# Opposition Brief — Hoechst Celanese Corp. v. United States

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## Record

- **Collection:** Supreme Court brief
- **Document type:** Opposition Brief
- **Published:** January 1, 1998
- **Citation:** 524 U.S. 952

## Text

teeiias
Supreme Court, U.S. |
a ee a

e MAY 26 1998

No. 97-1578 : ERK

In the Supreme Court of the Giuted States

OCTOBER TERM, 1997

HOECHST CELANESE CORPORATION, PETITIONER

UNITED STATES OF AMERICA

ON PETITION FOR A WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE FOURTH CIRCUIT

BRIEF FOR THE UNITED STATES IN OPPOSITION

SETH P. WAXMAN
Solicitor General
Counsel of Record
LoIs J. SCHIFFER
Assistant Attorney General
JOHN A. BRYSON
DAVID C. SHILTON
Attorneys
Department of Justice
Washington, D.C. 20530-0001

(202) 514-2217

QUESTIONS PRESENTED

Pursuant to Section 112 of the Clean Air Act, 42
U.S.C. 7412, the Environmental Protection Agency
(EPA) promulgated requirements for preventing
leaks of benzene from equipment, but exempted equip-
ment at plants “designed to produce or use less than
1,000 megagrams of benzene per year.” 40 C.F.R.
61.110(c)(2). Under EPA’s interpretation of “use,”
which includes all benzene employed in a process in-
cluding recycled benzene, petitioner’s Celriver Plant
is not entitled to the exemption. The court of appeals
held that EPA could seek civil penalties from peti-
tioner for its noncompliance with the regulatory re-
quirements for the period after petitioner received
direct notice of EPA’s regulatory interpretation, and
remanded for a determination of possible penalties.
The questions presented are:

1. Whether the court of appeals properly upheld
EPA’s interpretation of “use.”

2. Whether the court of appeals properly held that
petitioner was not entitled to a two-year waiver of the
requirements after the company received notice of
EPA’s regulatory interpretation.

(I)

TABLE OF CONTENTS

Page
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TABLE OF AUTHORITIES
Cases:
Arkansas v. Oklahoma, 503 U.S. 91 (1992) ............ 11
Auer v. Robbins, 117 S. Ct. 905 (1997) .................... 11
Bowles v. Seminole Rock & Sand Co., 325 U.S. 410
| ONSET ERS RE eR ar oe EES ERC RT TRE TOR ORO 10
Pauley v. BethEnergy Mines, Inc., 501 U.S. 680
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Thomas Jefferson Univ. v. Shalala, 512 U.S. 504
I aa cde Letine Lbduncncodeupucaks 10
Statutes and regulations:
Clean Air Act, Pub. L. No. 84-159, 69 Stat. 322,
42 U.S.C. 7401 et seq.:
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Clean Air Amendments of 1970, Pub. L. No. 91-604,
84 Stat. 1684-1685:
§ 111(b)(1)(A), 42 U.S.C. 7411(b)(1)(A) (1988)..... 2
§ 112(b)(1), 42 U.S.C. 7412(b)(1) (1988) 2.0.00... 2
§ 112(b)(1)(B)-(C), 42 U.S.C. 7412(b)(1)(B)-(C)
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§ 112(c)(1)(B)Gi), 42 U.S.C. 7412(¢)(1)(B)(ii)
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(IIT)

IV

Statutes and regulations—Continued:

Clean Air Act Amendments of 1977, Pub. L. No.
95-95, § 112(e), 91 Stat. 703, 42 U.S.C. 7412(e)
Ss RRR Nae aper eS Sty et sein Carus SRST Ch HES Ry MEE ee
Health Services Research, Health Statistics, and
Health Care Technology Act of 1978, Pub. L. No.
95-6238, § 112(e)(5), 92 Stat. 3458, 42 U.S.C. 7412(e)(5)
I se ae
40 C.F.R. 919:
Subpt. A (Sections 61.01-61.19):

CP a i
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Subpt. J (Sections 61.110-61.112):
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PORES Tan MIND nchcktni cissavcsdivicapaaacenciensiarcabcaberbds
Subpt. V (Sections 61.240-61.247) .............ccccccseesesees

Miscellaneous:

42 Fed. Reg. 29,332-29,333 (1977) ........ccscccccseccsscesesess
49 Fed. Reg. (1984):
Sh SORTA Sabihdsnvins Giistasuniasadibininiioddss axtaleinichamaaennil
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Black’s Law Dictionary (6th ed. 1990) ................0008

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In the Supreme Court of the Gnited States

OCTOBER TERM, 1997

No. 97-1578
HOECHST CELANESE CORPORATION, PETITIONER

v.

