Opposition Brief — Central Arizona Water Conservation District v. Environmental Protection Agency
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No. 92-2052 AUG 25 1993
OFFICE Ob wie OLERK
In the Supreme Court of the Giuted States
OCTOBER TERM, 1993
CENTRAL ARIZONA WATER CONSERVATION
DISTRICT, ET AL., PETITIONERS
Vv.
E;NVIRONMENTAL PROTECTION AGENCY, ET AL.
ON PETITION FOR A WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE NINTH CIRCUIT
BRIEF FOR THE FEDERAL RESPONDENT
IN OPPOSITION
DREW S. DAYS, III
Solicitor General
MYLES E. FLINT
Acting Assistant Attorney General
Scott A. SCHACHTER
Attorney
Department of Justice
Washington, D.C. 20530
(202) 514-2217
GERALD YAMADA
Acting General Counsel
ALAN ECKERT
Associate General Counsel
VICKIE PATTON
Attorney
Environmental Protection Agency
Washington, D.C. 20460
er ee —
BEST AVAILABLE COPY ack
QUESTION PRESENTED
Whether the court of appeals correctly upheld the En-
vironmental Protection Agency’s determination that vis-
ibility impairment in Grand Canyon National Park is
“reasonably attributable” to the Navajo Generating Sta-
tion, a major coal-fired power plant located near the
Park.
TABLE OF CONTENTS
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TABLE OF AUTHORITIES
Cases:
Arkansas v. Oklahoma, 112 S. Ct. 1046 (1992) .......... 10
Ellis v. Dizon, 349 U.S. 458 (1955) ...................cccsceee. i)
Maine v. Thomas, 874 F.2d 883 (Ist Cir. 1989) .......... 12, 13
Vermont v. Thomas, 850 F.2d 99 (2d Cir. 1988) ........ 2. i
Statutes and regulations:
Clean Air Act, 42 U.S.C. 7401 ef seq. ............ccsceecceceserseees 2
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§ 169A(g)(6), 42 U.S.C. T491(g)(6) «22... ceeeeeeeeeeeeeeeeeeees 2
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Miscellaneous:
136 Cong. Rec. (1990):
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pp. S3814-S3815 (daily ed. Apr. 3) ..........ccccceceeeeeeeeeeeeees 5
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53 Fed. Reg. (1988):
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54 Fed. Reg. (1989):
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56 Fed. Reg. (1991):
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H.R. Rep. No. 294, 95th Cong., Ist Sess. (1977) ............... 3
In the Supreme Court of the Guted States
OCTOBER TERM, 1993
No. 92-2052
CENTRAL ARIZONA WATER CONSERVATION
DISTRICT, ET AL., PETITIONERS
v.
ENVIRONMENTAL PROTECTION AGENCY, ET AL.
ON PETITION FOR A WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE NINTH CIRCUIT
BRIEF FOR THE FEDERAL RESPONDENT
IN OPPOSITION
OPINION BELOW
The opinion of the court of appeals (Pet. App. 2711-
2740) is reported at 990 F.2d 1531.
JURISDICTION
The judgment of the court of appeals was entered on
March 25, 1998. The petition for a writ of certiorari was
filed on June 23, 1993. The jurisdiction of this Court is
invoked under 28 U.S.C. 1254(1).
(1)
STATEMENT
Petitioners sought review of regulations issued by the
Environmental Protection Agency (EPA) under the
Clean Air Act (CAA), 42 U.S.C. 7401 et seq. 56 Fed. Reg.
50,172 (1991). Those regulations were designed to rem-
edy visibility impairment in the Grand Canyon National
Park (Park), which EPA found to be attributable to the
Navajo Generating Station (Navajo or NGS), a major
coal-fired power plant in northern Arizona located
approximately 15 miles from the Park. The court of ap-
peals upheld the regulations and denied the petition for
review.
1. Congress substantially amended the CAA in 1977.
As part of those amendments, Congress enacted Section
169A, 42 U.S.C. 7491, to address “visibility impairment.”
Section 169A(a)(1) set “as a national goal the prevention
of any future, and the remedying of any existing, im-
pairment of visibility in mandatory class I Federal areas
which impairment results from manmade air pollution.”
