Appendix — City of New York, New York v. Catskill Mountain Chapter of Trout Unlimited (No. 06-729)
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No. OFFI. JF “HE CLERK
IN THE
SUPREME COURT OF THE UNITED STATES
Ciry OF NEW YORK, NEW YorK City DEPARTMENT OF
ENVIRONMENTAL PROTECTION, and JOEL A. MIELE, SR..,
Commissioner of Department of Environmental Protection.
Petitioners,
“V.-
CATSKILL MOUNTAINS CHAPTER OF TROUT UNLIMITED, LTD.,
THEODORE GORDON FLYFISHERS, INC., CATSKILL-DELA WARE
NATURAL WATER ALLIANCE, INC., FEDERATED SPORTSMEN’S
CLUBS OF ULSTER COUNTY, INC., RIVERKEEPER, INC., STATE OF
NEW YORK, NEW YORK STATE DEPARTMENT OF
ENVIRONMENTAL CONSERVATION, and ERIN M. CROTTY,
Commissioner of the New York State Department of
Environmental! Conservation,
Respondents.
On Petition for a Writ of Certiorari to the
United States Court of Appeals for the Second Circuit
APPENDIX TO PETITION FOR A WRIT OF
CERTIORARI
LEONARD J. KOERNER,* MICHAEL A. CARDOZO,
HILARY MELTZER, Corporation Counsel of the
WILLIAM S. PLACHE, City of New York
BRIDGET EICHINGER.** 100 Church Street
of Counsel. New York, NY 10007
*Counsel of Record (212) 788-1585
** Awaiting Admission
November 20, 2006
. APPENDIX TO PETITION
FOR WRIT OF CERTIORARI
TABLE OF CONTENTS
Decision of the United States
Court of Appeals for the Second
Circuit, Dated June 13, 2006
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Memorandum-Decision and Order of the United States
District Court for the Northern District
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Decision and Order of the United States
District Court for the Northern District
of New York, Dated January 19, 2001 ...............:ccececcsseeeseees
Decision of the United States
Court of Appeals for the Second
Circuit, Dated October 3, 2001
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Order of the United States
District Court for the Northern District
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Memorandum-Decision and Order of the United States
District Court for the Northern District
of New York, Dated ;
February 6, 2003 (Reported at 244 F. Supp. 2d 41) ..............
Ordez and Amended Judgment of the United States
District Court for the Northern District
of New York, Dated October 23, 2006 ..................c0cccseccseeees
Order of the United States
Court of Appeals for the Second
Circuit, On Petition for Rehearing and Rehearing
ee 2, CUED ssvcereceeseecoccsesesevecevesvsovecsoeserss A139
Relevant Provisions of Federal Water
ec sconuovevevoreveoneseers A143
United States Environmental Protection Agency,
Notice of Proposed Rulemaking, National Pollutant
Discharge Elimination System (NPDES)
Water Transfers Proposed Rule,
71 Fed. Reg. 32, 887, (proposed June 7, 2006)
(to be codified at 40 C.F.R. pt. 122)
(“Notice of Proposed Rulemaking”’)...............::ccsceseeeeeeeees Al?70
Ann Klee & Benjamin Grumbles, United States
Environmental Protection Agency,
Agency Interpretation on Applicability of
Section 402 of the Clean Water Act to Water Transfers
(Aug. 5, 2005) (“EPA Interpretation”) ................:cccesseeeeeeeees A205
DECISION OF THE UNITED STATES
COURT OF APPEALS FOR THE SECOND
CIRCUIT, DATED JUNE 13, 2006
(Reported at 451 F.3d 77)
REPRODUCED FOLLOWING
Al
UNITED STATES COURT OF APPEALS
FOR THE SECOND CIRCUIT
August Term 2005
(Submitted: November 21, 2005
Decided: June 13, 2006)
Docket Nos. 03-7203 (L); 03-7253 (XAP)
CATSKILL MOUNTAINS CHAPTER OF TROUT
UNLIMITED, INC., THEODORE GORDON
FLYFISHERS, INC., CATSKILL-DELAWARE
NATURAL WATER ALLIANCE, INC., FEDER-ATED
SPROTSMEN’S CLUBS OF USLTER COUNTY, INC.
and RIVERKEEPER, INC.,
Plaintiffs-Appellees-Cross-Appellants,
- VY .7
CITY OF NEW YORK and NEW YORK CITY
DEPARTMENT OF ENVIRONMENTAL
PROTECTION,
Defendants-Third-Party-Plaintiffs-
Appellants-Cross-Appellees,
JOEL A. MIELE, SR., COMMISSIONER of the
Department of Environmental Protection,
Defendant-Appellant-Cross-Appellee,
- V. -
STATE OF NEW YORK, NEW YORK STATE
DEPARTMENT OF ENVIRONMENTAL CONSERVA-
TION, and ERIN M. CROTTY, Commissioner of the
A2
New York State Department of Environmental
Conservation,
Third-Party-Defendants-Appellees.
Before:
WALKER, Chief Judge,
OAKES and JACOBS, Circuit Judges.
Appeal from a decision of the United States District
Court for the Northern District of New York (Frederick J.
Scullin, Jr., Chief Judge) holding the City of New York
liable for violations of the Clean Water Act, imposing civil
penalties, and awarding injunctive relief to Plaintiffs-
Appellees-Cross-Appellants.
AFFIRMED in part and REMANDED in part.
KARL S. COPLAN, Pace _ Environmental
Litigation Clinic, Inc. (Kara E. Murphy, Legal
Intern, on the brief), White Plains, New York,
for Plaintiffs-Appellees-Cross-Appellants.
HILARY MELTZER, Assistant Corporation
Counsel (Michael A. Cardozo, Corporation
Counsel of the City of New York, William S.
Plache, on the brief), New York, New York,
for Defendants’ -Third- Party-Plaintiffs-
Appellants-Cross-Appellees. |
JAMES M. TIERNEY, Assistant Attorney
General (Eliot Spitzer, Attorney General of the
State of New York, Michelle Aronowitz,
Deputy Solicitor General, Peter H. Lehner,
A3
Chief, Environmental Protection Bureau,
Gordon J. Johnson, Deputy Bureau Chief,
Robert H. Easton, Assistant Solicitor General,
on the brief), Albany, New York, for Third-
Party-Defendants-Appellees.
JOHN M. WALKER, JR., Chief Judge:
The City of New York (“the City”) operates the
Shandaken Tunnel (“Shandaken Tunnel” or “the Tunnel”)
as part of its water-management system that delivers
drinking water to New York City and the immediate
surrounding area. Water from the Tunnel, which is high in
turbidity, discharges into the Esopus Creek (“Esopus
Creek” or “the Creek’’), a trout stream used for flyfishing
and other recreational activities. The Catskill Mountains
Chapter of Trout Unlimited, Inc., Theodore Gordon
Flyfishers, Inc., Catskill-Delaware Natural Water Alliance,
Inc., Federated Sportsmen’s Clubs of Ulster County, Inc.,
and Riverkeeper, Inc. (collectively “Catskills”) brought a
citizen suit against the City, alleging that the City’s use of
the Tunnel without a permit violated the Clean Water Act
(“CWA” or “Act”), 33 U.S.C. §§ 1251 et seq. In an
October 21, 2001, opinion, we held that the CWA permit:
requirements apply to the Shandaken Tunnel discharges
and remanded to the district court. On remand, the district
court assessed a $5,749,000 civil penalty against the City
and ordered the City to obtain a permit for the operation of
the Tunnel. This appeal followed.
BACKGROUND
I. Relevant Clean Water Act Provisions
The purpose of the CWA is “to restore and maintain
the chemical, physical, and biological integnty of the
Nation’s waters.” 33 U.S.C. § 1251(a). As part of the
program to achieve this goal, the Act states that “the
discharge of any- pollutant by any person shall be
unlawful,” id. § 1311(a), unless it is done in compliance
with other provisions of the Act. One of those other
provisions, the National Pollutant Discharge Elimination
System (“NPDES”), id. § 1342(a), establishes a permit
system. Under this provision, the Environmental Protection
Agency (“EPA”) or state administrators may issue a permit
for the discharge of a pollutant at levels below the effluent
limitations specified in the permit. Jd. The CWA broadly
defines “discharge of a pollutant” as “any addition of any
pollutant to navigable waters from any point source.” /d. §
1362(12).
Although the CWA establishes this federal
permitting scheme, the Act also recognizes that states retain
the primary role in planning the development and use of
land and water resources, id. § 1251(b), allocating
quantities of water within their jurisdictions, id. § 1251(g),
and regulating water pollution, as long as those state
regulations are not less stringent than the requirements set
by the CWA, id. § 1370.
Il. The Shandaken Tunnel and the Esopus Creek
As part of the water system that supplies New York
City with its dmnking water, the City maintains the
Schoharie Reservoir in the Catskill Mountains. To deliver
this water eventually to New York City, water from the
Schoharie Reservoir is diverted through the eighteen-mile
Shandaken Tunnel and discharged into the Esopus Creek.
The Creek’s water, in tum, flows into the Ashokan
Reservoir, through the Catskill Aqueduct, to a series of
reservoirs and tunnels along the east side of the Hudson
River, and eventually to New York City. Absent the man-
made diversion through the Tunnel, water from the
Schoharie Reservoir would never reach the Esopus Creek.
Catskill Mountains Ch. of Trout Unltd. v. City of New York,
273 F.3d 481, 484 (2d Cir. 2001) (“Catskills I’’).
Because water in the Schoharie Reservoir contains
suspended solids from both natural and man-made causes,
discharges from the Tunnel into the Creek are more turbid’
than the waters of the Esopus. This turbidity impairs use of
the Esopus for fly fishing and other recreational activities.
Pursuant to state regulations, the City has been studying
ways to reduce the turbidity in the water discharged from
the Tunnel but so far has failed to find a way to do so. Until
this lawsuit, neither the EPA nor the New York State
Department of Environmental Conservation (“NYDEC’”),
the agency that enforces the CWA in New York State, had
ever regulated the turbidity in the Tunnel under the CWA’s
permitting scheme.
Ill. Procedural History
In March 2000, Catskills, recreational users of the
Esopus Creek, brought this citizen suit under the CWA
alleging that the City’s discharge of turbid water from the
Tunnel violated 33 U.S.C. § 1311(a), which, as we said,
prohibits “the discharge of any pollutant” ‘without a
discharge permit. The district court dismissed the claim on
the pleadings, holding that the discharge from the Tunnel
did not constitute an ‘“‘addition” of a pollutant to the Creek
under 33 U.S.C. § 1362(12).
' The parties do not contest that turbidity qualifies as a pollutant under
the CWA.
A6
In October 2001, we reversed after concluding that
the discharge of water containing pollutants from one
distinct water body into another is an “addition of [a]
pollutant” under the CWA. Catskills /, 273 F.3d at 491-93.
As a result, we determined that the discharge from the
Tunnel into the Creek requires a permit.
On remand from Catskills J, the district court
granted summary judgment to the plaintiffs and went on to
deter-mine the civil penalties to be assessed against the
City. The district court concluded that no penalties should
be imposed for the City’s actions prior to June 22, 2002,
eight months after Catskills / put the City on notice that it
needed a permit for the Shandaken discharges. Finding a
delay of more than eight months unreasonable, however,
the district court imposed the maximum penalty for the
period from June 22, 2002, to December 31, 2002, when
the City filed its permit application; the penalty totaled
$5,749,000. This appeal followed.
DISCUSSION
In this appeal, the City asks us to reconsider our
holding in Catskills J that the discharge of turbid water
from the Shandaken Tunnel into the Esopus Creek requires
a permit. The City also argues that the penalty of
$5,749,000 is too high. In a cross-appeal, Catskills argues
that amount Is too low.
We are free to reconsider our holding in Catskills /
if there are cogent, compelling reasons for doing do, such
as a change in controlling law or newly discovered facts.
United States v. Tenzer, 213 F.3d 34, 39 (2d Cir. 2000).
Determining whether we should reconsider requires briefly
revisiting our reasoning in Catskills 1.
I. Catskills I
In concluding that the transfer of turbid water from
the Shandaken Tunnel to the Esopus Creek qualified as the
“discharge of [a] pollutant,” 33 U.S.C. § 131 | (a), requiring
an NPDES permit, Catskills I first noted the CWA’s broad
definition of the “discharge of a pollutant” as “any addition
of any pollutant to navigable waters from any point
source.” /d. § 1362(12). Because the Shandaken Tunnel
“plainly qualifies as a point source,” Catskills I, 273 F.3d at
493, our holding rested, in principal part, on the meaning of
“addition,” which the CWA leaves undefined. We decided
that “‘addition” means the introduction into navigable water
from the “outside world,” with the outside world being
defined as “any place outside the particular water body to
which pollutants are introduced.” /d. at 491.
In reaching this result, we distinguished the “dams
cases,” on which the City relied. In National Wildlife
Federation v. Gorsuch,’ 693 F.2d 156 (D.C. Cir. 1982), and
National Wildlife Federation v. Consumers Power Co. by
862 F.2d 580 (6th Cir. 1988), two sister circuits held that
water taken from a water source and then released back into
> This phrase comes from the definition of the word “addition” urged
by the EPA on the court in National Wildlife Federation v. Gorsuch,
693 P.2d 156, 175 (D.C. Cir. 1982). In Gorsuch, the EPA argued that
an “addition of a pollutant” takes place only if the point source
introduces a pollutant into the water from the outside world. /d.
* Gorsuch involved water released from a dam that, due to its impound-
ment, had a low dissolved oxygen rate, variable water temperature,
high concentrations of dissolved minerals and nutrients, increased
sediment levels, and was supersaturated with air---attributes that can be
harmful to downstream waters and the wildlife inhabiting them. /d. at
161-64.
* Consumers Power involved water pumped from Lake Michigan
through the turbines of a hydroelectric power plant and then released
back into the lake-a process that pureed fish and other aquatic life and
then released their remains as “polluiants” back into the lake. 862 F.2d
at 583.
that same source was not an “addition” to navigable waters
under the CWA, despite the fact that the water so released
contained “pollutants.” 693 F.2d at 183; 862 F.2d at 587.
This case differed from the dams cases, we believed,
because the Tunnel discharges water into the Creek from a
source that is a different, distinct body of water. Catskills I,
273 F.2d at 491-92. In Catskills I, we analogized the dams
cases to a soup ladle scooping soup out of a pot and
returning it to that pot, a type of water transfer known as an
intrabasin transfer. The Tunnel’s discharge, in contrast,
was like scooping soup from one pot and depositing it in
another pot, thereby adding soup to the second pot, an
interbasin transfer. Interbasin transfers, we held in Catskills
/, constitute “additions,” rendering the City’s reliance on
the dams cases misplaced. /d. at 492.
We also rejected the City’s “unitary water” theory
of navigable waters, which posits that all of the navigable
waters of the United States constitute a single water body,
such that the transfer of water from any body of water that
is part of the navigable waters to any other could never be
an “addition.” We pointed out that this theory would lead
to the absurd result that the transfer of water from a heavily
polluted, even toxic, water body to one that was pristine via
a point source would not constitute an “addition” of
pollutants and would not be subject to the CWA’s NPDES
permit requirement. /d. at 493. Catskills I rejected the
“unitary water” theory as inconsistent with the ordinary
meaning of the word “addition.” /d.
Finally, we rejected the contention that the
provisions of the CWA reserving power to the states could
overcome the express permit requirement for water
transfers that result in the addition of pollutants. We
pointed out that “like many complex statutes ... the CWA
balances a welter of consistent and inconsistent goals” but
that “none of the statute’s broad purposes sways us from
what we find to be the plain meaning of its text.” /d. at 494.
AQ
Il. Intervening Legal Developments
Following Catskills I, there have been two relevant
legal developments. The Supreme Court decided South
Florida Water Management District v. Miccosukee Tribe of
Indians, 541 U.S. 95 (2004), and the EPA issued an agency
interpretation addressing the applicability of the CWA’s
NPDES permit requirement to water transfers such as the
one at issue in this case.
Miccosukee was a citizen suit contending that an
NPDES permit is necessary for the South Florida Water
Management District to operate a pump that conveys water
from a polluted canal to an undeveloped wetland. The
pump serves both to prevent the basin surrounding the
canal from flooding and to preserve the wetland area. /d. at
100-01. Consistent with the dams cases, Miccosukee held
that if the canal and the wetlands are not meaningfully
distinct water bodies-an unresolved factual question-no
NPDES permit is required. /d. at 112; cf S.D. Warren Co.
v. Me. Bd. of Envtl. Prot., 126 S. Ct. 1843, 1850 (2006)
(“[I]f two identified volumes of water are simply two parts
of the same water body, pumping water from one into the
other cannot constitute an “addition” of pollutants.”
(quoting Miccosukee, 541 U.S. at 109) ).
On August 5, 2005, the EPA issued an agency
interpretation regarding whether the movement of
pollutants by a water transfer from one navigable water to a
separate one is the “addition” of a pollutant subjecting the
activity to the NPDES permitting requirement. According
to the EPA, several provisions of the CWA indicate
Congress’s intent that such transfers be regulated by the
states, not by the federal NPDES program. The EPA
interpretation argues that, rather than primarily focusing on
the meaning of the word “addition,” as we did in Catskills
I, a “holistic” view of the statute that takes this intent into
account is appropriate.
The City concedes that this EPA interpretation is
not entitled to Chevron deference. See Chevron U.S.A., Inc.
v. Natural Res. Def., 467 U.S. 837 (1984). Instead, the
deference described in Skidmore v. Swift & Co., 323 US.
134 (1944), and United States v. Mead Corp., 533 U.S. 218
(2001), is applicable. We thus defer to the agency interpre-
tation according to its “‘power to persuade.”” Mead, 529
U.S. at 235 (quoting Skidmore, 323 U.S. at 140).
III. Reconsideration of Catskills I
We turn to the City’s request that we reconsider our
holding in Catskills /. Rather than offering “compelling and
cogent” reasons for reconsideration, however, the City
basically serves us warmed-up arguments that we rejected
in Catskills [, with the additional contention that either the
Supreme Court’s Miccosukee decision, the EPA interpreta-
tion, or both compel a result different from the one we
reached earlier. We disagree.
The City first argues that new evidence developed
below and the Supreme Court’s decision in Miccosukee
invalidate the distinction between intrabasin and interbasin
water transfers. The “new evidence” the City points to
simply shows that the release of water from a dam into
down-stream water is no less likely to add pollutants as
would a transfer of water from a distinct water body.
