Amicus Curiae Brief — Atlantic Richfield Company, Petitioner v. Gregory A. Christian, et al.

Supreme Court briefMay 31, 2018

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No. 17-1498

IN THE

Supreme Court of the United States

————

ATLANTIC RICHFIELD COMPANY,

Petitioner,

v.

GREGORY A. CHRISTIAN, ET AL.,

Respondents.

————

On Petition for Writ of Certiorari

to the Supreme Court of Montana

————

BRIEF OF AMICI CURIAE CHAMBER OF COMMERCE

OF THE UNITED STATES OF AMERICA, NATIONAL

ASSOCIATION OF MANUFACTURERS, AMERICAN

FUEL & PETROCHEMICAL MANUFACTURERS, NATIONAL MINING ASSOCIATION, AMERICAN PETROLEUM INSTITUTE, AND SUPERFUND SETTLEMENTS

PROJECT SUPPORTING PETITIONER

STEVEN P. LEHOTSKY

MICHAEL B. SCHON

U.S. CHAMBER LITIGATION

CENTER

1615 H St., NW

Washington, D.C. 20062

(202) 659-6000

————

Counsel for Amicus Curiae Chamber of

Commerce of the United States of

America

(additional counsel listed on inside

cover)

AARON M. STREETT

Counsel of Record

J. MARK LITTLE

BAKER BOTTS L.L.P.

910 Louisiana St.

Houston, TX 77002

(713) 229-1234

aaron.streett@bakerbotts.com

MARTHA S. THOMSEN

BAKER BOTTS L.L.P.

The Warner

1299 Pennsylvania Ave., NW

Washington, D.C. 20004-2400

(202) 639-7700

Counsel for Amici Curiae Chamber of

Commerce of the United States of America,

National Association of Manufacturers,

American Fuel & Petrochemical Manufacturers, National Mining Association,

American Petroleum Institute, and Superfund Settlements Project

WILSON-EPES PRINTING CO., INC. – (202) 789-0096 – WASHINGTON, D.C. 20002

STACY R. LINDEN

MATTHEW A. HAYNIE

AMERICAN PETROLEUM INSTITUTE

1220 L St. NW

Washington, D.C. 20005

(202) 828-8000

Counsel for Amicus Curiae American

Petroleum Institute

PETER C. TOLSDORF

LELAND P. FROST

MANUFACTURERS’ CENTER FOR LEGAL

ACTION

733 10 Street, N.W., Suite 700

Washington, D.C. 20001

(202) 637-3000

Counsel for Amicus Curiae the National

Association of Manufacturers

i

QUESTIONS PRESENTED

1. Whether a common-law claim for restoration seeking

cleanup remedies that conflict with EPA-ordered remedies is a “challenge” to EPA’s cleanup jurisdictionally

barred by § 113 of CERCLA.

2. Whether a landowner at a Superfund site is a “potentially responsible party” that must seek EPA’s approval

under CERCLA § 122(e)(6) before engaging in remedial

action, even if EPA has never ordered the landowner to

pay for a cleanup.

3. Whether CERCLA preempts state common-law

claims for restoration that seek cleanup remedies that

conflict with EPA-ordered remedies.

ii

TABLE OF CONTENTS

Questions Presented ..................................................

Interest of Amici Curiae ...........................................

Summary of Argument ..............................................

Argument ....................................................................

I. The Montana Supreme Court’s Decision

Frustrates CERCLA’s Goals And Imperils Superfund Cleanups ..................................

A. CERCLA seeks to promote effective and expeditious cleanups by

mandating a regimented remedyselection procedure and prohibiting

challenges to EPA’s remedial decisions .........................................................

B. The Montana Supreme Court’s decision conflicts with CERCLA’s prohibition against challenging EPA’s

remedial decisions ..................................

C. The decision below frustrates the

achievement of CERCLA’s goals ........

II. CERCLA’S Robust Public Outreach

Mechanisms Provide The Proper Means

For Influencing EPA’s Superfund Decisions .................................................................

Conclusion ...................................................................

Page

i

1

3

6

6

6

11

15

22

26

iii

TABLE OF AUTHORITIES

Page

CASES

Broward Gardens Tenants Ass’n v. EPA,

311 F.3d 1066 (11th Cir. 2002) .............................. 10

Burlington N. & Santa Fe Ry. Co. v.

United States,

556 U.S. 599 (2009) ................................................... 6

Clinton Cty. Comm’rs v. EPA,

116 F.3d 1018 (3d Cir. 1997).................................... 9

Gen. Elec. Co. v. Jackson,

610 F.3d 110 (D.C. Cir. 2010) ................................ 21

Key Tronic Corp. v. United States,

511 U.S. 809 (1994) ............................................... 3, 4

McClellan Ecological Seepage Situation

v. Perry,

47 F.3d 325 (9th Cir. 1995) ................................ 9, 10

Razore v. Tulalip Tribes of Wash.,

66 F.3d 236 (9th Cir. 1995) .................................... 10

United States v. Cannons Eng’g Corp.,

899 F.2d 79 (1st Cir. 1990) .................................... 19

United States v. P.H. Glatfelter Co.,

768 F.3d 662 (7th Cir. 2014) .................................... 9

STATUTES

42 U.S.C. § 9604 ...................................................... 7, 21

42 U.S.C. § 9606 ............................................................ 9

42 U.S.C. § 9607 ...................................................... 4, 90

42 U.S.C. § 9613 .................... 4, 9, 10, 11, 15, 18, 19, 20

42 U.S.C. § 9617 .......................................................... 22

42 U.S.C. § 9621 ............................................................ 7

iv

TABLE OF AUTHORITIES—Continued

Page

REGULATORY AUTHORITIES

40 C.F.R. Part 300, Subpart I ................................... 23

40 C.F.R. § 300.420 ....................................................... 6

40 C.F.R. § 300.425 ..................................................... 23

40 C.F.R. § 300.430 ............................... 7, 12, 13, 23, 24

40 C.F.R. § 300.435 ..................................................... 24

National Oil and Hazardous Substances

Pollution Contingency Plan Preamble,

55 Fed. Reg. 8666 (Mar. 8, 1990) .......................... 21

OTHER AUTHORITIES

131 Cong. Rec. 24725 (1985) ...................................... 19

H.R. Rep. No. 99-253 (1985), reprinted in

1986 U.S.C.C.A.N. 2835......................................... 19

EPA and Montana Department of

Environmental Quality, Record of

Decision Amendment, Anaconda

Regional Water, Waste, and Soils

Operable Unit (Sept. 2011) ....................... 11, 12, 25

EPA, Community Advisory Groups:

Partners in Decisions at Hazardous

Waste Sites, Case Studies (Winter

1996) ........................................................................ 25

EPA, Grasse River Superfund Site

Cleanup Decision Announced (April

2013). ....................................................................... 16

EPA, Grasse River Superfund Site

Community Involvement Plan for

Remedial Design and Remedial Action

(Aug. 2014) ........................................................ 24, 25

v

TABLE OF AUTHORITIES—Continued

Page

EPA, Guidance on EPA Oversight of

Remedial Designs and Remedial

Actions Performed by Potentially

Responsible Parties (Interim Final),

(April 1990) ............................................................... 7

EPA, Record of Decision, Portland

Harbor Superfund Site, Portland,

Oregon (Jan. 2017) ........................................... 15, 16

EPA, Summary of Technical

Impracticability Waivers at National

Priorities List Sites (Aug. 2012) ............... 12, 17, 18

EPA, Superfund Program Proposed Plan,

BF Goodrich Superfund Site, Calvert

City, Marshall County, Kentucky (Nov.

30, 2017) .................................................................... 9

Gelber, U.S. Department of Justice,

Memorandum Defining “Matters

Addressed” in CERCLA Settlements

(Mar. 4, 1997) .......................................................... 18

Woolford, Office of Superfund

Remediation and Technology

Innovation, Clarification of the

Consultation Process for Evaluating

the Technical Impracticability of

Groundwater Restoration at CERCLA

Sites, OLEM Directive 9200.3-117

(Dec. 28, 2016) ........................................................ 13

IN THE

Supreme Court of the United States

————

NO. 17-1498

————

ATLANTIC RICHFIELD COMPANY,

Petitioner,

v.

GREGORY A. CHRISTIAN, et al.,

Respondents.

————

On Petition for a Writ of Certiorari

to the Supreme Court of Montana

————

BRIEF OF AMICI CURIAE CHAMBER OF

COMMERCE OF THE UNITED STATES OF

AMERICA, NATIONAL ASSOCIATION OF

MANUFACTURERS, AMERICAN FUEL &

PETROCHEMICAL MANUFACTURERS,

NATIONAL MINING ASSOCIATION, AMERICAN

PETROLEUM INSTITUTE, AND SUPERFUND

SETTLEMENTS PROJECT SUPPORTING

PETITIONER

————

INTEREST OF AMICI CURIAE1

Amici are six national trade associations. Their

members include many businesses that are involved in

Pursuant to Rule 37.2(a), amici provided timely notice of their

intention to file this brief to counsel for all parties. Petitioner’s

counsel of record and respondents’ counsel of record consented to

the filing of this brief. In accordance with this Court’s Rule 37.6, no

counsel for any party has authored this brief in whole or in part, and

no person or entity, other than amici, their members, or their

counsel, have made a monetary contribution to the preparation or

submission of this brief.

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the cleanup of Superfund sites across the country and,

accordingly, have a direct interest in the outcome of this

case. Amici all have strong interests in reversing the

decision below and preserving the U.S. Environmental

Protection Agency’s (EPA) authority under the

Comprehensive

Environmental

Response,

Compensation, and Liability Act (CERCLA) to

comprehensively, efficiently, and with finality address

remediation issues at Superfund sites.

The Chamber of Commerce of the United States (the

Chamber) is the world’s largest business federation. It

represents 300,000 members and indirectly represents

the interests of more than three million companies and

professional organizations of every size, in every industry

sector, and from every region of the country. A vital

function of the Chamber is to represent the interests of

its members in matters before this Court. The Chamber

regularly files amicus curiae briefs in cases such as this

one that raise issues of concern to the Nation’s business

community.

The National Association of Manufacturers (NAM) is

the largest manufacturing association in the United

States, representing small and large manufacturers in

every industrial sector and in all 50 states.

Manufacturing employs more than 12 million men and

women, contributes $2.25 trillion to the U.S. economy

annually, has the largest economic impact of any major

sector, and accounts for more than three-quarters of all

private-sector research and development in the nation.

The NAM is the voice of the manufacturing community

and the leading advocate for a policy agenda that helps

manufacturers compete in the global economy and create

jobs across the United States.

The National Mining Association (NMA) is a national

trade association whose members include the producers

of most of America’s coal, metals, and industrial and

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agricultural minerals; the manufacturers of mining and

mineral-processing machinery, equipment, and supplies;

and engineering and consulting firms, financial

institutions, and other firms serving the mining industry.

NMA often participates in litigation raising issues of

concern to the mining community.

American Fuel & Petrochemical Manufacturers

(AFPM) is a national trade association whose members

comprise virtually all refining and petrochemical

manufacturing capacity in the United States. AFPM’s

members supply consumers with a wide variety of

products that are used daily in homes and businesses.

Among its other missions, AFPM engages in legal

advocacy on issues important to its members.

The American Petroleum Institute (API) is a national

trade association representing more than 625 companies

involved in all aspects of the oil-and-natural-gas industry.

API frequently advocates for the interests of its

members by participating as an amicus curiae in cases

that are important to the oil-and-natural-gas community.