See Vermont v. Thomas, 850 F.2d 99, 100 (2d Cir. 1988).
“Mandatory class I Federal areas” are certain national
parks, wildernesses and international parks described in
42 U.S.C. 7472(a), which may not be designated as other
than class I. 42 U.S.C. 7491(g)(5).. The Park is such an
area. 40 C.F.R. 81.403. Those areas are the responsibil-
ity of federal land managers such as the Department of
the Interior (DOI). 42 U.S.C. 7602(i). “[V Jisibility im-
pairment” “include[s| reduction in visual range and at-
mospheric discoloration.” 42 U.S.C. 7491(g)(6).
The EPA is required to issue regulations to assure
“reasonable progress toward meeting the national goal,”
42 U.S.C. 7491(a)(4), including requiring each State with
a class I area where visibility is an important value to
3
| revise its state implementation plan (SIP)' to contain
| “such emission limits, schedules of compliance and other
measures as may be necessary to make reasonable
progress toward meeting the national goal.” 42 U.S.C.
7491(b)(2). Congress was especially concerned about vis-
ibility impairment in “areas of breathtaking panorama,”
including the Grand Canyon: “[A]reas such as the Grand
Canyon * * * have encountered a serious problem:
emissions from powerplants have cast, or threaten to
| cast, a pall in the atmosphere that drastically interferes
| with good visibility. This visibility problem is caused
| primarily by emission into the atmosphere of sulfur diox-
| ide * * * from inadequate|ly] controlled sources.” H.R.
| Rep. No. 294, 95th Cong., Ist Sess. 203-205 (1977). Navajo
was one of two power plants singled out: “‘ Much of this
[reduced visibility] can probably be attributed to emis-
sions from powerplants such as * * * Navaljljo.’” Jd. at
204 (citation omitted).
2. EPA originally promulgated regulations imple-
menting Section 169A in 1980. See 45 Fed. Reg. 80,084
(40 C.F.R. Pt. 51, subpt. P). Those regulations called on
affected States to develop SIPs that provide for, among
other things, identification of any existing stationary
source “which may reasonably be anticipated to * * *
contribute to impairment of visibility [which] is reason-
' Section 110 of the CAA, 42 U.S.C. 7410, provides a joint fed-
eral/state system for establishing and implementing air quality
goals, standards and emissions limitations. States must submit to
EPA for approval State Implementation Plans (SIPs) containing
such measures as necessary or appropriate to meet applicable re-
quirements in the CAA. Section 110(a)(2)(J), 42 U.S.C.
7410{a\(2)(J), directs that SIPs meet the requirements of the visi-
bility protection provisions in Section 169A of the CAA. Section
110(c)(1), 42 U.S.C. 7410(c)(i), requires EPA to promulgate regu-
lations setting forth a Federal Implementation Plan (FIP) when a
State fails to submit a required SIP or SIP revision.
_ 4
ably attributable to that existing stationary facility,” 40
C.F.R. 51.302(¢)(4)(), and “measures * * * necessary to
make reasonable progress toward the national goal.” /d.
§ 51.302(c)(2)(i). The regulations defined “visibility im-
pairment” as “any humanly perceptible change in visibil-
ity (visual range, contrast, coloration) from that which
would have existed under natural conditions.” /d.
§ 51.301(x). “Reasonably attributable” was defined as
“attributable by visual observation or any other tech-
nique the State deems appropriate.” /d. § 51.301(s). That
expansive definition was designed to provide broad
discretion to the States (or the Administrator of EPA in
the case of a FIP) in selecting appropriate methods to
attribute impairment to a source. 45 Fed. Reg. 80,094
(1980).
In the preamble to the 1980 regulations, EPA stated
that it would implement Section 169A in phases. Phase I
included the control of visibility impairment “that can be
traced to a single existing stationary facility or small
group of existing stationary facilities,” 45 Fed. Reg.
80,085 (1980), also known as “reasonably attributable”
impairment. KPA deferred addressing other types of
impairment. Specifically, EPA deferred action on
regional haze, which is “widespread, regionally
homogeneous haze from a multitude of sources which
impairs visibility in every direction over a large area,”
ibid., until, among other things, “regional scale models
become refined.” Jd. at 80,086."