Having considered the dams cases in Catskills I, we were
aware of the presence of pollutants in intrabasin transfers.
Gorsuch includes an extensive discussion of the nature of
water quality changes wrought by dammed water. 693 F.2d
at 161-64. And in Consumers Power, the water at issue
contained fish that were pulverized as they passed through
the turbines of a hydroelectric power plant and then were
reintroduced into Lake Michigan as biological waste. 862
F.2d at 582. Nonetheless, Catskills | concluded that, despite
the presence of pollutants in both interbasin and intrabasin
transfers, interbasin transfers are properly distinguished
All
because they “‘add” pollutants to the navigable waters. See
Catskills ', 273 F.3d at 492. This has not changed.
Nor does the Supreme Court’s decision in
Miccosukee render inter- and _ intra-basin _ transfers
indistinguishable. Miccosukee cited with approval our
“soup ladle” analogy and the distinction between inter- and
intra-basin transfers. 541 U.S. at 109-10. The Court
remanded the case to the district court to determine whether
the water bodies in question were “two pots of soup, not
one.” /d.; cf. S.D. Warren Co., 126 S. Ct. at 1850 n.6. This
remand would be unnecessary if there were no legally
significant distinction between inter- and _intra-basin
transfers.
The City also reasserts the unitary-water theory of
navigable waters. Our rejection of this theory in Catskills 1,
however, is supported by Miccosukee, not undermined by
it. In that case, the Supreme Court pointed out that several
provisions of the CWA seem to distinguish among water
bodies that are part of the navigable waters of the United
States, implying that, at least in the context of the CWA,
the unitary-water theory has no place. 541 U.S. at 105-09.
Miccosukee also noted that the EPA has never endorsed the
theory in any administrative documents. /d. at 107. Indeed,
the Supreme Court pointed out that “the agency once
reached the opposite conclusion.” /d. Thus, Miccosukee did
no more than note the existence of the theory and raise
possible arguments against it. This does not constitute a
change of controlling jaw warranting reconsideration of
this court’s previous decision on the issue.
Finally, the City points to the “holistic” argument,
reflected in the EPA’s 2005 agency interpretation,” to assert
> As noted above, the EPA’s agency interpretation is entitled to
deference only insofar as it has the power to persuade. See Skidmore,
323 US. at 140. Because the EPA and the City assert the same
Al2
that the proper allocation of rights and responsibilities
between the states and the federal government for water
regulation necessitates a reconsideration of our holding in
Catskills I. This proposition is supported by amicus curiae
briefs filed by western states who fear that the Catskills ]
rule will upend state regulation of water rights.
The argument relies on sections 101(g) and 510 of
the CWA, 33 U.S.C. §§ 1251(g), 1370, both of which
expressly reserve the authority of states over the water
within their jurisdiction, as well as section 304(f) of the
CWA, 33 U.S.C. § 1314(f), which governs non-point-
source pollution. Section 101(g) provides that “the
authority of each State to allocate quantities of water within
its jurisdiction shall not be superseded, abrogated or
otherwise impaired.” Section 510 states that “[e]xcept as
expressly provided in this chapter, nothing in this chapter
shall . . . be construed as impairing or in any manner
affecting any nght or jurisdiction of the States with respect
to the waters . :. of such States.” Because, according to the
City, there are no feasible means of reducing the pollution
in the Tunnel, a permit requirement would effectively
amount to a ban on the transfer of water from the Tunnel to
the Creek and thereby interfere with New York’s statutory
water allocation rights.
This argument, too, was raised by the City in
Catskills I, albeit less elaborately, and, as with the.
interbasin/ intrabasin distinction and the unitary-waters
theory, Miccosukee fails to alter the legal landscape to
support the “holistic” theory. The power of the states to
allocate quantities of water within their borders is not
contentions on this point, we address the City and the EPA’s position
as one. For reasons discussed below, we do not find the argument
persuasive and therefore decline to defer to the EPA.
Al3
inconsistent with federal regulation of water quality.
Section 510 provides for the prescrvation of the preexisting
rights of states not in conflict with the other requirements
of the CWA (“except as expressly proved in this chapter”).
Indeed, the Supreme Court has held that “{s]ections 101(g)
and 510(2) preserve the authority of each State to allocate
water quantity as between users; they do not limit the scope
of water pollution controls...” PUD No. 1 v. Wash. Dep't
of Ecology, 511 U.S. 700, 720 (1994)., To be sure,
Miccosukee acknowledged the possibility that “construing
the NPDES program to cover such transfers would . . . raise
the costs of water distribution prohibitively, and violate”
section 101(g). Miccosukee, 541 U.S. at 108. But in the
next sentence, the Court recognized that, despite their
potential cost, such permits nevertheless might be neces-
sary to protect water quality. /d.
Nor does Miccosukee support the EPA and the
City’s argument that the non-point-source provisions of the-
CWA indicate congressional intent to leave interbasin
water transfers outside the NPDES permitting scheme.
Section 304(f) of the CWA directs the EPA to study and
make recommendations for the regulation of pollutants
spread by non-point sources, such as “changes in the
movement, flow, or circulation of any navigable waters or
ground waters, including changes caused by the
construction of . . . flow diversion facilities.” 33 U.S.C. §
1314(f)(2)(F). From this language, the EPA and the City
claim that Congress intended that changes in the circulation
of navigable waters caused by the construction of “flow
diversion facilities,” such as the Tunnel, be exempt from
the permit requirements that apply to point sources. As the
Supreme Court pointed out in Miccosukee, however,
“1314(f(2)(F) does not explicitly exempt nonpoint
pollution sources from the NPDES program if they also fall
within the ‘point source’ definition.” 541 U.S. at 106.
In the end, while the City contends that nothing in
the text of the CWA supports a permit requirement for
interbasin transfers of pollutants, these “holistic” arguments
about the allocation of state and federal nghts, said to be
rooted in the structure of the statute, simply overlook its
plain language. NPDES permits are required for “the
discharge of any pollutant,” 33 U.S.C. § 1311(a), which is
defined as “any addition of any pollutant to navigable
waters from any point source,” id. § 1362(12). It is the
meaning of the word “addition” upon which the outcome of
Catskills I turned and which has not changed, despite the
City’s attempts to shift attention away from the text of the
CWA to its context. In Catskills I, we pointed out. that
complex statutes often have seemingly inconsistent goals
that must be balanced. 273 F.3d at 494. The CWA seeks to
achieve water allocation goals as well as to restore and
maintain the quality of the nation’s waters. The City and
the EPA would have us tip the balance toward the alloca-
tion goals. But in honoring the text, we adhere to the
balance that Congress has struck and remains free to
change.
The City’s final argument for reconsideration is that
other provisions of federal and state law are more appropri-
ate means of regulating the water discharged from the
Shandaken Tunnel. The City points to the Safe Drinking
Water Act, which limits the levels of contaminants that are
allowed in public drinking water; section 303(d) of the
CWA, which regulates pollution levels resulting from
pollution from both point and non-point sources; and
various provisions of state law that regulate water quality.
While these provisions no doubt contribute to the goals of
pollution reduction and regulation, the City does not
explain how their existence invalidates a separate, inde-
pendent requirement imposed by the permitting scheme of
the CWA.
Al5
The City’s plea for reconsideration appears to rest
upon the assumption that regulating the discharge from the
Tunnel would effectively require that the flow be stopped
altogether. This claim seems to us exaggerated. We think
the flexibility built into the CWA and the NPDES permit
scheme, a flexibility that the City has endorsed in a related
proceeding,® will allow federal authority over quality
regulation and state authority over quantity allocation to
coexist without materially impairing either.
We conclude this section with a somewhat detailed
and technical accounting of the flexibilities that exist.
Effluent limitations contained in NPDES permits fall into
two categories: technology-based effluent _limits’
(“TBELs”) and water-quality-based effluent limits
(“WQBELs”).® Where, as here, no applicable national
TBELs have been set, the permit-writer may set TBELs
using best professional judgment. See 33 US.C. §
1342(a)(1)(B); 40 C.F.R. § 125.3. In doing so, NYDEC will
consider the available technologies, costs in relation to
effluent reduction benefits, engineering aspects of various
control techniques, available best management practices,
and nonwater-quality environmental impacts. See 40 C.F.R.
§ 125.3(c), (d). This process thus affords the permit-writer
“considerable flexibility in establishing permit terms and
* The City has acknowledged the NPDES system's flexibility in hear-
ings related to its permit application. See /n re Application of the New
York Cite Department of Environmental Protection, DEC Application
No. 3-5150-00420/0000!1, 2005 N.Y. Envy. Lexis 40, at *24, *26 (June
27, 2005) (Ruling on Issues and Party Status).
’ Technology-based limits are based on the effluent levels that can be
achieved through the use of various water treatment technologies. See
40 CFR. § 125.3.
* Water-quality-based limits are those limits needed to ensure the
appropriate water quality of the receiving water body. That water
quality is specified by the state in which the water body is located.
conditions.” EPA, NPDES Permit Writers’ Manual 69
(1996). Only if the TBELs established by the NYDEC
prove insufficient to achieve the water quality standards set
by the state for the Esopus Creek’ will more stringent
WOBELs be adopted. 33 U.S.C. § 1312(a); 40 C.F.R. §
122.44(d).
If the City is unable to comply with the effluent
limitations adopted by the NYDEC, CWA provisions and
implementing regulations still provide means of enabling
the NYDEC to issue a valid permit to the City. The permit
may include a schedule of compliance, allowing the
permittee to achieve compliance over time. 33 U.S.C. §
1362(17); 40 C.F.R. § 122.47. Indeed, the current draft
permit prepared by the NYDEC in this case includes a
compliance schedule that requires the City to investigate
both technological and structural solutions to the turbidity
problem and to implement those solutions according to a
specified schedule. See NYS Env. Notice Bulletin, Notice
of Completed Application for Shandaken Tunnel Outlet 7-9
(August 4, 2004).
Second, the NYDEC may allow a variance to
WQBELs if the permittee demonstrates that achieving the
effluent limitation contained in the permit is not feasibie.
40 C.F.R. § 131.13; N.Y. Comp. Codes R. & Regs. tit. 6, §
702.17(b).'° A variance is temporary and must include
” With respect to turbidity for water bodies like the Esopus Creek, New
York’s water quality standards require that there be “[n]Jo increase that
will cause a substantial visible contrast to natural conditions.” N.Y.
Comp. Codes R. & Regs. tit. 6. § 703.2.
’ Under N.Y. Comp. Codes R. & Regs. tit. 6, ti 702.17, the City might
be eligible for a variance on the basis that its compliance with the
existing standard is precluded by “naturally occurring pollutant
concentrations,” id. § 702.17(b)(1); “human-caused . . . sources of
pollution,” id. § 702.17(b){3); “dams, diversions or other types of
hydrologic modifications,” id. § 702. 17(b)(4); or the fact that
Al7
conditions to assure that the permittee makes “reasonable
progress . . . toward achieving the [original] effluent
limitations.” Jd. § 702.17(e)(2). It may be renewed subject
to the same requirements. /d. § 702.17(g). Because the City
is investigating means of reducing the turbidity of the
Tunnel’s discharge pursuant to state requirements, a
temporary variance might well provide the time necessary
to implement any reasonable and feasible solutions to the
turbidity problem.
The draft Shandaken Tunnel permit issued by the
NYDEC on August 4, 2004, illustrates additional
flexibilities. The draft permit varies turbidity level
restrictions by season, accepting higher levels at times
when the natural turbidity level of the Creek is higher; it
also contains exemptions from the effluent limitations
when necessary to avoid drought conditions, to remedy
emergency threats, to avert threats to public health or
safety, or to allow repairs to the Schoharie Reservoir. See
NYS Env. Notice Bulletin, Notice of Completed
Application for Shandaken Tunnel Outlet 3, 4 n.2 (August
4, 2004).
The draft permit shows that the NPDES permit
scheme can ensure that the water discharged from the
Shandaken Tunnel will continue to meet the City’s needs
without unnecessarily sacrificing progress toward water
quality goals. We find the City’s position, that federal
regulation of interbasin water transfers will lead.to the ©
termination of those transfers in contravention of the rights
explicitly reserved to the states, to be alarmist and
unwarranted.
compliance would “result in substantial and widespread economic and
social impact,” id. § 702,17(11)(6 ).
At bottom, the City’s arguments for reconsideration
of our holding in Catskills I are simply embellishments of
those made in that case. Neither these arguments nor any
intervening developments lead us to conclude that our
earlier holding was reached in error or should otherwise be
modified. We note that every other court faced with this
issue has reached the same conclusion. See N. Plains Res.
Council v. Fidelity Exploration & Dev. Co.,'' 325 F.3d
1155 (9th Cir. 2003); Miccosukee Tribe of Indians v. S. Fla.
Water Mgmt. Dist.,'* 280 F.3d 1364 (1 1th Cir. 2002);
Dubois v. U.S. Dep't ofAgric.,'? 102 F.3d 1273 (ist Cir.
1996). While we recognize the incremental administrative
burden our interpretation entails, we have little doubt that it
nevertheless permits the City to deliver drinking water to
its citizens while furthering the CWA’s goal to “restore and
maintain the chemical, physical, and biological integrity of
the Nation’s waters.” 33 U.S.C. § 1251(a).
IV. Civil Penalty
'' Northern Plains held that the discharges of groundwater derived from
the extraction of coal bed methane into a river requires an NPDES
permit. The court reasoned that the alteration of the chemical integrity
of the river resulting from those discharges constituted an addition of a
pollutant because such groundwater would not have flowed into the
river but for the company’s methane extraction processes. 325 F.3d at
1163.
'? Before the Supreme Court granted certiorari in Miccosukee, the
Eleventh Circuit held that the transfer of water that was high in
phosphorus from a canal to a wetlands area required an NPDES permit.
280 F.3d at 1366, 1368-69.
'’ Dubois held that, when a ski area pumped water from a polluted river
and discharged it into a pristine pond into which it otherwise would not
(continued. ..)
have flowed as part of a snow-making process, an NPDES permit was
required for the discharge. 102 F.3d at 1296-99.
Al9
Both sides attack the $5,749,000 civil penalty
imposed on the City by the district court. District courts
have broad discretion in calculating civil penalties under
the CWA. See Tull v. United States, 481 U.S. 412, 427
(1987) (noting that “highly discretionary calculations that
take into account multiple factors are necessary in order to
set civil penalties under the Clean Water Act’); United
States v. Smithfield Foods, Inc., 191 F.3d 5 16, 526 (4th
Cir. 1999); Hawaii's Thousand Friends v. Honolulu, 821 F.
Supp. 1368, 1395 (D. Haw. 1993). A district court’s
findings of fact in support of a CWA penaity are reviewed
for clear error, e.g., Smithfield Foods, Inc., 191 F.3d at 526;
Sierra Club, Lone Star Ch. v. Cedar Point Oil Co., 73 F.3d
546, 573 (Sth Cir. 1996); Pub. Interest Research Group of
N.J., Inc. v. Powell Duffryn Terminals, Inc., 913 F.2d 64,
79 (3d Cit.. 1990), and the district court’s determination of
the penalty based on those facts is reviewed for abuse of
discretion, e.g., Smithfield Foods, 191 F.3d at 526; Sierra
Club, 73 F.3d at 573. In calculating civil penalties under
the CWA, the court may begin either with the violator’s
estimated economic benefit from noncompliance (known as
the “bottom-up” method) or with the statutory maximum
allowable penalty (known as the “top-down” method). E.
g., Smithfield Foods, 191 F.3d at 528 & n.7; United States
v. Man. Auth. of Union Twp., 150 F.3d 259, 265 (3d Cir.
1998). This starting figure then may be adjusted after
considering the six factors enumerated in section 309(d) of
the CWA: (1) the seriousness of the violations; (2) the
economic benefit resulting from the violation; (3) any
history of violations; (4) good-faith efforts to comply with
applicable requirements; (5) the economic impact of the
penalty on the violator; and (6) other matters as justice may
require. 33 U.S.C. § 1319(d). E.g., Sierra Club, 73 F.3d at
528, n.7. The court below opted to use the “top-down’”’
method. Although neither party objected to this general
approach, both sides take issue with the details of its
implementation.
The district court began with the maximum
statutory penalty and reduced that number due to factors
mitigating in the City’s favor. First, the district court found
that the seriousness factor mitigated in favor of the City.
Second, because the City’s belief that it did not need a
permit to operate the Tunnel was reasonable until the
October 2001 decision of this court, the district court
determined that the City should not be penalized for its
history of violations. Third, the district court credited the
City’s ongoing efforts to reduce the turbidity of the water in
the Tunnel pursuant to non-CWA regulation and _ its
eventual application for a NPDES permit as indicating a
good-faith effort to comply with applicable requirements.
Finally, the district court considered the City’s reasonable
belief that a CWA permit was not necessary to be a
mitigating factor.
Catskills faults the district court for its
determination that the seriousness factor mitigated in favor
of the City. This determination was based on three
considerations: the pollution at issue resulted from natural
conditions that caused turbidity and not toxic pollutants;
there was no evidence that downstream fish were adversely
affected by the discharge; and finally, the discharge, while
turbid, actually improved the habitat for trout by raising
low water levels. Because these findings have evidentiary
support, we will not disturb them or the district court’s
conclusiem that, taken together, they were a mitigating
facter.
Both parties take issue with the district court’s June
22, 2002, starting date for penalties, after which the court
imposed the maximum penalty. Catskills argues that the
starting date should have been October 21, 2001, the date
of Catskills 1, while the City contends that December 2002
would have been reasonable and that, in any event, the
mitigating factors should have reduced the penalty imposed
after the starting date. The district court did impose the
A21
maximum daily penalty, but for only about nine per cent of
the period for which the district court could have penalized
the City.'* The district court’s choice of starting date
accounted both for a reasonable time for the City to come
into compliance. with the CWA and for the mitigating
factors; it will be sustained.
Both parties also attack the penalty figure based on
the “economic benefit resulting from the violations” factor.
The City argues that it is receiving no economic benefit
from operating the Tunnel without a permit, so this factor
should be treated as a mitigating factor. Catskills, on the
other hand, argues that the City reaped a benefit by not
having to build a filtration plant to screen the turbidity from
the Tunnel’s water, which Catskills says would cost $27
million. Even assuming the feasibility of such a plant, as to
which the district court was skeptical, the district court
found that construction of the plant would not have begun
until 1995 at the earliest. Therefore, only costs that would
have been incurred after that date, a figure consider-ably
below $27 million, would be appropnately considered. In
addition, there is a substantial question as to whether the
City should be faulted for not building a plant during a
period (prior to Catskills f) in which it did not believe it
was in violation of the CWA. Considering the evidence on
both sides of this issue, the district court did not abuse its
discretion in determining that the issue of cost savings to
the City from not building a plant should be deemed neither
a mitigating factor nor a cause for in-creased penalties.
