Amicus Curiae Brief — Fidelity Exploration & Production Co. v. Northern Plains Resource Council, Inc.
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FILED
(Lj) | SEP 18 2003
OFFICE OF THE CLERK
No. 03-257
IN THE
Supreme Court of the United States
FIDELITY EXPLORATION AND PRODUCTION COMPANY,
Petitioner,
v.
NORTHERN PLAINS RESOURCE COUNCIL, INC.,
Respondent.
On PETITION FOR A WRIT OF CERTIORARI TO THE
UNITED STATES CourT OF APPEALS
FOR THE NINTH CIRCUIT
BRIEF OF AMICUS CURIAE
NORTHERN CHEYENNE TRIBE
IN SUPPORT OF RESPONDENT
JOHN B. ARUM
Counsel of Record
STEVEN H. CHESTNUT
ZIONTZ, CHESTNUT, VARNELL
BERLEY & SLONIM
2101 Fourth Avenue
Suite 1230
Seattle, WA 98121-2331
(206) 448-1230
Attorneys for Amicus Curiae
183062 g
COUNSEL PRESS
(800) 274-3321 + (800) 359-6859
t
—
» i
TABLE OF CONTENTS
Page
Table of Cited Authorities ................2505- li
Interests of the Amicus Curiae ...............5. l
Statutory Provisions Involved ................. 2
SUMtOMNOT OT TIS CORE ww. cic cc esc eens cose +
_ A. The Threat to Water Quality Posed by the
| Coal Bed Methane Industry. ............. 4
B. Proceedings Below. ..... 0... .ccssvscess 5
Reasons for Denying the Petition ............... 6
I. Water Discharged As A Result Of Natural Gas
Production Is A “Pollutant” Under The Plain
Language Of The Clean Water Act. ....... 7
A. Fidelity’s Discharge is “Industrial Waste.”
LTPULS em O eee eis Ua SRN CO os 7
B. Water Derived in Association with
the Production of Natural Gas is a
“Pollutant” under the Clean Water Act.
Ped eNee a eed oan ex eee es 10
I]. This Case Does Not Turn On The Outcome
PCC Te Pee TTT eee eT eee 16
III. Practical Considerations Do Not Support
Issuance Of A Writ Of Certiorari. ......... 18
ee ee et ee ee 20
il
TABLE OF CITED AUTHORITIES
Page
Cases:
Andrus v. Glover Constr. Co., 446 U.S. 608 (1980)
Seatac eee en eens 5 6 a tenna 11
BP Exploration & Oil v. United States Envtl.
Protection Agency, 66 F.3d 784 (6th Cir. 1995)
MPOUEREUee TT 12
Catskill Mountains Chapter of Trout Unlimited v.
City of New York, 273 F.2d 481 (2d Cir. 2002) .. 16, 17
Dubois v. United States Dept of Agric., 102 F.3d
1273 (1st Cir. 1996), cert. denied, 521 U.S. 1119
(1997) . . .. <6 06 0s eo 16, 17
Miccosukee Tribe of Indians v. South Florida Water
Management Dist., 280 F.3d 1364 (11th Cir. 2002)
ees e nsec ee see 5 6 en inne 7, 16, 17, 18
Montana Envt'l Info. Center v. Montana Dept of
Envtl. Quality, 296 Mont. 207, 988 P.2d 1236
G4.) MI 10
National Wildlife Fed'’n v. Consumers Power Co.,
862 F.2d 580 (6th Cir. 1988) ........ era 8, 16, 17
National Wildlife Fed’n v. Gorsuch, 693 F.3d 156
(D.C. Cir. 1908) .. .. 2. 6c due ee 8, 16, 17
iil
Cited Authorities
Page
Okanogan Highlands Alliance v. Williams, 236 F.3d
468 (9th Cir. 2000) ......-- eee e reer etree: 10
Sierra Club v. Cedar Point Oil, 73 F.3d 546 (5th Cir.),
cert. denied, 519 U.S. 811 (1996) .. 5, 6, 8, Hi, 12, $5
Southern Colorado C.U.R.E. v.Evergreen Operating
Corp., No. 98-WM-1518 (D. Colo. 1999) ...... 19
State Water Resources Department v. City of Klamath
Falls, 68 Or. App. 148, 682 P.2d 779 (1984) ... 10
Swartz v. Beach, 229 F. Supp. 2d 1239 (D. Wyo.
aad wa Wad Rene Keen ees teres 19
TRW Inc. v. Andrews, 534 U.S. 19 (2001) ...----- 11
United States v. Hamel, 551 F.2d 107 (6th Cir 1977)
(QUES oo eee eee 8
United States v. Standard Oil Co., 384 U.S. 224
ESE ied 9
Village of Oconomowoc v. Dayton Hudson Corp.,
24 F.3d 962 (7th Cir.), cert. denied, 513 U.S. 930
Uap aes e sien ansreseoedekaedres es 9
iv
Cited Authorities
Page
Statutes:
Pub. L. 102-374, 106 Stat. 1186 (Sept. 30, 1992) .. 1
ENA Saat 8 Serene er rrr ner ey Pr nr 8
gk Oe Ye reer te meee 2
Pe es © ERE vet oka Re eee aes
pie tee os | eee ey Pre re er rire 2
Pe es OEE - ccc iekee ctee seed passim
gtk 5 oe Bg: re a ne errr rrr 9
OP Ws REED os 6. sce 6s been eeeee ines 9
PP Rae EOE 6. 64x 40K vs tanew eee moans 6
Ce Bok a Be rer rrr rr a err 2
Regulations:
ee FM Ge rr rrr ner Pree 9
ee a ee rr er ee Te 12
Op Ge POE ov kph dv eles cosets 12
Vv
Cited Authorities
Page
Other:
55 Fed. Reg. 40,235 (Oct. 2, TOGO. cvcevaurneives 19
66 Fed. Reg. 46,455 (Sept. 5, yer 19
A Legislative History of the Water Pollution Control
Act Amendments of 1972 (Envtl. Pol. Div., Cong.
