Respondents Brief — Eastern Oregon Mining Association, et al., Petitioners v. Oregon Department of Environmental Quality, et al.
Supreme Court briefMay 8, 2020
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No. 19-839
_____________________________________________________________
_____________________________________________________________
IN THE SUPREME COURT OF THE UNITED STATES
___________________
EASTERN OREGON MINING ASSOCIATION, et al.,
Petitioners,
v.
OREGON DEPARTMENT OF ENVIRONMENTAL QUALITY, et al.,
Respondents.
___________________
RESPONDENTS’ BRIEF IN OPPOSITION
___________________
On Petition for Writ of Certiorari to the
Supreme Court of the State of Oregon
___________________
ELLEN F. ROSENBLUM
Attorney General
BENJAMIN GUTMAN*
Solicitor General
DENISE G. FJORDBECK
Attorney-in-Charge
1162 Court St. NE
Salem, Oregon 97301-4096
Telephone: (503) 378-4402
denise.fjordbeck@doj.state.or.us
Attorneys for Respondents
*
Counsel of Record
_______________________________________________________________
_______________________________________________________________
QUESTION PRESENTED
Did the Oregon Supreme Court correctly hold, in agreement with the
views of the U.S. Environmental Protection Agency, that the discharged
wastewater from suction dredge mining requires a permit under section 402 of
the Clean Water Act?
i
TABLE OF CONTENTS
QUESTION PRESENTED................................................................................... I
INTRODUCTION ................................................................................................1
STATEMENT.......................................................................................................2
A.
The state regulates suction dredge mining under both the
Clean Water Act and state law.........................................................2
B.
The Oregon Supreme Court upheld DEQ’s authority to issue
the 2010 permit allowing suction dredge mining under
certain conditions. ............................................................................7
ARGUMENT........................................................................................................9
A.
There is a serious question whether this case is moot under
Article III standards........................................................................10
B.
The Clean Water Act question has little practical
significance for petitioners because their mining can be and
is regulated under state law............................................................13
C.
The Oregon Supreme Court’s ruling is correct, matches the
EPA’s longstanding interpretation of the Clean Water Act,
and does not conflict with decisions of this Court or the
courts of appeals.............................................................................15
CONCLUSION...................................................................................................23
ii
TABLE OF AUTHORITIES
Cases Cited
ASARCO Inc. v. Kadish,
490 U.S. 605 (1989) .................................................................................12
Bohmker v. Oregon,
903 F.3d 1029 (9th Cir. 2018),
cert. den., 139 S. Ct. 1621 (2019) ..............................................................6
Catskill Mountain Chapter of Trout Unlimited, Inc.
v. City of New York,
273 F.3d 481 (2d Cir. 2001) .............................................................. 19, 22
County of Maui v. Hawaii Wildlife Fund,
__ U.S. __ (April 20, 2020)......................................................................18
DeFunis v. Odegaard,
416 U.S. 312 (1974) .................................................................................12
Kingdomware Technologies, Inc. v. United States,
136 S. Ct. 1969 (2016) .............................................................................11
Local No. 8-6, Oil, Chem. & Atomic Workers Int’l Union,
AFL-CIO v. Missouri,
361 U.S. 363 (1960) .................................................................................12
Los Angeles County Flood Control Dist. v. Natural Resources
Defense Council, Inc.,
568 U.S. 78 (2013) ...................................................................................19
National Min. Assn. v. U.S. Army Corps of Engineers,
145 F.3d 1399 (D.C. Cir. 1998) ...............................................................22
National Wildlife Fed. v. Consumers Power Co.,
862 F.2d 580 (6th Cir. 1988)....................................................................21
National Wildlife Federation v. Gorsuch,
693 F.2d 156 (D.C. Cir. 1982) .................................................................21
Nw. Envtl. Def. Council v. Envtl. Quality Comm’n,
223 P.3d 1071 (Or. App. 2009)
rev. allowed, 240 P.3d 1097,
rev. dismissed, 245 P.3d 130 (Or. 2010) ........................................... 4, 5, 8
Penn v. Bd. of Parole & Post-Prison Supervision,
451 P.3d 589 (Or. 2019) ...........................................................................11
PUD No. 1 of Jefferson County v. Washington Dept. of Ecology,
511 U.S. 700 (1994) ...................................................................................3
Richardson v. Ramirez,
418 U.S. 24 (1974) ...................................................................................12
iii
Rybachek v. EPA,
904 F.2d 1276 (9th Cir. 1990)....................................................... 9, 20, 21
South Florida Water Management Dist. v.