The Superfund Settlements Project (SSP) is an

association of major companies from many different

sectors of American industry. It was organized in 1986 in

order to help improve the effectiveness of the Superfund

program by encouraging settlements, streamlining the

settlement process, and reducing transaction costs for all

concerned. SSP provides constructive input to EPA,

other federal agencies, and Congress on critical policy

issues affecting the cleanup of contaminated sites and

engages in legal advocacy in the CERCLA arena.

SUMMARY OF ARGUMENT

“As its name implies, CERCLA is a comprehensive

statute that grants the President broad power to

command government agencies and private parties to

clean up hazardous waste sites.” Key Tronic Corp. v.

4

United States, 511 U.S. 809, 814 (1994). CERCLA aims

to place a premium on efficient cleanup, which often can

be achieved only through settlement with private parties.

The statute delegates decision making about the type and

degree of cleanup to EPA, with significant opportunity

for public input, while limiting any party’s ability to

challenge those decisions. See 42 U.S.C. § 9613(h).

Meanwhile, any “responsible parties” can be held jointly

and severally liable for cleanup costs, regardless of their

degree of responsibility. Id. § 9607. For some sites, those

costs can stretch into the billions of dollars.

For all of its imperfections, this system provides a

silver lining for those facing liability—relative certainty.

CERCLA cleanups and settlements can set fixed

liabilities, which ensures a stable environment for

businesses, shareholders, insurers, creditors, and others

to make decisions about future investments. Indeed, the

statute creates heavy incentives for early settlement

among potentially responsible parties and EPA.2 Those

incentives would be meaningless without a degree of

certainty regarding the ultimate financial exposure (i.e.,

cleanup costs) and a relatively “hard target” for parties

negotiating among themselves to fund the cleanup.

In the decision below, the Montana Supreme Court

created a new CERCLA regime in which EPA’s

generally binding remediation decisions are viewed as

mere suggestions, with any jury having the power to

order other remediation efforts—even ones that EPA

specifically considered and rejected. That approach

destroys the stability CERCLA promises to the business

community and imperils EPA’s ability to achieve

CERCLA’s central purpose—the prompt cleanup, based

For example, § 9613(f)(2) shields those who resolve liability to the

United States or a state from contribution claims by others. And

§ 9607(c)(3) exposes uncooperative parties to treble damages.

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on sound science, of the Nation’s thousands of

contaminated Superfund sites.

The result will be chaos in Montana’s many Superfund

sites, with EPA pursuing one remediation course and

various ad hoc private lawsuits mandating different,

potentially dangerous or conflicting remediation work.

Worse yet, the business community—which bears the

remediation costs—now faces unlimited liability, for the

decision below stripped EPA of the power to enter into

settlements to fix remediation obligations. Under the

decision below, businesses have a reduced incentive to

cooperate with EPA by entering into settlements, thus

further prolonging what Congress intended to be an

efficient and definitive cleanup process. All of that flies

in the face of CERCLA’s core aim of promoting

expeditious and effective remediation of Superfund sites

for the protection of human health and the environment.

Beyond the clear errors in statutory interpretation,

the decision below cannot be defended on public-policy

grounds. CERCLA and its accompanying regulations

offer myriad opportunities for public involvement in the

Superfund process.

Those avenues ensure that

interested parties can make their voices heard. But EPA

has the final say under CERCLA—or at least it did until

now. The Montana Supreme Court has created a

blueprint for making precisely the type of challenge

Congress, in CERCLA, sought to prevent: any interested

party who fails to obtain its desired remediation plan

from EPA is now free to pursue its preferred plan in

collateral litigation. That renders CERCLA’s robust

public-participation provisions redundant and frustrates

its most central goals.

This Court’s review is needed to ensure the proper

functioning of CERCLA, end the Superfund chaos that

now reigns in Montana, and prevent the spread of this

disruptive regime to other jurisdictions.

6

ARGUMENT

I. THE MONTANA SUPREME COURT’S DECISION

FRUSTRATES CERCLA’S GOALS AND IMPERILS

SUPERFUND CLEANUPS

One of CERCLA’s primary goals is to promote

“timely cleanup of hazardous waste sites.” Burlington N.

& Santa Fe Ry. Co. v. United States, 556 U.S. 599, 602

(2009). Two important and necessary tools to achieve

that goal are EPA’s exclusive decision-making authority

and CERCLA’s emphasis on settlements as a means to

effectuate cleanup. By interfering with EPA’s powers

under CERCLA, the Montana Supreme Court’s decision

frustrates EPA’s efforts to achieve that primary goal

and, indeed, undermines the entire statutory and

regulatory program of Superfund cleanups.

A. CERCLA seeks to promote effective and

expeditious cleanups by mandating a

regimented remedy-selection procedure and

prohibiting challenges to EPA’s remedial

decisions

CERCLA (1) mandates that EPA follow a regimented

remedy-selection process and (2) bars any collateral

challenges to EPA’s remedial decisions pursuant to that

process. It is through the combination of those two

features that CERCLA acts as a powerful force for the

effective and expeditious cleanup of Superfund sites.

1. CERCLA and its accompanying regulations

establish a strict path for EPA to follow when selecting a

remedy to clean up a Superfund site. Required steps

include: (1) conducting a remedial preliminary

assessment, 40 C.F.R. § 300.420(b); (2) undertaking a

remedial site inspection, id. § 300.420(c); (3) conducting a

remedial investigation that collects “data necessary to

adequately characterize the site for purposes of

developing

and

evaluating

effective

remedial

7

alternatives,” id. § 300.430(d); (4) drafting a feasibility

study that evaluates and provides a detailed analysis of

“appropriate remedial alternatives,” id. § 300.430(e); (5)

presenting to the public a proposed plan detailing the

preferred remedial alternative, id. § 300.430(f)(2); (6)

soliciting comment from the public on the proposed plan,

id. § 300.430(f)(3); (7) reassessing EPA’s “initial

determination” regarding its preferred alternative and

factoring in any new information and community

comments before making a final remedy-selection

decision, id. § 300.430(f)(4); and (8) documenting EPA’s

final remedy-selection decision through the issuance of a

record of decision, id. § 300.430(f)(5).3

The following depiction that EPA recently provided in

connection with a different Superfund site visually

illustrates the myriad steps involved in this detailed,

orderly process from site selection to completion of

remediation:

Once selected, the remedial action will be conducted either by EPA

or by a responsible party with substantial EPA oversight. 42 U.S.C.