Research Serv. 1973) .....----eeee eres yaw dy br ho
H.R. Rep. No. 92-911 (1972) ....-- +++ s eee eeees 14
S. Rep. No. 92-414 (1971) «0... - +e seers 8, 13
Supreme Court Rule 37.2(a) ..-...---++++++05: 1
W.H. Rodgers, Environmental Law: Air and Water
§ 4.9 (West Publishing 1986) .........---++->. 8,9
l
INTERESTS OF THE AMICUS CURIAE
This brief is filed by amicus curiae Northern Cheyenne
Tribe (the “Tribe”) in opposition to the Petition for Certiorari
filed by Fidelity Exploration and Production Company
(“Fidelity”). The Tribe participated as amicus curiae below, and
files this brief pursuant to Supreme Court Rule 37.2(a)'.
The Tribe has a direct interest in the case because Fidelity and
other natural gas producers operating upstream of the Northern
Cheyenne Reservation discharge waste water associated with
coal bed methane production into the Tongue River, the mid-
channel of which forms the eastern boundary of the
Reservation.” /d. The Tribe holds reserved water rights to the
Tongue River which were recognized in a Tribal-State compact
ratified by Congress on September 30, 1992. Pub. L. 102-374,
106 Stat. 1186. Tribal members, as well as many off-Reservation
farmers and ranchers, depend on the Tongue River to irrigate
their farms and pastures.
This case concerns whether natural gas producers may
discharge salty waste water generated in association with the
production of natural gas from coal beds (coal bed methane or
‘““CBM”) into the Tongue River of southeastern Montana without
a National Pollutant Discharge Elimination System (“NPDES”)
permit issued by the State of Montana under the federal Clean
Water Act. The answer to this question does not turn on the
outcome of South Florida Water Management District v.
1. The parties have consented to the filing of this brief. Their letters
of consent are on file with the Clerk of the Court. This brief has been
authored in its entirety by undersigned counsel for the amicus curiae.
No person or entity, other than the named amicus and their counsel,
made any monetary contribution to the preparation and submission of
this brief.
2. The Northern Cheyenne Tribe has approximately 8,000 members
and occupies a Reservation comprising approximately 445,000 acres of
land in southeastern Montana. About 90 percent of the Reservation’s
population is Northern Cheyenne and all but one percent of the land is
held in trust by the United States for the Tribe and its members.
2
Miccosukee Tribe of Indians, No. 02-626, a case the Court will
hear in its October 2003 term. Rather, it turns on whether CBM
waste water falls under the plain language of the Clean Water
Act’s definition of the term “pollutant.” 33 U.S.C. § 1362(6).
The Ninth Circuit held that Fidelity’s discharge falls under the
Act’s definition because (1) it is an “industrial waste,” and
(2) it is “produced water” i.e. “water derived in association with
the production of. . . gas” which the Act treats as a “pollutant”
unless it is disposed of in a State-approved well in the manner
specified by 33 U.S.C. § 1362(6)(B). App 9a-11a. These narrow
rulings affect only one component of the natural gas industry,
are consistent with the language and legislative history of the
Clean Water Act, follow the holdings of other circuits addressing
the disposal of produced water, and accord with current agency
and industry practice. Notwithstanding the grant of certiorari in
Miccosukee, the Court should deny Fidelity’s petition here.
STATUTORY PROV’ sIONS INVOLVED
The Clean Water Act was enacted to “restore and maintain
the chemical, physical, and biological integrity of the Nation’s
waters.” 33 U.S.C. § 1251. Under the Act, the “discharge of
any pollutant” from a“‘pcint source” into the waters of the United
States is unlawful, unless the discharge is made in accordance
with an NPDES permit issued by either the United States
Environmental Protection Agency (“EPA”) or a state or tribal
agency authorized by EPA to administer the NPDES permit
program. 33 U.S.C. §§ 1311(a), 1342. NPDES permits must
contain conditions that ensure that discharges fall within
technology-based effluent limitations, which in turn must be
sufficiently stringent to provide for compliance with state or
tribal water quality standards.’ 33 U.S.C. §§ 1311(b)(1)(C),
1342(a)(1)(A).
3. The EPA is authorized to treat Indian tribes as States for various
purposes of the Act, including the promulgation of water quality standards
and the issuance of NPDES permits. 33 U.S.C. § 1377(e). The Tribe has
applied for treatment as a state for the purpose of implementing the
Act’s water quality standards program.
3
The sole issue in this case is whether CBM waste water
discharged into the Tongue River is a “pollutant” as that term is
defined in the Act, 33 U.S.C. § 1362(6). App. 7a. Fidelity’s
Petition for Certiorari fails to include the Act’s entire definition
of “pollutant,” omitting a crucial clause which pertains to “water
derived in association with oil or gas production.” 33 U.S.C.