Miccosukee Tribe of Indians,
541 U.S. 95 (2004) ...................................................................................19
U.S. v. Law,
979 F.2d 977 (4th Cir. 1992) .....................................................................22
United States v. Sanchez-Gomez,
138 S. Ct. 1532 (2018) .............................................................................10
Constitutional and Statutory Provisions
33 U.S.C. § 1251...................................................................................................3
33 U.S.C. § 1251(a) ..............................................................................................3
33 U.S.C. § 1251(b) ..............................................................................................3
33 U.S.C. § 1311(a) ........................................................................................3, 15
33 U.S.C. § 1314(a)(4)....................................................................................4, 15
33 U.S.C. § 1342(a)(1)..........................................................................................4
33 U.S.C. § 1342(b) ........................................................................................4, 13
33 U.S.C. § 1342(c)(1)..........................................................................................4
33 U.S.C. § 1362(12) ......................................................................................3, 15
33 U.S.C. § 1362(6) ........................................................................................4, 15
33 U.S.C. § 1370.............................................................................................4, 14
Or. Laws. 2013, ch. 783 § 1..................................................................................5
Or. Rev. Stat. § 14.175..........................................................................................7
Or. Rev. Stat. § 468.116........................................................................................6
Or. Rev. Stat. § 468B.114(1) ..........................................................................6, 14
Or. Rev. Stat. § 468B.114(2) ................................................................................6
Administrative Rules
40 C.F.R. 122.3(i) ...............................................................................................18
iv
RESPONDENTS’ BRIEF IN OPPOSITION
__________
INTRODUCTION
The question presented in this case is narrow, easily answered, and of
little forward-looking consequence to the parties to this case. Suction dredge
mining discharges a turbid mixture of stream water and sediment from the
streambed back into the stream. The question is whether that activity involves
the “addition of any pollutant” to the stream; if it does, it requires a permit
under section 402 of the Clean Water Act.
In 2010, respondent Oregon Department of Environmental Quality
(DEQ) issued a general permit under section 402 that allowed individuals to
engage in small-scale suction dredge mining as long as they met certain waterquality criteria. Petitioners challenged the permit, arguing that it was beyond
DEQ’s authority under section 402. The permit expired in 2014, and Oregon
has since adopted a different and more restrictive set of regulations of suction
dredge mining as a matter of state law. Whether the now-expired 2010 permit
should or should not have issued under the Clean Water Act has little forwardlooking significance for petitioners, who must comply with state law regardless
how the Clean Water Act is interpreted.
As explained below, there are strong prudential reasons to deny review
here even if the question presented otherwise deserved this Court’s attention. In
2
particular, there is a serious mootness issue that this Court would have to
address if it granted review. But in any event, the question presented does not
warrant review. The Oregon Supreme Court’s interpretation of the Clean Water
Act here is consistent with the longstanding views of the U.S. Environmental
Protection Agency (EPA) and the conclusion of every other appellate court to
consider the issue. Its ruling does not conflict with any decisions of this Court
and does not implicate any circuit split. For those reasons, the Court should
deny the petition.
STATEMENT
A.
The state regulates suction dredge mining under both the Clean
Water Act and state law.
Suction dredge mining involves the use of a small motorized pump to
vacuum up water and sediment. Pet. App. A-3. The material is then passed
over a sluice tray, separating out heavy metals including gold, and the
remainder is discharged into the stream. Id. Ejection of the water and sediment
creates a plume of turbid wastewater, and re-mobilizes pollutants such as
mercury that would otherwise have remained undisturbed and inactive in the
stream bed. Pet. App. A-3 to A-4.
Because of the adverse effects that suction dredge mining can have on
water quality, it is regulated under both federal and state law. At issue here are
now-expired general permits that the state issued under section 402 of the Clean
3
Water Act to allow suction dredge mining as long as that activity met certain
water-quality standards.