“ Pursuant to the 1990 CAA Amendments, EPA established the
Grand Canyon Visibility Transport Commission (GCVTC), which
includes eight western states and is charged with transmitting to
EPA by 1995 recommendations on “the promulgation of regula-
tions under section [169A] * * * for addressing regional haze” in
the Park. 42 U.S.C. 7492(d)(2)(C). 56 Fed. Reg. 57,522 (1991); id.
at 50,172 n.l. The GCVTC is a “long-term” complement to EPA’s
efforts to remedy impairment in the Park attributable to Navajo.
5
3. Pursuant to 40 C.F.R. 51.302(¢)(1), DOI certified
the existence of visibility impairment in all class I areas
within its jurisdiction in the lower 48 States. 56 Fed.
Reg. 50,173 (1991). DOI supplemented its certification
and identified Navajo as a suspected source of reasonably
attributable visibility impairment in the Park, based on
photographic evidence. Docket A-89-02, II-D-8 at 2. In
November 1987, acting pursuant to a consent decree re-
quiring EPA to implement its 1980 regulations where
States had failed to do so, as required by Sections 110(c)
and 169A of the CAA, EPA disapproved the Arizona SIP,
among other reasons, because it did not contain provi-
sions addressing visibility impairment, and promulgated
a partial visibility FIP. See 56 Fed. Reg. 50,173 (1991).
In September 1989, EPA preliminarily concluded that
a significant portion of wintertime visibility impairment
at the Park is reasonably attributable to Navajo,*® and so-
- licited public comment. 54 Fed. Reg. 36,948-36,949 (1989).
136 Cong. Rec. 52890 (daily ed. Mar. 21, 1990). Jd. at S8814-S3815
(daily ed. Apr. 3, 1990). The GCVTC is expected to “be especially
helpful in addressing pollution sources outside the immediate
vicinity of the canyon.” Id. at S3815.
* Navajo is a 2250 megawatt coal-fired electric generating plant,
located near Page, in northern Arizona, approximately 15 miles
from the Park. 56 Fed. Reg. 50,174 (1991). Navajo emits more
than 70,000 tons of uncontrolled sulfur dioxide (SO,) per year and
is the second largest single source of SO, in the western United
States, emitting more SO, than is emitted in the entire Los Angeles
basin. Docket A-89-02A, II-D-36 at 13. SO, is transformed in the
atmosphere to visibility-impairing sulfate (SO,) particles or aerosol.
Salt River Project (SRP), an intervenor-respondent below, is the
operator of Navajo and owns 21.7% of Navajo for its own use and
benefit, and 24.8% for the use and benefit of the United States
Bureau of Reclamation. The Los Angeles Department of Water &
Power, the Arizona Public Service Company, the Nevada Power
Company, and the Tucson Electric Power Company are the
remaining owners of Navajo. 56 Fed. Reg. 50,174 & n.7 (1991).
een
6
EPA’s preliminary finding was based on the draft final
report from a 1987 wintertime field study, the Winter
Haze Intensive Tracer Experiment (WHITEX), con-
ducted by the Park Service, ibid., that, among other
things, involved the injection of a unique tracer at
Navajo that “fingerprinted” Navajo’s emissions when de-
tected downwind. Pet. App. 2720. In February 1991, after
reviewing additional information—including the final
WHITEX report, a review of the WHITEX study by the
National Academy of Sciences, preliminary results from
another Park Service monitoring study that documented
intense impairment below the rim of the canyon, and ini-
tial data analysis from a visibility study by SRP, the op-
erator and a co-owner of Navajo—EPA proposed to find
that certain winter visibility impairment episodes at the
Park are reasonably attributable to Navajo and again so-
licited comment. 56 Fed. Reg. 5,178, 5,176-5,177, 5,178-
5,180 (1991).*
After the public comment period closed, senior EPA
policy officials facilitated discussions among various en-
tities—including the Navajo owners, the State of Ari-
zona, and environmental groups—to explore more envi-
ronmentally protective and economically efficient con-
trol options. See 56 Fed. Reg. 50,176-50,177 (1991). The
meetings resulted-in a Memorandum of Understanding
(MOU) between the Navajo owners and the environmen-
tal groups. The MOU recommended to EPA a regula-
tory approach that would achieve significantly more en-
vironmental benefit at much less cost than EPA’s
proposal. EPA published the recommended regulatory
4 Based on the attribution proposal, EPA proposed to require a
70% continuous SO, emission limitation for Navajo, determined on
a 30-day rolling average, phased-in between 1995 and 1999. EPA
requested comment on this and three other control options,
including a 90% emission limitation. 56 Fed. Reg. 5178 (1991).