§ 1362(6)(B). The full definition of “pollutant,” including the
omitted language reads:
The term “pollutant” means dredged spoil, solid
waste, incinerator residue, sewage, garbage, sewage
sludge, munitions, chemical wastes, biological
materials, radioactive materials, heat, wrecked or
discarded equipment, rock, sand, cellar dirt, and
industrial, municipal, and agricultural waste
discharged into water. This term does not mean
(A) “sewage from vessels or a discharge incidental
to the normal operation of a vessel of the Armed
Forces” within the meaning of section 1322 of this
title, or (B) water, gas, or other material which is
injected into a well to facilitate production of oil
and gas, or water derived in association with oil or
gas production and disposed of in a well, if the well
used either to facilitate production or for disposal
purposes is approved by authority of the State in
which the well is located, and if such State
determines that such injection or disposal will not
result in degradation of ground or surface water
resources.
33 U.S.C. § 1362(6) (emphasis added). The Ninth Circuit held
that Fidelity’s waste water falls within this definition because it
is “industrial . .. waste discharged into water” and because it is
“water derived in association with .. . gas production” that is
not disposed of in accordance with the subsection B exception
(i.e. via State-approved injection wells).
STATEMENT OF THE CASE
A. The Threat to Water Quality Posed by the Coal Bed
Methane Industry.
Fidelity extracts natural gas from coal seams underlying
the Tongue River valley of southeastern Montana from a well
field upstream of the Northern Cheyenne Reservation.
To produce CBM in this region, the coal seam aquifer must
be partially dewatered, a process that produces 13,000 to 17,000
gallons of waste water daily per well. App. 3a.
The waste water produced by Fidelity’s natural gas wells is
“salty.” It is about three times more saline that the ambient waters
of the Tongue River and has a Sodium Absorption Ratio (SAR),
a measure of the ratio of sodium to calcium and magnesium in
the water, which is 40 to 60 times higher than river water.
App. 4a. Use of high SAR water for irrigation causes long-term
damage to soils, especially the clayey soils which predominate
in the Tongue River valley. /d.
Currently there are about 250 producing CBM wells in
Montana. However, the coal beds underlying the Tongue River
valley have been targeted by Fidelity and other natural gas
producers for larger-scale production. A Final Environmental
Impact Statement recently released by the United States Bureau
of Land Management and the State of Montana forecasts up to
14,000 producing CBM wells in Montana portion of the Tongue
River watershed over the next 20 years. Montana Statewide Final
Oil and Gas Environmental Impact Statement (January 2003)
(“FEIS”’) at 4-5, available at www.mt.blm.gov/mcfo/cbm/eis.
Tens of thousands of additional wells are projected in the
upstream Wyoming portion of the watershed. Jd. at 4-9.
The FEIS warns that with this level of development, unregulated
discharge of produced water could lead to “severe” degradation
of water quality that would “limit the uses of affected waters”
on the Northern Cheyenne Reservation. /d. at 4-72.
B. Proceedings Below.
This case began when the Northern Plains Resource Council
(NPRC) brought a citizen enforcement action against Fidelity
under the Clean Water Act alleging that Fidelity was discharging _
waste water from its CBM wells without an NPDES permit.
In the district court, the parties stipulated that Fidelity was
engaged in a discharge of waste water from a point source to a
navigable water without a permit. The only issue before the
court was whether Fidelity’s waste water is a “pollutant.” In an
oral ruling granting Fidelity’s motion for summary judgment,
the district court held that Fidelity’s waste water is not a pollutant
requiring an NPDES permit. App. 7a. The district court never
issued a written opinion.
NPRC appealed to the Ninth Circuit Court of Appeals.
The Tribe as well as several irrigation districts and associations
supported NPRC’s appeal as amici curiae. App. 7a n.3.
On April 10, 2003, the Ninth Circuit issued an opinion reversing
the district court. App. 1a-18a. The Ninth Circuit held that the
“plain language” of the Clean Water Act requires the conclusion
that CBM waste water is a “pollutant” subject to regulation under
the Act. App. 9a.
First, the Court held that Fidelity’s waste water is “industrial
waste,” a term specifically included in the Act’s definition of
“pollutant.” App. 9a. The Court reasoned that “[b]ecause Fidelity
is engaged in production of methane gas for commercial sale
and because CBM water is an unwanted byproduct of the
extraction process, CBM water falls squarely with the ordinary
meaning of ‘industrial waste.’” Jd. at 10a.
Second, the Court held that CBM waste water is a
“pollutant” because it is ““produced water’ derived from gas
extraction.” App. 10a (citing Sierra Club v. Cedar Point Oil,
73 F.3d 546, 568 (Sth Cir.), cert. denied, 519 U.S. 811 (1996)).
The Court reasoned that CBM waste water falls into the EPA’s
definition of the term “produced water” and that the Act
6
“only exempts water derived from gas extraction from regulation
when the water is disposed of in a well and will not result in the
degradation of other water bodies.” /d. at 11a (citing 33 U.S.C.
§ 1362(6)(B)). Because Fidelity discharges its waste water
‘directly into the Tongue, not by reinjection into a state-approved
well,” its waste water “does not meet § 1362(6) exemption
criteria,” and is “a pollutant within the plain meaning of the
{Clean Water Act].” Jd.