The Clean Water Act, 33 U.S.C. § 1251 et seq., is a comprehensive
statute designed to “restore and maintain the chemical, physical, and biological
integrity of the Nation’s waters.” Id. § 1251(a). To accomplish that goal, the
Act assigns “distinct roles for the Federal and State Governments.” PUD No. 1
of Jefferson County v. Washington Dept. of Ecology, 511 U.S. 700, 704 (1994).
That structure gives states, not the federal government, primary responsibility
for regulating water quality. “It is the policy of the Congress to recognize,
preserve, and protect the primary responsibilities and rights of States to
prevent, reduce, and eliminate pollution” in the Nation’s waters. 33 U.S.C.
§ 1251(b) (emphasis added); see also PUD No. 1 of Jefferson County, 511 U.S.
at 707.
In general terms, the Clean Water Act makes it unlawful to discharge any
pollutant without a permit. 33 U.S.C. § 1311(a) (“Except as in compliance with
this section and sections 1312, 1316, 1317, 1328, 1342, and 1344 of this title,
the discharge of any pollutant by any person shall be unlawful.”). The term
“discharge of a pollutant,” in turn, is defined as “any addition of any pollutant
to navigable waters from any point source[.]” 33 U.S.C. § 1362(12) (emphasis
4
added). The Act’s definition of “pollutant” explicitly includes the materials
ejected from suction dredges:
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.
33 U.S.C. § 1362(6) (emphasis added). Furthermore, suspended solids are
specifically included in the definition of conventional pollutants. 33 U.S.C.
§ 1314(a)(4).
The EPA is empowered, under Section 402 of the Act, to issue permits
for the discharge of pollutants. 33 U.S.C. § 1342(a)(1). In the alternative, a
state may opt to administer its own program. 33 U.S.C. § 1342(b). If the state
program is approved by the EPA, it supplants EPA’s role in issuing permits for
discharges to water. 33 U.S.C. § 1342(c)(1). Any such state program must be
at least as stringent as that administered by the EPA, but states are free to adopt
standards that are more stringent than required by the Clean Water Act. 33
U.S.C. § 1370.
In 2005, the Oregon Environmental Quality Commission issued a fiveyear general permit allowing anyone to engage in small-scale suction dredge
mining as long as they complied with state water quality standards. Nw. Envtl.
Def. Council v. Envtl. Quality Comm’n, 223 P.3d 1071, 1074 (Or. App. 2009)
5
(“NEDC”). Both miners and environmentalists challenged the permit in state
court. The Oregon Court of Appeals concluded that the process of suction
dredge mining created turbid wastewater plumes that required a section 402
permit. Id. at 1085. It also held, however, that the permit was overbroad to the
extent it regulated dredged material within the exclusive jurisdiction of the
Army Corps of Engineers. Id. at 1086. The Oregon Supreme Court allowed
review, 240 P.3d 1097 (Or. 2010), but later dismissed the petition for review as
moot after the permit expired by its own terms in 2010, 245 P.3d 130 (Or.
2010).
In 2010, DEQ issued another five-year general permit, tailored to match
the requirements set by the Court of Appeals in the NEDC case. Pet. App. C-4.
That permit, which expired at the end of 2014 (Pet. App. D-3), is the subject of
this case. Pet. App. H.
In the meantime, the state has also taken action under state law to
regulate suction dredge mining and mitigate its impacts on water quality. In
2013, the legislature adopted a moratorium on motorized mining in streams
containing salmon habitat and adjoining uplands. 2013 Or. Laws, ch, 783,
available at https://www.oregonlegislature.gov/bills_laws/lawsstatutes/
2013orLaw0783.pdf. In passing that law, the legislature found that the practice
had increased significantly in recent years, raising concerns about cumulative
6
impacts, and that the practice posed “significant risks to Oregon’s natural
resources, including fish and other wildlife, riparian areas, water quality, the
investments of this state in habitat enhancement and areas of cultural
significance to Indian tribes.” Id. § 1(4)–(5).
The moratorium was to remain in effect until January 2, 2021. Id. § 2.
The legislature directed the governor to consult with relevant state and federal
agencies, tribes, and affected stakeholders and propose a revised regulatory
framework. Id. § 8. In 2017, the legislature acted again, enacting a prohibition
on motorized mining operations in streams designated as “essential indigenous
anadromous salmonid habitat.” Or. Rev. Stat. § 468B.114(2). Motorized
mining is allowed in streams not so designated, provided that the operator has
an individual permit or is covered under a general permit. Or. Rev. Stat.