Finally, Catskills challenges the City’s good faith
belief that it did not need a permit to operate the Tunnel.
'* Catskills filed its complaint on March 31, 2000. Because the CWA
has a five--year statute of limitations, 28 U.S.C. ti 2462, that is tolled
sixty days before the filing of a complaint, Sierra Club v. Chevron
U.S.A.. Inc., 834 F.2d 1517, 1524 (9th Cir. 1987), January 30, 1995, is
the date on which the City became liable for penalties.
A???
The district court’s determination that the City had such a
good faith belief, based on credibility assessments, 1s
deserving of deference and nothing in the record leads us to
question it. Neither the EPA nor the NYDEC had ever
indicated the necessity of a permit. The district court’s
decision not to penalize the City for a reasonable, albeit
incorrect, interpretation of a statute is not an abuse of
discretion.
In arriving at the penalty imposed below, the district
court carefully considered the six factors laid out in section
309(d) of the CWA, relied on facts not clearly erroneous,
and did not abuse its discretion in deciding the penalty. We
have, however, uncovered a calculation error. The district
court stated that the maximum statutory penalty for the
final 131 days of 2002 was $31,500 per day. In fact, the
maximum daily penalty remained $27,500 until March of
2004. 40 C.F.R. § 19.4. Thus, the maximum possible
penalty was $62,725,000, not $63,249,000 as stated by the
district court. Had the district court been aware that its
initial calculation of the statutory maximum was $524,000
too high, it might have reduced the penalty by that amount.
Or, even being aware of the true statutory maximum, it
might have imposed the same penalty. Or it might have
arrived at a penalty somewhere in between. Because we
have no way to determine how the district court’s
calculation of the penalty would have differed, if at all, had
it accurately determined the maximum statutory penalty,
we remand the case for recalculation of the penalty in light
of the true statutory maximum.
CONCLUSION
For the foregoing reasons, we affirm the district
court’s judgment except as to the amount of the civil
penalty imposed on the City of New York and remand the
case to the district court to recalculate that penalty.
A23
MEMORANDUM-DECISION AND ORDER OF THE
UNITED STATES DISTRICT COURT FOR THE
NORTHERN DISTRICT OF THE NEW YORK,
DATED OCTOBER 4, 2000
REPRODUCED FOLLOWING
UNITED STATES DISTRICT COURT
NORTHERN DISTRICT OF NEW YORK
CATSKILL MOUNTAINS
CHAPTER OF TROUT
UNLIMITED, INC., THEODORE
GORDON FLYFISHERS, INC.,
CATSKILLDELAWARE
NATURAL WATER ALLIANCE,
INC., FEDERATED
SPORTSMEN’S CLUBS OF
ULSTER COUNTY, INC., and
RIVERKEEPER, INC.,
Plaintuff(s),
-~against-
THE CITY OF NEW YORK, NEW
YORK CITY DEPARTMENT OF
ENVIRONMENTAL
PROTECTION, and JOEL A.
MIELE, SR., COMMISSIONER
OF DEPARTMENT OF
ENVIRONMENTAL
PROTECTION,
Defendant(s).
SEE ee i te et i le te
AVE
1:00-CV-
511
(FJS/
RFT)
APPEARANCES OF COUNSEL
PACE KARL S.
ENVIRONMENTAL COPLAN, ESQ.'
LITIGATION CLINIC,
INC,
78 North Broadway
White Plains, New York
10603
Attorneys for Plaintiffs
CITY OF NEW YORK SUSAN C.
OFFICE OF MOON, ESQ.
CORPORATION
COUNSEL
100 Church Street
New York, New York
10007-2601
Attorneys for Defendants
SCULLIN, Chief Judge
U.S. DISTRICT COURT - N.D. OF N.Y.
FILED OCTOBER 6, 2000, LAWRENCE K.
BAERMAN, CLERK-SYRACUSE
! ’ ~ ° _
With the Court’s permission, Basil Saggos, a law student, argued on
Plaintiffs’ behalt
A26
MEMORANDUM-DECISION AND ORDER
I. INTRODUCTION
Presently before the Court are Defendants’ motions
(1) to dismiss Plaintiffs’ turbidity and thermal discharge
claims, pursuant to Rule 12(b)(1) of the Federal Rules of
Civil Procedure, for lack of subject matter jurisdiction; (2)
to dismiss Plaintiff's suspended solids claim, pursuant to
Rule 12(b)(6) of the Federal Rules of Civil Procedure, for
failure to state a claim upon which relief can be granted;
and (3) for a more definite statement pursuant to Rule 12(e)
of the Federal Rules of Civil Procedure. On September 22,
2000, the Court heard oral argument on these motions and
reserved decision. The following constitutes the Court’s
analysis and conclusions with respect to these motions.
If, BACKGROUND
On November 20, 1998, Plaintiffs mailed notice of
alleged violations of the Clean Water Act (“CWA”) and of
Plaintiffs’ intent to file suit to the Administrator of the
United States Environmental Protection Agency, the New
York State Department of Environmental Conservation,
and to Defendants as required by Section 505(b)(I)(A) of
the CWA, 33 U.S.C. § 1365(b)(1)(A). Fourteen months
later, Plainuffs filed the instant complaint. Plaintiffs
brought this citizen suit seeking declaratory and injunctive
relief under Section 301 of the CWA, 33 U.S.C. § 1311 (a),
against Defendants for allegedly violating the CWA by
their unpermitted and unlawful discharge of pollutants from
the Shandaken Tunnel into Esopus Creek.
Defendants operate the Shandaken Tunnel as part
of the New York City Catskill Water Supply System. See
Complaint at § 20. The Shandaken Tunnel begins at the
Schoharie Reservoir in Delaware County, passes through
Green County, and into Ulster County where it discharges
A27
into Esopus Creek. See id. at 4 19. When the Shandaken
Tunnel is in operation, the intake pipe accepts water from
the Schoharie Reservoir and adds it into the Shandaken
Tunnel. The water flows through the Shandaken Tunnel
and is discharged into Esopus Creek. See id. at 4 21. In the
absence of the Shandaken Tunnel, water from the
Schoharie Reservoir would not reach Esopus Creek
because Esopus Creek is located in a different watershed
than the Schoharie Reservoir. See id. at 4] 22, 37.
The water in Esopus Creek is naturally more clear,
or less turbid and lower in suspended solids, than the water
of the Schoharie basin. See id. at { 23. The New York State
Department of Environmental Conservation (“DEC”) has
designated Esopus Creek, between the outlet of the
Shandaken Tunnel and the inlet of the Ashokan Reservoir,
as a Class A(T) stream. This classification signifies high
quality water that is suitable for a trout fishery. See id. at 4
22. The discharge from the Shandaken Tunnel into Esopus
Creek contains a high level of turbidity and suspended
solids in the form of fine red clay particles. See id. at 44 27-
28. The discharge from the Shandaken Tunnel periodically
contains elevated temperatures that stress trout populations
in Esopus Creek. See id. at 4 30.
The City of New York has neither applied for, nor
been granted, a National Pollutant Discharge Elimination
System (“NPDES”) or a State Pollutant Discharge
Elimination System (“SPDES”) permit for its discharges
into Esopus Creek. See id. at 4 35. Plaintiffs assert . that
Defendants have violated and will continue to violate “an
effluent standard or limitation” under § 505(a)(1)(A) of the
CWA, 33 U.S.C. § 1365(a)(1 (A), because of their illegal
and unpermitted discharge from the Shandaken Tunnel into
Esopus Creek. Sce id. at 4 38.
lil. DISCUSSION
A. Subject Matter Jurisdiction
The CWA authorizes a citizen to bring a suit in
federal court against any person who is alleged to be in
violation of “‘an effluent standard or limitation” as defined
by the CWA. To commence a suit, however, a citizen must
comply with § 1365(b), which provides, in pertinent part,
No action may be commenced -
(1) under subsection (a)(1) of this section -
(A) prior to sixty days after the plaintiff
has given notice of the alleged violation
(i) to the Administrator [of the EPA], (ii)
to the State in which the alleged violation
occurs, and (iii) to any alleged violator of
the standard, limitation, or order, .. .
33 U.S.C. § 1365(b).
The purpose of this notice requirement “‘is to give
[the alleged violator] an opportunity to bring itself into
compliance with the Act and thus likewise render
unnecessary a citizen suit.”* Atlantic States Legal Found.,
Inc. v. Stroh Die Casting Co., 116 F.3d 814, 818 (7"" Cir.
- 1997) (quoting [Gwaltrey,}] 484 U.S. at 60, 108 S. Ct at
383) (other citation omitted}.
In the preseat case, Defendants do not dispute that
Plaintiffs sent them a notice letter. Rather, they claim that
Plaintiffs’ notice letter lacks the specificity required by the
CWA and its regulaticns to put Defendants on notice of the
violations upon which Plaintiffs intended to sue.
Specifically, Defendants contend that Plaintiffs’ letter
failed to identify the specific standard, limitation or order
alleged to have been violated and failed to list two of the
A29
pollutants -- turbidity and thermal discharge - which,
together with suspended solids, form the basis of Plaintiffs’
complaint. Due to this alleged lack of specificity,
Defendants argue that the notice is legally insufficient and,
therefore, the Court lacks subject matter jurisdiction over
Plaintiff's turbidity and thermal discharge claims.
Defendants rely upon Hallstrom v. Tillamook
County, 493 U.S. 20 41989), to support their position that
this Court lacks subject matter jurisdiction over Plaintiffs’
turbidity and thermal discharge claims because Plaintiffs’
notice letter lacks the necessary specificity. The issue
before the Court in Hallstrom was whether compliance
with the Resource Conservation and Recovery Act’s
(“RCRA”) 60-day notice provision (modeled on the
CWA’s notice provision) was “a mandatory precondition to
suit or [could] be disregarded by the district court at its
discretion.” Id. at 23. The Court concluded that “{u]nder a
literal reading of the statute, compliance with the 60-day
notice provision is a mandatory, not optional, condition
precedent for suit.” Id. at 26. Unlike the situation here,
however, the plaintiff in Hallstrom sent no notice letter
prior to commencing suit. Therefore, the Court in
Hallstrom had no occasion to address the sufficiency of the
contents of a RCRA notice. Accordingly, Hallstrorn is not
dispositive of the issue before this Court.
What are dispositive, however, are the EPA’s
regulations which set forth the notice requirements:
* There is no question that had Plaintiffs not complied with the
CWA’s 60-day notice requirement, the Court would have to dismiss
the complaint (even if Defendants had learned about the claims in
another way). Plaintiffs, however, did provide Defendants with
notice. Thus, the question is whether the Court must dismiss the
turbidity and thermal discharge claims because. these claims were
not explicitly mentioned in Plaintiffs’ notice letter.
A30
Notice regarding an alleged violation of
an.effluent standard or limitation or of an
order with respect thereto, shall include
sufficient information to permit the
recipient to identify the specific standard,
limitation, or order alleged to have been
violated, the activity alleged to constitute
a violation, the person or _ persons
responsible for the alleged violation, the
location of the alleged violation, the date
or dates of such violation, and the full
name, address, and telephone number of
the person giving notice.
40 C.F.R. § 135.3(a).
Defendants argue that Plaintiffs’ notice letter fails
to meet those requirements because (1) it fails to provide
notice of the “parameters” or “types” of violations which
Plaintiffs assert in their complaint; (2) it mentions neither
turbidity nor thermal discharge; and (3) it fails to disclose
the activities which allegedly constitute these regulatory
violations.
Plaintiffs’ notice letter states, in pertinent part,
[Plaintiffs] believe that the City of New
York has violated and continues to violate
‘an effluent standard or limitation” under
section 505(a)(1)(A), by discharging
pollutants from a point source without a
permit in violation of section 301(a) of the
CWA, 33 U.S.C. § 1311(a).
Based on data collected by the Catskill
Delaware Natural Water Alliance, Inc.,
Complainants believe that the City of New
York has discharged from the Shandaken
aqueduct, and continues to discharge,
pollutants in the form of Total Suspended
Solids and Settleable Solids into the
Esopus Creek, a class A stream, 6
NYCRR § 862.6. These violations have
occurred and continue to occur every day
that the Shandaken tunnel delivers water
into the Esopus Creek, which has been
every day that the tunnel operates for at
least the past five years (the statute of
limitations period under the Clean Water
Act). .
See Plaintiffs’ Ntice Letter, attached as Exhibit “B” to
the Affidavit of Susan Moon, dated May 25, 2000.
Plaintiffs’ notice letter clearly provides the notice
required by 40 C.F.R. § 135.3(a), at least with respect to
suspended and settleable solids. The only issue, therefore,
is whether turbidity and thermal discharges -- which are not
explicitly mentioned in the notice letter - are similar
enough to suspended and settleable solids to have put
Defendants on notice that these pollutants also formed the
basis for Plaintiffs’ complaint.
In support of their claim that turbidity and thermal
discharge are inseparable from suspended solids, Plaintiffs
direct the Court to the common meaning of these terms. In
this regard, Plaintiffs assert that the term “suspended
solids” is commonly equated with turbidity. See Plaintiffs’
Memorandum of Law at 19 (citing The American Heritage
Dictionary of the English Language (Copyright 1996,
Houghton Mifflin Company) (“turbid is defined as ‘having
sediment or foreign particles stirred up or suspended;
* Plaintiffs’ notice letter also contains the full names, addresses, and
telephone numbers of all Plaintiffs.
A32
muddy,’ while the word turbidity has the meaning
‘muddiness created by stirring up sediment or having
foreign particles suspended.”*). Moreover, Plaintiffs claim
that the EPA, Office of Water, on its website, states that
“higher turbidity increases water temperatures because
suspended particles absorb more heat.” See id, Based upon
these definitions, Plaintiffs conclude that “suspended
solids, turbidity and thermal discharges are inseparably
linked in such a way that the notice of suspended solids
was sufficient to place Defendants on notice thereby
satisfying its purpose.” Id. at 10-11. Based upon the
relationship between suspended solids (which were
referenced in the notice letter) and their effect on turbidity
and water temperature, the Court finds that Plaintiffs’
notice letter sufficiently notified Defendants of these claims
and, therefore, complies with § 135.3(a). Accordingly, the
Court denies Defendants’ motion to dismiss Plaintiffs’
turbidity and thermal discharge claims for lack of subject
matter jurésdiction. |
B. Defendants’ Motion to Dismiss for Failure to
State a Claim
To state a claim for the improper discharge of a
pollutant without an NPDES permit pursuant to § 301 of
the CWA, “five elements must be present: (1) a pollutant
must be (2) added (3) to navigable waters (4) from (5) a
point source.” National Wildlife Fed’n v. Gorsuch, 693
F.2d 156, 165 (D.C. Cir. 1982). Defendants contend that
Plaintiffs have failed to allege sufficient facts to state a
claim that the discharge of suspended sediments into
Esopus Creck is an illegal and unpermitted discharge
within the meaning of the CWA. Specificaily, Defendants
contend that Plaintiffs’ failure to state in their complaint
that suspended sediments are a “pollutant” is fatal to their
claim.
A careful reading of Plaintiffs’ complaint,
however, demonstrates that Plaintiffs have alleged
A33
sufficient facts from which it can be inferred that
suspended sediments are a pollutant. In this regard,
Plaintiffs’ complaint states that “Defendant’s discharges of
suspended solids, turbidity, and heat into the Esopus Creek
are illegal and unpermitted discharges within the meaning
of section 301(a) of the Clean Water Act, 33 U.S.C. §
1311(a).” See Complaint at 39. Since a discharge is illegal
only if the discharged substance is a pollutant, it can
reasonably be inferred from the complaint that Plaintiffs are
alleging that suspended solids are a pollutant within the
meaning of the CWA. Moreover, because in addressing a
motion to dismiss the Court must draw all reasonable
inferences in Plaintiffs’ favor, the Court concludes that
Plaintiffs have sufficiently alleged that suspended solids are
a pollutant for purposes of their CWA claims.
More troubling, and ultimately dispositive of this
motion, is Defendants’ contention that Plaintiffs have failed
to allege that the discharge of suspended solids, turbidity
and heat into Esopus Creek is “an addition” of pollutants
“from” a point source. According to Defendants, an
“addition” occurs only if “the point source itself physically
introduces a pollutant into water from the outside world.”
See Defendants’ Reply Memorandum of Law at 2 (quoting
Nat’] Wildlife Fed’n v. Gorsuch, 693 F.2d 156, 165, 174-75
(D.C. Cir. 1982)). Therefore, Defendants argue that
Plaintiffs’ allegation that Defendants’ redirection of water,
which already contains suspended solids, from one body of
water to another constitutes a point source discharge is not
sufficient to establish an “addition” for purposes of the
CWA. See Defendants’ Memorandum of Law at 14.
In response, Plaintiffs assert that Defendants are
adding pollutants in the form of suspended solids, turbidity
and heat from the Schohane Reservoir through the
Shandaken Tunnel into Esopus Creek. They ciaimn that
“{t]his type of ‘addition’ is precisely what the Clean Water
Act is intended to prohibit, since it has turned a renowned
A34
trout stream into a water body that is now unsuitable for
trout fishing.” See Plaintiffs’ Memorandum of Law at 13-
14. Therefore, Plaintiffs assert that “in order to continue the
discharge of suspended solids, turbidity and elevated
temperatures into the Esopus Creek within the limits of the
law, [Defendants] must be required to apply for and be
granted a NPDES/SPDES permit,” as required by § 402 of
the CWA, 33 U.S.C. § 1342. See id. at 14."
The only case that arguably supports Plaintiffs’
position is Dubois v. United States Dep’t of Agric., 102
F.3d 1273 (1996). Plaintiffs rely upon Dubois for the
proposition that Defendants’ diversion of water is an
“addition” because the Schoharie Reservoir and Esopus
Creek are two separate bodies of water. In response,
Defendants rely upon National Wildlife Fed’n v. Gorsuch,
693 F.2d 156 (D.C. Cir. 1982), and National Wildlife Fed’n
v. Consumers Power Co., 862 F.2d 580 (6" Cir. 1988), to
support their argument that the mere diversion of water
without more does not constitute an “addition.”