§ 9604(a)(1); see also EPA, Guidance on EPA Oversight of Remedial

Designs and Remedial Actions Performed by Potentially

Responsible Parties (Interim Final), EPA/540/G-90/001, OSWER

9355.5-01(April 1990), https://semspub.epa.gov/work/11/174047.pdf.

For any remedy where hazardous substances remain on site above

levels that permit unrestricted use and unlimited exposure, EPA, in

addition, must conduct a review of the remedy no less often than

every five years after initiation of the remedial action to assure that

the remedy remains protective of human health and the environment

and, if does not, initiate action to make it so. 42 U.S.C. § 9621(c); see

also 40 C.F.R. § 300.430(f)(4)(ii).

3

8

9

EPA, Superfund Program Proposed Plan, BF Goodrich

Superfund Site, Calvert City, Marshall County,

Kentucky, at 2 (Nov. 30, 2017).4

2. Navigating through this comprehensive process

can, and does, take years or even decades. Recognizing

the need to prevent collateral attacks from shortcircuiting EPA’s deliberate progression through these

steps, “Congress enacted [42 U.S.C.] § 9613(h) to prevent

judicial interference, however well-intentioned, from

hindering EPA’s efforts to promptly remediate sites that

present significant danger to public health and the

environment.” Clinton Cty. Comm’rs v. EPA, 116 F.3d

1018, 1023 (3d Cir. 1997); see also McClellan Ecological

Seepage Situation v. Perry, 47 F.3d 325, 329 (9th Cir.

1995) (Section 9613(h) “protects the execution of a

CERCLA plan during its pendency from lawsuits that

might interfere with the expeditious cleanup effort.”)

(emphasis omitted). That provision bars “any challenges

to * * * remedial action” outside of certain defined

circumstances not implicated here.5 42 U.S.C. § 9613(h);

see also Pet. 24 (explaining that § 9613(b)’s grant of

https://semspub.epa.gov/work/04/11095220.pdf.

For instance, if EPA initiates suit to recover response costs or

enforce a cleanup order, CERCLA permits the defendant potentially

responsible parties to challenge the cleanup plan as “arbitrary and

capricious or otherwise not in accordance with law.” 42 U.S.C.

§§ 9613 (j)(2), (h)(1), (h)(2); see, e.g., United States v. P.H. Glatfelter

Co., 768 F.3d 662, 668 (7th Cir. 2014). It should be noted, however,

that allowable suits challenging remedy selection before

implementation are infrequent. For EPA to bring a suit to enforce a

cleanup order, for instance, it must first issue a unilateral

administrative order under CERCLA Section 106 and the potentially

responsible party must refuse to comply. Since such refusal risks

daily penalties and treble damages, 42 U.S.C. §§ 9606(b)(1),

9607(c)(3), suits by EPA to enforce these orders are typically

unnecessary.

4

5

10

exclusive jurisdiction to federal courts over “all

controversies arising under” CERCLA “[e]xcept as

provided in subsections (a) and (h)” deprives state courts

of jurisdiction over challenges barred under § 9613(h) as

well); Pet. App. 67a n.2 (U.S. amicus brief) (“[S]tate

courts, like federal courts, lack subject matter

jurisdiction to decide claims like the landowners’

restoration damages claim.”).

Courts have taken a commonsense approach to

determining when a lawsuit constitutes a “challenge” that

would interfere with EPA’s implementation of its

selected remedial plan. The term “challenge” naturally

encompasses lawsuits directly seeking a change or

alteration in EPA’s cleanup plan, but it also includes

other suits that are “related to the goals of a cleanup.”

Razore v. Tulalip Tribes of Wash., 66 F.3d 236, 239 (9th

Cir. 1995). Accordingly, courts have barred suits that

seek to impose additional reporting and permitting

requirements on an ongoing CERCLA cleanup because,

even though such requirements might not directly

change the substance of the work, “such relief would

constitute the kind of interference with the cleanup plan

that Congress sought to avoid or delay by the enactment

of Section [9613(h)].” McClellan Ecological Seepage

Situation, 47. F.3d at 330. The same goes for claims for

injunctive relief that seek to implement “stricter

standards in the remedial plan.” Broward Gardens

Tenants Ass’n v. EPA, 311 F.3d 1066, 1070, 1073 (11th

Cir. 2002). The guiding principle in these decisions is

that if EPA could have ordered certain measures, but

“chose not to do so,” Section 9613(h) bars any challenge

to that choice. See id. at 1073 (“Asserting that a remedial

plan is inadequate because it fails to include a measure

that [EPA] could have included is challenging the plan

for section [9613(h)] purposes.”).

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B. The Montana Supreme Court’s decision

conflicts with CERCLA’s prohibition against

challenging EPA’s remedial decisions

In the decision below, the Montana Supreme Court

opened a gaping hole in Section 9613(h)’s prohibition

against “challenge[s]” to EPA’s remedy-selection

decisions. Contrary to uniform federal law, it held that a

private lawsuit does not constitute a “challenge” to

EPA’s remedy selection unless it would “stop, delay, or

change the work EPA is doing.” Pet. App. 11a-12a.