The Court explained that its conclusion is supported by the
Act’s definition of “pollution” which is the “man-made or man
induced alteration of the chemical, physical, biological and
radiological integrity of water.” App lla (citing 33 U.S.C.
§ 1362(19)). The Court reasoned that by discharging CBM water
into the Tongue River, Fidelity “alters the water quality of the
Tongue River.” /d. A holding that “the massive pumping of
salty, industrial waste water into protected waters does
not involve the discharge of a ‘pollutant,’” the Court found,
would “undermine the integrity of [the CWA’s] prohibitions.”
Id. at 12a.
REASONS FOR DENYING THE PETITION
1. The plain language of the Clean Water Act supports the
Ninth Circuit’s decision that CBM waste water falls under the
Act’s definition of “pollutant.” Fidelity’s discharge is not only
an “industrial waste,” it also is “produced water,” i.e. “water
derived in association with the production of. . . gas.” 33 U.S.C.
§ 1362(6). Fidelity discharges its waste water directly into the
Tongue River, not via injection into a State-approved well in
accordance with the “produced water” exemption provided for
in 33 U.S.C. § 1362(6)(B). There is no circuit split on the issue
of whether “water derived in association with ... gas
production” is a “pollutant” under the Clean Water Act when it
is discharged directly into the surface waters of the United States.
To the contrary, the only other circuit court decision to address
this issue, Sierra Club v. Cedar Point Oil, 73 F.3d 546
(Sth Cir.), reached the same conclusion as the Ninth Circuit
here, and this Court denied certiorari. 519 U.S. 811 (1996).
7
2. This case is distinguishable from Miccosukee and similar
cases addressing whether dams and other surface water
management activities “add” pollutants to navigable waters.
In the case at bar, the waste water at issue ori ginates from deep
below the surface of the earth (outside the “waters of the United
States”) and is the byproduct of an industrial process ~— the
production of natural gas from coal seams. Even if this Court
reverses the Eleventh Circuit’s ruling in Miccosukee, it would
not affect the Ninth Circuit’s ruling that Fidelity’s CBM
discharge falls within the plain language of the Clean Water
Act’s definition of “pollutant” because it is both “industrial
waste” and “produced water.”
3. The EPA has long required NPDES permits for the
disposal of CBM waste water on lands within its jurisdiction,
as have major CBM producing states such as Colorado and
Wyoming. Fidelity has already obtained NPDES permits from
the State of Montana for all of the discharges at issue in this
case. The lack of any practical or immediate controversy over
the application of the NPDES permit requirement to the
discharge of CBM waste water counsels against a grant of
certiorari which would upset the status quo and create regulatory
uncertainty at a time when CBM production is burgeoning
throughout the Rocky Mountain west.
I. WATER DISCHARGED ASA RESULT OF NATURAL
GAS PRODUCTION IS A “POLLUTANT” UNDER
THE PLAIN LANGUAGE OF THE CLEAN WATER
ACT.
A. Fidelity’s Discharge is “Industrial Waste.”
The first basis for the Ninth Circuit’s ruling that Fidelity’s
discharge is a “pollutant” under the Clean Water Act was that it
fits within the broad category “industrial waste.” App. 9a.
Applying the ordinary meanings of the terms “industrial” and
“waste,” the Court of Appeals concluded that an industrial waste
is “any useless byproduct derived from the commercial
production of goods and services.” App. 10a. Because Fidelity
8
is engaged in the commercial production of natural gas and
because its waste water is an “unwanted byproduct of the
extraction process,” Fidelity’s waste water “falls squarely within
the ordinary meaning of ‘industrial waste.” Jd.
The Ninth Circuit’s ruling not only accords with the
plain meaning of “industrial waste,” it also accords with the
legislative history of the Act’s definition of the term “pollutant.”
4 This history demonstrates that Congress intended to adopt a
definition of “pollutant” that would be “at least as broad” as
that found in the Refuse Act of 1899, 33 U.S.C. § 407, which
prohibits the discharge of ‘‘any refuse matter of any kind or
description whatever” into any navigable water. See United
States v. Hamel, 551 F.2d 107, 110-11 (6th Cir 1977), citing
S. Rep. No. 92-414 at 76, reprinted in, A Legislative History of
the Water Pollution Control Act Amendments of 1972 2:1494
(Envtl. Pol. Div., Cong. Research Serv. 1973) (hereafter “1972
Leg. Hist.”); see also, 2 W.H. Rodgers, Environmental Law:
Air and Water, § 4.9, at 144 (Congress “meant to carry on the
tradition of the Refuse Act and that tradition was to construe
the word ‘refuse’ as condemning each and every variation of
damage-inducing wastes that changing technologies could
invent.”). Thus, while the definition of “pollutant” includes some
very specific items such as cellar dirt,” it also broadly lists
“industrial, municipal and agricultural wastes,” thereby
sanctioning “the inclusion of discharged substances that are not
specifically listed into these broad categories.” Cedar Point Oil,
73 F.3d at 565; see also National Wildlife Fed’n v. Gorsuch,
693 F.3d 156, 174 n.56 (D.C. Cir. 1982); Hamel, 551 F.2d
at 110-111.
Fidelity claims that its discharge does not constitute a
“pollutant” because it does not physically introduce pollutants
from the “outside world” into the waters of the United States.
