# Amicus Brief — American Petroleum Institute v. Gorsuch

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URL: https://www.frixlaw.com/law-library/documents/brief%3Amicro_IA40385008_0819%3A3

## Record

- **Collection:** Supreme Court brief
- **Document type:** Amicus Brief
- **Published:** January 1, 1982
- **Citation:** 455 U.S. 1034

## Text

Office - Supreme Court, U.S.
FILED
6g 10
No. 81-1019 FEB 20 Wee
ALBMANDER L. STEVAS,
** * CLERK zx
IN THE

SUPREME COURT OF THE UNITED STATES
OCTOBER TERM, 1981.

CITY OF HOUSTON, TEXAS,
Petitioner
Vv.

ANNE M. GORSUCH, ADMINISTRATOR,
AND
ENVIRONMENTAL PROTECTION AGENCY,

Respondents,
* * *

BRIEF OF THE STATE OF TEXAS
AS AMICUS CURIAE

MARK WHITE
Attorney General of Texas

JOHN W. FAINTER, JR.
First Assistant
Attorney General

RICHARD E. GRAY, III
Executive Assistant
Attorney General

TIM BROWN
Chief, Environmental Protection
Division

P.O. Box 12548
Austin, Texas 78711
(512) 475-4143

TABLE OF CONTENTS

PAGE
INTEREST OF THE STATE OF TEXAS ................ ne
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I. The Agency and the Court of Appeals
Erroneously Retused to Consider
Whether the Ozone Standard Will Be
Attainable in the Houston Area.................... 2
II. The Agency's Regulations Impose
Specific Control Strategies on the States,
Contrary to the Provisions of the Clean
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TABLE OF AUTHORITIES
CASES

Alabama Power Co. v. Costle, 636 F2d 323
et cmeee ees

Lead Industries Association v. EPA, 647 F2d
1130 (D.C. Cir.), cert. denied, 449 U.S.
ee

Natural Resources Defense Council v. EPA,
656 F2d 768 (D.C. Cir.1981)................

Train v. Natural Resources Defense Council,

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Union Electric Co. v. EPA, 427 U.S. 246 (1976). .
STATUTES
Clean Air Act

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$110, 42 U.S.C. §7410 ...................

§172, 42 U.S.C. §7472 ..............0..0...

REGULATIONS

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LEGISLATIVE MATERIALS

S. Rep. No. 91-1196, 91st Cong., lst Sess.
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PAGE

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position. The Act makes no provision for substantial
compliance; the sanctions provided in the Act (such as
the ban on construction of new stationary sources re-
quired by Section 110(a)(2I), 42 U.S.C. §7410
(a(2)(1) are triggered by noncompliance with the
NAAQS as set by the EPA. Conceding the EPA's good
faith in setting the standards, the exclusion of all
evidence on attainability blinds the Agency to a crucial
consideration in its decision-making. There is nothing
in the Clean Air Act to suggest that the EPA may ig-
nore information on a point that would have such an im-
pact on the states.

Thus the decision of the Court of Appeals confuses
relations between the states and the EPA under the Act,
and raises a conflict between impossible standards and
strict compliance requirements. This conflict has been
highlighted in earlier opinions by the District of Colum-
bia Circuit. In Natural Resources Defense Council v.
EPA, 656 F.2d 768, 785 (D.C. Cir. 1981), the Court of
Appeals appeared to base its approval of water quality
monitoring regulations on assurances that they would
be enforced with flexibility and discretion. And in
Alabama Power Co. v. Costle, 636 F.2d 323, 372 (D.C.
Cir. 1979), the Court of Appeals purported to find an ex-
cuse from compliance where ‘good faith effort’’ had
failed.’ These opinions suggest that the D.C. Circuit has
recognized and attempted to mitigate the harshness of
technology forcing requirements, even where mere dif-
ficulty, and not impossibility, was involved. However,
these assurances conflict with the Clean Air Act's clear

2. “Of course even a congressional mandate, such as a
technology-forcing requirement based on a congressional pro-
jection of technology for the future, is subject to a justified ex-
cuse from compliance where good faith effort to comply has
not been fruitful of results. That is far different from the ex-
emption created by EPA on the basis of current technological
infeasibility."’ 636 F.2d at 372

-6-

requirement of full compliance with the pollution
standards. The decision below opens the door to a
literally impossible standard, increasing the burden on
the states, with no reliable prospect that enforcement of
the ozone standard will be relaxed. While enforcement
of the standard is not before the Court, the case at bar
represents the inital departure from the statutory
scheme, which will cause far greater problems in the
future.