Using that logic, the court permitted local landowners to

proceed with their lawsuit that sought “restoration work

in excess of what the EPA required * * * in its selected

remedy.” Id. at 4a (emphasis added). In other words,

the court found no problem with EPA’s proceeding with

its ARCO-funded remedial plan in parallel to the

landowners’ forcing ARCO to fund their different

preferred remediation plan, provided that “a jury of

twelve Montanans” agree with them. Id. at 13a.

The court was unmoved by the fact that EPA had

considered—and rejected—the restoration work the

landowners were pursuing in their lawsuit. For example,

the landowners sought to “remove the top two feet of soil

from affected properties” and “install permeable walls to

remove arsenic from the groundwater.” Id. at 4a, 72a.

But EPA had already “considered construction of an

underground Permeable Reactive Barrier (PRB), similar

to the barrier proposed by the landowners” and

concluded “that this approach would not necessarily

achieve the human health standard in Willow Creek and

would not eliminate exceedances of arsenic in

downstream receiving waters.” Id. at 63a (United States’

amicus brief below); see also EPA and Montana

Department of Environmental Quality, Record of

Decision Amendment, Anaconda Regional Water, Waste,

12

and Soils Operable Unit, § 6.4.2 (Sept. 2011).6

Additionally, the remedial work the landowners seek

would require “[t]earing up” the protective layer of soil

EPA chose to put in place as part of its selected remedy,

which “could expose the neighborhood to an increased

risk of dust transfer or contaminant ingestion.” Pet.

App. 73a (U.S. amicus brief).7

EPA followed CERCLA’s rigorous decisional

procedures. EPA conducted extensive studies of the

arsenic issue and ultimately concluded that “it was

technically

impracticable

to

reduce

arsenic

concentrations below 10 ppb” in groundwater in one of

the relevant areas of the site and “therefore did not

select below-ground structures to address groundwater

arsenic concentrations.” Id. at 63a (U.S. amicus brief);

Record of Decision Amendment § 6.4.4; see also EPA,

Summary of Technical Impracticability Waivers at

National Priorities List Sites, at A-80 (Aug. 2012).8 EPA

thus issued a technical impracticability waiver related to

groundwater restoration for a portion of the site.

The

technical-impracticability-waiver

process

demands a careful, regimented analysis. “EPA expects

to return usable groundwaters to their beneficial uses

wherever practicable, within a timeframe that is

reasonable given the circumstances of the site.” 40

C.F.R. § 300.430(a)(1)(iii)(F) (emphasis added). But the

governing regulation permits waiving that requirement

https://semspub.epa.gov/work/08/1211311.pdf.

Importantly, those impacts would be from the Superfund site, and

EPA and ARCO would then be required to address those impacts

under CERCLA.

See, e.g., 40 C.F.R. § 300.430(a)(iii)(A) (In

developing remedial plans “EPA expects to use treatment to address

the principal threats posed by a site, wherever practicable.”)

(emphasis added).

8

https://semspub.epa.gov/work/HQ/175391.pdf.

6

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13

when it “is technically impracticable from an engineering

perspective.” Id. § 300.430(f)(1)(ii)(C)(3).

EPA has

expounded on these directives in multiple guidance

documents addressing the technical-impracticabilitywaiver process for groundwater at Superfund sites,

culminating in a 2016 guidance document designed to

compile and clarify all “existing relevant Superfund

policy and guidance” on the subject. Woolford, Office of

Superfund Remediation and Technology Innovation,

Clarification of the Consultation Process for Evaluating

the Technical Impracticability of Groundwater

Restoration at CERCLA Sites, OLEM Directive 9200.3117, at 1 (Dec. 28, 2016).9 It includes a flowchart to

illustrate the intricate workings of the technicalimpracticability-waiver process:

9

https://semspub.epa.gov/work/HQ/198193.pdf.

14

Id. at Attachment 1.

As a result of that thorough, mandatory decisional

process, EPA concluded that a technical impracticability

waiver was warranted for groundwater at a portion of the

site. Yet the Montana Supreme Court has empowered a

15

“jury of twelve Montanans” to overrule EPA on this

point (and any other Superfund remedial decision),

thereby circumventing Section 9613(h)’s bar and opening

the door to all manner of challenges to EPA’s remedial

decisions at Superfund sites. Pet. App. 13a.

C. The decision below frustrates the achievement

of CERCLA’s goals

This weakening of Section 9613(h)’s prohibition on

challenging EPA’s remedial decisions threatens the core

goals of CERCLA. Effective and expeditious cleanup is

impossible if third parties are allowed to second-guess

every EPA remedial decision before a jury. Avoiding the

chaos that would result from such challenges is the entire

point of Section 9613(h)’s bar. Yet for the many

Superfund sites in Montana and perhaps for others

across the country, that chaos will become the norm.

1. The Court need not guess at how the Montana

Supreme Court’s overhaul of CERCLA will play out.

The history of other Superfund projects is fertile ground

for posing counterfactuals regarding what would have

occurred had this new legal regime been in place at other

Superfund sites.

Consider the Portland Harbor Superfund Site in

Oregon and the Grasse River Superfund Site in New

York.

At Portland Harbor, EPA developed and

evaluated nine separate remedial alternatives for

cleaning up contaminated sediments at the bottom of the

harbor. EPA, Record of Decision, Portland Harbor

Superfund Site, Portland, Oregon § 10 (Jan. 2017).10 In

conducting that analysis, EPA concluded that dredging

could be counterproductive in some areas because

disturbing contaminated sediment would risk additional

“potential releases to the environment.” Id. § 10.2.8. For

10

https://semspub.epa.gov/work/10/100036257.pdf.

16

that and other reasons, EPA chose to dredge only a

portion of the site. Id. §§ 10.2.6, 14.