Although none of these cases are directly on point,
they offer some insight into factors courts have considered
to determine what constitutes an “addition” for purposes of
the CWA. In Dubois, the Loon Mountain Recreation
Corporation drew water from Loon Pond and the
Pemigewasset River for its snowmaking operations. After it
- had used the water to pressurize and prevent freezing in its
snowmaking equipment, it discharged the water into Loon
Pond.
* Plaintiffs also contend that they have adequately alleged the
“addition” of a pollutant because water from the Schoharie
Reservoir would not reach Esopus Creek in the absence of the
Shandaken Tunnel and the water of Esopus Creek is naturally more
clear, or less turbid and lower in total suspended solids, than the
water of the Schoharie basin. See Plaintiffs’ Memorandum of Law
at 18.
Based upon these facts, the First Circuit concluded
that the diversion of the river water with its pollutants into
Loon Pond (which was not connected to the river) was an
addition which required a permit under the CWA. In
reaching its decision, the First Circuit specifically
distinguished Gorsuch, which it characterized as involving
a dam that merely accumulated water and Consumers
Power Co., which involved a pump storage facility that
stored water from one source in a different place, from the
situation in Dubois in which water was moved from one
flowing water body into another stationary, cold body of
water. See Dubois, 102 F.3d at 1299.
Unlike Dubois, the court in Gorsuch concluded that
the mere diversion of water did not constitute an “addition”
for purposes of the CWA. In that case, the plaintiff argued
(similarly to Plaintiffs in this case) that any adverse change
in the quality of reservoir water from its natural state
involved a “pollutant” and that release of polluted water
through a dam into a downstream river constituted the
“addition” of a pollutant to navigable waters “from” a point
source. To the contrary, the EPA argued that for an addition
of a pollutant from a point source to occur, the point source
must introduce the pollutant into navigable water from the
outside world. See Gorsuch, 693 F.2d at 174-75. According
to the EPA, dam-caused pollution, in contrast, merely
passed through the dam from one body of navigable water
(the reservoir) into another (the downstream river). In
addition, although the EPA conceded that all adverse water
quality changes are “pollution” - broadly defined in §
1362(19) as “‘the man-made or man-induced alteration of
the chemical, physical, biological, and radiological
integrity of water -- [the] EPA argue[d] that low dissolved
oxygen, cold, and supersaturation were not included in the
narrower statutory term ‘pollutant,’ defined in § 502(6), 33
U.S.C. § 1362(6) as: ‘dredged spoil, solid waste,
incinerator residue, sewage, garbage, sewage sludge,
A36
munitions, chemical wastes, biological materials,
radioactive materials, heat, wrecked or discarded
equipment, rock, sand, cellar dirt and industrial, municipal,
and agricultural waste discharged into the water.’ Id. at 165
(footnote omitted).
The court in Gorsuch recognized that the CWA did
not define what constitutes an “addition of a pollutant.” It
also recognized that Congress had not expressly addressed
whether the EPA should have discretion to define
“addition.” The court noted, however, that Congress had
given the EPA the reasonable discretion to define “point
source” and “pollutant” Therefore, the court concluded that
it was “likely that Congress would have given EPA similar
discretion to define ‘addition’ had it expected the meaning
of the term to be disputed.” Id. at 175. Based upon its
finding that the EPA’s interpretation of “addition” was
reasonable, the court concluded that because the EPA had
concluded that the dam did not “add” pollutants into the
downstream river, its interpretation was entitled to great
deference and must be upheld. See id. at 166-68, 175.
The Sixth Circuit in Consumers Power Co. also
found no “addition” of a pollutant based upon the facts
before it. In that case, the district court had concluded that
the defendant’s hydro-electric facility’s release of turbine
generating water containing entrained fish into Lake
Michigan required an NPDES permit The Sixth Circuit
reversed, finding that the facility’s movement of pollutants
already in the water was not an “addition” of pollutants to
navigable waters of the United States.
Relying upon Gorsuch, the Sixth Circuit concluded
that “[t]o the extent that no more has been shown than that
unclean water flows out of the dam, Congress clearly
displayed an intention to exempt dams from the Clean
Water Act.” Consumers Power Co., 862 F.2d at 586. The
court distinguished the case before it, in which a facility
A37
merely transmitted water coming into it, from the situation
in which the dam itself added pollutants to the water and,
therefore, would be subject to the NPDES permits system.
The court also noted that even if the facility had released
heat into the water, the result would have been the same.
See id. (“Indeed, it is fair to say that the release of water
containing heat could be quite harmful to the fishery
resources inhabiting a lake, yet the harmful character still
would not make the water and its contents an ‘addition’ of
pollutants into navigable waters of the United States.”).
in every case other than Dubois, where a court has
found an “addition” of a pollutant, more has been involved
than the simple diversion of water from one navigable body
of water to another. See, e.g. Committee to Save
Mokelumne River v. East Bay Mun. Utility Dist., 13 F.3d
305 (9" Cir. 1993) (court distinguished Gorsuch and
Consumer Power Co. because the facility did not merely
pass pollution from one body of navigable water to another.
Rather, the source of pollution was “surface runoff that is
collected or channeled by” the defendants from an
abandoned mine site); United States v. Law, 979 F.2d 977
(4" Cir. 1992) (court distinguished Gorsuch and Consumer
Power C., because the defendant’s water treatment system
collected runoff and leachate subject to an NPDES permit
and the system was not part of the “waters of the United
States”); Hudson River Fishermen’s Ass’n v. City of New
York, 751 F. Supp. 1088 (S.D.N.Y. 1990), aff'd without
opinion, 940 F.2d 649 (2d Cir 199I) (court held that the
City had violated the CWA by discharging chlorine and
alum floc into the reservoir without first obtaining a
pollution emissions permit).
In light of the EPA’s interpretation of what
constitutes an “addition” for purposes of the CWA (which
the Dubois court did not consider) and the lack of any
evidence that Defendants added anything to the water in the
Reservoir before releasing it through the Shandaken tunnel,
the Court concludes that Plaintiffs have failed to estabiish a
necessary element of their claim; i.c., that Defendants’
diversion of water from the Schoharie Reservoir to Esopus
Creek through the Shandaken tunnel constitutes an
“addition” of pollutants “from” a _ point source.
Accordingly, the Court grants Defendants’ motion to
dismiss Plaintiffs’ complaint for failure to state a claim
upon which relief can be granted.
. Defendants’ motion for a more definite
statement
In light of. the Court’s decision to grant
Defendants’ motion to dismiss Plaintiffs’ complaint
pursuant to Rule 12(bX6) for failure to state a claim, the
Court denies Defendants’ motion for a more definite
statement as moot.
IV. CONCLUSION
After carefully considering the file in this matter,
the oral arguments and submissions of the parties and the
applicable law, and for the reasons stated herein, it is
hereby
ORDERED that Defendants’ motion to dismiss
Plaintiffs’ complaint for lack of subject matter jurisdiction
is DENIED, and it is further
ORDERED that Defendants’ motion to dismiss
Plaintiffs’ turbidity and thermal discharge claims for failure
to state a clam is GRANTED, and it is further
ORDERED that Defendants’ motion for a more
definite statement is DENIED as moot; and it is further
ORDERED that the Clerk of the Court enter
judgment in favor of Defendants and against Plainuffs and
close this case.
IT IS SO ORDERED.
Dated: October 4 , 2000 Syracuse, New York
S/ 2
Frederick J. Scullin, Jr.
Chief United States District Judge
DECISION AND ORDER OF THE UNITED STATES
DISTRICT COURT FOR THE NORTHERN
DISTRICT
OF NEW YORK, DATED JANUARY 19, 2001
REPRODUCED FOLLOWING
A4]
UNITED STATES DISTRICT COURT
NORTHERN DISTRICT OF NEW YORK
CATSKILL MOUNTAINS
CHAPTER OF TROUT
UNLIMITED, INC., THEODORE
GORDON FLYFISHERS, INC.,
CATSKILL DELAWARE
NATURAL WATER ALLIANCE,
INC., FEDERATED
SPORTSMEN’S CLUBS OF
ULSTER COUNTY, INC., and
RIVERKEEPER, INC.,
1:00-CV-511
(FJS/RFT)
Plaintiff(s),
-against-
THE CITY OF NEW YORK, NEW
YORK CITY DEPARTMENT OF
ENVIRONMENTAL
PROTECTION, and JOEL A.
MIELE, SR., COMMISSIONER OF
DEPARTMENT OF
ENVIRONMENTAL
PROTECTION,
Defendant(s).
APPEARANCES OF COUNSEL
PACE ENVIRONMENTAL | KARL S. COPLAN,
LITIGATION CLINIC, | ESQ.
INC. |
78 North Broadway
White Plains, New York a
}
| 10603
| Attorneys for Plaintiffs |
| CITY OF NEW YORK SUSAN C. MOON, |
| OFFICE OF | ESQ
| CORPORATION
| COUNSEL |
| 160 Church Street |
' New York, New York 10007- |
| 2601
| Attorneys for Defendants
SCULLIN, Chief Judge | |
ORDER
1. INTRODUCTION
After hearing oral argument on Defendants’ motion
on September 22, 2000, the Court issued a Memorandum-
Decision and Order, dated October 6,.2000, in which the
Court, among other things, granted Defendants’ motion to
dismiss Plaintiffs; complaint for failure to state a claim
upon which relief could be granted.
Plaintiffs now move for reconsideration on the
grounds that “the Court committec clear error on the level
of deference appropriate to the EPA interpretation of the
A43
words ‘addition of a pollutant’ for the purpose of the Clean
Water Act, as controlling Supreme Court jurisprudence was
overlooked.” See Plaintiffs’ Memorandum of Law at 3.
Specifically, Plaintiffs argue that, in light of the Supreme
Court’s recent decision in Chnstensen v. Harris County,
120 S. Ct. 1655 (2000), the Court gave too much deference
to the EPA’s interpretation of what constitutes an
“addition” for purpose of the Clean Water Act (“CWA”).
II. DISCUSSION
A. Standard of Review
Generally, the courts in this district recognize only
three possible bases upon which motions for
eee
reconsideration may be granted: ““(1) an intervening
change in controlling law, (2) the availability of new
evidence not previously available, or (3) the need to correct
a clear error of law or prevent manifest injustice.”* Sumner
v. McCall, 103 F. Supp. 2d 555, 558 (N.D.N.Y. 2000)
(quoting In re C-TC 9" Ave. Partnership, 182 B.R. 1, 3
(N.D.N.Y. 1995) (McAvoy, C.J.)). Parties who base their
motion on the third ground have a demanding standard to
meet. Under the “clear error” test, the court’s previous
decision will be disregarded only when the court has a
“clear conviction of error” with respect to a point of law on
which it based its previous decision. See Fogel _v.
Chestnutt, 668 F.2d 100, 109 (2d Cir. 1981). Thus, a party
considering a motion for reconsideration should evaluate
‘whether what may seem to be a clear error of law is in
fact simply a point of disagreement between the Court and
996
the litigant.”* Sumner, 103 F. Supp. 2d at 559 quoting In re
C-TC 9" Ave, Partnership, 182 B.R. at 3).
As discussed beiow, Plaintiffs have not
demonstrated that the Court committed a clear error of law
| in reaching its conclusion that Plaintiffs had failed to
establish that Defendants’ actions constituted an “addition”
for purposes of the CWA. Thereiore, the Court denies their
motion for reconsideration.
B. “Clear Error” Standard
Plaintiffs claim that in light of the Supreme Court’s
AAS
decision in Christensen, the Court committed clear error by
affording too much deference to the EPA’s interpretation of
what constitutes an “‘addition” for purposes of the CWA. In
Christensen, the Court held that agency interpretations such
as those in opinion letters, policy statements, agency
manuals, and enforcement guidelines, do not warrant the
high level of deference afforded by Chevron, U.S.A., Inc.
v. Natural Resources Defense Council, Inc., 467 U.S. 837
(1984). Leg Chnstensen, 120 S. Ct. at 1662. Rather, the
Court stated that “interpretations contained in formats such
as opinion letters are ‘entitled to respect,’ . . ., but only to
the extent that those interpretations have the ‘power to
,
persuade.””’ Id. at 1663 (internal quotation and citation
omitted)
Based upon this statement in Christensen, Plaintiffs
argue that the EPA’s interpretation of “addition” in
National Wildlife Fed’n v. Gorsuch. 693 F.2d 156 (D.C.
Cir. 1982), is entitled to little deference because that
interpretation was never subjected to adjudication or notice
and comment rulemaking. See Plaintiffs’ Memorandum of
Law at 6. Moreover, Plaintiffs assert that since Gorsuch, is
factually distinguishable from this case, the EPA’s
‘interpretation in Gorsuch should be given even less
deference. Sec id. Defendants oppose Plaintiffs’ motion for
reconsideration on several grounds. First, Defendants argue
that the Court’s dismissal of Plaintiffs’ complaint was
based upon prior case law, not on undue deference to the
EPA’s interpretation of the Clean Water Act. See
Defendants’ Memorandum of Law at 5. Second,
Defendants assert that the Court should not excuse
Plaintiffs’ failure to raise this argument in opposition to
Defendants’ motion to dismiss. See id. at 6-7. Finally,
Defendants contend that there is no reasonable expectation
that reconsideration of the Court’s decision in light of
Christensen would alter the conclusion the Court has
already reached. See id. at 7-8.
Plaintiffs’ argument, in essence, is premised upon
their conclusion that the Court relied entirely upon the
AAT
EPA’s interpretation of the term “addition” in determining
that Defendants’ diversion of water from the Schoharie
Reservoir to Esopus Creek through the Shandaken tunnel
did not constitute an “addition” of pollutants “from” a point
source as required for a violation of the CWA. Sce
Memorandum-Decision and Order at 13. Plaintiffs,
however, place too much emphasis on part of one sentence
in the Court’s Memorandum-Decision and Order. See id.
When this sentence is read in its entirety, it is clear that the
Court did not rely entirely upon the EPA’s interpretation of
the term “addition” as a basis for its conclusion that
Defendants’ actions did not constitute an “addition.” The
sentence reads in full:
In light of the EPA’s interpretation of what
constitutes an ‘addition’ for purposes of the
CWA (which the Dubois court did not
consider) and the lack of any evidence that
Defendants added anything to the water in
the Reservoir before releasing it through the
Shandaken tunnel, the Court concludes that
Plaintiffs have failed to establish a necessary
element of their claim; i.e., that Defendants’
diversion of water from the Schoharie
Reservoir to Esopus Creek through the
A48
Shandaken tunnel constitutes an ‘addition’
of pollutants ‘from’ a point source.
See id.
Moreover, this statement appeared at the very end
of the Court’s decision and followed the Court’s analysis of
the decisions in Gorsuch and National Wildlife Fed’n v.
Consumers Power Co., 862 F.2d 580 (6" Cit. 1988), which
it found persuasive, and after it had distinguished Dubois v.
United States Dep’t of Agric., 102 F.3d 1273 (1996), the
case upon which Plaintiffs relied to support their argument
that Defendants’ diversion of water constituted an
“addition”’ for purposes of the CWA.
When the Court’s reference to the EPA’s
interpretation of the term addition” is read in the context of
the Court’s entire opinion, it is apparent that the Court gave
no more deference to the EPA s interpretation of the term
“addition” than it was entitled to under Christensen; i.e., the
Court relied upon the EPA’s interpretation only to the
extent that it had the power to persuade. As set forth in its
AAO
discussion, the Court found the reasoning in Gorsuch and
Consumers Power Co., to be persuasive in reaching its
conclusion that Plaintiffs had failed to establish that
Defendants’ actions constituted an “addition” for purposes
of the CWA and, thus, had failed to state a claim upon
which relief could be granted.
Plaintiffs obviously disagree with the Court’s
decision and find Dubois more persuasive than Gorsuch
and Consumers Power Co. However, this disagreement
constitutes nothing more than a difference of opinion and
does not rise to the level of a clear error of law which
would warrant granting Plaintiffs’ motion for
reconsideration.
Ill. CONCLUSION
After carefully considering the file in this matter,
the submissions of the parties and the relevant law, and for
the reasons stated herein, it is hereby
ORDERED that’ =—s~wPPilaintiffs’ motion for
reconsideration is DENIED.
ASO
IT ISSO ORDERED.
Dated: January 19, 2001
Syracuse, New York
j
Si _
Frederick J. Scullin, Jr.
Chief United State District Judge
DECISION OF THE UNITED STATES
COURT OF APPEALS FOR THE SECOND
CIRCUIT, DATED OCTOBER 3, 2001
(Reported at 273 F.3d 481)
REPRODUCED FOLLOWING
UNITED STATES COURT OF APPEALS
FOR THE SECOND CIRCUIT
At a stated Term of the United States Court of
Appeals for the Second Circuit, held at the United States
Courthouse, Foley Square, in the City of New York, on the
23™ day of October, two thousand and one.
BEFORE: Hon. John M. Walker, Jr., Chief
Judge
Hon. Robert A. Katzmann.
Hon. Richard D. Cudahy"
Circuit Judges.
Docket No. 00-9447
CATSKILL MOUNTAINS CHAPTER OF TROUT
UNLIMITED, INC., THEODORE GORDON
FLYFISHERS, INC., CATSKILL-DELAWARE
NATURAL WATER ALLIANCE, INC., FEDERATED
SPORTMEN’S CLUBS OF ULSTER COUNTY. INC. and
RIVERKEEPER, INC.,
Plaintiffs-Appellants,
V.
THE CITY OF NEW YORK, NEW YORK CITY
DEPARTMENT OF ENVIRONMENTAL PROTECTION
and JOEL A. MIELE, SR., Commissioner of Department of
Environmental Protection,
Defendants-Appellees.
* The Honorable Richard D. Cudahy of United States Court of Appeals
for the Seventh Circuit, sitting by designation.
AS3
Appeal from the United States District Court for the
Northern District of New York.
This cause came on to be heard on the transcript of
record from the United States District Court for the
Northern District of New York and was argued by counsel.
ON CONSIDERATION WHEREOF, it is hereby
ORDERED, ADJUDGED and DECREED that the
judgment of said district court be and it hereby is
REVERSED in part, AFFIRMED in part and REMANDED
for further proceedings in accordance with the opinion of
this Court. Costs are awarded to appeilants.