7
approach and reopened the public comment period. 56
Fed. Reg. 38,399 (1991).
4. In October 1991, EPA published a Final Rule con-
taining (1) EPA’s final determination that certain Visi-
bility impairment episodes in the Park are reasonably
attributable to Navajo, and (2) federal revisions to the
visibility SIP to remedy such impairment. 56 Fed. Reg.
50,172 (1991). EPA based the attribution finding upon ex-
tensive data, studies, analyses, reports and comments in
the record, which demonstrated that Navajo is a signifi-
cant, and at times dominant, contributor to impairment
in the Park. Jd. at 50,177. Those included data submitted
during the comment period, which confirmed photo-
graphic data from WHITEX showing that visibility be-
low the rim of the canyon is impaired more often and to a
greater degree than visibility above the rim of the
canyon. /d. at 50,180. With respect to the measures re-
quired to remedy the attributable impairment, EPA’s
Final Rule was consistent with the MOU, requiring a
90% SO, emission reduction, and providing a greater de-
gree of expected visibility improvement at a lower cost
than that originally proposed. Id. at 50,177, 50,178-50,179,
50,183.
5. Petitioners sought review of the Final Rule in the
United States Court of Appeals for the Ninth Circuit.
The court of appeals rejected petitioners’ contention that
the Final Rule impermissibly regulates “regional haze,”
noting that while Navajo was not the sole source of visi-
bility impairment at the Park, “EPA still has the statu-
tory authority to address that portion of the visibility
impairment problem which is, in fact, ‘reasonably at-
tributable’ to” Navajo. Pet. App. 2731. The court also re-
jected petitioners’ argument that EPA was limited to ad-
dressing visibility impairment directly traceable to pol-
luting plumes that are noticeable by visual inspection or
simple monitoring techniques. The court explained that
8
in promulgating a FIP under 42 U.S.C. 7410(c), EPA
stands in the shoes of the defaulting State, and that EPA
may therefore determine whether impairment is
“reasonably attributable” to a given source not only by
visual observation but also “by * * * any other tech-
nique [it] deems appropriate.” Pet. App. 2732 (quoting 40
C.F.R. 51.301(s)). The court concluded that the technical
scientific record compiled by EPA more than adequately
supported EPA’s determination that visibility impair-
ment in the Park is “reasonably attributable” to Navajo.
Pet. App. 2732, 2739-2740. Accordingly, the court denied
the petition for review.
ARGUMENT
Petitioners contend that visibility impairment in the
Park is not “reasonably attributable” to Navajo. The
cour’ of appeals properly construed the applicable statu-
tory and regulatory provisions, and its decision does not
conflict with any decision of this Court or any court of
appeals. The court of appeals’ rejection of petitioners’
fact-bound arguments does not warrant further review.
1. Petitioners renew their contention that EPA acted
beyond its regulatory authority because the visibility
impairment in the Park is “regional haze,” rather than
visibility impairment “reasonably attributable” to
Navajo. Pet. 11-19. That contention lacks merit. EPA
relied on several qualitative and quantitative scientific
analyses of extensive monitored data, which taken
together presented a clear relationship between certain
visibility impairment episodes in the Park and SO,
emissions from Navajo. E.g., Docket A-89-02A, II-D-29,
IV-D-210, IV-D-164, II-D-24, II-B-19, IV-D-171, IV-D-
381, App. H. Indeed, after reviewing only one of these
studies, the National Academy of Sciences confirmed
that “NGS contributed significantly to haze in” the
Park, Docket A-89-02A, II-D-36 at 3, that “NGS emis-
i
sions significantly contributed to SO, aerosol and
resultant haze at Hopi Point in” the Park, id. at 20, and
that the “rate of SO, emissions from NGS is easily large
enough to serve as the source of sulfur measured in the”
Park. Id. at 33. The National Academy of Sciences also
concluded that “if NGS emissions were controlled, then
wintertime haze at [the Park] would most likely be re-
duced.” /d. at 5.