UNITED STATES OF AMERICA

ON PETITION FOR A WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE FOURTH CIRCUIT

BRIEF FOR THE UNITED STATES IN OPPOSITION

OPINIONS BELOW

The opinion of the court of appeals (Pet. App. la-
33a) is reported at 128 F.3d 216. The opinion of the
district court (Pet. App. 34a-72a) is reported at 964 F.
Supp. 967.

JURISDICTION

The judgment of the court of appeals was entered on
October 27, 1997. A petition for rehearing was denied
on December 23, 1997 (Pet. App. 74a-75a). The peti-
tion for a writ of certiorari was filed on March 23,
1998. The jurisdiction of this Court is invoked under
28 U.S.C. 1254(1).

STATEMENT

1, The Clean Air Act (Act) authorizes the Envi-
ronmental Protection Agency (EPA) to identify haz-
ardous air pollutants and their sources, and to prom-

(1)

RRL a ee ee vn ee

ulgate emission controls for those sources.' Prior to
1990, Section 112(b)(1)(B) and (C) of the Act (42 U.S.C.
7412(b)(1)(B) & (C) (1988)) instructed EPA to set Na-
tional Emission Standards for Hazardous Air Pollut-
ants (NESHAPs) “at the level which in [the Admin-
istrator’s] judgment provides an ample margin of
safety to protect the public health from such haz-
ardous air pollutant,” and specified that such stan-
dards “shall become effective upon promulgation.”
Pet. App. 78a.

EPA listed benzene as a hazardous air pollutant in
1977, based on evidence that benzene is a human
carcinogen. 42 Fed. Reg. 29,332-29,333. EPA promul-
gated the final NESHAP for benzene equipment leaks
on June 6, 1984. 49 Fed. Reg. 23,479 (Pet. App. 85a).
The Benzene Leaks NESHAP applies to specified
equipment, such as pumps, valves, and flanges (40
C.F.R. 61.110(a)), and requires regular monitoring
and maintenance of leaking equipment, installation of
equipment designed to reduce emissions, record
keeping and reporting (40 C.F.R. 61.112(a), 61.240-
61.247 (Subpt. V)). Violators of the regulations are
subject to civil penalties pursuant to Section 113(b) of
the Act (42 U.S.C. 7413(b)).

The dispute in this case concerns 40 C.F.R.
61.110(c)(2), which provides that “equipment in ben-
zene service that is located at a plant site designed to
produce or use less than 1,000 megagrams of ben-

1 Clean Air Amendments of 1970, Pub. L. No. 91-604, §§
111(b)(1)(A), 112(b)), 84 Stat. 1684-1685; Clean Air Act
Amendments of 1977, Pub. L. No. 95-95, § 112(e), 91 Stat. 703;
Health Services Research, Health Statistics, and Health Care
Technology Act of 1978, Pub. L. No. 95-623, § 112(e)(5), 92 Stat.
3458 (currently codified at 42 U.S.C. 7411-7412). Section 112
before the 1990 amendments is reproduced at Pet. App. 77a.

zene per year is exempt from the requirements of
§ 61.112.” Pet. App. 124a.° Thus, an exempted plant
does not have to follow the equipment and monitoring
requirements imposed by Section 61.112 and Subpart
V, though other requirements, such as reporting, re-
main applicable. 40 C.F.R. 61.10(a), 61.110(¢)(1). EPA
explained this exemption in a section of the preamble
to the final rule entitled “[iJmpacts on smal] plants.”
49 Fed. Reg. 23,510 (1984); Pet. App. 112a. The ex-
emption reflected EPA’s conclusion that the benefits
achievable by regulating small volume users such as
“research facilities, pilot plants, and intermittent
users of benzene” did not justify the costs of compli-
ance. Id. at 113a. The preamble referenced a “Back-
ground Information Document” which found that a
plant with a design production capacity of about 1000
megagrams per year would typically contain around
87 pieces of equipment in benzene service and would
be expected to emit only about six megagrams of
benzene per year. Jd. at 8a-9a. Applying the proposed
regulations to such a small plant would result in a
reduction of only four megagrams per year, which
was not considered cost effective. Jd. at 9a. The rule
became effective June 6, 1984. Jd. at 85a.