Petition for Certiorari at 22-23 (citing National Wildlife Fed’n
v. Consumers Power Co., 862 F.2d 580, 584, 586 (6th Cir. 1988)
and Gorsuch, 693 F.2d at 174-75). The force of Fidelity’s
argument, however, depends on how one defines the “outside
world.” From the perspective of the Clean Water Act, the
“outside world” is any place outside “navigable waters” or the
“waters of the United States.” See 33 U.S.C. § 1362(12)
(“discharge of a pollutant” means the “addition of any pollutant
to navigable waters from any point source” [emphasis added});
id. § 1362(7) (“navigable waters” means the “waters of the
United States”). The “waters of the United States” do not include
ground waters. See 40 C.F.R. § 122.2; Village of Oconomowoc
v. Dayton Hudson Corp., 24 F.3d 962, 965 (7th Cir.), cert.
denied, 513 U.S. 930 (1994). Because Fidelity extracts “salty”
groundwater from deep below the earth, water that would
otherwise “never reach the Tongue River were it not for Fidelity’s
extraction process,” App. 3a, and discharges it as a waste product
to the river, it does add pollutants from the “outside world” to
the “waters of the United States.”
Fidelity also argues that the Ninth Circuit’s analysis was
faulty because CBM waste water “‘can be and is used for” various
beneficial purposes including domestic use, stock watering and
wildlife. Petition for Certiorari at 18 n.7. But the mere fact that
CBM waste water has many potential beneficial uses cannot
alter the fact that Fidelity discharges water to the Tongue River
as an unwanted by-product which, if unregulated, will degrade
the natural and economic value of the river’s waters. No doubt,
beneficial uses can be found for many of the other substances
listed in the Act’s definition of “pollutant.” See 33 U.S.C.
§ 1362(6) (listing “rock” and “sand” as pollutants). But under
the Clean Water Act, like the earlier Refuse Act, such substances,
no matter how useful in certain applications, become
“pollutants” once they are discharged as unwanted by-products
into the Nation’s waterways. See United States v. Standard Oil
Co., 384 U.S. 224, 226 (1966) (rejecting contention that the
phrase “refuse matter” in the Refuse Act excluded valuable
substances and holding gasoline to be a “pollutant” under that
statute); 2 Rodgers, supra, § 4.9, at 144 (under Clean Water Act
a “pollutant” can be viewed as a “resource out of place’).
10
In essence, Fidelity argues that “unaltered groundwater”
can never be an “industrial waste” or a “pollutant” under the
Clean Water Act. See Petition for Certiorari at 18. But as the
Ninth Circuit reasoned, such a per se rule would “upset the
integrity” of the Act. App. 14a. The fact that groundwater is
“natural” or “unaltered” does not necessarily mean that it is
benign.* Indeed, the record shows that CBM waste water is
“salty” and contains high levels of SAR which can render surface
waters unusable for irrigation. App. 4a. There is no “compelling
reason” why this Court should grant a wnit of certiorari to review
the Ninth Circuit’s fact-bound ruling that the unwanted, “salty”
water that is discharged into the Tongue River as a result of
Fidelity’s CBM extraction process is an “industrial waste” and
therefore a “pollutant” under the Clean Water Act.
B. Water Derived in Association with the Production
of Natural Gas is a “Pollutant” under the Clean
Water Act.
The Act’s broad definition of “pollutant,” which
encompasses all “industrial, municipal and agricultural waste
discharged into water,” is subject to a narrowly drawn exception
for “water derived in association with oil or gas production”
when the water is “disposed of in a well” which has been
4. Many industries discharge “unaltered groundwater” that may
be hazardous to public health and the environment. For example, mining
operations often result in discharges of “natural” but nevertheless toxic
groundwater. See, e.g., Okanogan Highlands Alliance v. Williams, 236
F.3d 468, 473-75 (9th Cir. 2000) (groundwater filling mine pit and
discharged to adjacent surface waters could exceed State water quality
standards); Montana Envt’l Info. Center v. Montana Dept of Envil.
Quality, 296 Mont. 207, 988 P.2d 1236, 1239 (1999) (mining company’s
discharge of groundwater containing naturally high levels of arsenic).
Similarly, naturally occurring groundwater extracted for geothermal
energy development can pose environmental hazards. See, e.g., State
Water Resources Department v. City of Klamath Falls, 68 Or. App. 148,
682 P.2d 779, 784 & n.5 (1984) (State pollution discharge permit required
for disposal of geothermal fluids derived from wells).
1]
approved by a state based on a determination that underground
disposal will not degrade ground or surface waters. 33 U.S.C.
§ 1362(6)(B). The Ninth Circuit held that F idelity’s discharge
is a “pollutant” because it is “produced water,” i.e. “water derived
in association with . . . gas production,” that is nor disposed of
in accordance with the terms of this exemption. App. 10a-1 1a.
The Ninth Circuit’s holding is consistent with the
Congressional intent. Congress’s use of the broad term
“industrial waste’ in defining pollutant coupled with its crafting
of a very narrow, conditional exception for “water derived in
association with oil or gas production” is an indication that it
intended that such produced water would be treated as a
“pollutant” if it is not disposed of in accordance with the
conditions specified in 33 U.S.C. § 1362(6)(B). TRW Inc. vy.
Andrews, 534 U.S. 19, 28-29 (2001) (“Where Congress
explicitly enumerates certain exceptions to a general prohibition,
additional exceptions are not to be implied, in the absence of
evidence of a contrary legislative intent”); Andrus v. Glover
Constr. Co., 446 U.S. 608, 616-17 (1980). Congress would not
have created this very narrow, conditional exception, if it
intended that all water produced as a byproduct of gas production
would be exempt from the Act.