Similarly, at Grasse River, EPA specifically

considered whether it could “return[] the lower Grasse

River to its previous pristine conditions” by dredging all

river sediment areas containing a threshold level of

polychlorinated biphenyls (PCBs). EPA, Grasse River

Superfund Site Cleanup Decision Announced, at 2 (April

2013).11 EPA instead selected a cleanup plan that would

dredge only some areas of contamination, based on the

following three conclusions: (1) dredging all areas of

contamination would not “return the lower Grasse River

to pristine conditions”; (2) the short-term impacts of such

a path forward would be “severe” and require off-site

disposal of 1.5 million cubic yards of dredged sediment,

which carries its own set of risks; and (3) a complete

dredge of the river would take “nearly three times as

long as the selected remedy to achieve PCB interim

target levels in fish.” Ibid.

EPA’s final decisions were given their binding effect

under CERCLA in those instances. But under the

Montana Supreme Court’s decision, those remedial

choices would be reduced to mere suggestions.

Interested parties would be free to hold jury trials over

whether the entire sites should be dredged as

“restoration work in excess of what EPA required.” Pet.

App. 4a. While that remedy would directly contradict

EPA’s remedial decisions and risk further contamination,

it would pass muster under the decision below because it

would not “stop, delay, or change the work EPA is

doing.” Id. at 11a.

The UGI Columbia Gas Plant Superfund Site in

Pennsylvania offers another disturbing window into the

https://www.epa.gov/sites/production/files/2017-03/documents/facts

heet_alcoa_4-2013.pdf.

11

17

future under the Montana Supreme Court’s vision of

CERCLA.

There, EPA issued a technicalimpracticability waiver after finding that complete

restoration of the groundwater at that site was

inappropriate. Summary of Technical Impracticability

Waivers at National Priorities List Sites, at A-45.

Specifically, EPA determined that the remaining

contamination at the site was related to dense nonaqueous phase liquid (DNAPL), which could be removed

only by first mobilizing it and then extracting it. Ibid.

EPA determined that while mobilizing the DNAPL was

possible, there existed no known technologies capable of

extracting it from the complicated fractured bedrock

geologic system.

Ibid.

Moreover, mobilizing the

DNAPL was a risky endeavor because any attempt to do

so “may cause ecological and human health risks, which

currently do not exist in the vicinity of the site and

Susquehanna River.” Ibid. EPA thus made a decision,

based on site-specific conditions, available technology,

and risk considerations, that complete removal of

DNAPL was not warranted. Ibid. But under the

Montana Supreme Court’s approach, private litigants

would be free to convince a jury of their peers that

attempting DNAPL removal—“restoration work in

excess of what the EPA required,” Pet. App. 4a—was in

fact warranted despite the risks and seemingly

insurmountable technical challenges.

The final example in this series is more than

theoretical because it is in Montana and thus governed by

the Montana Supreme Court’s decision. At the Silver

Bow Creek/Butte Area Site, EPA issued a technicalimpracticability waiver because it concluded that the

remedy could not reduce concentrations of arsenic,

cadmium, lead, copper, and sulfate to levels normally

required in a Superfund cleanup. Summary of Technical

18

Impracticability Waivers at National Priorities List

Sites, at A-73. Specifically, EPA reasoned:

A [technical-impracticability waiver] is

required because * * * the extremely large

horizontal and vertical extent of the

contamination problem—the sheer size of

the source, calculated to be 27 billion cubic

yards—would leave an open pit about 62

times larger than the current Berkeley Pit,

would eliminate the historic city of Butte,

and would have untold environmental

consequences.

Ibid.

EPA further considered, and rejected, all

“potentially applicable remediation technologies” to

address the groundwater contamination at that site,

concluding that such an attempt would be ineffective at

best and could “reverse the currently observable trends

of improving bedrock quality” at worst. Ibid. Yet under

the Montana Supreme Court’s ruling, any interested

party remains free to file a lawsuit for restoration

damages to conduct the remedial actions EPA rejected—

despite EPA’s determinations that such remediation

would be infeasible, could do more harm than good, and

would wipe an entire city off the map.

2. Permitting circumvention of Section 9613(h)’s bar

undermines CERCLA in less obvious, but no less

important, ways as well. In order to promote expeditious

remediation of Superfund sites, CERCLA authorizes

EPA to negotiate settlements with responsible parties to

fund or perform investigation and cleanup efforts. 42

U.S.C. § 9613(f)(2); see generally Gelber, U.S.

Department of Justice, Memorandum Defining “Matters

19

Addressed” in CERCLA Settlements, at 4 n.3 (Mar. 14,

1997).12

With that settlement authority, EPA wields the power

to fix a responsible party’s otherwise open-ended liability

at a definite sum in return for cooperation during the

cleanup efforts. 42 U.S.C. § 9613(f)(2). That ability to

bring certainty to a responsible party’s remediation

obligations is a crucial tool for negotiating quick cleanup

of Superfund sites because, as the Government explained

below, “the main incentive for a responsible party to

enter into a CERCLA consent decree with the United

States is to fix the party’s cleanup obligations.” Pet. App.

71a. Indeed, § 9613(f)(2) was added to CERCLA as part

of the 1986 Superfund Amendments and Reauthorization

Act in an effort to induce responsible parties to settle

their liability with the agency overseeing the cleanup so

the settling party would have a “measure of finality.”

United States v. Cannons Eng’g Corp., 899 F.2d 79, 92

(1st Cir. 1990). Incentivizing settlement was intended by

Congress to “encourage quicker, more equitable

settlements, decrease litigation and thus facilitate

cleanups.” H.R. Rep. No. 99-253, at *6 (1985), reprinted

in 1986 U.S.C.C.A.N. 2835, 2840-41; see also 131 Cong.

Rec. 24725, 24730 (1985) (statement of Sen. Domenici)

(“The goal of CERCLA is to achieve effective and

expedited cleanup of as many uncontrolled hazardous

waste facilities as possible. One important component of

the realistic strategy must be the encouragement of

voluntary cleanup actions or funding without having the

President relying on the panoply of administrative and

judicial tools available.”).

