review’. See 36 Fed. Reg. 22898, 22400,
22406 (1971) ; 88 Fed. Reg. 15834, 15886, 16886 (1978).
13
(Br. 16-17, 34) that the Offset Ruliny, in referring to a
“major source,” essentially tracked the language of the
NSPS definition (41 Fed. Reg. 55528 (1976)). Nor can
it be disputed that Congress was well aware of the Offset
Ruling when it passed the 1977 Act.“ But we find no
evidence of congressional intent to ratify—indeed, to
freeze—this definition of “source” for purposes of the
NSR program.
The critical fact is that in 1977 Congress determined
that the Offset Ruling should not be enshrined into per-
manent national policy. It was adopted as a temporary
measure to apply to nonattainment areas until July 1,
1979. See 42 U.S.C. 7502 note, 3 Leg. Hist. 251.% Even
in this interim period, the one specific feature of the Rul-
ing that Congress addressed—the “baseline” to be used
for calculating the level of available offsets (ibid.)—was
amended to make it easier to build or alter a “source”
in nonattainment areas. And with respect to all other
aspects of the Ruling during the pre-1979 period, the
statute expressly provided that they “may be modified
by rule of the Administrator” (ibid.). Surely this lim-
ited interim continuation of the Offset Ruling is a giant
step from the proposition that Congress intended in per-
petuity to freeze its approach to new source review. In
any event, Congress made it clear that it intended no
such thing. After the interim period, Congress specified
its own approach to the problem of nonattainment. And,
in doing so, it stated explicitly that one of the “two
main purposes” of the NSR program was “to allow
States greater flexibility for the former purpose [i.e.,
allowing ‘reasonable economic growth to continue in an
% However, EPA did not explain or elaborate on its use of the
NSPS language in defining “major source.” It is not surprising,
therefore, that respondents cannot point to any evidence that Con-
gress knew about or focused on the specific definitional issue.
‘oe See also H.R. Conf. Rep. 95-564, 96th Cong., Ist Sess. 157
(1977), 8 Leg. Hist. 687; H.R. Rep. 96-294, supra, at 14, 211, 4 Leg.
Hist. 2481, 2678.
14
area while making reasonable further progress to assure
attainment’) than EPA's present interpretative regula-
tions afford” (H.R. Rep. 95-294, supra, at 211, 4 Leg.
Hist. 2678 (emphasis added) ). Against this background,
it is hardly plausible that Congress should have intended,
sub silentio, to freeze into place an approach to new source
review that would prevent the Administrator from giving
states any discretion to adopt a definition of the (statu-
torily undefined) term “source” precisely calculated to
achieve the statute’s “main purposes.”
We submit that the most siggpificant fact about the
“administrative” history of the question at issue is not
the pre-1977 history at all. It is that, ever since the
1977 Amendments were adopted, EPA has taken the
position that the statute does not itself mandate one au-
thoritative definition of “source” for purposes of new
source review. As our principal brief recounts in detail
(at 9-14), from the first time that it addressed the 1977
Amendments the agency has asserted the power to allow
states to adopt a plantwide approach. (Respondents’ ar-
gument (Br. 18) that EPA’s 1979 proposals were some-
what narrower than the rules adopted in 1981 is, of
course, irrelevant on the question at issue: whether
EPA has power to permit states to use the “bubble”
concept at all.) In fact, when EPA in August 1980
adopted the dual definition, it did not assert that it has
no discretion in the premises; its action constituted an
exercise of that discretion. This case is, then, one for
the application of the conventional rule of administra-
tive law that a court should defer to the agency’s view
of its own authority under a statute committed to it
for enforcement. See Gov’t Br. 22.
15
than-even offset and therefore conflicts with the purpose
of “[{mJaking the construction of major new sources a
force for reducing pollution” (Br. 38). As shown in
our opening brief (at 26-27, 28, 35), however, the pur-
pose of new source review is to ensure that emissions
from new or modified sources do not prejudice the tran-
sition to attainment. New source review is only one part
of an integrated and complex scheme; it was not de-
signed to carry by itself the burden of improving air
quality in nonattainment regions. By looking to the net
impact on pollution levels of a new or modified source,
the plantwide definition serves the preventive objective
of the NSR program.