FOR THE COURT,
ROSEANN B. MACKECHNIE, Clerk
by s/
Arthur M. Heller,
Administrative Attorney
A54
UNITED STATES COURT OF APPEALS
FOR THE SECOND CIRCUIT
August Term 2000
(Argued May 25, 2001 Decided: October 23, 2001)
Docket Nos. 00-9447
CATSKILL MOUNTAINS CHAPTER OF
TROUT UNLIMITED, INC., THEODORE
GORDON FLYFISHERS, INC., CATSKILL-
DELAWARE NATURAL WATER
ALLIANCE, INC., FEDERATED
SPORTSMEN’S CLUBS OF ULSTER
COUNTY, INC. and RIVERKEEPER, INC.,
Plaintiffs-Appellants,
oe Y , ae
CITY OF NEW YORK and NEW YORK CITY
“~DEPARTMENT OF ENVIRONMENTAL
PROTECTION and JOEL A. MIELE, SR.,
Commissioner of Department of
Environmental Protection,
Defendants- Appellees,
A55
Before:
WALKER, Chief Judge,
KATZMANN and CUDAHY, * Circuit Judges.
Plaintiff environmental organizations appeal from an
October 6, 2000 order of the United States District Court
for the Northern District of New York (Frederick J.
Scullin, Jr., Chief District Judge) granting defendants’
motion to dismiss under Fed. R. Civ. P. 12(b)(6).
Reversed in part, affirmed in part, and remanded. |
KARL S. COPLAN, ESQ., Pace Environmental
Litigation Clinic, Inc. (Basil B. Seggos, on the
brief), White Plains, New York, for Appellants.
ELLEN S. RAVITCH, ESQ., Office of the
Corporation Counsel of the City of New York
(Michael D. Hess, Stephen J. McGrath, Hillary
Meltzer, and William S. Plache, on the brief), .
New York, New York, for Appellees.
JOHN M. WALKER, JR., Chief Judge:
* The Honorable Richard D. Cuday of the United States Court of
Appeals for the Seventh Circuit, sitting by designation.
A56
Plaintiff environmental organizations Catskill
Mountains Chapter of Trout Unlimited, Inc., Theodore
Gordon Flyfishers, Inc., Catskill-Delaware Natural Water
Alliance, Inc., Federated Sportsmen’s Clubs of Ulster
County, Inc., and Riverkeeper, Inc. (collectively
“Catskill”) appeal from an October 6, 2000 order of the
United States District Court for the Northern District of
New York (Frederick J. Scullin, Jr., Chief District Judge)
granting a motion to dismiss under Fed. R. Civ. P. 12(b)(6)
made by defendants City of New York, New York City
Department of Environmental Protection, and Joel A.
Miele. Sr., Commissioner of the Department of
Environmental Protection (collectively “New York City”
or “the City”). We conclude that some of Catskill’s claims
should not have been dismissed and those that were
properly dismissed should have been dismissed without
prejudice. Accordingly, we reverse in part, vacate in part,
and remand for further proceedings consistent with this
opinion.
BACKGROUND
Since before World War II, New York City has
operated Schoharie Dam and Reservoir in the Catskill
Mountains, to provide drinking water for New York City.
Water is diverted south from the Schoharie Reservoir (“the
Reservoir’) through the Shandaken Tunnel (“the Tunnel’)
for several miles and released into Esopus Creck (“the
Creek”), which in turn empties into Ashokan Reservoir.
The transfer of water from the Reservoir to Esopus Creek
and Ashokan Reservoir facilitates its delivery to New York
City for use as drinking water.
Absent the tunnel, water leaving the Reservoir would
flow north in Schoharie Creek, join the Mohawk River, and
flow into the Hudson River. Water from Esopus Creek, on
the other hand, makes its way southeast to the Hudson by
AS7
way of Ashokan Reservoir. Schoharie Reservoir and
Esopus Creek are hydrologically connected only insofar as
both are tributaries of the Hudson. Under natural
conditions, water from ihe Schoharie Reservoir would
never reach Esopus Creek.
Plaintiffs-appellants primarily represent recreational
users of Esopus Creek. On November 20, 1998, Catskill
sent a letter to the City, the United States Environmental
Protection Agency (“EPA”), and the New York State
Department of Conservation (“NYSDEC”), indicating
Catskill’s intention to file suit in district court under the .
federal Clean Water Act (“CWA,” “the Act’), 33 U.S.C. §
1251 et seq. The Act permits aggrieved parties to bring
civil action to enforce certain of the statute’s requirements
against violators. See 33 U.S.C. § 1365 (“Citizen suits.”).
On March 31, 2000, Catskill filed a complaint in
district court alleging that the City, as owner and owner
and operator of the Schoharie Reservoir and Shandaken
Tunnel, was is violation of 33 U.S.C. § 1311(a), which
prohibits “the discharge of any pollutant” unless those
discharges are conducted in accordance with a duly issued
discharge permit. 33 U.S.C. § 1311(a) (citing permit
requirement in 33 U.S.C. § 1342). Catskill alleged that the
Tunnel! discharges pollutants in the form of “suspended
solids,” “turbidity,” and heat into Esopus Creek. They
alleged that the suspended solids and turbidity are the
result of earth-disturbing activities within the Reservoir’s
_ watershed that produce fine, red-clay sediments in the
Reservoir. They further alleged that the discharges cause
the Creek -to violate state water quality standards for
turbidity and temperature. Esopus Cree«x, Catskill
contended, is naturally clearer and cooler than the water
entering it from the Tunnel and supports “one of the
premier trout fishing streams in the Catskill Region.”
AS5S8
The City responded by moving under Fed. R. Civ. P.
12(b)(1) that the case be dismissed for want of jurisdiction
because Catskill’s notice-of-intent-to-sue letter (“NOI
letter”) was inadequate, and a proper NOI letter, they
argued, is a jurisdictional prerequisite for a CWA citizen
suit. The City also moved pursuant to Fed. R. Civ. P.
12(b)(6) that the case be dismissed because, although the
City admits that it lacks a permit to discharge into Esopus
Creek, it need not obtain one because its releases do not
constitute “discharges” as defined by the CWA.
The distnct court denied the City’s Rule 12(b)(I)
motion, concluding that Catskill’s NOI letter comported
with the requirements of the Act and EPA regulations, but
granted Rule 12(b)(6) motion. It found that, as a matter of
law, the Reservoir and Tunnel did not effect an “addition”
of a pollutant to the Creek, as required to tngger the
CWA’s permit requirement. See 33 U.S.C. § 1362(12)
(defining “discharge of a pollutant” to mean “any addition
of any pollutant to navigable waters from any point
source’). Catskill appealed.
DISCUSSION
The City makes two arguments in support of the
district court’s dismissal. It first argues that the district
court and this court lack subject matter jurisdiction over the
case because Catskill’s NOI letter, required by the CWA’s
citizen suit pro-vision, was inadequate and that a proper
NOI letter is a pre-requisite to the court’s subject-matter
jurisdiction. Second, the City reiterates its successful
argument in the district court, that the complaint failed to
state a claim, because Shandaken Tunnel does not effect an
“addition” of a pollutant, as required to constitute a
“discharge” for which a permit must be sought.
We agree with the City that the NOI letter did not
provide adequate notice of Catskill’s eventual claim
ASI
regarding thermal discharges, but find the letter adequate to
notify the City of the balance of Catskill’s claims. The
district court should have dismissed the thermal discharge
claims without prejudice, however, and we therefore vacate
the judgment with respect to those claims and remand with
direction to dismiss them without prejudice to refiling after
submission of a conforming NOI letter and after the 60-day
delay required by the CWA. We also conclude that the
district court erred in dismissing Catskill’s complaint on
the theory that Shandaken Tunnel does not “discharge”
pollutants into Esopus Creek. We therefore reverse the
judgment on the remaining claims and remand the case for
further proceedings.
I. The Statutory Framework .
We begin with an overview of the regulatory regime.
The CWA’s primary function is to regulate the discharge
of pollutants into navigable waters. Although the Act
contains the lofty goal of eliminating water pollutant
discharges altogether, see 33 U.S.C. § 1251(a)(1), the
regulatory regime it creates requires principally that
discharges be regulated by permit, not prohibited outright.
The Act mandates that “the discharge of any pollutant by
any person shall be unlawful,” 33 U.S.C. § 1311(a),
“{e]xcept as in compliance” with other provisions of the
statute, one of which establishes a permitting program, the
“National Pollutant Discharge Elimination System”
(“NPDES”), 33 U.S.C. § 1342. Section 1342 in tum
provides for the issuance of discharge permits (“NPDES
permits”) that allow the holder to discharge pollutants at ©
levels below thresholds incorporated in the permit. 33
U.S.C. § 1342(a ); see also 40 C.F.R. § 122.1 et seq. In
New York, the NPDES program is administered by
NYSDEC and referred to as the State Pollution Discharge
Elimination System (“SPDES”). See 33 U.S.C. § 1342(b)
(authorizing state implementation of the NPDES program);
N.Y. Envtl. Conserv. Law §§ 17-0105(13), 17-0701.
A60
In the instant case, Catskill alleges that the City has
been violating the CWA’s unpermitted discharge
prohibition by discharging water containing pollutants
from Shandaken Tunnel into Esopus Creek without first
obtaining an NPDES permit. The Act defines “discharge of
a pollutant” to include “any addition of any pollutant to
navigable waters from any point source.” 33 U.S.C. §
1362(12). The Act defines “pollutant,” “navigable waters,”
and “point source,” 33 U.S.C. § 1362(6), (7), and (14) but
the crux of this appeal is the meaning of “addition,” which
the Act does not define.
In addition to providing for enforcement by state
agencies and the EPA, the CWA allows private parties to
enforce its mandates, including the prohibition of
unpermitted discharges in § 1311(a), against alleged
violators in so-called “citizen suits.” See 33 U.S.C. §
1365(a)(1 ), (f). An aggneved plaintiff may bring a civil
action for specific relief, such as the imposition of
particular compliance measures, or civil penalties payable
to the treasury, see 33 U.S.C. § 1365{a), and may recover
attorney’s fees, see 33 U.S.C. § 1365(d). At least 60 days
prior to filing, however, the prospective plaintiff must
provide notice of its claims to the potential defendant, the
EPA, and the state in which the violations allegedly
occurred. See 33 U.S.C. § 1365(b)(1)(A). If a competent
state or federal enforcement agency brings a civil
enforcement action against the defendant prior to the
citizen complaints being filed, or an administrative
enforcement proceeding prior to the plaintiff's NOI letter,
the citizen suit is pre-empted and must be dismissed. See
33 U.S.C. §§ 1319(g)(6), 1365(b)(1)(B).
I]. Catskill’s Notice of Intent to Sue
-The City claims that Catskill’s NOI letter was
inadequate because, while it was provided in a timely
fashion to the proper parties, the letter failed to give the
A6él
City adequate notice of the claims that Catskill intended to
bring. Catskill’s complaint as filed alleged discharges of “a
high! * of turbidity,” “suspended solids,” and “elevated
tempe. — -es.” Yet the NOI letter stated only that the City
has discharged “pollutants in the form of Total Suspended
Solids and Settleable Solids into the Esopus Creek.” The
City argues that by failing to provide notice of the claims
of turbidity and thermal. discharges ultimately alleged in
the complaint, the NOI letter was fatally detective,
requiring the suit to be dismissed. Although the district
court did not rely on this theory in dismissing the
complaint, we may affirm on a basis not relied on by the
district court. See Name.Space, Inc. v. Network Solutions,
Inc., 202. F.3d 573, 584 (2d Cir. 2000). We conclude that
the NOI letter failed to notify the City of Catskill’s thermal
discharge claims, but that fact does not invalidate Catskill’s
complaint in its entirety. Accordingly, we hold that those
claims were properly dismissed.
The CWA does not describe the content of the
required notice. but directs that “[nJotice . . . shall be given
in such manner as the Administrator shall prescribe by
regulation.” 33 U.S.C. § 1365(b). The EPA has adopted
such regulations. which mandate, inter alia, as follows:
Notice regarding an alleged violation of an
effluent standard or limitation or of an order
with respect thereto, shall include sufficient
information to permit the recipient to identify
the specific standard, limitation, or order
alleged to have been violated, the activity
alleged to constitute a violation, the person
Or persons responsible for the alleged
violation, the location of the alleged
violation, the date or dates of such violation,
and the full name, address, and telephone
number of the person giving notice.
A62
40 C.F.R. § 135.3(a). In the past, we have refused to
“allow form to prevail over substance” in considering the
content required of an NOI letter, and have looked instead
to what the particular notice given may reasonably be
expected to accomplish. Dague v. City of Burlington. 935
F.2d 1343, 1354 (2d Cir. 1991), rev’d in part on other
grounds, 505 U.S. 557 (1992).
The City contends that the EPA regulations require a
potential plaintiff to include in an NOI letter each separate
pollutant that will be alleged in a subsequent complaint as
the. basis of a violation of the Act. At least one circuit has
adopted such a rule. See Pub. Interest Research Group v.
Hercules, 50 F.3d 1239, 1248 (3d Cir. 1995). On this
theory, for example, a plaintiff could not bring suit for
discharges of mercury, lead, and copper if the NOI letter
alleged violations based only on discharges of copper. In
that case, the claims of copper violations would stand, but
the claims based on mercury and lead discharges would
need to be dismissed. We agree with the City that such a
rule logically follows from the regulatory scheme and
therefore adopt it.
The EPA regulations require that an NOI letter
“include sufficient information to permit the recipient to
identify the specific standard, limitation, or order alleged to
have been violated, [and] the activity alleged to constitute a
violation.” 40 C.F.R. § 135.3(a). We believe that to be
“sufficient,” the information provided must include the
pollutant alleged to be the basis of a violation subsequently
alleged in the complaint.
Because each discharge of a pollutant represents a
distinct violation of the Act, see 33 U.S.C. § 1311(a) (“the
discharge of any pollutant . . . shall be unlawful”); Ati.
States Legal Found., Inc. v. Tyson Foods, Inc., 897 F.2d
1128, 1138 n.19 (11" Cir. 1990), identification in an NOI
letter of a pollutant allegedly discharged is essential to
A63
provide adequate notice of the alleged violation.
Discharges of mercury and lead, for instance, could he
distinct violations, each subject to penalties of up to
$25,000 per day. See 33 U.S.C.§§ 1319(d), 1365(a). To
provide adequate notice of each violation that will be
targeted in the citizen suit, the NOI letter must differentiate
pollutants from nonpollutants and one pollutant from
another. The rationale for such a rule is most apparent in
the context of a suit alleging discharges in excess of
NPDES permit limitations, in which the defendant may he
discharging some pollutants lawfully and _ others
unlawfully. To enable the defendant to identify each:
violation that will be alleged, then, the NOI letter must
specify each pollutant unlawfully discharged that will be
alleged in a subsequent complaint. The principle applies
equally where, as here, the defendant has failed altogether
to obtain a permit. To state a claim based on unpermitted
discharges, the plaintiff must allege some pollutant that
was discharged without a permit. It follows, then, that to
the extent the plaintiff intends to prosecute multiple
violations involving multiple pollutants, each pollutant that
will be the basis of such a claim must be set forth in the
NOI letter.
The policies underlying the NOI requirement are
furthered by this rule The notice and 60-day delay
requirements allow a potential defendant to identify its own
violations and bring itself into compliance voluntarily, thus
making a costly lawsuit unnecessary. See Hallstrom v.
_ Tillamlook County, 493 U.S. 20, 29-30 (1989); Dague, 935
F.2d at 1351; see also Gwaltney of Smithfield, Ltd. v.
Chesapeake Bay Found., 484 U.S. 49 (1987) (holding that
if the defendant ceases its violations prior to the filing of
the complaint, the action is barred). Specific knowledge of
the pollutants allegedly discharged unlawfully makes it
easier for the defendant to promptly rectify the problem.
Cf Atl. States Legal Found., Inc. v. Stroh Die Casting Co.,
A64
!
—_—_——_
116 F.3d 814, 819-20 (7" Cir. 1997) (“In practical terms,
the notice must be sufficiently specific to inform the
alleged violator about what it is doing wrong, so that it will
know what corrective actions will avert a lawsuit. . . . The
key to notice is to give the accused company the
opportunity to correct the problem.”’).
The notice and delay requirements are also designed
to allow the enforcer of first resort, the EPA or the
appropriate state agency, to bring its own enforcement
action, see Hallstrom, 493 U.S. at 29, which would
preempt the citizen lawsuit, see 33 U.S.C. § 1365(b)(1)(B).
Inclusion of each pollutant forming the basis of a alleged
violation better allows enforcement agencies to identify
and prosecute a potential defendant’s violations, giving
effect to Congress’s intention that citizen enforcers
supplement, not supplant, public enforcement. See id.
(citing Gwaltney, 484 U.S. at 60).
Accordingly, we hold that an NOI letter must identify
with reasonable specificity each pollutant that the
defendant is alleged to have discharged unlawfully. Failure
to do so will justify a district court’s dismissing claims
based on pollutants not properly noticed.
Turning to the case at hand, we conclude that
Catskill’s NOI letter adequately notified the City of some
but not all of the violations subsequently alleged in the
complaint. The district court found, and Catskill argues on
appeal, that inclusion of “suspended solids” and “settleable
solids” was sufficient to notify the City of Catskill’s claims
of turbidity and thermal discharges, because of the logical
and empirical associations between suspended solids on the
one hand and turbidity and thermal discharges on the other.
We agree with respect to Catskill’s claims of turbidity
discharges, but not with respect to thermal discharges.
A65
Turbid water, by definition, is water carrying high
levels of solids in suspension. The presence of elevated
levels of suspended solids inevitably produces iurbidi‘y.
“Turbid” is defined as “having the lees or sediment
disturbed: thick or opaque with matter in suspension.”
Webster's Third New International Dictionary 2464
(1981). Water cannot be turbid without suspended solids,
and some level of turbidity is inherent where suspended
solids are preseni. Because each logically depends on the
other, notice of discharges of suspended solids is sufficient
to notify of an eventual claim based on discharges of
“turbidity.”
On the other hand, the relationship between suspended
solids and temperature is one of association, not identify.
To be sure, increased turbidity often produces increased
water temperature. Particles suspended in water absorb
heat, raising the temperature of the water. But the presence
of suspended solids does not inevitably raise water
temperature. The effect of suspended solids on
temperature depends on a third variable, radiant heat,
usually in the form of sunlight. Increased turbidity in a
cold, dark place may not affect the temperature of the
water at all, or may do so only infinitesimally, because no
source of radiant heat is present. As a result, unlike
suspended solids and turbidity, there is no necessary
relationship between suspended solids and increased
temperature. The relationship is only one of frequent
association under ordinary circumstances.