2. This case concerns the Celriver plant owned by
petitioner Hoechst Celanese Corporation in Rock
Hill, South Carolina. During the period at issue, Cel-
river used benzene to cool hot ketene gases and to
help separate water and other compounds from acetic
anhydride and acetic acid; after each use, the benzene
was cooled, purified and reused in these processes.
Pet. App. 4a-5a. Because petitioner never applied for
an exemption for Celriver or filed reports as to its

2 A megagram equals about 2200 pounds. Pet. App. 4a n.1.

ee

benzene usage, EPA did not become aware until 1989
that this plant was not complying with the ben-
zene leak regulations and was emitting substantial
amounts of fugitive benzene. Jd. at 5a. While Celriver
had nearly 17,000 individual sources of benzene leaks
and was one of the largest sources of fugitive benzene
emissions in the nation at that time (id. at Qa),
petitioner claimed that it believed the plant was
exempt because it “consum[ed]” less than 1,000 mega-
grams of benzene yearly. Jd. at 5a.

EPA issued a notice of violation for Celriver on
February 20, 1990. In April 1990, petitioner submitted
a plan to bring Celriver into compliance with the
regulations (Pet. App. 21a), and eventually achieved
compliance in August 1992. Jd. at 26a.

3. The United States brought this action in July
1992, seeking civil penalties against petitioner for the
period between 1984 and 1992 when Celriver was not
in compliance with the regulations. The parties filed
motions for summary judgment on the issue of liabil-
ity. The district court sustained EPA’s interpreta-
tion that “use” for purposes of the exemption provi-
sion included the total amount of benzene utilized or
employed in a process, including recycled benzene.
Pet. App. 38a-52a. However, the district court found
that EPA did not provide petitioner with fair notice of
this interpretation, even after EPA’s Region 4, which
has jurisdiction over Célriver, informed petitioner by
letter dated June 13, 1989, that when benzene is recy-
cled, “‘use’ for purposes of the exemption must be cal-
culated on the basis ‘of total cumulative flow through
the process rather than net benzene consumption or
usage.’” Jd. at 20a. Region 4 reiterated this position
in August 1989, in a letter that set out an example of
how petitioner should calculate the amount of benzene

ae See mM MR or Senna ARN NT eM TEEN ro PP

“useld]” for purposes of the exemption (id. at 21a), and
in September 1989 petitioner carried out the re-
quested calculation and determined that its annual
use of benzene far exceeded the threshold for the ex-
emption. Jbid. The district court nevertheless con-
cluded that petitioner still did not receive fair notice
because petitioner allegedly had a “legitimate basis
for believing” that the letters from Region 4 did not
“speak[]| for the Administrator” of EPA. Jd. at 68a.
The district court also concluded that petitioner
should not be liable for penalties because EPA did not
object to a compliance plan submitted by petitioner in
1990 and because petitioner purportedly would have
been entitled to a two-year waiver if it had applied for
such a waiver. Jd. at 69a-70a.

On cross-appeals, the court of appeals first upheld
the district court’s ruling that EPA’s interpretation
of the exemption provision was entitled to deference.
The court found that EPA’s interpretation is in
accord with the ordinary meaning of the word “use,”
and consistent with both the overall purposes of the
statute and the stated purpose of the provision to
exempt only small plants from the leak detection and
repair requirements. Pet App. 7a-10a. The court of
appeals upheld the district court’s ruling that peti-
tioner did not have fair notice of EPA’s interpretation
for the period before the 1989 letters to petitioner
from Region 4. Critical in this regard was the fact
that the Texas Air Control Board, which had been
delegated authority to administer the NESHAP pro-
gram in that State, applied the exemption provision to
petitioner’s plants in Texas in a manner that could
have led petitioner to believe that petitioner’s inter-
pretation was accurate. Jd. at 16a-18a.