Respondents also object (Br. 4, 18, 20, 40 n.69) that
the EPA regulation does not require new source review
even when there is not a total offset in emissions at a
plant. This objection, however, does not bear on the
issue of the NSR definition of “source.” Rather, it is
an attack on the significance levels that EPA has set
pursuant to the decision in Alabama Power Co. v. Costle,
supra, which were not challenged in a proceeding for
judicial review and whose validity is not before the
Court. It should: also be noted that respondents’ argu-
ment applies to the dual as well as the plantwide defini-
tion: the significance levels are applicable under both
definitions (see Gov’t Br. 6 n.10, 9 n.14, 28 n.36). In
fact the increases permitted by the significance levels
are truly de minimis (see Gov’t Br. 28 n.36). The NSR
statute itself excludes—as “minor’—sources that emit
less than 100 tons per year of a pollutant (see Gov't
Br. 6 n.10, 9 n.14); surely it should not be read to re-
quire a dual definition of “source” in order to trigger
review of every marginal increase in emissions. The
existing EPA regulation fairly effectuates the statutory
purpose of new source review: to ensure that emissions
™ See Gov't Br. 6 n.10; 40 C. F.. 61.18(j) (1) (x); % CA.
52.24(f) (10); 45 Fed. Reg. 62676, 62706 (1980).
t
16
resulting from economic growth and industrial expan-
sion do not interfere with the goal of attainment.”
Respondents further urge (Br. 2, 4, 32, 40-41) that
it is illogical and contrary to the purposes of the Act to
require new source review when a large piece of equip-
ment is installed at a new site, but not to require it
when that same piece of equipment is installed (and
offsetting pollution reductions are made) at an existing
plant. But, once again, respondents have overlooked the
“hold harmless” purpose of new source review in the
overall context of the nonattainment program. In the
case of the existing plant, the plantwide definition en-
sures that the industrial modernization or expansion
does not interfere with air quality attainment. On the
other hand, the project at the new site, by hypothesis,
22 As discussed in our opening brief (at 13, 14, 29-84), the
plantwide definition can facilitate reductions in emissions by en-
couraging the replacement of older, heavily polluting equipment
with newer, cleaner equipment. (Respondents’ claim that this con-
tention was abandoned in the court of appeals (Br. 22, 44, 45, 46)
is unfounded; see EPA C. A. Br. 12, 87 n.34.) Respondents echo
(Br. 42, 44-47) the court of appeals’ criticism (82-1005 Pet. App.
Al18 n.41 (emphasis in original)) that, “in abandoning [in 1981]
its earlier position [in the 1980 regulation], EPA did not cite, nor
have we found in the record, any study, survey, or support for the
opposite position, now tendered by EPA, that the dual definition
would indeed retard improvement of air quality in the aggregate
* * * byWiscouraging replacement of older processes or equipment
with newer, cleaner varieties.” This fails to recognize that the
Administrator's conclusion involved a prediction of how business
and investment decisions would differ in response to the plantwide
and dual definitions. “[T]o the extent that factual determinations
17
results in a new increase in emissions that significantly
worsen the level of pollution, thus interfering with the
goal of attainment. To make new source review a func-
tion of a project’s net impact on air quality and its con-
sequences for attainment, as the plantwide definition
does, is in full accord with the design and purpose of the
NSR program.”
23 For the same reason, there is no merit to respondents’ argu-
ment (Br. 40-41) that the EPA regulation improperly discriminates
between existing and new business competitors in a nonattainment
area.
In much the same vein, the amici states argue that the EPA
regulation, by not requiring a uniform national definition of
“source,” will allow a state to be pressured into adopting the defi-
nition that minimizee its environmental controls in order to attract
new businesses; in effect, amici ask the “ourt to relieve them
of the hard choices about accommodating growth and environmental
protection (see State Am. Br. 11) that Congress desired in 1977
to leave to the states. Their argument—which would be satisfied by
any nationwide definition and therefore lends no support to the
dual definition as such—overlooks the fact that the Act requires
the states to have an EPA-approved implementation plan that con-
forms to the requirements of the Act and provides for reasonable
progress toward and timely attainment of national air quality
standards. That states have flexibility to design the detailed
methods and enforcement procedures for achieving attainment, con-
sistent with federal law, and to make economic choices between
existing and new sources or between present and future growth, is
exactly what Congress intended in 1977 (see Gov't Br. 28, 35-41) 7
indeed, the statutory provision that allows a state to budget, at its
option, an emissions ellowance for growth (42 U.S.C. 7502 (b) (5) )
clearly reflects this intent. Amici have cited nothing in the legisla-
tive history to indicate that Congress was so concerned about
18
VI.