Accordingly, to be sufficient, the allegations in an
NOI letter must suggest that these ordinary circumstances
were also prevalent. Where alleged circumstances. indicate
that suspended solids and increased temperature are very
likely to be associated, notice of suspended solids may be
sufficient to notify a reasonable person of a thermal
discharge claim. In the instant case, Catskill’s NOI letter
does not state that such circumstances were prevalent.
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For the foregoing reasons, we hold that Catskill’s
claims of unpermitted thermal discharges were properly
dismissed under Rule 12(b)(6). However, those claims
should have been dismissed without prejudice. Thus we
vacate so much of the judgment as dismissed Catskill’s
thermal discharge claims with prejudice and remand those
claims with direction that they be dismissed without
prejudice to refilling after full compliance with 33 U.S.C.
1365(b)(1)(A).
Ill Interbasin Transfer as a “Release” Under
the CWA
As we have noted, the CWA prohibits, unless
otherwise allowed by permit, “the discharge of any
pollutant,” 33 U.S.C. 1311(a), which the Act defines to
mean “any addition of any pollutant to navigable waters
from any point source,” 33 U.S.C. § 1362(12). The statute
does not define “addition.” The City argues that the release
of water from Schoharie Reservoir into Esopus Creek is
not an “addition,” citing National Wildlife Federation v.
Gorsuch, 693 F.2d 156 (D.C. Cir. 1982), and National
Wildlife Federation v. Consumers Power Co., 862 F.2d 580
(6" Cir. 1988), both of which accorded substantial
deference to the EPA’s position that the CWA’s discharge
permit requirement does not apply to discharges from
dams. Catskill counters that the Gorsuch and Consumers
‘ Power courts accorded unjustified deference to the EPA’s
interpretation of “addition,” that the cases are
distinguishable on their facts, and that the City’s conduct
here qualifies as an “addition” under the plain meaning of
that word. We agree with Catskill and accordingly reverse
the district court and remand for further proceedings on
Catskill’s remaining claims.
A. The EPA’s Position and the Proper Standard of
Deference
A67
In several policy statements made in opinion letters
and reports to Congress in the 1980s and 1980s, the EPA
took the position that dam releases should not be
considered “discharges” under the CWA and thus NPDES
permits would not be required for those releases.’ See
Gorsuch, 693 F.2d at 167-69. This position was never
formalized in a notice-and-comment rulemaking or formal
adjudication under the Administrative Procedure Act, 5
U.S.C. §§ 553, 554, although the EPA subsequently
reiterated its position in the Gorsuch and Consumers
Power cases, as a defendant and amicus curiae,
respectively. See’ Consumers Power, 862 F.2d at 583;
Gorsuch, 693 F.2d at 165. Both courts rested their
decisions on the conclusion that the EPA position deserved
substantial deference and was reasonable. Given
subsequent Supreme Court decisions governing judicial
deference to federal agencies’ constructions of the statutes
that they implement, we hold that the EPA position is due
less deference than that accorded it by the Gorsuch and
Consumers Power courts.
In 1982, in Gorsuch, the District of Columbia Circuit
deferred to the EPA’s position that dam releases wer not
“additions” under the CWA, which it upheld as a
reasonable construction of the statute. The Gorsuch
plaintiffs had sued the EPA under 33 U.S.C. § 1365(a)(2),
seeking a declaration that the EPA had a nondiscretionary
duty to require NPDES permits from dam operators. After
an extensive exegesis of the CWA’s statutory text,
structure, and legislative history, the court concluded that
the EPA could reasonably conclude that dam releases were
' The original documents in which the EPA staked out its position
were not included in the filings before this court and were not
published in the usual sources of administrative law, the Code of
Federal Regulations at.d the Federal Register. We accordingly base
our discussion of the EPA’s position on that included in the District of
Columbia Circuit’s comprehensive opinion in Gorsuch.
A68
not “additions.” See 693 F.2d at 170-83. Notwithstanding
the court’s extensive investigation of legislative intent, its
relied ultimately on deference to the agency:
[W]e emphasize the narrowness of our
decision. It is not our function to decide
whether EPA’s interpretation . . . is the best
one or even whether it is more reasonable
than the Wildlife Federation’s interpretation.
We hold merely that EPA’s interpretation is
reasonable, not inconsistent with
congressional intent, and entitled to great
deference; therefore, it must be upheld.
693 F.2d at 183. In 1988, the Sixth Circuit reached the
same conclusion. See Consumers Power, 862 F.2d at 584-
87.
If the EPA’s position had been adopted in a
rulemaking or other formal proceeding, deference of the
sort applied by the Gorsuch and Consumers Power courts
might be appropriate. Instead, the EPA’s position is based
on a series of informal policy statements made and
consistent litigation positions taken by the EPA over the
years, primarily in the 1970s and 1980s. Recent Supreme
Court cases emphasize that such agency statements do not
deserve broad deference of the sort accorded by the
Gorsuch and Consumers Power courts.’ See United States
v. Mead Corp., 121 S. Ct. 2164 (2001); Christensen v.
Harris County, 529 U.S. 576 (2000). In Christensen, the
Supreme Court held that “‘[i]nterpretations such as those in
opinion letters — hke imterpretations contained in policy
7
Consumers Power expressly applied the standard of deference
elaborated in Chevron U.S.. Inc. v. Natural Resources Defense Council,
467 US. 837 (1984). See 862 F.2d at 584-85. Gorsuch, which predated
Chevron, applied essentially the same degree of deference. See 693
F.2d at 166-67.
A69
statements, agency manuals, and enforcement guidelines,
all of which lack the force of law — do not warrant
Chevron-style deference.” 529 U.S. at 587. “Instead,” the
Court continued, “interpretations contained in formats such
as opinion letters are ‘entitled to respect’ . . . but only to the
extent that those interpretations have the ‘power to
persuade.’” /d. (citation omitted). The Court consequently
held that an opinion letter by the Department of Labor
deserved only this form of limited deference in its
interpretation of a provision of the Fair Labor Standards
Act. See id.
Like positions taken by the Department of Labor in its
opinion letter in Christensen, the EPA position on dam
discharges has never been articulated in circumstances that
would give it the “force of law.” Gorsuch describes only a
series of letters and several presentations for Congress in
reports and testimony that outlined the EPA’s position. See
Gorsuch, 693 F.2d at 167-69. None of these sources come
close to the sort of formal, binding articulation of an
agency’s views that would justify Chevron deference after
Christensen. That the EPA later relied on its position in-
litigation does not alter our analysis; a position adopted in
the course of litigation lacks the indicia of expertise,
regularity, mgorous consideration, and public scrutiny that
justify Chevron deference. See Bowen v. Georgetown
Univ. Hosp., 488 U.S. 204, 212 (1988); Ball v. Memphis
Bar-B-Q Co., 228 F.3d 360, 365 (4th Cir. 2000); S. Utah
Wilderness Alliance v. Dabney, 222 F.3d 819, 828 (10th °
Cir. 2000).
However, as Mead and Christensen make clear, courts
do not face a choice between Chevron deference and no
deference at all. Administrative decisions not subject to
Chevron deference may be entitled to a lesser degree of
deference: the agency position should be followed to the
extent persuasive. See Mead, 121 S. Ct. at 2175-76 (citing
Skidmore v. Swift & Co., 323 U.S. 134, 140 (1944). For
A70
the reasons that follow, however, we do not find the EPA’s
position to be persuasive.
B. Defining “Addition”
The EPA’s position, upheld by the Gorsuch and
Consumers Power courts, is that for there to be an
“addition,” a “point source must introduce the pollutant
into navigable water from the outside world.” Gorsuch,
693 F.2d at 165. We agree with this view provided that
“outside world” is construed as any place outside the
particular water body to which pollutants are introduced.
Given that understanding of “addition,” the transfer of
water containing pollutants from one body of water to
another, distinct body of water is plainly an addition and
thus a “discharge” that demands an NPDES permit.
Both Gorsuch and Consumers Power essentially
involved the recirculation of water, without anything added .
“from the outside world.” Such recirculation, they
concluded, could not be an “addition.” In Gorsuch, water
was released from a reservoir through a dam to the stream
below. Plaintiffs complained that such a release amounted
to a regulated discharge under the Act, requiring a permit.
The reservoir above the dam and the stream below, at least
arguably, were sufficiently the “same” water that the
release might not be considered an “addition”; nothing was
introduced to the water that was not, in some sense, already
there. See 693 F.2d at 174-75.
In Consumers Power, the defendant had withdrawn
water from Lake Michigan, along with some surprised fish,
for hydroelectric power generation. The water and fish
were then returned to the Lake after passing through
hydroelectric generators, which pureed some of the fish.
The court found that returning the fish to the Lake, albeit in
a different form, was not an “addition” because the fish had
already been there. See 862 F.2d at 586. Indeed, the court
A7l
concluded that “(t]he water which passes through the
(defendant’s hydropower works] never loses its status as
water of the United States.” /d. at 589. The navigable
water was recirculated, but nothing was added. The Sixth
Circuit therefore also concluded that the releases from the
defendant’s hydropower works were not “introduced from
the outside world.” See id. at 586. Beyond Consumers
Power, several cases from other circuits, despite having
found “additions” to have occurred, in dicta reiterated the
Gorsuch holding. See, e.g., Comm. To Save Mokelumne
River v. E. Bay Mun. Util. Dist., 13 F.3d 305, 308-09 (9th
Cir. 1993); United States v. Law, 979 F.2d 977, 979 (4th
Cir. 1992) (“Where ‘pollutants’ exist[ | in the waters of the
United States before contact with these facilities, the mere
diversion in the flow of the waters [does] not constitute
‘additions’ of pollutants to the water.”’).
The Gorsuch and Consumers Power decisions
comport with the plain meaning of “addition” assuming
that the water from which the discharges came is the same
as that to which they go.’ 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
(beyond, perhaps, a de minimis quantity of airborne dust
that fell into the ladle). In requiring a permit for such a
“discharge,” the EPA might as easily require a permit for
Niagra Falls.
The present case, however, strains past the breaking
point the assumption of “sameness” made by the Gorsuch
and Consumers Power courts. Here, water is artificially
diverted from its natural course and travels several miles
> We need not and do not decide whether those courts were correct in
accepting that the source and destination waters were identical and thus
whether we would reach their conclusions if presented with the same
facts.
A72
from the Reservoir through Shandaken Tunnel to Esopus
Creek, a body of water utterly unrelated in any relevant
sense to the Schoharie Reservoir and its watershed. No
one can reasonably argue that the water in the Reservoir
and the Esopus are in any sense the “same,” such that
“addition” of one to the other is a logical impossibility.
When the water and the suspended sediment therein passes
from the Tunnel into the Creek, an “addition” of a
“pollutant” from a “point source” has been made to a
“navigable water,” and the terms of the statute are satisfied.
In Dague v. City of Burlington, 935 F.2d 1343 (2d Cir.
1991), we implicitly held the release of polluted water from
one water body to a distinct, less-polluted water body to be
an addition of pollutants to the latter. We concluded that a
“discharge” had occurred where leachate from a landfill
entered a pond and thereafter water from the pond, polluted
with the leachate, flowed through a culvert into a
surrounding marsh. We held that (1) the pond and marsh
were different navigable waters; (2) the culvert was the
relevant point source; and (3) the release of pond water
through the ? was a “discharge.” We thus necessarily
implied that the transfer of water from the pond to the
marsh was an “addition” /d at 1354-55. We also expressly
rejected the defendant’s argument that the water flowing
from pond to marsh was not an “addition,” noting that
“({ujnder this argument, pollutants would be ‘added’ only
when they are introduced into navigable waters for the first
time.” /d. at 1354.
The First Circuit reached a similar conclusion in
Dubois v. U.S. Dep’t of Agriculture, 102 F.3d 1273 (\st
Cir. 1996). In that case, a ski resort operator on
Department of Agriculture property pumped water without
a permit from a polluted river into a less-polluted pond to
operate its snowmaking equipment. The court held that the
transfer of polluted water from one water body to a distinct
water body constitutes an “addition” of pollutants to the
A73
destination water body. The court emphasized that the two
bodies of water, for all relevant purposes, were distinct:
although water naturally flowed from the pond into the
river, water would never naturally flow from river to pond.
That difference made the pumping an “addition.” See id. at
1296-97. The court distinguished Gorsuch and Consumers
Power as involving movement of water within the same
water body. See id. at 1299.
The City also argues that “addition” draws meaning
from its association with the phrase “from point source.”
This view misunderstands the import of the term “point -
source,” which does not necessarily refer to the place
where the pollutant was created but rather refers only the
proximate source from which pollutant is directly
introduced to the destination water body. A pipe from a
factory draining effluent into a navigable water is a point
source, but the factory itself is not. This is clear from the
text of the Act, which defines “point source,” in relevant
part, as any discernible, confined and discrete conveyance,
including but not limited to any pipe, ditch, channel,
tunnel, conduit, well, discrete fissure, container, rolling
stock, concentrated animal feeding operation, or vessel or
other floating craft, from which pollutants are or may be
discharged.
33 U.S.C. § 1362(14). Under most circumstances, a “pipe,
ditch, channel, tunnel, [or] conduit” is unlikely to have
created the pollutants that it releases, but rather transports
them from their original source to the destination water
body.
As a “tunnel,” Shandaken Tunnel plainly qualifies as
a point source. The tunnel itself need not have created the
pollution; it is enough that it conveys the pollutants from
their original source to the navigable water. See United
States v. Plaza Health Labs., Inc., 3 F.3d 643, 646 (2d Cir.
1993). The City’s proposed interpretation of “from a point
A74
source” is inconsistent with the CWA’s definition of a
point source.
Given the ordinary meaning of the CWA’s text and
our holding in Dague, we cannot accept the Gorsuch and
Consumers Power courts’ understanding of “addition,” at
least insofar as it implies acceptance of what the Dubois
court called a “singular entity” theory of navigable waters,
in which an addition to one water body is deemed an
addition to all of the waters of the United States. See
Dubois, 102 F.3d at 1296-97. We properly rejected that
approach in Dague. . Such a theory would mean that
movement of water from one discrete water body to
another would not be an addition even if it involved a
transfer of water from a water body contaminated with
myriad pollutants to a pristine water body containing few
or no pollutants. Such an interpretation is inconsistent with
the ordinary meaning of the word “addition.”
Even if we were to conclude that the proper
application of the statutory text to the present facts was
sufficiently ambiguous to justify reliance on the legislative
history of the statute, see Blum v. Stenson, 465 U.S. 886,
896 (1984), that source of legislative intent would not help
the City. The legislative history is silent on the meaning of
“addition.” See Gorsuch, 693 F.2d at 175. Instead, the
City relies principally on evidence from other provisions of
the statute that Congress sought (1) to target industrial and
municipal wastes specifically, see Plaza Health Labs., 3
F.3d at 647, and (2) to leave the regulation of water
supply—and therefore dam and reservoir operations—to
the states, see 33 U.S.C. § 1251(g) (“It is the policy of
Congress that the authority of each State to allocate
quantities of water within its jurisdiction shall not be
superseded, abrogated, or otherwise impaired by this
[Act].’’).
A75
‘Yet like many complex statutes (and the CWA is
among the most complex), the CWA balances a welter of
consistent and inconsistent goals. In contrast with the
policies cited by the City, the CWA also expressly includes
a broad and uncompromising policy of “restor[ing] and
maintain{ing] the chemical, physical, and biological
integrity of the Nation’s waters.” 33 U.S.C. § 1251(a).
Artificially transferring water and pollutants between
watersheds as the City has done here might well interfere
with that integrity, as Catskill has alleged. Moreover, in
the past we have applied the Act’s proscriptions beyond
industrial discharges. See Concerned Area Residents for
the Env’t v. Southview Farm, 34 F.3d 114 (2d Cir. 1994)
(involving discharges of agricultural waste).
In any event, none of the statute’s broad purposes
sways us from what we find to be the plain meaning of its
text. Cf Plaza Health Labs., 3 F.3d at 647 (“The narrow
questions posed by this case . . . may not be resolved
merely by simple reference to [the CWA’s] admirable
goal[s].”") Where a statute seeks to balance competing
policies, congressional intent is not served by elevating one
policy above the others, particularly where the balance
struck in the text is sufficiently clear to point to an answer.
We find that the textual requirements of the discharge
prohibition in § 1311(a) and the definition of “discharge of
a pollutant’ in § 1362(12) are met here.
CONCLUSION
The judgment of the district court is hereby reversed
in part, vacated in part, and the case is remanded. We
vacate so much of the judgment as dismissed Catskill’s
thermal discharge claims and remand the direction that
those claims be dismissed without prejudice to refilling
after full compliance with 33 U.S.C. § 1365(b) (1) (A).
The remainder of the judgment dismissing the complaint is
A76
reversed and remanded for further proceedings consistent
with this opinion. Costs are awarded to the appellants.
ORDER OF THE UNITED STATES
DISTRICT COURT FOR THE
NORTHERN DISTRICT
OF NEW YORK, DATED JUNE 4, 2002
REPRODUCED FOLLOWING
UNITED STATES DISTRICT COURT
NORTHERN DISTRICT OF NEW YORK
CATSKILL MOUNTAINS CHAPTER
OF TROUT UNLIMITED, INC.,
THEODORE GORDON FLYFISHERS,
INC., CATSKILLDELAWARE
NATURAL WATER ALLIANCE, INC.,
FEDERATED SPORTSMEN’S CLUBS
OF ULSTER COUNTY, INC., and
RIVERKEEPER, INC.,
Plaintiff(s), 1 .99.cVy-51]
dita: (FJS/RFT)
THE CITY OF NEW YORK, NEW
YORK CITY DEPARTMENT OF
ENVIRONMENTAL PROTECTION,
and JOEL A. MIELE, SR.,
COMMISSIONER OF DEPARTMENT
OF ENVIRONMENTAL
PROTECTION,
Defendant(s).
APPEARANCES OF COUNSEL
PACE ENVIRONMENTAL | KARL S. COPLAN,
LITIGATION CLINIC, | ESQ.
INC.
78 North Broadway
White Plains, New York
10603
Attorneys for Plaintiffs
A79
CITY OF NEW YORK WILLIAM PLACHE,
OFFICE OF | ESQ.
CORPORATION HILARY
COUNSEL MELTZER, ESQ.
100 Church Street
New York, New York 10007-
2601
Attorneys for Defendants
SCULLIN, Chief Judge
U.S. DISTRICT COURT-N.D. OF N.Y.