6

“he court of appeals reversed the district court’s
holding that the 1989 letters from Region 4 regarding
Celriver did not provide adequate notice of how EPA
interpreted the exemption. The majority found that
Region 4’s letters provided petitioner with direct
notice of EPA’s interpretation, and cited minutes of a
meeting of senior Celriver officials showing that they
understood EPA’s interpretation. Pet. App. 20a-21a.
The majority found that the regulations required
compliance within 90 days, unless EPA issued a
discretionary waiver, and rejected petitioner’s argu-
ment that it should presume that a waiver would have
been granted if it had been sought. Jd. at 26a. The
court ruled that petitioner’s efforts in achieving
compliance, while not relevant to liability, could be
considered in determining “if, and in what amount,
penalties should be imposed for the post-August 1989
violations of [petitioner’s] Celriver plant.” Jd. at 25a,
27a.’ Petitioner’s petition for rehearing and sugges-
tion for rehearing en banc was denied on December
23,1997. Id. at 74a-75a.

ARGUMENT

The court of appeals’ decision is correct and does
not conflict with any decision of this Court or with
any decision of another court of appeals. Accordingly,
further review is not warranted.

1. Petitioner first argues (Pet. 9-18) that the court
of appeals misapplied this Court’s decisions on the
proper scope of deference to agency interpretations of

* Judge Niemeyer, dissenting from the judgment insofar as
it found that petitioner could be liable for penalties after
August 1989, found that Region 4’s letters did not “constitute a
definitive agency-wide EPA notice such that penalties could be
imposed” (Pet. App. 33a).

7

their own regulations. Alternatively, petitioner sug-
gests (Pet. 22-23) that this Court should “abandon the
‘deference’ principle and direct the reviewing court to
determine the single correct meaning of the [regu-
lation].” Neither claim has merit.

a. Petitioner’s first argument is based on a misin-
terpretation of the decision below. The court of ap-
peals did not defer to EPA’s interpretation of the
exemption provision “as a matter of course” (Pet. 10),
or on the sole basis that the interpretation was “not
‘nonsensical’” (Pet. 9, quoting Pet. App. 8a). The
court analyzed the language and purpose of the regu-
latory provision and the statute, and concluded that
EPA’s interpretation in this case is consistent with
both. The court found EPA’s interpretation of “use”
to be “consistent with the ordinary meaning” of that
term, that is “to make use of, to employ” (Pet. App. 7a,
quoting Black’s Law Dictionary 1541 (6th ed. 1990)).
The court found that “EPA’s interpretation of its own
regulatory exemption harmonizes with the purpose of
the authorizing statute,” which is to achieve “the
maximum degree in reduction in emissions of the
hazardous air pollutants” subject to the Clean Air
Act (Pet. App. 8a, quoting 42 U.S.C. 7412(d)(2)). The
court then found that “EPA’s interpretation of its
exemption accords with the purpose of the exemption
itself” which was to exclude only small plants from
the leak-prevention requirements (Pet. App. 8a-9a).
Petitioner thus errs in arguing (Pet. i, 8, 9-13, 23)
that the sole test the court of appeals applied was
whether the agency’s interpretation was not
“nonsensical.” The court used that phrase in the
course of explaining why EPA’s interpretation har-
monized with the statute. Pet. App. 8a. But the main
thrust of the decision below is that “EPA’s inter-

ES ee a CR RL Te een Ee
8

pretation accords with the plain language of the
NESHAP, as well as the purposes of the Clean Air
Act and of the exemption itself.” Jd. at 10a. Peti-
tioner’s warning (Pet. 22) that “the prospect that
EPA should be able to read a rule any way EPA
pleases so long as that reading is not ‘nonsensical’
should ring alarm bells in the judiciary,” is, accord-
ingly, a false alarm.*

Arguing against a straw man, petitioner fails to
come to grips with the actual reasoning of the court
below. Petitioner instead urges (Pet. 15) that “it is
not appropriate for federal courts to defer to agency
interpretations that defy the very language of a

* Amici American Automobile Manufacturers Ass’n, et al.
similarly misread the majority opinion as concluding that an
agency regional office can establish a binding interpretation of
a regulation “notwithstanding that other regions have adopted
contrary interpretations.” Br. 6. In fact, the majority did not
accept petitioner’s allegations that Region 4’s interpretation
was contrary to that of other EPA regional offices. It simply
noted that petitioner had presented no evidence that it knew of
or relied on any “asserted contrary interpretation of ‘use’ by
other EPA offices or state agencies.” Pet. App. 23a (emphasis
added). While petitioner claimed that EPA Region 6 had ap-
proved an interpretation contrary to that of Region 4, the
evidence consisted, at most, only of acquiescence by Region 6 in
the Texas Air Control Board’s largely unexplained grant of
exemptions to two plants. Jd. at 56a-57a. That acquiescence
hardly amounted to a contrary interpretation. In any event, it
was Region 4’s interpretation that followed the consistent |
guidance provided by EPA headquarters that “use” meant
“processing rates rather than net consumption.” Jd. at 1la-12a
(quoting October 5, 1984 EPA letter). Contrary to amici’s
claim (Br. 10), Region 4’s interpretation was “authoritative”
because it was clearly explained and consistent with the rule-
making itself and with EPA headquarters’ interpretations
thereof. Pet. App. 7a-12a.