These settlements have downstream predictability

effects as well. An EPA settlement with one responsible

https://www.epa.gov/sites/production/files/2013-09/documents/defin

-cersett-mem.pdf.

12

20

party gives the other potentially responsible parties an

idea of what kind of settlement EPA will accept for them.

Additionally, EPA’s reaching settlements with all of the

largest potentially responsible parties often sets the

practical upper limit on all potentially responsible third

parties’ total combined liability. That is because at many

sites EPA focuses its enforcement efforts on a subset of

responsible parties and leaves it to those parties who

settle to bring contribution claims against the nonsettling potentially responsible parties to recover a

portion of the monies paid in settlement. 42 U.S.C.

§ 9613(f)(3)(B).

The settlement mechanism thus can

sometimes set the practical outer bounds of liability for

the non-settling potentially responsible parties too.

The Montana Supreme Court’s decision removes that

incentive for cooperation and the ability of potentially

responsible parties to fix their liability because it strips

EPA of the power to bring certainty and finality to a

potentially responsible party’s remediation obligations.

Instead, private litigants can file lawsuits seeking

additional “restoration work in excess of what the EPA

required” in any settlement agreement. Pet. App. 4a.

Permitting such lawsuits prevents responsible parties

from ever obtaining the final resolution of their liability

that CERCLA empowered EPA to provide.

The

Montana Supreme Court’s decision thus frustrates

21

EPA’s ability to bring parties to the bargaining table and

achieve CERCLA’s goal of a prompt cleanup.13

3. Allowing private lawsuits also distorts the holistic

lens through which Congress required EPA to assess

remediation. Interested parties may want to challenge

cleanup plans because they believe their preferred

approach would be better for them, regardless of the

negative externalities it may inflict on the rest of the

site. But CERCLA charges EPA to identify the solution

that is best for “the public health” and “environment” as

a whole. 42 U.S.C. § 9604(a)(1); National Oil and

Hazardous Substances Pollution Contingency Plan

Preamble, 55 Fed. Reg. 8666, 8695 (Mar. 8, 1990)

(CERCLA remedial actions should “comprehensively

address all threats at a site.”). Allowing a jury to

evaluate third parties’ preferred remedy addresses only

a fraction of the relevant question and, worse, can lead to

a result that is detrimental to the larger community.

CERCLA allows interested parties to make their

individualized interests known through the public-input

process but assigns EPA the task of selecting the optimal

measures for the entire affected population. The decision

below departed from this design by permitting third

parties to elevate their narrow self-interest above that of

the broader public.

In absence of settlement, to obtain cleanup EPA must either

conduct the cleanup itself and then pursue potentially responsible

parties for reimbursement, or try to force the potentially responsible

parties to perform the cleanup through administrative order and/or

court action. See Gen. Elec. Co. v. Jackson, 610 F.3d 110, 114 (D.C.

Cir. 2010) (summarizing EPA’s four options for conducting cleanup

at a Superfund site).

These routes typically take longer,

jeopardizing EPA’s ability to obtain prompt cleanup and straining

Government resources by requiring the Government to pay or

litigate in the first instance.

13

22

II. CERCLA’S

ROBUST

PUBLIC

OUTREACH

MECHANISMS PROVIDE THE PROPER MEANS FOR

INFLUENCING EPA’S SUPERFUND DECISIONS

Reversing the Montana Supreme Court’s decision and

restoring the congressional vision of CERCLA would not

thwart public involvement in EPA’s remedy-selection

process. Far from it. While court challenges to EPA’s

selected remedy would be prohibited, CERCLA provides

many other avenues for interested parties to make their

voices heard. Reversal of the decision below would thus

ensure that—in Montana and elsewhere—interested

parties’ concerns will be channeled into the statutory

mechanisms Congress designed for precisely that

purpose.

A. CERCLA establishes a robust public-participation

framework. Before adopting a remediation plan, EPA

must “[p]ublish a notice and brief analysis of the

proposed plan and make such plan available to the

public.” 42 U.S.C. § 9617(a). EPA then must “[p]rovide a

reasonable opportunity for submission of written and oral

comments and an opportunity for a public meeting at or

near the facility at issue regarding the proposed plan.”

Ibid. Reflecting the importance of this notice-andcomment process, EPA’s “final plan shall be accompanied

by a discussion of any significant changes (and the

reasons for such changes) in the proposed plan and a

response to each of the significant comments, criticisms,

and new data submitted.”

Id. § 9617(b).

Similar

obligations apply after adoption of a final remediation

plan. If EPA’s later actions “differ[] in any significant

respects from the final plan,” then it “shall publish an

explanation of the significant differences and the reasons

such changes were made.”

Id. § 9617(c).

By

implementing a notice-and-comment process and

imposing on EPA a continuing obligation to explain its

rejection of any significant comments, these statutory

23

mandates ensure that the interested parties have a voice

in the remedy-selection process.

CERCLA’s regulations add more public-participation

mandates on top of those statutory requirements,

ensuring that EPA consults with interested parties at

nearly every step in the Superfund process. Before

placing a site on the National Priorities List, EPA must

publish notice in the Federal Register, solicit comments,

and “make available a response to each significant

comment and any significant new data submitted during

the comment period.” 40 C.F.R. § 300.425(d)(5). Then,

before commencing the remedial investigation, EPA

must (1) conduct “interviews with local officials,

community residents, public interest groups, or other

interested or affected parties, as appropriate, to solicit

their

concerns

and

information

needs,”

id.

§ 300.430(c)(2)(i), and (2) prepare a “formal community

relations plan” to “ensure the public appropriate

opportunities for involvement in a wide variety of siterelated decisions, including site analysis and

characterization, alternatives analysis, and selection of

remedy,” id. § 300.430(c)(2)(ii).

Additionally, EPA

maintains an administrative record for each site so that

any person has easy access to relevant studies, data and

information. See generally 40 C.F.R. Part 300, Subpart

I.