Respondents lastly contend (Br. 4-5 n.11, 19-20, 40
n.69, 42, 44) that the EPA regulation, even if valid
with respect to construction or modifications in areas
in which there is an approved state implementation
plan, is improper in areas that do not have an approved
plan and are subject to the construction moratorium
(see Gov’t Br. 7). Respondents suggest no reason why
EPA should be required to give two different meanings
to the term „source“ in the NSR program,“ and to
do so would exacerbate the regulatory complexities and
burdens that the 1981 regulations were intended to re-
duce (see Gov’t Br. 12-14, 35 n.45). Furthermore, the
regulation is consistent with the purposes of the mora-
torium: by allowing industrial growth that does not
adversely affect air quality while prohibiting both the
construction of all new facilities and the renovation of
existing facilities for which there is a non-de minimis
emissions increase, it prevents a deterioration in air
quality during the period an approved implementation
plan is not in place and provides a strong incentive for
the prompt submission of a plan that complies with fed-
eral requirements (see Gov’t Br. 27-28 n.35, 29 n.87,
34-35 n.44). Accordingly, application of the EPA reg-
ulation in areas subject to the construction moratorium
is not invalid.
VII.
Even if the NSPS definition of source“ “any build-
ing, structure, facility, or installation which emits or
may emit any air pollutant” (42 U.S.C. 1857e-6 (a) (3)
and 7411 (a) (3)) —were formally applicable to new
source review, it would not resolve the question pre-
company’s decision where to locate its operations. See C. Duerksen,
Environmental Regulation of Industrial Plant Siting 56-71 (Con-
servation Foundation 1983).
As the court below noted (82-1005 Pet. App. A1l7 n.40), the
moratorium “has been cast, not as a discrete program, but as an
integral part of a larger production, the nonattainment scheme.”
19
sented in this case: the industrial unit or entity that
is subject to such review. Consistent with general prin-
ciples of administrative law, the D.C. Circuit has rec-
ognized, in this case“ and in other cases involving the
Clean Air Act,“ that EPA has discretion to construe the
constituent terms of the definition in light of the lan-
guage, history, and purposes of the particular program
under consideration; as these decisions “illustrate, dif-
ferent delineations may be appropriate for different stat-
utory programs” (82-1005 Pet. App. A9 n.22). Once the
“bright line“ test adopted by the Gourt below is set
aside—as even respondents do not contest it must be—
there is no reason why the terms “building,” “struc-
ture,” “facility,” and “installation” cannot be under-
stood to embrace an entire plant rather than a specific,
individual item of equipment.”
Respondents offer two arguments in response to this
analysis. First, they assert (Br. 29-30 n.56) that a dual
definition applies throughout the Clean Air Act and that
Alabama Power supports that conclusion. But Alabama
Power does no such thing. As the court below under-
stood (82-1005 Pet. App. A2-A3, A13, A16), Alabama
Power clearly holds that the plantwide definition is re-
quired in the PSD program and that the dual definition
is impermissible (636 F.2d at 396-398, 401-402).
Second, respondents argue (Br. 8, 27, 41-42) that in
the NSPS program itself every individual piece of
25 82-1005 Pet. App. A9 n.22.
26 Alabama Power Co. v. Costle, 636 F.2d at 396-398, 410;
ASARCO, Inc. v. EPA, 578 F.2d 319, 824 n.17 (1978).
27 We note that in any event the NSPS definition in no way re-
quires a dual definition of “source.”
28In Alabama Power, the court stated (636 F.2d at 397) that,
in order “!t)o allow an entire plant or other appropriate grouping
of industrial activity to be subject as a single unit to PSD, as
Congress clearly intended, EPA should devise regulatory definitions
of the terms ‘structure,’ ‘building,’ ‘facility,’ and ‘installation’ to
provide for the aggregation, where appropriate, of industrial activi-
ties according to considerations such as proximity and ownership.”