The question which remains unanswered is whether
the EPA can set unattainable standards, as the Court of
Appeals decision in the present case states that it can,
and then insist upon strict compliance, as the Clean Air
Act intends that it will. The Court of Appeals has ruled
that the EPA need not even hear evidence that a given
standard may be impossible to attain. This will remove
the technology forcing rationale that is a key to the Act,
give the EPA undue power over the State Implementa-
tion Plans, and expose the states to the statutory sanc-
tions without hope of compliance. The decision below
presents an important question of federal law, one that
is central to the workings of the Clean Air Act. The out-
come of this case will have national impact upon
federal/state relationships, upon the public health, and
upon the economy, as the costs of compliance
mount. This Court should grant certiorari in order to
consider and clarify these questions.

II. The Agency’s Regulations Impose Specific
Control Strategies on the States, Contrary to
the Provisions of the Clean Air Act.

The Court of Appeals has approved EPA regulations
which require, as a specific strategy for the attainment
of the ozone standard, control of hydrocarbon emissions
to levels set in accordance with one of four types of
models. 40 C.F.R. §51.14(c)(7). This approval is at odds
with the role given to the states by the Clean Air Act,
and with the fundamental purpose of the Act.

-7-

Section 110 of the Clean Air Act gives the states
primary responsibility in developing the State Im-
plementation Plan. Clean Air Act, Section 110, 42
U.S.C. §7410. As long as the requirements of §110(a)(2)
are met, the choice of particular control strategies lies
with the states. This Court recognized the relative roles
of the states and the EPA in Train v. Natural Resources
Defense Council, 421 U.S. 60 (1975), wherein it is stated:

The Act gives the Agency no authority to ques-
tion the wisdom of a State’s choices of emission
limitations if they are part of a plan which
satisfies the standards of §110(a)(2), and the
Agency may devise and promulgate a specific
plan of its own only if a State fails to submit an
implementation plan which satisfies those stan-
dards. §110(c). Thus, so long as the ultimate
effect of a State’s choice of emission limitations
is compliance with the national standards for
ambient air, the State is at liberty to adopt
whatever mix of emission limitations it deems
best suited to its particular situation.

421 U.S. at 79.

The effect of this statutory scheme is to give the states
meaningful discretion in designing their plans, and
preclude the Agency from requiring particular means of
control.

This discretion is in accord with the purposes of the
Clean Air Act and the concepts of federalism built into
it. Section 101 of the Clean Air Act reflects the Con-
gressional intent that prevention and control of air
pollution at its source be the primary responsibility of
state and 'ocal governments, and that the appropriate
federal role consists of leadership and financial
assistance. Clean Air Act, Section 101(a){3), (4); 42
U.S.C. §7401(a)(3), (4). Accordingly, the major purposes

-R-

of the Act include provision for national research ef-
forts, and technical and financial assistance to the
states. Clean Air Act, Section 101(b)(2), (3); 42 U.S.C.
§7401(b)(2), (3). The control strategy requirements
associated with the ozone standard reflect a complete
departure from this framework both in terms of the
state/federal relationship and in terms of EPA's obliga-
tion to provide adequate technical assistance.

The regulations at issue require that the control
strategy include an assessment of the amount of
hydrocarbon reduction necessary to attain the ozone
standard. 40 C.F.R. §51.14(c)(7). This requirement,
seemingly related only to the form of information to be
submitted, will in practice limit the discretion of the
states in developing a control strategy. The actual ef-
fect will be to discourage the use of control methods
other than hydrocarbon control, and to limit the means
by which the problem is studied.