9

published rule,” ignoring the ruling below that EPA’s
interpretation is in fact consistent with the plain
language of the regulation. Pet. App. 7a. Petitioner
nowhere explains why the phrase “designed to* * *
use” (id. at 124a, quoting 40 C.F.R. 61.110(c)(2)) must
mean only “designed to consume” and cannot, as the
court of appeals found, mean designed to “utiliz[e]” or
“employ[].” Jd. at lla. Nor does petitioner suggest
how limiting “use” to “consumption” can be recon-
ciled with the statute, since that interpretation would
allow plants that are designed to re-use benzene to
escape regulation, even though (as was the case with
the Celriver Plant) they represent some of the
largest sources of benzene leaks. See id. at 5a.
Petitioner similarly fails to deal with the court of
appeals’ analysis of the preamble to the regulation and
the rulemaking record, which showed that the
exemption was intended to apply to a “small plant”
(id. at 8a, quoting 49 Fed. Reg. 23,510 (1984)) which
emits about six megagrams of fugitive benzene per
year, not a huge plant like Celriver with annual
emissions reaching 226 megagrams per year. /d. at 9a.
As the court’s analysis of the preamble and rule-
making record indicates, petitioner’s charge (Pet. 14)
that “agency staffers change[d] their minds about
what they wish[{ed] the law to be” is incorrect; the
exemption was never intended to limit “use” to “con-
sumption” so as to exempt a facility like Celriver.’ In

® Similarly, since an interpretation that counts all benzene
utilized in a process, including recycled benzene, as “used” is
consistent with the language and purpose of the rule, there was
no need for a new rulemaking, and (contrary to petitioner’s
submission at Pet. 17 & n.16) no inconsistency with the
directive of Section 301(a) of the Clean Air Act, 42 U.S.C.

re

10

sum, the decision below rests not on an unthinking
deference to any agency construction that is not non-
sensical, but on a careful and considered application of
this Court’s oft-stated rule that an agency’s inter-
pretation of its own regulations should be sustained
unless “plainly erroneous or inconsistent” with the
regulation. Thomas Jefferson Univ. v. Shalala, 512
U.S. 504, 512 (1994); see also Bowles v. Seminole Rock
& Sand Co., 325 U.S. 410, 414 (1945).

b. Petitioner seeks to overturn decades of this
Court’s rulings on deference by urging that “defer-
ence is not appropriate where an agency’s post-
promulgation interpretation of a regulation is con-
cerned,” and that courts should determine which is
the “single correct” or “best” interpretation of a
regulation without deferring to the interpretation of
the agency. Pet. 22-23. However, this Court has

7601(a); Pet. App. 84a, that the Administrator may delegate his
powers and duties “except the making of regulations.”

Petitioner’s complaints of a “secret interpretation” of the
regulations (Pet. i), and of interpretations that “were pre-
sented, for the first time, in the government’s briefs” (Pet. 17
n.15), were also properly rejected by the court of appeals. The
court pointed to numerous instances where sources contacted
EPA regarding their eligibility for an exemption and were
explicitly informed that “the 1,000 megagrams per year cut off
limit is applicable to total processing rates, rather than net
consumption (usage) or net production.” Pet. App. lla-
12a (quoting EPA responses to letters from companies). Thus,
the interpretation was hardly “secret.” Moreover, petitioner
found out only a few months after the regulations had been
promulgated that EPA had rejected the use-equals-consump-
tion interpretation in responding to an inquiry from a Texaco
facility. Jd. at 16a. Indeed, petitioner no longer disputes that
it received direct notice of this interpretation in the summer of
1989. See Pet. 25-26.