FILED JUNE 4, 2002
LAWRENCE K. BAERMAN, CLERK-SYRACUSE
ORDER
Plaintiffs commenced this action under the citizen
suit provision of the Clean Water Act (“CWA”), 33 U.S.C.
§ 1365, to enjoin Defendants from polluting the Esopus
Creek, a world-class trout ‘stream, with highly turbid,
muddy water, and for civil penalties for past violations.
Presently before the Court is Plaintiffs’ motion for
_ partial summary judgment declaring that Defendants are in
violation of the CWA, 33 U.S.C. § 1311(a), every day that
Shandaken Tunnel is in operation and that Defendants have
violated CWA § 1311(a) on at least 347 days between
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February 1, 1995 and December 30, 1998. On May 29,
2002, the Court heard oral argument with respect to this
motion. At that time, the Court orally granted Plaintiffs’
motion for partial summary judgment and advised counsel
that a written Order would be forthcoming. The following
constitutes the Court’s written decision with respect to the
pending motion.
The CWA prohibits the addition of any pollutant
into navigable waters from any point source by an person
without a permit. See 33 U.S.C. §§ 1311(a), 1362(12).
Violators of r prohibition are strictly liable. See
Connecticut Fund for the Env't, Inc. v. Upjohn Co., 660 F.
Supp. 1397, 1409 (D. Conn. 1987).
In the present case, there is no dispute that Esopus
Creek is a navigable water, that Defendants are persons.
within the meaning of the CWA, and that Defendants do
not have a permit. Nor can there be any dispute that the
Shandaken Tunnel is a point source and that suspended
sediment constitutes a pollutant now that the Second
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Circuit has held that “{w]hen the water and the suspended
sediment therein pass from the [Shandaken] Tunnel into the
{Esopus} Creek, an ‘addition’ of a ‘pollutant’ from a ‘point
source’ has been made to a ‘navigable water,’ and the terms
of the statute are satisfied.” Catskill Mountains Chapter of
Trout Unlimited, Inc. v. City of N.Y., 273 F.3d 481, 492 (2d
Cir. 2001).
pan Defendants filed papers in opposition to
Plaintiffs’ motion, they conceded in their papers as well as
at oral argument thaf “{unnder the Second Circuit’s
decision, because the City has discharged and continues to .
discharge water containing suspended solids and turbidity
through the Shandaken Tunnel into Esopus Creek, and
‘because the City has no Clean Water permit for those
discharges, . . . it may be viewed as strictly liable under the
Act.” See Defendants” Memorandum of Law at 2.
Given: that the Second Circuit has already
determined that whenever Defendants divert water and
suspended sediment through the Shandaken Tunnel into
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Esopus Creek, “the terms of the statute have been
satisfied,” Catskill Mountains Chapter of Trout Unlimited,
Inc., 273 F.3d at 492, and Defendants’ concession that in
light of the Second Circuit’s decision they have violated the
CWA, the Court concludes that Plaintiffs are entitled to
partial vinnineey judgment with respect to the issue of
liability. Accordingly, the Court hereby
ORDERS that Plaintiffs’ motion for partial
summary judgment with regard to the issue of liability is
GRANTED; and the Court further
ORDERS that the parties are to contact Magistrate
‘Judge Treece’s chambers within ten days of the date of this
Order to schedule a conference to discuss how this nites
can be expedited to ensure that a trial on the issue of
damages can be scheduled as soon as possible.
IT IS SO ORDERED.
Dated: June 4, 2002
Syracuse, New York
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s/
Frederick J. Scuilin, Jr.
Chief United States District Judge
A&4
MEMORANDUM-DECISION AND ORDER OF THE
UNITED STATES
DISTRICT COURT FOR THE NORTHERN
DISTRICT OF NEW YORK, DATED FEBRUARY 6,
2003
(Reported at 244 F. SUPP. 2d 41)
REPRODUCED FOLLOWING
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UNITED STATES DISTRICT COURT
NORTHERN DISTRICT OF NEW YORK
---- -- ---- X
sree
———————
CATSKILL MOUNTAINS
CHAPTER OF TROUT
UNLIMITED, INC., THEODORE
GORDON FLYFISHERS, INC.,
CATSKILLDELAWARE
NATURAL WATER ALLIANCE,
INC., FEDERATED
" SPORTSMEN’S CLUBS OF
ULSTER COUNTY, INC., and
RIVERKEEPER, INC., paetdiend
Plaintiff(s),
-against-
THE CITY OF NEW YORK, NEW
YORK CITY DEPARTMENT OF
ENVIRONMENTAL
PROTECTION, and JOEL A.
MIELE, SR., COMMISSIONER OF
DEPARTMENT OF
ENVIRONMENTAL
PROTECTION,
Defendant(s).
- @ wawoeownwaewoconacece 4
APPEARANCES OF COUNSEL
PACE ENVIRONMENTAL | KARL S. COPLAN,
LITIGATION CLINIC, | ESQ.
INC. MEGAN BRILLAULT,
78 North Broadway Legal Intern
White Plains, New York} LISA COX, Legal
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10603 Intern
Attomeys for Plaintiffs NICOLE PARISI-
| SMITH, Legal Intern
JOHN PAUL, Legal
Intern
CITY OF NEW YORK WILLIAM PLACHE,
OFFICE OF | ESQ.
CORPORATION HILARY MELTZER,
COUNSEL ESQ.
100 Church Street JANET SIEGEL, ESQ.
New York, New York 10007-
2601
Attorneys for Defendants
SCULLIN, Chief Judge
U.S. DIST. COURT-N.D. OF N.Y. .
FILED FEBRUARY 6, 2003
LAWRENCE K. BAERMAN
MEMORANDUM-DECISION AND ORDER
I. INTRODUCTION
On November 20, 1998, Plaintiffs served
Defendants, the New York State Department of
Environmental Conservation (“DEC”), and __ the
Environmental Protection Agency (“EPA”) with a Notice
of Intent to Sue. On March 31, 2000, Plaintiffs filed their
complaint in this action. See Dkt. No. 1. On October 6,
2000, this Court dismissed Plaintiffs’ turbidity and thermal
discharge claims for failure to state a claim. See Dkt. No.
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19. Thereafter, on October 21, 2001, the Second Circuit
reversed in part this Court’s decision and remanded this
action for further proceedings. See Dkt. No. 32.
Subsequently, Plaintiffs filed a motion for partial
summary judgment, seeking a declaration that Defendants
had violated the Clean Water Act (“CWA”), 33 U.S.C. §
1311(a), by diciaabie turbidity and suspended solids
from the Shandaken Tunnel into the Esopus Creek without
a permit, including 347 days between February 1, 1995
and December 30, 1998.' See Dkt. No. 44. On June 4,
2002, the Court granted Plaintiffs’ motion for summary
judgment on the issue of liability and directed the parties
to contact Magistrate Judge Treece’s chambers to discuss
how this action could be expedited to ensure that a trial on
the issue of damages could be scheduled as soon as
possible. See Dkt. No. 66.
' According to Defendants’ Exhibit “D-17,” the Shandaken Tunnel was
in operation on 1,015 days between February |, 1995 and December
30, 1998.
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The Court held a bench trial commencing on
January 8, 2003, to determine the amount of civil penalties,
if any, that Defendants should be required to pay pursuant
to 33 U.S.C. § 1319(d), and what form of injunctive relief,
if any, the Court should impose upon Defendants for
operating the Shandaken Tunnel without a SPDES permit
in violation of the CWA. Pursuant to Rule 52(a) of the
Federal Rules of Civil Procedure, the following constitutes
the Court’s findings of fact and conclusions of law with
respect to these issues.
Il. DISCUSSION
A. Findings of Fact
Plaintiffs Catskill Mountains Chapter of Trout
Unlimited, Inc. (““CMCTU”), Theodore Gordon Flyfishers,
Inc. (“TGF”), Catskill-Delaware Natural Water Alliance
(“CDNWA”), Federated Sportsmen’s Clubs of Ulster
County, Inc. (“FSC”), and Riewineiie. Inc., are not-for-
profit corporations organized under the laws of the State of
New York. Members of CMCTU, TGF, CDNWA, and FSC
A8&9
live near the Esopus Creek and enjoy the Esopus Creek for
numerous activities, including, but not limited to,
flyfishing. Riverkeeper, whose mission is to protect the
environmental resources of the Hudson River and its
tributaries, including the Esopus Creek, has members who
fish in the Esopus Creek.
At trial, Bert Darrow, a member of TGF and
CMCTU and a professional flyfisherman and _ licensed
flyfishing guide, testified that prior to 1996 he used the
Esopus Creek as his primary fishing location for personal
as well as business uses. However, since that time, the
turbid water in the Esopus Creek has made fishing difficult
because the trout cannot see cast lines and flies and
dangerous because the fishermen cannot see the bottom of
the Creek. As a result, he does not fish in the Esopus Creek
very often, and he takes his clients to other streams.
Ron Urban and Bruce Duffy, who are also members
of CMCTU, testified that they have observed a significant
increase in turbidity in the Esopus Creek below the
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Shandaken Tunnel and that they find that the turbidity 1s
visually offensive and creates unsafe conditions for wading.
Brother John Farrell, a member of ESC, has fished in the
Esopus Creek since the mid-1980s. He testified that since
1996 he has observed that the Esopus Creek below the
Shandaken Tunnel has become more turbid, causing it to be
unsafe and affecting his aesthetic enjoyment of the Esopus
Creek. He also testified that he very seldom fishes below
the Shandaken Tunnel, except with an older friend who
lives on the Esopus Creek in that area.
Defendant City of New York, by and through
Defendant New York City Department of Environmental
Protection (“NYCDEP”’), is the owner and operator of the
largest unfiltered drinking water supply in the United
States.2 Defendants provide high quality water to more
than nine million residents of New York State, including
eight million people who live in New York City and
approximately one million people who live in Westchester,
AQ]
Putnam, and Rockland Counties. Defendant NYCDEP
conducts and oversees operation of the Shandaken Tunnel.
The Catskill water supply system provides
approximately forty percent of New York City’s daily
drinking water needs under normal operating conditions.
This system consists of two reservoirs, the Ashokan and the
Schoharie. The Shandaken Tunnel began operating in 1924.
The water in the Schoharie Reservoir is diverted to the
Esopus Creek, the main tributary to the Ashokan Reservoir,
through the Shandaken Tunnel. The Shandaken Tunnel has
a flow capacity of up to 650 million gallons per day. When —
the Shandaken Tunnel is in operation, water from the
Schoharie Reservoir enters the Shandaken Tunnel ieee
an intake channel on or in the bed of the Schoharie
Reservoir. The Shandaken Tunnel runs approximately ~
eighteen miles from the intake structure at the Schoharie
Reservoir to the portal from which it discharges into the
Esopus Creek eleven miles upstream of the Ashokan
? Defendant Joel Miele is the Commissioner of NYCDEP.
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Reservoir. The Catskill aqueduct, which moves water from
the Ashokan Reservoir to New York City’s Kensico
Reservoir in Westchester County, has a capacity of up to
610 million gallons per day. Two aqueducts bring water
from the Kensico Reservoir into New York City.
The Catskill Mountains are characterized by
extensive deposits of silts and clays that are continuous for
miles in the valleys through which streams tributary to the
Catskill reservoirs now flow. The Ashokan Reservoir is
designed to provide settling time to minimize the turbidity
of Catskill water by the time it enters the Catskill aqueduct
on its way to New York City so that the water entering
New York City’s distribution system meets drinking water
standards. The water discharged through the Shandaken
Tunnel into the Esopus Creek is frequently substantially,
visibly more turbid and higher in suspended solids than the
receiving water because of the system design and the
geology of the Schoharie drainage basin. The suspended
solids present in the Schoharie Reservoir are caused, at
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least in part, by erosion in the Schoharie Watershed,
including erosion resulting from land disturbance from
human activities.
The New York State Department of Environmental
Conservation (“DEC”) has designated the Esopus Creek,
between the outlet of the Shandaken Tunnel and the inlet of
the Ashokan Reservoir, as a class A(T) stream. The water
quality standard for discharges of turbidity to a class A(T)
stream is “no increase that will cause a substantial visible
contrast to natural conditions.” N.Y. Comp. Codes R. &
Regs. tit. 6, § 703 {2) (2002).
Pursuant to 33 U.S.C. § 1342, the Administrator of
the EPA has delegated to the State of New York the
authority to issue State Pollutant Discharge Elimination
System (“SPDES”) permits to dischargers in this State.
DEC is the state agency that administers the SPDES
program in New York. Defendants do not have a CWA
permit or a SPDES permit for the operation of the
Shandaken Tunnel, and, until the Second Circuit’s decision
A94
on October 21, 2001, they maintain that they believed that
they did not need a SPDES permit to operate the
Shandaken Tunnel. Defendants operated the Shandaken
Tunnel without a permit and, thus, in violation of the CWA
on a total of 2,326 days from February 1, 1995 to
December 31, 2002. See Defendants’ Exhibit “D-17;”
Letter to Court dated January 23, 2003.”
B. Conclusions of Law
I. Standing
An organization has standing to bring an action on
behalf of its members if it can establish that “its members
would otherwise have standing to sue in their own right, the
interests at stake are germane to the organization’s purpose,
and neither the claim asserted nor the relief requested
requires the participation of individual members in the
lawsuit.” Friends of the Earth, Inc. v. Laidlaw Envtl. Servs.
* After the trial was completed, the Court requested that Defendants
submit a record of the discharges through the Shandaken Tunnel for
the calendar year 2002, rather than rely upon an approximation based
upon prior history. Defendants responded to the Court’s request with
the January 23, 2003 letter and attached chart.
A95
(TOC), Inc., 528 U.S. 167, 181 (2000) (citation omitted).
To establish individual standing a person must show
(1) [that he/she] has suffered an “injury in fact” that
is (a) concrete and particularized and (b) actual or
imminent, not conjectural or hypothetical; (2) the
injury is fairly traceable to the challenged action of
the defendant; and (3) it is likely, as opposed to
merely speculative, that the injury will be redressed
by a favorable decision.
Id. at 180-81.
In the present case, the testimony of Bert Darrow,
Ron Urban, Bruce Duffy, and Brother John Farrow
establishes that Plaintiffs have standing to bring this suit on
behalf of their members. Each of these individuals testified
that, at least since 1996, Defendants’ discharge of water
through the Shandaken Tunnel into the Esopus Creek has
interfered with their enjoyment of the Esopus Creek -- both
aesthetically and in their ability to fish safely in the Esopus
Creek --and, in the case of Bert Darrow, has interfered with
his ahdiaie as a fly-fishing guide. Such injury is both
concrete and particularized as well as fairly traceable to
Defendants’ actions. In addition, a decision in Plaintiffs’
A96
favor - i.e., requiring Defendants to reduce the turbidity of
the water that flows through the Shandaken Tunnel into the
Esopus Creek - will redress their injuries.
Accordingly, based upon the testimony of
Plaintiffs’ members, the Court concludes that Plaintiffs
have standing to bring suit against Defendants under the
citizen-suit provision of the CWA.
peeavins 2. Civil Penalties
As noted, this Court previously determined, upon remand
from the Second Circuit, that Defendants had violated the
CWA. Thus, the only remaining issue is the amount of
civil penalties and the nature of the injunctive relief that
the Court should assess against Defendants.° In making its
* The Court notes that Defendants have never challenged Plaintiffs’ ”
standing. Moreover, at the summary judgment stage, both this Court
and the Second Circuit implicitly concluded that Plaintiffs had
standing to maintain this suit.
* Defendants conceded that, in light of the Second Circuit’s October
21, 2001 decision, they were liable for violating the CWA.
* Several courts have stated that “[c]ivil penalties are mandatory
once Clean Water Act violations are found, although the amount
t be assessed is wholly within the discretion of the court.
Hawaii's Thousand Friends v. City & County of Honolulu, 821 F.
A97
determination, the Court must keep in mind that the
purpose of the CWA’s penalty provision is “deterrence
with respect to both the violator’s future conduct (specific
deterrence) and the general population regulated by the Act
(general deterrence).” United States v. Mun. Auth. of Union
Township, 929 F. Supp. 800, 806 (M.D. Pa. 1996), aff'd,
150 F.3d 259 (3d Cir. 1998) (citation omitted). To attain
the goal of deterrence, the penalty must have two
components: (1) “it must encompass the economic benefit
of noncompliance to ensure that the violator does not profit
from its violation of the law” and (2) it “must include a
punitive component in the form of a sum in addition to
Supp. /368, 1394 (D. Haw. 1993) (citing Atlantic States Legal
Foundation v. Tyson Foods, Inc., 897 F.2d 1128, 1142 (11th Cir.
1990); Stoddard v. Western Carolina Regional Sewer Authority,
784 F.2d 1200, 1208 (4th Cir. 1986)); see also Piney Run Pres.
Ass'n v. County Comm'rs of Carroll County, 82 F. Supp. 2d 464,
470 (D. Md. 2000), vacated and remanded on other grounds, 268
F.3d 255 (4th Cir. 2001) (“The ‘highly discretionary calculations
necessary to assess penalties [under the CWA) are particularly
within the purview of trial judges’ and, therefore, are granted wide
deference.” (quotation omitted)). In addition, some courts have held
that the issues of intent and fault are not relevant to the issue of
whether the court should impose penalties but are only relevant
with respect to the issue of the amount of the penalty. See, e.g.,
United States v. Ohio Edison Co., 725 F. Supp. 928, 934 (N.D.
Ohio /98¥9) (citations omitted).
A98
economic benefit which accounts for the degree of
seriousness and/or willfulness of the violations.” /d.
Section 1319 of the CWA sets forth six factors that
a court must consider when determining the amount of civil
penalties to impose against a defendant:
[1] the seriousness of the violation
or violations, [2] the economic
benefit (if any) resulting from the
violation, [3] any history of such
violations, [4] any good-faith efforts
to comply with the applicable
requirements, [5] the economic
impact of the penalty on the
violator, and [6] such other matters
as justice may require.
33 U.S.C. § 1319(d).
Moreover, when applying these factors to a particular
situation, “courts generally employ either a ‘top-down’ or
‘bottom-up’ method.”’ Piney Run Pres. Ass'n v. County
Comm'rs of Carroll County, 82 F. Supp. 2d 464, 470 (D.
Md. 2000), vacated and remanded on other grounds, 268
’ The Second Circuit has not determined whether the “top-down” or
the “bottom-up” approach is the appropriate means of calculating
civil penalties under the CWA.