Petitioners nonetheless argue that EPA is without
authority to attribute visibility impairment on the basis
of “sophisticated and unproven mathematical models and
complex monitoring techniques,” but-may rely only on
“visual observation or simple monitoring techniques.”
Pet. 14. Petitioners do not really dispute, as indeed they
cannot, the court of appeals’ conclusion that no such lim-
itation can plausibly be read into the broad definition of
“reasonably attributable” in the enabling regulations—a
definition that specifically contemplates attributions
based on visual observation “or any other technique the
State deems appropriate.” 40 C.F.R. 51.301(s) (emphasis
added). Petitioners contend instead that the court of ap-
peals erred in upholding EPA’s reliance on the definition
of “reasonably attributable” in 40 C.F.R. 51.301(s) be-
cause that regulation applies only to States, and that
EPA instead should have considered 40 C.F.R. 52.26(c),
which in petitioners’ view limits EPA’s discretion in se-
lecting attribution techniques. Pet. 5 & n.3, 11 n.10.
Because petitioners failed to present their contention be-
low, it has been waived. Ellis v. Dixon, 349 U.S. 458, 460
(1955). In any event, the federal visibility monitoring
regulations at 40 C.F.R. 52.26 do not define “reasonably
attributable” impairment, id. § 52.26(b), or contain re-
medial authority.” Aside from their obvious disagree-
® Because of the large number of States in need of visibility
FIPs and in light of the on-going nature of the regulatory re-
10
ment with the result reached by EPA in this case, peti-
tioners offer no substantial argument for failing to ac-
cord EKPA’s interpretation of its own regulations the
“great deference” to which that interpretation is enti-
tled. See Arkansas v. Oklahoma, 112 S. Ct. 1046, 1058-
1061 (1992). Indeed, petitioners’ proposed interpretation
would introduce a discrepancy between the SIP and FIP
authority that would be implausible as a means of imple-
menting the statutory scheme (in which, as we have ex-
plained, SIPs and FIPs have a similar functional role).
Petitioners’ argument that EPA’s Phase I authority
is limited to impairment that is detectable by visual ob-
servation or simple monitoring techniques also distorts
the nature of SO, regulation under the Phase I regula-
tions. Phase I is not limited to visual tracing. In order
to trigger Phase I action under the 1980 regulations, it
is necessary only that impairment “can be physically
traced to a source.” Docket A-89-02, II-A-1 at 6. See also
quirements, EPA issued provisions in 40 C.F.R. Pt. 52 that func-
tioned as federal companions to the state visibility monitoring
strategy, new source review rules, and long-range strategies issued
in 1980 at 40 C.F.R. Pt. 51. 54 Fed. Reg. 36,953 (1989). EPA de-
termined that, with respect to source-attribution and remediation
provisions, it would rely on its regulations in 40 C.F.R. Pt. 51,
since “Arizona is the only State for which remedial Federal mea-
sures are even potentially needed at this time.” 54 Fed. Reg.
36,953 (1989). EPA further reasoned that it was appropriate to
interpret the references to the rights and duties of a “State” under
40 C.F.R. Pt. 51 to include the “Administrator” in the case of a
FIP issued under Section 110(c)—especially since, as the court of
appeals recognized (Pet. App. 2732), EPA stands in the shoes of
the defaulting State when acting pursuant to Section 110(c). EPA
twice solicited public comment on its interpretive view that the
Administrator, like a State, may utilize whatever techniques he
deems appropriate in making reasonable attribution findings. bid.
See also 56 Fed. Reg. 5,189 (1991). That interpretation is plainly
reasonable and, until now, has not been challenged by petitioners in
any forum.
———
11
45 Fed. Reg. 80,085 (1980). That requirement was clearly
met here. In any event, petitioners’ claim fails even un-
der their own theory. Contrary to petitioners’ premise
that SO, “does not cause visible plumes and cannot give
rise to plume blight,” Pet. 7, “sulfates can and do
contribute to visible plumes and single source haze * * *
[and sources] should be required to * * * reduce SO,
emissions where improvement in visibility is antici-
pated.” Docket A-89-02, II-A-1 at 14.