11

recently reaffirmed the doctrine of deference to
agency interpretations of regulations, Auer v. Rob-
bins, 117 S.Ct. 905, 911 (1997), and has consistently
rejected attempts by courts to substitute their own
view of the “best” interpretation of agency regu-
lations. E.g., Arkansas v. Oklahoma, 503 U.S. 91, 112
(1992).

This Court has explained that deference is particu-
larly warranted when a regulation concerns “a com-
plex and highly technical regulatory program,” in
which applications of the regulation “necessarily re-
quire significant expertise and entail the exercise of
judgment grounded in policy concerns.” Pauley v.
BethEnergy Mines, Inc., 501 U.S. 680, 697 (1991).
That is precisely the situation here, where determin-
ing the appropriate scope of an exemption to leak-
prevention rules applicable to a great variety of manu-
facturing operations requires significant technical
expertise joined with an appreciation of the statutory
policy. See Pet. App. 39a (“A court’s review of regu-
lations under Section 112 of the Clean Air Act * * *
is particularly limited because of the broad discretion
Congress gave EPA to control hazardous air pollut-
ants. * * * This court treads lightly when constru-
ing the scope of an exemption that allows a source of
hazardous air pollutants to go unregulated.”). Peti-
tioner provides no convincing reason for the radical
departure it advocates from existing precedent—a
departure that would encourage litigation and prolong
uncertainty concerning the meaning of regulations.

2. Petitioner does not take issue with the court of
appeals’ rulings that the company received actual
notice of EPA’s interpretation of the exemption in the
summer of 1989 (Pet. App. 24a), and that the Celriver
Plant continued to violate the regulations at least

SEee ea eee ee
12

until August 1992. Jd. at 26a. Instead, petitioner
maintains (Pet. 25-26) that the court of appeals should
not have remanded for a determination of possible
penalties because the company allegedly was entitled
to a waiver of the leak-prevention requirements for
two years after receiving EPA’s letters in the sum-
mer of 1989.

Petitioner does not suggest that the court of ap-
peals’ rejection of its waiver theory conflicts with any
decision of this Court or any lower court. Moreover,
the ruling below (Pet. App. 26a) is plainly correct.
Contrary to petitioner’s assumption (Pet. 25), a
waiver would not have been automatic. Section 112(c)
(1)(B)@i) of the Act (42 U.S.C. 7412(c)(1)(B)Gi) (1988)),
provided that “the Administrator may grant a waiver
permitting such source a period of up to two years
after the effective date of a standard to comply,” but
only “if he finds that such period is necessary for the
installation of controls and that steps will be taken
during the period of the waiver to assure that the
health of persons will be protected from imminent
endangerment.” Pet. App. 78a-79a (emphasis added).*
Petitioner’s argument (Pet. 25 n. 21) that EPA “must
grant a waiver when a source makes a showing that
satisfies the statutory test,” overlooks the dis-
cretionary language of the provision.

In any event, petitioner has made no showing that
the requirements for a waiver were met for Celriver.

° EPA’s implementing regulations provide that “the Admin-
istrator may grant a waiver of compliance with a standard for
a period not exceeding 2 years” and set out in detail the re-
quirements for a waiver application, including a description of
controls, compliance schedules, and interim emission control
steps to be taken during the waiver period. 40 C.F.R. 61.11.

13

Petitioner suggests (Pet. 25 n. 21) that since its
Pampa, Texas, facility was granted a waiver by the
Texas Air Control Board in 1985, the Celriver Plant
would have qualified for one as well. However, peti-
tioner does not explain why the public health and
technological feasibility criteria that govern waivers
would apply in exactly the same way at two different
plants in different States during different time peri-
ods. Had EPA been presented with a waiver applica-
tion for the South Carolina plant, it would not have
been bound by the waiver determination made by the
Texas agency.

In sum, petitioner has failed to show any error in
the court of appeals’ holding that it was not required
to assume that petitioner was entitled to a two-year
waiver of the benzene leak requirements after it
received actual notice of EPA’s interpretation of the
exemption provision.

CONCLUSION

The petition for a writ of certiorari should be
denied.

Respectfully submitted.

SETH P. WAXMAN
Solicitor General
LOIS J. SCHIFFER
Assistant Attorney General

JOHN A. BRYSON
DAVID C. SHILTON
Attorneys

MAY 1998

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Source: Frix Law Library, https://www.frixlaw.com/law-library/documents/brief%3Amicro_IA40386006_1292%3A03. Public record. Not legal advice.