A99
F.3d 255 (4th Cir. 2001) (citation omitted); compare Union
Township, 929 F. Supp. at 806 (finding that “top-down”
approach is not appropriate and choosing, instead, to “begin
with economic gain and add a sum to that figure guided by
the other § 1319(d) factors and the need for punishment and
deterrence’); with Atlantic States Legal Found., Inc. v.
Tyson Foods, Inc., 897 F.2d 1128, 1137 (11th Cir. 1990)
(finding that “top-down” approach is the appropriate
methodology for calculating CWA penalties).
If the “top-down” approach is used, the court will
“first calculate the maximum penalty based on the $25,000
[$27,500 or $31,500] per day figure,® then adjust the figure
down, as necessary, to account for the six factors listed in
§ 1319(d).” Piney Run, 82 F. Supp. 2d at 470 (citing
[Smithfield, 191 F.3d] at 528 n.7); see 40 C.F.R. § 19.4. If,
on the other hand, the court employs the “bottom up”
* The maximum penalty is $25,000 per day for violations occur'ing
_ on or before January 30, 1997, see 33 U.S.C. § 1319(d), $27,500
per day for violations occurring between January 31, 1997 and
August 19, 2002, and $31,500 per day for violations occurring
thereafter, see 40 C.F.R. § 19.4.
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method, the court will first “determine the economic
benefit the defendant derived by violating the [CWA], and
then adjust that figure upward or downward using the
remaining five factors in § 1319(d).” Piney Run, 82 F.
Supp. 2d at 470 (citing /Smithfield, 191 F.3d at 528)).
For the reasons addressed below in its discussion of
the economic benefit factor, based upon the circumstances
of this case, the Court concludes that the “top down”
approach provides the appropriate manner in which to
determine the amount of civil penalties that should be
awarded against Defendants for their violations of the
CWA.
a. Maximum amount of penalties
Although the parties stipulated that the Shandaken
Tunnel discharged water into the Esopus Creek on 1,983
days between February 1, 1995 and December 31, 2001,
and approximately 150 days in 2002, the Court reviewed
Defendants’ Exhibit “D-17” (Bates 15935-15942), plus the
additional data for the year 2002, which the Court
Al0l
requested, and determined that the Shandaken Tunnel was
in operation for a total of 2,326 days during this period: 308
days (1995) + 185 days (1996) + 247 days (1997) + 275
days (1998) + 320 days (1999) + 280 days (2000) + 349
days (2001) + 362 days (2002).
Using these numbers, the Court then calculated the
maximum civil penalties as follows:
Year Days Maximum Penalty Total
Per Day
1995 308 $25,000 $ 7,700,000
1996 185 $25,000 $ 4,625,000
1997 3 $25,000 $ 75,000
244 $27,500 $ 6,710,000
1998 275 $27,500 $ 7,562,500
1999 = 320 $27,500 $ 8,800,000
2000 = =280 $27,500 $ 7,700,000
2001 349 $27,500 $ 9,597,500
2002 = 231 $27,500 $ 6,352,500
131 $31,500 $ 4,126,500 _
TOTAL: $63,249,00
Using this figure as a starting point, the Court will
address each of the six factors set forth in § 1319(d) in turn.
b. The seriousness of the violation or violations
To determine the seriousness of a defendant's
violations, the court should consider “the frequency and
severity of the violations as well as their effect on the
environment.” Piney Run, 82 F. Supp. 2d at 471 (citing
United States v. Smithfield Foods, Inc., 972 F. Supp. 338,
343 (E.D. Va. 1997)). Although some courts have
acknowledged _ that “a significant penalty maybe
appropriate even absent proof of actual negative effect,” id.
(citing (/Smithfield, 972 F. Supp.] at 344), other courts
have found that the lack of material environmental harm is
a significant mitigating factor even though the defendant
has violated the CWA a significant number of times. See
Atlantic States Legal Found. Inc. v. Universal Tool &
Stamping Co., Inc., 786 F. Supp. 743, 747-49 (N.D. Ind.
1992) (finding that, even though the defendant had violated
its CWA permit more than 1,900 times during the relevant
period, the lack of material environmental harm was a
significant mitigating factor).
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As noted, Defendants operated the Shandaken
Tunnel without a permit, and thus violated the CWA, on
2,326 days between February I, 1995 and December 31,
2002.’ While this is a significant number of violations, the
Court must also weigh the fact that the turbidity and
suspended solids which Defendants discharged through the
Shandaken Tunnel were not toxic and, at least in part, were
the result of the natural conditions of the water that flowed
through that Tunnel. Moreover, although there was some
evidence at trial that the trout below the Shandaken Tunnel
were smaller than the trout above the Shandaken Tunnel,
there was no evidence of a significant decrease in the
number of trout or of any trout kill as a result of the
discharges. In fact, there was evidence that without the
” February 1, 1995 is the appropriate starting date for determining
the amount of civil penalties to be awarded in this case because
“in citizen enforcement actions the five-year statute of limitations
period (set forth.in 28 U.S.C. § 2462] is tolled sixty days before
the filing of the complaint, to accommodate the statutorily-
mandated sixty-day notice period.” Sierra Cluh v. Chevron U.S.A...
Inc., 834 F.2d 1517, 1524 (9th Cir. 1987). Since Plaintiffs filed
their complaint in this action on March 31, 2000, the five-year
statute of limitations was tolled on February 1, 1995.
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discharge of the water through the Shandaken Tunnel, there
would have less habitat for trout because of low water
levels. Based upon this evidence, the Court considers this
clement to be a mitigating factor.
c. The economic benefit resulting from the
violations
The economic benefit that the violator enjoys as a
result of violating the CWA is “{a] critical component of
any penalty analysis under the [CWA] ....” United States v.
Allegheny Ludlum Corp., 187 F. Supp. 2d 426, 436 (W.D.
Pa. 2002). “The goal of economic benefit analysis is to
prevent a violator from profiting from its wrongdoing.” /d.
(citing Dean Dairy, 150 F.3d at 263). Since it is difficult to
prove precise economic’. benefit, ‘“‘reasonable
approximations ... will suffice.’’ Piney Run, 82 F. Supp. 2d
at 470 (quoting Smithfield, 191 F.3d at 529). In making this
determination, “the court must endeavor to reach a
‘rational estimate of [the violator’s] economic benefit,
resolving uncertainties in favor of a higher estimate."**
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Union Township, 929 F. Supp. at 806 (quotation omitted).
“The estimate ‘must encompass every benefit that
defendants received from violation of the law.’ /d.
(quotation omitted). “It would eviscerate the [CWA] to
allow violators to escape civil penalties on the ground that
such penalties cannot be calculated with precision.” /d. at
806-07.
There are two elements to the calculation of
economic benefit: “(1) the benefit that .1e [defendant]
received from delayed capital spending (i.e., money saved
by delay in issuing and making payments on general
obligation bonds to finance the construction of the required
pollution control equipment); and (2) the operating and
maintenance (“O & M”’) expenses for the pollution control
equipment that the [defendant] avoided operating during
the period compliance was delayed.” Hawaii's Thousand
Friends, 82] F. Supp. at 1387.
Plaintiffs did not submit any evidence with respect
to the benefit that Defendants received by delaying capital
A106
spending. Rather, they focused their proof with respect to
economic benefit on the operating and maintenance
expenses that Defendants would have incurred had they
built a coagulation plant near the Shandaken Tunnel. Dr.
Bell testified that, by not building a coagulation plant,
Defendants saved $27,083,833 in operational and
maintenance costs for the period of February 1, 1995
through December 31, 2001. Although Defendants offered
the testimony of David Nickols to rebut Dr. Bell’s figures
and the feasibility of Dr. Bell’s design and his estimates of
operational and maintenance costs, they did not present any
other figure for the Court’s consideration. In fact, based
upon Mr. Nickols’ testimony, if the Court were to take
some of Defendants’ arguments into consideration, the
potential “economic benefit” to Defendants of not building
a coagulation plant would increase.
That being said, however, the Court has some
problems with Dr. Bell’s testimony as it relates to the
economic benefit that Defendants received as a result of
A107
their violation of the CWA. First, the Court canis the
feasibility of Dr. Bell’s plan, both from a design and
construction eile as well as an operational and
maintenance perspective since he did not take into account
the environmental impact of his design or the on-going
effects on the environment -- such as the increased traffic --
that the construction of such a plant would have. In
addition, Dr. Bell did not take into consideration the time
required to design and construct such a facility. Mr.
Nickols, however, estimated that it would take several
years.
Allowing for several years to construct a
coagulation plant of the type Dr. Bell suggested, the Cour
then must determine the appropriate date from which to
measure the economic benefit of not constructing.such a ©
facility. If the Court were to measure the operational and
maintenance savings from February 1, 1995, as Dr. Bell
did, this would require a finding that Defendants should
have begun work on the design and construction of a
A 1TNHe
coagulation plant in approximately 1990.'° If, on the other
hand, the Court determines that Defendants should have
begun work on the design and construction of a coagulation
plant on February 1, 1995 (when the statute of limitations
was tolled for purposes of this action), November 20, 1998
(the date on which Plaintiffs served Defendants with their
Notice of Intent to Sue), or October 21, 2001 (when the
Second Circuit issued its decision), the operational and
maintenance costs that Plaintiffs avoided would be far less
than the $27,083,833 that Dr. Bell estimated because
Defendants would not have incurred such costs until
several years after they began construction on _ the
coagulation plant. ||
'° It wou'd be unreasonable for the Court to measure Defendants’
economic benefit from this date in light of the Court’s finding, see
discussion infra Part 11.B.2.d, that it was reasonable for Defendants
to believe, prior to October 21, 2001, that they did not need a
SPDES permit to operate the Shandaken Tunnel.
'' Assuming that it would have taken Defendants five years to
design and build a coagulation plant, the earliest date that such a
plant would have come on line, using February 1, 1995, as a
Starting date, is approximately February 1, 2000. Applying the
numbers in Dr. Bell’s Table 5-1, see Plaintiffs’ Exhibit “P-83,” the
approximate operational and maintenance costs that Defendants
A109
Nonetheless, despite the Court’s problems with Dr.
Bell’s opinion regarding the economic benefit that inured to
Defendants by not building a coagulation plant, the Court
finds that this element is not a mitigating factor.’
d. Any history of such violations
In determining the history of a defendant’s
violations, the court must consider “not only pone
violations in the past, but also the duration and continuity
of the [defendant’s] present violations.” Piney Run, 82 F.
Supp. 2d at 471 (citing Smithfield Foods, 972 F. Supp. at
avoided by not having the coagulation plant in operation for the
years 2000 through 2002 is roughly $13,684,759 ($4,198,979
(2000) + $4,551,718 (2001) + $4,934,062 (2002), assuming that
the costs in 2002 increased by 8.4% over 2001. This is a very
rough estimate because in Dr. Bell's table all costs are shown in
2001 dollars and the Court’s 2002 costs are not.
'? The Court notes that § 1319(d)’s economic benefit
element, the purpose of which is, at least in part, to ensure that a
violator does not gain an economic advantage over its
competitors, is of limited assistance to a court’s determination of
the appropriate amount of civil penalties to assess against a
municipality which does not compete to provide water to its
citizens. Moreover, a court must balance the economic feasibility
of any proposed solution against the need of the municipality's
citizens for an adequate water supply.
A110
349).
The evidence adduced at trial demonstrated that
Defendants recognized the need to address, and have
worked to formulate a plan to address, the turbidity
problem in the Catskill system since 1993.'> However, as
Dr. Principe testified, Defendants did not believe that they
needed a SPDES permit to operate the Shandaken Tunnel
until October 21, 2001, when the Second Circuit concluded
that such a permit was necessary.
The Court finds that Defendants’ belief, prior to
October 21, 2001, that they did not need a SPDES permit to
operate the Shandaken Tunnel was reasonable. In this
"In 1993, a Filtration Avoidance Determination (“FAD”) was
issued, which addressed the turbidity problems in the Catskill
system. See Defendants’ Exhibit “D-12” - “Short- and Long-term
Plans to Reduce Turbidity in Schoharie and Ashokan Reservoirs,”
dated June 1993; Defendants’ Exhibit “D-14” - “Determination on
Filtration of New York City’s Catskill and Delaware Water
Supplies, dated January 19, 1993; Defendants’ Exhibit “D-23” -
“Short- and Long-terra. Plans to Reduce Turbidity in Schoharie
and Ashokan Reservoirs, 1993 4th Quarter Report,” dated January
1994. In addition, the most recent FAD, dated November 2002,
included long-term programs to reduce turbidity with time lines.
See Defendants’ Exhibit “D-61” - “New York City Filtration
Avoidance Determination,” USEPA - November 2002 - “Surface
Water Treatment Rule Determiantion for New York City’s
Catskill/Delaware Water Supply System.”
Alll
regard, the Court notes that, although the EPA and DEC
closely monitored the quality of Defendants’ water supply
pursuant to other statutes and were aware that Defendants
discharged water through the Shandaken Tunnel as part of
their water system, Dr. Principe testified that neither the
EPA nor DEC ever suggested to Defendants that they
needed a SPDES permit to operate the Shandaken Tunnel.’
For these reasons, the Court finds that this element is a
mitigating factor.
e. Any good faith efforts to comply with the
applicable requirements
Once Defendants were aware that they were
required to have a SPDES permit to operate the Shandaken
Tunnel (October 21, 2001), they began discussions with
DEC to determine what information DEC would need
before it could issue Defendants such a permit. Although
Defendants and DEC met on only one or two occasions
'* In fact, on numerous occasions, DEC required Defendants to
release water through the Shandaken Tunnel. See, e.g. Defendants’
Exhibits “D-6,” “D-8.”
Ali2
during the year following the Second Circuit’s decision, as
Dr. Principe noted, at the time Defendants received the
Second Circuit’s decision, shortly after the terrorist attack
on September 11, 2001, they were in the midst of
addressing other serious issues, including the safety of New
York City’s water supply.'® In addition, although
somewhat belatedly, Defendants did file a SPDES permit
application on December 31, 2002.'°
Based upon the evidence presented at trial, the
Court concludes that Defendants’ failure to apply for a
SPDES _— until fourteen months after the Second
Circuit’s decision does not evidence a lack of good faith.
When viewed against the backdrop of the September 11,
2001 terrorist attack arid Defendants’ compelling need to
'* The Court notes that it found Dr. Principe to be a very credible
and forthright witness, who readily acknowledged the need to
address the turbidity problem in the Catskill water supply system.
Moreover, the Court found Dr. Principe’s knowledge of Defendants’
water supply system and the regulations that govern this system to
be very helpful to its analysis.
'© Dr. Principe acknowledged that at least part of the impetus for
filing the permit at that time was the pending trial in this matter.
A113
ensure, as their first priority, that New York City’s water
supply was safe, this delay -- although somewhat extended
-- was not undue. Moreover, although Plaintiffs make much
of the fact that everything that Defendants have done in the
past with respect to the turbidity problem was done because
of other statutes, and not in an attempt to comply with the
CWA, the Court is not convinced that the particular
impetus for Defendants’ actions is as important as the fact
that Defendants have made efforts to abate the turbidity
problem and continue to do so. Accordingly, based upon
Defendants’ ongoing efforts to address the turbidity issue
and the fact that Defendants reasonably believed that they
did not need a SPDES permit to operate the Shandaken
Tunnel prior to the Second Circuit’s decision on October
21, 2001, the Court finds that this element is a significant
mitigating factor.’ ’
'? The Court notes, however, its concern that Defendants provided
the Court with very little evidence to explain why they apparently
failed to take any affirmative steps to comply with the Second
Circuit’s October 21, 2001 decision in a more expeditious manner.
Had they done so, the Court would have been inclined to find that this
All4
f- The economic impact of the penalty on the
violator
“The central purpose of CWA penalties is to deter
the defendant, and others, from committing future
violations.” Piney Run, 82 F. Supp. 2d at 472 (citation
omitted). “A davai award that is limited to economic
benefit, therefore, is no deterrent at all because the violator
would be no worse off than if it had complied in the first
place.” /d. (citation omitted); see also Hawaii's Thousand
Friends, 821 F. Supp. at 1396 (finding that the economic
impact of the penalty was not a mitigating factor where the
-penalty would result in only “a slight increase in the
monthly rates paid by users of the sewer system’).
The only evidence at tnal with regard to this
element indicates that Defendants could absorb the
maximum penalty without serious consequences to their
financial well-being. At his deposition, William
element required an even greater mitigation of the maximum penalty
allowable under § 1319(d).
A115
Kusterbeck, Treasurer of the New York City Water Board,
stated that the New York City Water Board maintains a
$60,000,000 operations and maintenance reserve fund,
equal to one month’s operations and maintenance expenses,
in part, to pay for unanticipated NYCDEP expenses
incurred in water supply or distribution. See Transcript of
Deposition of William Kusterbeck, dated September 18,
2002, at 28. Moreover, every million dollars in assessed
penalties will result in only a one-time $.30 increase in the
average water user’s annual rate payment. Thus, the Court
concludes that this element is not a mitigating factor.
g. Such other matters as justice may require
Assessing a monetary penalty in this one would be
tantamount to saying that if you believe in good faith that
your activities are not subject to a CWA permit and neither
the EPA nor DEC has ever indicated that you needed such
a permit, you can be penalized if a citizen suit is
commenced against you and the court finds that you are
wrong. See United States v. Bay-Houston Towing Co., Inc.,
197 F. Supp. 2d 788, 826 (E. D. Mich. 2002). Thus, the
Court finds that this element is a mitigating factor.
h. Calculation of civil penalties
As noted, the Court has used the top-down approach
to calculate the amount of civil penalties to be assessed
against Defendants. Therefore, the Court began its
calculation with the maximum civil penalties that could be
awarded against Defendants for the period from February
1, 1995 through December 31, 2002, i.e., $63,249,000.
Having analyzed the other § 1319 factors, the Court finds
that the lack of material environmental harm, Defendants’
reasonable belief, prior to October 21, 2001, that they did
not need a SPDES permit to operate the Shandaken Tunnel,
and Defendants’ efforts to address the turbidity problems,
both before and after October 21, 2001, are mitigating
factors. The Court also finds that, at the time of the Second
Circuit’s decision, it was reasonable for Defendants to
focus much, if not all, of their attention upon the need to
protect the water supply from any future terrorist attacks.
All?
Thus, their delay in submitting an application for a SPDES
permit for at least several months was reasonable. Although
the Court finds that the fourteen month delay was
somewhat extended, the Court, nonetheless, concludes that
an eight month delay, 1.c., unt
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