§468B.114(1). The legislation also imposes additional restrictions, such as
limiting the size of dredge hoses. Or. Rev. Stat. § 468.116. Miners challenged
the state law, but the Ninth Circuit held that it was a reasonable state
environmental regulation that was not preempted by federal mining laws, and
this Court denied review of that ruling. Bohmker v. Oregon, 903 F.3d 1029 (9th
Cir. 2018), cert. den., 139 S. Ct. 1621 (2019).
7
B.
The Oregon Supreme Court upheld DEQ’s authority to issue the
2010 permit allowing suction dredge mining under certain
conditions.
As noted earlier, in 2010 ODEQ exercised its authority under section 402
of the Clean Water Act to issue a new five-year general permit allowing smallscale suction dredge mining as long as it complied with water-quality standards.
Petitioners challenged the permit, arguing (among other things) that section 402
did not give DEQ authority to regulate their suction dredge mining. Pet. App.
C-5.
That challenge was still pending in the Oregon Court of Appeals at the
end of 2014, when the permit expired. Pet. App. C-6. That court held that the
case was moot and dismissed the appeal. Pet. App. D-4.
The Oregon Supreme Court reversed. Pet. App. C-14. The court agreed
with the Court of Appeals that the case was moot. Pet. App. C-8. But because
there is no “case or controversy” provision in the Oregon Constitution, Oregon
courts have the discretion, under certain circumstances, to decide moot cases.
Pet. App. C-10. Those circumstances are defined by a statute, Or. Rev. Stat.
§ 14.175, that sets forth a standard similar to but not exactly the same as the
capable-of-repetition-yet-evading-review standard that applies in federal court:
In any action in which a party alleges that an act, policy or practice
of a public body, as defined in ORS 174.109, or of any officer,
employee or agent of a public body, as defined in ORS 174.109, is
unconstitutional or is otherwise contrary to law, the party may
8
continue to prosecute the action and the court may issue a
judgment on the validity of the challenged act, policy or practice
even though the specific act, policy or practice giving rise to the
action no longer has a practical effect on the party if the court
determines that:
(1) The party had standing to commence the action;
(2) The act challenged by the party is capable of repetition, or the
policy or practice challenged by the party continues in effect; and
(3) The challenged policy or practice, or similar acts, are likely to
evade judicial review in the future.
Applying that standard, the Oregon Supreme Court held the case met the
statutory criteria and that the Court of Appeals therefore had the discretion to
decide to hear the case notwithstanding that it was moot. Pet. App. C-13. It
remanded the case to the Court of Appeals for that court to decide whether to
exercise that discretion. Id.
On remand, the Court of Appeals upheld the order and general permit.
Pet. App. B-27. The court determined that it would exercise its discretion to
consider a single issue: whether DEQ had authority, under Section 402 of the
Clean Water Act, to regulate turbid wastewater discharges from suction
dredges. Pet. App. B-16 to B-20. On that issue, the court adhered to its 2009
NEDC opinion, noting again that the EPA has consistently agreed that the
turbid wastewater discharge was a “pollutant” subject to regulation under
Section 402. Pet. App. B-21 to B-27.
9
The Oregon Supreme Court affirmed. Pet. App. A-3. The court rejected
petitioners’ argument that suction dredge mining did not add a pollutant to the
water. Pet. App. A-10. It agreed with the holding of Rybachek v. EPA, 904
F.2d 1276 (9th Cir. 1990), that even if the material discharged as a result of the
mining comes from the streambed itself, the resuspension of the material in the
water constitutes the addition of a pollutant that requires a permit. Pet. App. A6 to A-7. The court noted that the EPA confirmed that conclusion as recently as
2018, stating that no permit is necessary if “only water was picked up and
placed back within the same waterbody” but that when bed material is also
picked up with the water that causes the addition of pollutants to the stream.
Pet. App. A-7 to A-8.
The Oregon Supreme Court also rejected at much greater length a
separate argument that petitioners do not raise here: that the discharge from
suction dredge mining is a discharge of fill material regulated under section 404
of the Clean Water Act rather than under Section 402. Pet. App. A-10 to A-58.
One justice dissented as to that issue alone. Pet App. A-58 to A-76.