In Cedar Point Oil, 73 F.3d at 567-69, the Fifth Circuit
held that waste water derived in association with oil and gas
production was a “pollutant” when discharged into the waters
of Galveston Bay. The court reasoned that the Act’s conditional
exception for “water derived in association with oil or gas
production” from the meaning of “pollutant” was a “strong
indicator of Congress’s concern over the efiects of produced
water on the environment.” Jd. at 568. The court further
reasoned:
[I]f Congress felt that it was necessary to draft a
detailed exemption for produced water that has been
disposed of in a state-approved reinjection well, it
may be that Congress believed that such produced
water would otherwise be a pollutant. If, absent an
12
exemption, produced water reinjected into a state-
approved well is a pollutant, then it is hardly a stretch
to say that produced water deposited directly into a
bay is also a pollutant.
Id. (emphasis in original). The Court emphasized that because
Congress provided a “clear avenue” for oil or gas producers to
avoid regulation by the Clean Water Act, a producer that “chose
not to avail itself” of that avenue should be subject to the Act.
Id. at 568 n.36.
Fidelity attempts to distinguish Cedar Point Oil on the basis
that the “produced water” at issue in that case apparently
included materials added to water in the oil and gas production
process.’ Petition for Certiorari at 18-19. However, as the Ninth
Circuit’s opinion points out, EPA defines “produced water” to
mean “water (brine) brought up from the hyrdocarbon-bearing
strata during the extraction of oil and gas,” a definition which
“does not turn on the addition of chemicals or any other
alteration.” App. 10a (quoting 40 C.F.R. 435.41(bb)).°
Furthermore, the Act’s definition of “pollutant” does not use
the term “produced water,” but instead uses the more inclusive
term “water derived in association with oil or gas production.”
33 U.S.C. § 1362(6)(B). in this case, there can be no dispute
that the waste water discharged by Fidelity into the Tongue River
is “derived in association with . . . gas production ,” and 's not
5. In some cases, produced water contains residual quantities of
crude oil, a “natural” constituent of groundwater found in association
with crude oil deposits. See BP Expioration & Oil v. United States Envil.
Protection Agency, 66 F.3d 784, 792 (6th Cir. 1995). Fidelity position
would mean that “unaltered groundwater” containing naturally occurring
crude oil residues could not be treated as a pollutant when brought to
the surface in an oil well. °
6. Fidelity points out that this definition of “produced water”
applies only to offshore and coastal oil and gas operations. Petition for
Certiorari at 20 n.9. Nevertheless, the regulations applicable to onshore
oil and gas operations specifically list “produced water” as a “waste
water pollutant.” 40 C.F.R. § 435.32.
_ 13
“disposed of in a well” approved by the State of Montana.
Petition for Certiorari at 2-3. Accordingly, the Ninth Circuit
logically concluded that Fidelity’s waste water is a “pollutant”
under the plain language of the Clean Water Act, 33 U.S.C.
§ 1362(6)(B).
The legislative history of the Clean Water Act strongly
supports the Ninth Circuit’s conclusion. The Senate Committee
Report for the legislation that became the Clean Water Act
indicates that the Senate intended to create only “two specific
exceptions from the term pollutant: sewage from vessels, as
that term is defined and controlled through the provisions of
Section 312, and water, gas, or other materials associated with
the secondary recovery of oil.” S. Rep. No. 92-414 at 76 (1971),
reprinted in, 1972 Leg. Hist. 2: 1494 (emphasis added).
The Senate intended to exempt “water derived in association
with oil or gas production” only if the water was “disposed in a
well. . . approved by authority of the State in which the well is
located.” 1972 Leg. Hist. 2:1698.
The House version of the bill further tightened the Senate’s
already narrow exemption by requiring not only that the water
be disposed of in a State-approved well but also that the State
make a determination that the well disposal “will not result in
the degradation of ground or surface water resources.” Compare
1972 Leg. Hist. 1:1068, with id. 2:1697-98. The House
Committee Report emphasized that this exception was to be
construed very narrowly:
It is the intent of Congress that the exclusion from
the term “pollutant” relating to the injection of water,
gas, or other materials into wells applies only . . . to
the properly executed disposal in wells of brines
derived in association with the production of crude
oil or natural gas, with appropriate precautions taken
to assure that such injection or disposal does not
lead to, or make substantially more likely, the
degradation of usable water resources. For such
14
exclusion to be effective, the State is required (1) to
approve the well used either to facilitate production
or for disposal purposes, and (2) to make a
determination, based on sufficient investigation and
evidence, that such degradation has not taken place
and has not been or will not be made substantially
more likely as a result of such injection or disposal.
H.R. Rep. No. 92-911 at 131 (1972), reprinted in, 1972 Leg.
Hist. 1:818 (emphasis added).
The debate on the floor of the House confirms that Congress
would not have intended that produced water be exempt from
the NPDES requirement except under the specific conditions
spelled out in the definition of “‘pollutant.” It also shows that
Congress was concerned about the deleterious effects of the
produced water itself, not only the materials that may be added
to the water in the oil and gas production process. 1972 Leg.
Hist. 1:595. On the House floor, Representative Aspin proposed
an amendment to strike the exception altogether. /d. at 1:589.