— —
20
pollution-emitting equipment must be deemed to be a
“source.” Again, this is incorrect. The NSPS program
calls upon the Administrator to “publish * * * a list of
categories of stationary sources * * * [that] in his judg-
ment * * cause[], or contribute[] significantly to, air
pollution” (42 U.S.C. 1857c-6 (b) (1) (A)) and 7411(b)
(1) (A)), and to establish “Federal standards of per-
formance for new sources within [each] such category”
(42 U.S.C. 1857e-6 (b) (1) (B) and 7411(b) (1) (B)); in
establishing such standards the Administrator is author-
ized to “distinguish among classes, types and sizes within
categories of new sources” (42 U.S.C. 1857c-6(b) (2) and
7411(b) (2)). Thus, in the NSPS program itself, the Ad-
ministrator exercises discretion and judgment in listing
categories of sources and in determining the appropriate
“source” to be subject to a given standard. In contrast,
if the NSPS meaning of “source” were simply carried
over to new source review, such flexibility would be lost.
Instead—and this is the very result respondents seek—
the NSR program would rigidly encompass any and all
industrial units that fall within the expanse of the NSPS
definition. Such an outcome wrenches the NSPS defini-
tion from its substantive and statutory context; it is nei-
ther good law nor good sense.
This brings us back to where we began. Our submis-
sion is that the definitional issue in this case is, like many
other questions brought to the courts, a matter of sound
policy, not legal validity. Respondents bear a heavy bur-
den in challenging that submission. To prevail, they must
demonstrate that the Act precludes the regulation and
that the Administrator has no discretion—either in prom-
ulgating a definition of “source” for NSR or in inter-
preting the constituent terms in the NSPS definition.
Nothing in the text, history, or policies of the Act, or in
its administrative implementation, warrants such an ex-
treme conclusion.
21
For the foregoing reasons and those stated in our
opening brief, it is respectfully submitted that the judg-
ment of the court of appeals should be reversed.
REX E. LEE
Solicitor General
FEBRUARY 1984
la
APPENDIX A
As enected in 1970, Section 110 (a), 42 U.S.C. 1857c-
5(a), provided in pertinent part:
State implementation plans for national primary and
secondary ambient air quality standards
(a) Submission to Administrator; time for submis-
sion; State procedures; required contents of
plans for approval by Administrator; approval
of revised plan by Administrator
(1) Each State shall, after reasonable notice and
public hearings, adopt and submit to the Adminis-
trator, within nine months after the promulgation
of a national primary ambient air quality standard
(or any revision thereof) under section 1857c-4 of
this title for any air pollutant, a plan which pro-
vides for implementation, maintenance, and enforce-
ment of such primary standard in each air quality
control region (or portion thereof) within such
State. In addition, such State shall adopt and sub-
mit to the Administrator (either as a part of a plan
submitted under the preceding sentence or sepa-
rately) within nine months after the promulgation
of a national ambient air quality secondary stan-
dard (or revision thereof), a plan which provides for
implementation, maintenance, and enforcement of
such secondary standard in each air quality control
region (or portion thereof) within such State. Un-
less a separate public hearing is provided, each State
shall consider its plan implementing such secondary
2a
determines that it was adopted after reasonable
notice and hearing and that—
(D) it includes a procedure, meeting the re-
quirements of paragraph (4), for review (prior
to construction or modification) of the location
of new sources to which a standard of per-
formance will apply.]
(4) The procedure referred to in paragraph (2)
(D) for review, prior to construction or modifica-
tion, of the location of new sources shall (A) pro-
vide for adequate authority to prevent the construc-
tion or modification of any new source to which a
standard of performance under section 1857c-6 of
this title will apply at any location which the State
determines will prevent the attainment or mainte-
nance within any air quality control region (or
portion thereof) within such State of a national am-
bient air quality primary or secondary standard,
and (B) require that prior to commencing construc-
tion or modification of any such source, the owner
or operator thereof shall submit to such State such
information as may be necessary to permit the State
to make a determination under clause (A).
W „ 4 „. everea, 1904 4h 20.
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.