ARGUMENT
This Court should deny the petition for certiorari both because of
problems with using this case as a vehicle to decide the question presented and
because that question does not warrant this Court’s review. First, there is a
10
serious question whether this case is moot under Article III standards, even
though it satisfied the looser requirements for adjudication in state court. The
petition does not grapple with that question. Regardless whether mootness is a
jurisdictional problem here, it is a strong prudential reason to deny review.
Second, the question presented has limited practical significance to petitioners
because their mining activities can be (and are) regulated just as much under
state law. Finally, the Oregon Supreme Court’s decision does not conflict with
prior decisions of this court or decisions of the federal courts of appeals.
Whatever other issues may arise in interpreting the Clean Water Act, the courts
and the EPA agree that vacuuming up heavy metals and other materials from
the streambed, resuspending them in water, and then discharging the turbid
wastewater is the addition of a pollutant to the stream that requires a Clean
Water Act permit.
A.
There is a serious question whether this case is moot under Article
III standards.
The judicial power under Article III extends to “Cases” and
“Controversies.” A case that becomes moot at any point during the proceedings
is no longer a case or controversy for purposes of Article III. United States v.
Sanchez-Gomez, 138 S. Ct. 1532, 1537 (2018). There is an exception for a
controversy that is “capable of repetition, yet evading review.” Id. at 1540. But
that exception applies only if “(1) the challenged action is in its duration too
11
short to be fully litigated prior to its cessation or expiration, and (2) there is a
reasonable expectation that the same complaining party will be subjected to the
same action again.” Id. (emphasis added).
The same constraints do not apply in Oregon’s state courts. In particular,
the state capable-of-repetition exception to mootness does not require a
showing that the same party will again be affected by a similar action. Penn v.
Bd. of Parole & Post-Prison Supervision, 451 P.3d 589, 620 (Or. 2019).
Here, the permit that petitioners challenged expired in 2014. Pet. App.
D-3. The state courts nonetheless decided the case under the broader state
capable-of-repetition exception to mootness, on the ground that five years (the
permit’s length) is too short to allow full litigation of the permit’s validity. Pet.
App. C-12.
But it is unclear whether those circumstances would also satisfy Article
III’s stricter requirements. First, although this Court has held that duration of
less than two years may satisfy the evading-review prong, see Kingdomware
Technologies, Inc. v. United States, 136 S. Ct. 1969, 1976 (2016), the period of
time here—five years—is longer than anything this Court approved under that
prong. Second, there may be other procedural vehicles for addressing the
question presented that will not go moot when the permit expires. For example,
a challenge to a permit’s validity likely will not evade review, regardless when
12
the permit expires, if the challenger is fined for violating it and contests the
fine. Finally, the record does not reflect whether petitioners personally will be
affected by the permitting question in the future in light of the more recent state
laws restricting suction dredge mining in certain streams.
This Court’s precedents suggest that it cannot review a case that is moot
under Article III standards even if the state courts would choose to adjudicate
them. “Whatever the practice in the courts” of Oregon, “the duty of this Court
is to decide actual controversies by a judgment which can be carried into effect,
and not to give opinions upon moot questions or abstract propositions, or to
declare principles or rules of law which cannot affect the matter in issue in the
case before it.” Local No. 8-6, Oil, Chem. & Atomic Workers Int’l Union, AFLCIO v. Missouri, 361 U.S. 363, 367 (1960); see also Richardson v. Ramirez,
418 U.S. 24, 36 (1974) (“While the Supreme Court of California may choose to
adjudicate a controversy simply because of its public importance, and the
desirability of a statewide decision, we are limited by the case-or-controversy
requirement of Art. III to adjudication of actual disputes between adverse
parties.”); DeFunis v. Odegaard, 416 U.S. 312, 316 (1974). But cf. ASARCO
Inc. v. Kadish, 490 U.S. 605, 617–18 (1989) (holding that a state court
adjudication of a federal question can give rise to Article III standing even if the
plaintiff would not have met the requirements for standing in federal court).
13
But even if this case satisfied Article III requirements, either under the
capable-of-repetition exception or because the state court addressed the merits
of the federal issue, the serious mootness question would be a strong prudential
reason to deny review. It is all the more compelling a reason to deny review
when the petition does not grapple with the question or explain why the
mootness issue that the Court would inevitably have to confront warrants
review.