In sum, EPA’s Phase I authority extends to the type of
visibility impairment at issue in this case—impairment
caused by SO, emissions actually traced to a single facil-
ity—and that authority is not extinguished because, in
addition to photographic data and various basic analyses
of monitored data, those emissions were attributed by
relatively complex methodologies.
2. Petitioners also argue (Pet. 17-18) that EPA’s ap-
plication of its regulations in this case is arbitrary and
capricious because it is inconsistent with prior agency
interpretations of those regulations. In pressing that
claim, petitioners principally rely on the preamble to a
proposed regulation on attribution that in fact was not
adopted in the form proposed. Pet. 18 (citing 45 Fed. Reg.
34,779 (1980)). On the contrary, in response to public
comments on that proposal, EPA adopted a regulation
that gives the decisionmaker wide discretion in selecting
appropriate techniques on which to base a source attri-
bution finding. See 45 Fed. Reg. 80,094 (1980).
Nor is there merit to petitioners’ claim (Pet. 18) that
KPA’s methodology in attributing visibility impairment
to Navajo is inconsistent with the methods used in de-
clining to consider the imposition of control measures
for the protection of other class I areas. The Park rep-
resents the only instance to date in which EPA has re-
quired emission reductions at an existing source to
remedy attributable impairment. Nevertheless, EPA
12
has relied on a wide range of techniques in deciding not
to require further analysis with respect to other class I
areas. See, e.g., 53 Fed. Reg. 35,956, 35,957-35,959 (1988)
(time lapse photography and modeling for Voyageurs Na-
tional Park, Minnesota; emissions inventory analysis
and photographic data for Saguaro Wilderness, Arizona;
modeling analysis predicting potential impacts at the
Roosevelt Campobello International Park near New
Brunswick, Canada). Here, a potential problem affecting
the Park was initially uncovered by photographic data.
Docket A-89-02, II-D-8 at 2. When EPA undertook a
more detailed and thorough source-attribution analysis,
its decisionmaking involved consideration of a complete
set of monitoring data and detailed analyses of those
data. Those procedures were in no sense “inconsistent”
with those employed in declining to proceed with further
analysis of visibility impairment in other class I areas.°
Finally, there is no merit to petitioners’ contention
(Pet. 12-21) that the decision below “contradicts the de-
cisions reached” in Vermont v. Thomas, supra, and
Maine v. Thomas, 874 F.2d 883 (1st Cir. 1989). In the
Vermont case, the Second Circuit upheld EPA’s refusal
to take action on a proposal by the State of Vermont that
was designed to address regional haze in the Lye Brook
Wilderness Area. Vermont v. Thomas, 850 F.2d at 101.
The court did not interpret EPA’s Phase I regulations,
except to indicate that they did not on their face autho-
rize regional haze measures such as those proposed by
the State of Vermont. 850 F.2d at 103-104. That case
therefore simply stands for the unremarkable proposi-
tion that regional haze is not within the scope of EPA’s
6 Petitioners’ final argument—that the challenged regulations
amount to a procedurally invalid revision of the 1980 regulations
designed to address regional haze, Pet. 19-21—lacks merit because
it is premised entirely upon the erroneous supposition that EPA
acted beyond its Phase I authority in regulating haze in the Park.
|
13
Phase I regulations. The Maine case is even farther
afield. In that case, the First Circuit affirmed a district
court’s decision that it lacked jurisdiction under Section
304 of the CAA, 42 U.S.C. 7604, to compel EPA to issue
regional haze regulations. Maine v. Thomas, 874 F.2d at
885. The court did not address the scope of EPA’s au-
thority to regulate visibility under its 1980 regulations.
Neither case casts doubt on the correctness of the con-
clusion reached by the court of appeals in this case.
CONCLUSION >
The petition for writ of certiorari should be denied.
Respectfully submitted.
DREW S. DAys, III
Solicitor General
MYLES E. FLINT
Acting Assistant Attorney General
SCOTT A. SCHACHTER
Attorney
GERALD YAMADA
Acting General Counsel
ALAN ECKERT
Associate General Counsel
VICKIE PATTON
Attorney
Environmental Protection Agency
AUGUST 1993
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.