The regulations focus on hydrocarbon reductions
alone as the key bit of information by which the Plan
will be evaluated. While the states are technically free
to pursue other means, the emphasis on hydrocarbons in
the regulations will inevitably encourage the states to
adopt this ‘‘approved”’ strategy, and direct efforts away
from possible alternatives. The evidence submitted by
the City of Houston suggests that control of hydrocar-
bons alone will not be an effective means of controlling
ozone levels, and the City has argued that control of ox-
ides of nitrogen (*‘NOx’’) may be a crucial part of an ef-
fective stategy.’ The regulations place a redundant
burden on the State and City to control hydrocarbons in

3. It remains questionable whether attainment of the 0.12 stan-
dard will be possible with any strategy. But it remains impor-
tant to search for the most helpful methods, to bring about the
most improvement possible in air quality. That search is for
the states to direct.

-9-

addition to taking such other means as they might find
helpful. Under the Act it is the State’s prerogative to
choose the mix of control methods. The EPA has in-
truded on that prerogative by requiring a showing of
hydrocarbon reductions.

The second effect of the requirement is to limit the
means by which the problem can be evaluated. The
regulations specify four models, one of which must be
used to estimate the need for hydrocarbon reductions.
40 C.F.R. §51.14(c)(7). This requirement discourages the
states from making an independent study by mandating
the use of limited time and resources on the required
studies. To argue that the states are free to undertake
such additional studies as they may desire again places
a redundant burden on the states, with no prospect of
corresponding benefits. If state discretion under the
Act is to mean anything, the states must be free to
evaluate the problems and policy choices in whatever
way they find appropriate, as a first step to the
autonomous development of the State Implementation
Plan. If these evaluations and plans can be shown to
meet the requirements of the Act, the EPA has no alter-
native but to approve. The regulations in question go
beyond that role, thus exceeding the authority given to
the Agency by Congress and violating the concepts of
federalism built into the Clean Air Act.

The State of Texas further believes that the Court of
Appeals’ approach regarding this issue is at odds with
its own reasoning in the case of Alabama Power v. Cos-
tle, supra. There, the court sustained guideline regula-
tions regarding diffusion modeling requirements for per-
mit applications under the PSD program, qualifying its
decision as follows:

But though we today sustain EPA’s model-
ing regulations, a final observation is in

-10-

order. Of great importance is a reasoned agen-
cy response to substantial questions of fact,
policy or science raised in comments on recom-
mended models or in proposals to employ new
techniques . . .. Modeling, the agency tells us, is
on ‘the frontiers of scientific knowledge,’ but
the lack of scientific certitude about modeling
techniques increases rather than reduces the
need for the agency to critically examine all
substantial questions of fact and science emerg-
ing from the commenting process. EPA's
guideline warns that all proposed deviations
from the endorsed models must be fully sup-
ported, but this language should not be overem-
phasized, for the models presently specified in
the guidelines are concededly flawed.

636 F.2d at 387-388.

In a footnote, the court then stated:

We would associate ourselves with the observa-
tion that ‘decisions which are not arbitrary and
capricious in the light of existing knowledge
may beccme so by the dint of scientific ad-
vances. By its use of estimations and sparce
data, the EPA creates a continuing respon-
sibility to develop, review and apply updated
and more sophisticated information.”’ Texas v.
EPA, 499 F.2d 289, 301 n.16. (5th Cir. 1974).
636 F.2d 388, n.116.

That concern was prompted by technical uncertainty
similar to that now at issue. Texas believes that the
continued focus on hydrocarbon control alone through
the use of four totally vague alternative models falls far
short of EPA’s “responsibility to develop . . . and apply
updated and more sophisticated information,’’ and
renders the present requirement arbitrary and
capricious.

e§$-
CONCLUSION

For the foregoing reasons, the State of Texas believes
that this case presents important issues for review and
clarification by this Court, and that the petition for writ
of certiorari by the City of Houston should be granted.

Respectfully submitted,

MARK WHITE
Attorney General of Texas

JOHN W. FAINTER, JR.
First Assistant
Attorney General

RICHARD E. GRAY, III
Executive Assistant
Attorney General

TIMOTHY L. BROWN

Assistant Attorney General

Chief, Environmental
Protection Division

P.O. Box 12548
Austin, Texas 78711
(512) 475-4143

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Source: Frix Law Library, https://www.frixlaw.com/law-library/documents/brief%3Amicro_IA40385008_0819%3A3. Public record. Not legal advice.