B.
The Clean Water Act question has little practical significance for
petitioners because their mining can be and is regulated under state
law.
This Court also should deny review because the question presented, even
if otherwise certworthy, will have limited forward-looking significance for
petitioners. Even if the Clean Water Act did not require them to get a section
402 permit to engage in suction dredge mining, the state could (and would)
insist that they get a materially identical permit under state law. It is of limited
practical significance whether the permit is required by federal or state law or
both.
At the time that this matter was filed, the regulations adopted by DEQ
were based on the authority delegated to states under the Clean Water Act. 33
U.S.C. § 1342(b). Since that time, the Oregon legislature has exercised its own
authority to impose stricter environmental regulations to protect sensitive fish
14
and other species. The Clean Water Act explicitly allows states to do so. 33
U.S.C. § 1370.
The fundamental premise advanced by the petitioners is that the Clean
Water Act does not authorize DEQ to regulate the discharge of the small
suction dredges that they operate. Even if that were true, the Oregon
Legislature required in 2013 and again in 2017 that operators of motorized instream dredges obtain a permit from DEQ. The current statute, Or. Rev. Stat.
§ 468B.114(1) states, “An operator may not allow a discharge to waters of the
state from a motorized in-stream placer mining operation or activity without
having an individual permit or being covered by a general permit issued under
ORS 468B.050.” The latter statute refers to water quality permits issued by
DEQ or, for agricultural operations within its delegated authority, the Oregon
Department of Agriculture. These Oregon statutes provide independent
authority to DEQ to regulate the discharge of turbid wastewater from motorized
suction dredges through a permit system. As a result, petitioners are subject to
the same requirements regardless whether those requirements arise under
federal or state law.
15
C.
The Oregon Supreme Court’s ruling is correct, matches the EPA’s
longstanding interpretation of the Clean Water Act, and does not
conflict with decisions of this Court or the courts of appeals.
Even if the procedural and practical reasons discussed above for denying
review were not present, the question presented here does not warrant this
Court’s review. The Oregon Supreme Court correctly held that discharging
turbid wastewater through suction dredge mining is the addition of a pollutant
to a stream that requires a permit under section 402. That uncontroversial
decision follows straightforwardly from the text of the Clean Water Act, is
consistent with the EPA’s interpretation of the statute and this Court’s
precedent, and neither creates nor implicates any circuit split.
1.
The Clean Water Act requires a person to obtain a permit, such as
a section 402 permit, to “discharge any pollutant.” 33 U.S.C. § 1311(a). The
term “discharge of a pollutant” is defined as “any addition of any pollutant to
navigable waters from any point source.” 33 U.S.C. § 1362(12). The definition
of “pollutant” includes “dredged spoil,” “rock,” and “sand,” and another section
of the Act expressly recognizes “suspended solids” as pollutants. 33 U.S.C.
§ 1314(a)(4), 1362(6).
Suction dredge mining involves vacuuming up water and sediment from
a streambed, running it over a sluice to remove some of the heavier metals, and
discharging the turbid wastewater back into a stream. Pet. App. A-3. There is
16
no dispute for purposes of this petition that the turbid wastewater is a pollutant,
the streams at issue are navigable waters, and the suction dredge is a point
source; the sole dispute is whether the mining causes the “addition” of the
pollutant to the waters. Petitioners argue that it does not because the suspended
solids in the wastewater came from the streambed, so they are merely moving
pollutants from one part of a waterbody to another part of the same waterbody.
Pet. 20. But as the Oregon Supreme Court correctly held, the turbid wastewater
that comes out of a suction dredge is not the same as what went in.
The court explained that “suction dredge mining adds suspended solids to
the water and can ‘remobilize’ heavy metals that otherwise would have
remained undisturbed and relatively inactive in the sediment of stream and river
beds.” Pet. App. A-10. It thus does not “merely transfer polluted water from
one part of the same water body to another.” Id. (brackets and quotation marks
omitted). Thus, even if the solids came from the streambed, “the suspension of
solids and the remobilization of heavy metals resulting from suction dredge
mining constitutes the ‘addition’ of a pollutant that requires a permit under the
Clean Water Act.” Id.
2.