However, the supporters of the exception led by Representative
Harsha successfully argued that water produced in association
with oil and gas extraction should not be regulated under the
Clean Water Act as long as it was disposed of in a well regulated
under existing state schemes applicable to the oil and gas
industry. Representative Harsha explained that “/h/uge volumes
of water are commonly found in the same underground
strata as oil and gas and come up with produced oil and gas.”
Id. at 1:595 (emphasis added). He noted the “injection of brine
water resulting from petroleum operations back into the earth
for disposal purposes is itself an important form of pollution
control” and argued that it was not appropriate that this form
of control would be “displaced by new Federal authority.”
Id. at 1:596 (emphasis added). Representative Harsha also
explained that the House Committee had previously considered
Representative Aspin’s proposal but had instead added an
amendment providing additional safeguards that were not
present in the Senate bill. He pointed out:
15
[The House bill] is much more stringent than S. 2770
— its Senate-passed counterpart on this issue. [It]. . .
tightens this provision [in S. 2770] down
considerably and will not permit this process until
the State makes a finding or determination that such
process will not degrade the waters.
Id. 1:595.
The Conference Committee largely retained the House
language. According to Senator Muskie, the bill’s sponsor:
The language of the House amendment as regards
pollutants associated with oil and gas production was
clarified to indicate that the process of injection and
disposal of materials associated with oi] and gas
production from wells would be excluded only where
a State regulatory program existed. The Conferees
intend that this provision assure that no injection or
disposal occur in such a manner as to present a
potential hazard to ground water quality.
1972 Leg. Hist. 1:178 (emphasis added). Thus, the legislative
history shows that the exemption for “water derived in
association with oil or gas production” was enacted on the
premise that it was unnecessary to treat water produced by oil
or gas wells as a pollutant under the Clean Water Act only in
cases where the water is disposed of in a State-approved well
pursuant to an adequate State program to protect ground and
surface waters. The debate on this issue confirms that Congress
clearly did not contemplate that “water derived in association
with ... gas production” would be exempt from the Act’s
definition of “pollutant” when discharged directly to surface
waters where it could harm crops, soils, fish and wildlife.
In short, the Ninth Circuit’s holding is consistent with the
plain language of the Act, the Act’s legislative history and the
decision of the Fifth Circuit in Cedar Point Oil. Fidelity has
identified no circuit split on this issue and no other basis that
would warrant the issuance of a writ of certiorari.
16
Il. THIS CASE DOES NOT TURN ON THE OUTCOME
IN MICCOSUKEE.
In an effort to convince the Court to at least provisionally
grant certiorari pending the outcome in Miccosukee, Fidelity
argues that this case turns upon the issue before the Court in
Miccosukee: viz. whether dams and other types of surface water
management activities should be subject to the NPDES
requirement of the Clean Water Act. See Petition for Certiorari
at 29. In Miccosukee Tribe of Indians v. South Florida Water
Management Dist., 280 F.3d 1364, 1367-69 (11th Cir. 2002),
the Eleventh Circuit held that a public agency that manages a
flood control project consisting of a system of levees, canals
and water impoundment areas must obtain an NPDES permit
when it pumps polluted water from one water impoundment
area to another because such pumping constitutes the “addition”
of a pollutant “from” a point source. The First and Second
Circuits have likewise held that an NPDES permit is required
_ for activities that involve interbasin transfers of surface water.
Catskill Mountains Chapter of Trout Unlimited v. City of New
York, 273 F.2d 481, 492 (2d Cir. 2002) (diversion of water from
a reservoir containing pollutants through a tunnel into a creek
constituted “addition” of pollutants from a point source); Dubois
v. United States Dep t of Agric., 102 F.3d 1273, 1299 (Ast Cir.
1996) (pumping of polluted surface water for use in snowmaking
and its subsequent discharge into a lake would constitute an
“addition” of pollutants from a point source), cert. denied, 521
U.S. 1119 (1997). On the other hand, the D.C. Circuit and the
Sixth Circuit have held that dams and other surface water
management facilities do not require an NPDES permit where
they do not “add” pollutants from the “outside world,” i.e. from
outside the “waters of the United States,” into navigable waters.’
7. The above cases have differences as well as similarities.
For example, Consumers Power and Gorsuch involved exchanges of
water from the same water body, while Catskill Mountains and Dubois
involved interbasin transfers. Dubois unlike the other three cases involved
a discharge resulting from a private commercial activity (snowmaking)
rather than more traditional “surface water management.”
17
Consumers Power Co., 862 F.2d at 589; Gorsuch, 693 F.2d at
175.
The case sub judice is distinguishable from the above cases
on at least three important grounds. First, it does not involve a
transfer between two bodies of navigable waters. Second, it does
not involve “surface water management,” but instead involves
an industrial process that produces copious amounts of
groundwater as a waste product — water that would otherwise
remain deep below the earth and never enter the “waters of the
United States.” Finally, the waste water at issue here is “produced
water,” i.e. “water derived in association with ... gas
production,” a waste product which is expressly mentioned in
the Act’s definition of “pollutant” and which is afforded a unique
status under that definition. 33 U.S.C. § 1362(6)(B). These three
differences are entirely dispositive of the issues in this case.