The regulations continue to impose publicparticipation obligations after EPA has made an initial

determination regarding the preferred remedy. At that

point, it must “[p]rovide a reasonable opportunity * * *

for submission of written and oral comments on the

proposed plan and the supporting analysis” and hold a

“public meeting * * * at or near the site at issue.” Id. §

300.430(f)(3)(i). Following the comment period on the

proposed plan, EPA must “reassess its initial

determination[,] * * * factoring in any new information or

24

points of view expressed by the * * * community during

the public comment period.”

Id. § 300.430(f)(4)(i).

Indeed, the regulations specifically contemplate that

“comments may prompt [EPA] to modify aspects of the

preferred alternative or decide that another alternative

provides a more appropriate balance.” Ibid. Taking all

of this into account, EPA then must document and justify

its final remedy selection in a publicly available record of

decision. Id. § 300.430(f)(3), (5). Before carrying out the

final plan, EPA must determine whether it is necessary

to revise its community-relations plan to “describe

further public involvement activities.” Id. § 300.435(c)(1).

In sum, there is no shortage of public involvement in

EPA’s Superfund identification and remediation process.

Preventing interested parties from challenging EPA’s

remediation decisions through private lawsuits would

enforce the statutory design, while leaving ample means

of public expression. Indeed, interested parties would

continue to actively participate through the host of

carefully calibrated mechanisms provided by CERCLA

and its regulations, just as Congress intended.

B. Examples of a few EPA community-relations

plans provide a real-world glimpse into the functioning of

CERCLA’s public-participation mechanisms.

At the Grasse River Superfund Site, EPA engaged the

public with fact sheets, flyers, public notices, door-todoor solicitations, school outreach, mail, email, websites,

and social media. EPA, Grasse River Superfund Site

Community Involvement Plan for Remedial Design and

Remedial Action, at 19-23 (Aug. 2014).14 That was in

addition to EPA’s coordination efforts with state and

tribal authorities. Ibid. This aggressive public-outreach

strategy paid dividends, as the Community Advisory

https://www.epa.gov/sites/production/files/2017-03/documents/gras

se-river-cip.pdf.

14

25

Panel “played a valuable role in representing community

viewpoints * * * [and] helped guide and inform the EPA’s

decision-making process at the site.” Id. at 23.

Community involvement at the Colorado School of

Mines Research Institute Superfund Site likewise proved

effective. The public there had a demonstrably direct

impact on the remedial alternatives considered: “By

going to the community up front, EPA was able to screen

out remedial alternatives that the community simply

would not accept prior to spending EPA resources on

analysis of their feasibility.” EPA, Community Advisory

Groups: Partners in Decisions at Hazardous Waste Sites,

Case Studies, at 40 (Winter 1996).15

The record similarly reflects the public-participation

process for the Anaconda Smelter Superfund Site at

issue here. As the Government’s amicus brief below

detailed, EPA has ensured that “[t]he remedy-selection

process continues to respond to public concerns and new

data. For example, EPA significantly amended the

[records of decision] in 2011 and 2013 based on new

information.” Pet. App. 65a. On the September 2011

Record of Decision Amendment alone, EPA received and

responded to comments from Anaconda-Deer Lodge

County, the Clark Fork River Technical Assistance

Committee, the Clark Fork Coalition, the Arrowhead

Foundation, and others. Record of Decision Amendment,

Anaconda Regional Water, Waste, and Soils Operable

Unit, Responsiveness Summary & Appendix A.

C. Respondents were well aware of CERCLA’s

public-participation framework. Indeed, Respondent

Penny Ryan submitted a number of comments to EPA

objecting to various aspects of its remediation plan. Id.

at Responsive Summary § 6.0.C. EPA considered and

responded to her comments. Ibid. Then it rendered its

15

https://semspub.epa.gov/work/HQ/174150.pdf.

26

own expert decision on how to move forward with the

cleanup. The court below erred by allowing collateral

attacks on the outcome of this process.

*

*

*

CERCLA’s text, structure, and purpose cannot

countenance interference through private lawsuits by

interested third parties. Yet that option now bears the

imprimatur of the Montana Supreme Court. Without

this Court’s intervention, that decision will imperil the

remediation efforts at the many Superfund sites in

Montana and potentially others across the country.

CONCLUSION

The petition for a writ of certiorari should be granted.

27

Respectfully submitted.

STEVEN P. LEHOTSKY

MICHAEL B. SCHON

U.S. CHAMBER LITIGATION

CENTER

1615 H St., NW

Washington, D.C. 20062

(202) 659-6000

Counsel for Amicus Curiae

Chamber of Commerce of

the United States of

America

AARON M. STREETT

Counsel of Record

J. MARK LITTLE

BAKER BOTTS L.L.P.

910 Louisiana St.

Houston, TX 77002

(713) 229-1234

aaron.streett@bakerbotts.com

MARTHA S. THOMSEN

BAKER BOTTS L.L.P.

The Warner

1299 Pennsylvania Ave.,

STACY R. LINDEN

NW

MATTHEW A. HAYNIE

Washington, D.C. 20004AMERICAN PETROLEUM

2400

INSTITUTE

(202) 639-7700

1220 L St. NW

Washington, D.C. 20005

Counsel for Amici Curiae

(202) 828-8000

Chamber of Commerce of

United States of

Counsel for Amicus Curiae the

America,

National

American Petroleum

Association

of

Institute

Manufacturers, American

Fuel & Petrochemical

PETER C. TOLSDORF

Manufacturers, National

LELAND P. FROST

Mining Association,

MANUFACTURERS’

American Petroleum

CENTER FOR LEGAL

Institute, and Superfund

ACTION

Settlements Project

733 10 STREET, N.W.,

SUITE 700

WASHINGTON, D.C. 20001

(202) 637-3000

Counsel for Amicus Curiae

the National Association

of Manufacturers

May 2018

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.

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