The EPA has consistently interpreted the Clean Water Act the
same way. For decades, it has regulated the operation of suction dredges in the
states that have chosen not to accept a delegation of authority under section 402
17
of the Act. For example, in 2018, EPA issued a general permit for small
suction dredge operators in Idaho. See Pet. App. A-7 to A-8. The primary
pollutant of concern was described as suspended solids resulting from agitation
of the stream water and bed materials while processing it through the dredge.
EPA, IDG370000 Fact Sheet, at 8, available at https://www.epa.gov/sites/
production/files/2017-12/documents/r10-npdes-idaho-suction-dredge-gpidg370000-fact-sheet-2017.pdf (last visited Apr. 16, 2020). In describing the
permit, EPA stated:
Operators of small suction dredges in Idaho must obtain NPDES
permit coverage. The permit places conditions on the discharge of
rock and sand from each mining operation to protect water quality
and aquatic resources. These conditions include best management
practices and prohibited areas.
EPA, NPDES General Permit for Small Suction Dredge Placer Mining in
Idaho, available at https://www.epa.gov/npdes-permits/npdes-general-permitsmall-suction-dredge-placer-miners-idaho (last visited Apr. 16, 2020). In
response to a comment similar to the argument made here, that suction dredging
simply moves material from one place to another within the same body of
water, EPA explained the difference between merely moving water around and
manipulating it to make it more turbid:
If, during suction dredging, only water was picked up and placed
back within the same waterbody, the commenter would be correct
that no permit would be necessary. However, in suction dredging,
bed material is also picked up with water. Picking up the bed
18
material is in fact the very purpose of suction dredging – the bed
material is processed to produce gold. This process is an
intervening use that causes the addition of pollutants [rock and
sand, see CWA § 502(6)] to be discharged to waters of the United
States. As a result, the water transfer exclusion in 40 CFR 122.3(i)
does not apply, and an NPDES permit is required for the discharge
from this activity.
EPA, Response to Comments, at 6 (May 2018), available at
https://www.epa.gov/sites/production/files/2018-05/documents/r10-npdesidaho-suction-dredge-gp-idg370000-rtc-2018.pdf (last visited Apr. 29, 2020)
(citation omitted; brackets in original).
This Court often pays particular attention to the views of the agencies
charged with enforcing legislation, “in light of the agency’s expertise in a given
area, its knowledge gained through practical experience, and its familiarity with
the interpretive demands of administrative need.” County of Maui v. Hawaii
Wildlife Fund, __ U.S. __ (slip op. at 12) (April 20, 2020). EPA has
consistently treated the material emitted from small suction dredges is a
pollutant to be regulated under Section 402 of the Clean Water Act. EPA’s
views confirm that the Oregon Supreme Court ruled correctly here.
3.
The Oregon Supreme Court’s ruling is consistent with this Court’s
precedent under the Clean Water Act. Petitioners argue that the ruling conflicts
with two of this Court’s opinions (Pet. 14–16), but neither addressed the issue
presented here.
19
In South Florida Water Management Dist. v. Miccosukee Tribe of
Indians, 541 U.S. 95 (2004), the dispute was about whether a permit was
needed when a water district pumped water from a canal into a reservoir a short
distance away. This Court ultimately remanded to the district court for further
factual development about whether the canal and the reservoir were distinct
water bodies. Id. at 99. The parties agreed that no permit was required if they
were a single waterbody: “if one takes a ladle of soup from a pot, lifts it above
the pot, and pours it back into the pot, one has not ‘added’ soup or anything else
to the pot.” Id. at 110 (quoting Catskill Mountain Chapter of Trout Unlimited,
Inc. v. City of New York, 273 F.3d 481, 492 (2d Cir. 2001)) (brackets omitted).
The ladle analogy explains why a permit is not needed when a point
source (the ladle) merely takes water (soup) from a body (pot) and moves it to
unchanged to another part of the body. Here, however, suction dredge mining
does not take a ladle of “soup” (clean water) from the stream and redeposit it. It
takes the soup, mixes it with sediment that was not in the water, and pours the
turbid mixture with suspended solids it back into the pot. It is not the simple
movement of water from one place in a stream to another. South Florida Water
Management did not address anything like the activity at issue here.