Thus, regardless of how the Court may in Miccosukee resolve
the perceived circuit conflict over whether dams and other
surface water management activities “add” pollutants to
navigable waters, the Court’s decision would not detract from
the Ninth Circuit’s holding that groundwater produced in the
CBM extraction process is a “pollutant” under the Clean Water
Act.®
It is true that the Ninth Circuit cited Miccosukee, Catskill
Mountains and Dubois for the proposition that “transporting
water from one water body to another [without an NPDES
8. Fidelity’s petition repeatedly seizes on the Ninth Circuit’s
statement that the issue of whether CBM water is a pollutant is
“practicably indistinguishable” from the issues considered in Miccosukee
and other similar cases. App. 15a. But as the Ninth Circuit itself
recognized elsewhere in its opinion, the determination of whether
Fidelity’s waste water is a “pollutant” ultimately turns on the plain
language of Act’s definition of “pollutant,” rather than on case law
construing the meaning of the term “addition.” Ironically, Fidelity argued
below that this case was distinguishable from Miccosukee for precisely
this reason. /d. It is only now that the Court granted certiorari in
Miccosukee that Fidelity has changed its position to embrace the alleged
similarities between the two cases.
18
permit] can violate the [Clean Water Act].” App 14a-15a
(emphasis added). But this statement merely responded to
Fidelity’s extreme position that a discharge of “unaltered water”
would never require an NPDES permit under any circumstances,
a proposition that finds no support in the case law. /d. at 15a
(rejecting argument that “discharge of water cannot be a
pollutant simply because the discharged water is unaltered”’).
As shown above, the Ninth Circuit was right to reject that
argument and hold that a discharge of “‘unaltered water” without
a permit does violate the Clean Water Act at least where the
water is a waste product of an industrial process, originates from
deep below the “waters of the United States,” is “derived in
association with oil or gas production,” and is not injected in a
State-approved well. 33 U.S.C. § 1362(6)(B).
Because these important statutory rules were not implicated
in the line of cases addressing dams and other surface water
management activities, the Court’s decision in Miccosukee will
not address the issue presented by this case. Accordingly, there
is no reason for the Court to grant certiorari pending its decision
in Miccosukee as Fidelity requests. See Petition for Certiorari
at 29. On the contrary, because there is no authority supporting
Fidelity’s position on the narrow issue of whether waste water
discharged in the CBM extraction process is a “pollutant” under
the Clean Water Act, Fidelity’s petition should be denied in its
entirety.
Il. PRACTICAL CONSIDERATIONS DO NOT
SUPPORT ISSUANCE OF A WRIT OF
CERTIORARI.
There is no practical necessity for the Court to grant
certiorari to decide whether the waste water generated as aresult
of CBM production should be treated as a “pollutant” under the
Clean Water Act. There is remarkable unanimity among federal
and state agencies that waste water derived from the production
of CBM is a “pollutant” under the Clean Water Act and that its
discharge requires an NPDES permit. The EPA requires CBM
producers to obtain NPDES permits on Indian reservations, the
19
only places where it exercises direct Clean Water Act
jurisdiction.’ Likewise, environmental agencies in major CBM
producing States such as Colorado and Wyoming currently
require NPDES permits for discharges of CBM produced
water.'° Fidelity has itself obtained NPDES permits for all of
the discharges at issue in this case. App. 7a n.2. Fidelity does
not attempt to make any showing that the NPDES permit
requirement has imposed any unreasonable burden on natural
gas producers in Montana or in other states. Indeed, Fidelity is
currently seeking to expand its Montana operation
notwithstanding the NPDES permit requirement.
Fidelity maintains that certiorari should be granted because
the Ninth Circuit’s decision raises federalism concerns. But it
is important to note that the effects of CBM discharges are not
confined to the boundaries of individual states. For example,
CBM discharges in Wyoming already affect water quality in
the downstream Montana reaches of the Tongue River. Fidelity’s
discharges in Montana similarly affect water quality on the
nearby Northern Cheyenne Reservation. The NPDES permit
requirement ensures that the water quality standards of
neighboring states and tribes are respected when another state
decides to allow discharges of CBM water into the “waters of
the United States.” The Tribe believes that disposal of the
massive quantities of waste water produced by this rapidly
expanding new industry should conform to the requirements of
9. See 66 Fed. Reg. 46,455 (Sept. 5, 2001) (announcing
development of “Best Professional Judgment” determination of effluent
limitations for NPDES permitting of CBM wells on Indian lands);
55 Fed. Reg. 40,235, 40,236 (Oct. 2, 1990) (issuing general NPDES
permit for CBM wells on Colorado’s Southern Ute Reservation).
10. See http://deq.state.wy.us/wqd/watershed/91131.pdf (Wyoming
general NPDES permit for CBM production); Swartz v. Beach, 229
F. Supp. 2d 1239, 1270-72 (D. Wyo. 2002); Southern Colorado C.U.R.E.
v. Evergreen Operating Corp., No. 98-WM-1518 (D. Colo. 1999)
Recommendation of Magistrate Judge at 23-24; Colorado NPDES Permit
Issued to J.M. Huber Corp. (Appellee’s Excerpts of Record at 178-80).
20
the federal Clean Water Act and should not be left solely to the
policy choices of individual states.
CONCLUSION
The Petition for Certiorari should be denied.
Respectfully submitted,
JOHN B. ARUM
Counsel of Record
STEVEN H. CHESTNUT
ZIONTZ, CHESTNUT, VARNELL
BERLEY & SLONIM
2101 Fourth Avenue
Suite 1230
Seattle, WA 98121-2331
(206) 448-1230
Attorneys for Amicus Curiae
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