Neither did Los Angeles County Flood Control Dist. v. Natural
Resources Defense Council, Inc., 568 U.S. 78 (2013). The question presented
20
there was, “Under the CWA, does a “discharge of pollutants” occur when
polluted water ‘flows from one portion of a river that is navigable water of the
United States, through a concrete channel or other engineered improvement in
the river,’ and then ‘into a lower portion of the same river’?” Id. at 82. This
court held that “no discharge of pollutants occurs when water, rather than being
removed and then returned to a water body, simply flows from one portion of
the water body to another.” Id. at 83. But suction dredge mining does not
involve water “simply flow[ing] from one portion of the water body to
another.” It removes material from a stream and its streambed, processes the
material, and returns the result to a stream in an entirely different state than it
entered.
4.
Finally, petitioners are incorrect in asserting that there is an
“entrenched conflict” between decisions of federal circuit courts of appeal
about the question presented here. Pet. 17. To the contrary, those courts that
have considered the issue presented here—whether suction dredge mining
causes the addition of a pollutant that requires a Clean Water Act permit—have
uniformly decided the issue in the same way that the Oregon Supreme Court
did. There is no conflict that requires resolution by this court.
In Rybachek, the Ninth Circuit squarely addressed the issue presented
here and rejected the argument that suction dredge mining does not add any
21
pollutant to the water. 904 F.2d at 1286. Citing cases from the Fifth and
Eleventh Circuits, as well as EPA’s longstanding interpretation, the court
concluded that “resuspension” of solids in the wastewater from the dredge was
within Section 402’s purview as discharge of pollutants from a point source. Id.
at 1285–86.
The decision in Rybachek is not at odds with National Wildlife
Federation v. Gorsuch, 693 F.2d 156 (D.C. Cir. 1982). There, the court
adopted an interpretation set forth by the EPA that the discharge from
hydroelectric dams did not introduce “pollutants” into the water. Id. at 161.
The question turned on whether low dissolved oxygen, cold, or supersaturation
are pollutants, and whether “addition” of those qualities was a discharge from a
point source under Section 402. Id. at 171–75. The court deferred to EPA’s
longstanding position, since the Act was adopted, that dams are not subject to
Section 402. Id. at 171. EPA’s position was reasonable, because unlike the
pollutants in this case (dredged spoil, rock, and sand), the conditions brought
about by dams were not listed as pollutants in the Act, and they were conditions
rather than substances. Id. at 171; see also National Wildlife Fed. v. Consumers
Power Co., 862 F.2d 580 (6th Cir. 1988) (adopting EPA’s distinction between
facilities that remove fish from water and discharge dead fish from a facility
that, in the process of moving water, causes some fish mortality).
22
The other cases that petitioners cite to support the argument that there is a
circuit split are not to the contrary. Petitioner refer to a selective quote in
United States v. Law, 979 F.2d 977 (4th Cir. 1992), but the holding in that
case—affirming a felony conviction for discharging pollutants without a
Section 402 permit—confirms rather than conflicts with the consistent position
of the federal courts of appeals. Similarly, in Catskill Mountains, 273 F.3d 481,
the Second Circuit held that a discharge of water containing sediments from a
tunnel into a creek was a discharge of pollutants. And National Mining
Association v. U.S. Army Corps of Engineers, 145 F.3d 1399 (D.C. Cir. 1998),
dealt with incidental fallback of dredged material from a permitted dredging
operation. The court held that fallback of material into the same place from
where it was removed is not a discharge of pollutants. That case did not
address the discharge of suspended solids creating a turbid plume.
The federal appellate courts have consistently held that the movement of
suspended materials such as dredge spoil, soil, and rock—as opposed to the
mere movement of water from one place to another—creates the discharge of a
pollutant that is subject to the requirements of the Clean Water Act. Whatever
other disagreements there may be about how to interpret the Clean Water Act,
the question presented here does not implicate any circuit split that requires
resolution by this court.
23
CONCLUSION
The petition for a writ of certiorari should be denied.
Respectfully submitted,
ELLEN F. ROSENBLUM
Attorney General
/s/ Benjamin Gutman
_________________________________
BENJAMIN GUTMAN
Solicitor General
benjamin.gutman@doj.state.or.us
DENISE G. FJORDBECK
Attorney-in-Charge
denise.fjordbeck@doj.state.or.us
Attorneys for Respondents
DGF:aw2/10227390
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.