Kentucky Waterways Alliance et al v. Kentucky Utilities Co.
Filing
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MEMORANDUM OPINION & ORDER: 1) 16 MOTION to Dismiss is GRANTED. 2) Plas' RCRA claim is DISMISSED w/o prejudice. 3) Plas' CWA claim is DISMISSED w prejudice. 4) A corresponding Judgment will be entered this date. Signed by Judge Danny C. Reeves on 12/28/2017.(SCD)cc: COR
UNITED STATES DISTRICT COURT
EASTERN DISTRICT OF KENTUCKY
CENTRAL DIVISION
(at Lexington)
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KENTUCKY WATERWAYS
ALLIANCE, et al.,
Plaintiffs,
V.
KENTUCKY UTILITIES CO.,
Defendant.
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Civil Action No. 5: 17-292-DCR
MEMORANDUM OPINION
AND ORDER
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This is a citizen enforcement action brought by Plaintiffs Kentucky Waterways
Alliance and Sierra Club against Defendant Kentucky Utilities Co. (“KU”). [Record No. 1]
The plaintiffs allege that KU’s handling, storage, treatment, transportation, and disposal of
coal combustion residuals at the E.W. Brown Generating Station presents an imminent and
substantial endangerment to human health and the environment in violation of the Resource
Conservation and Recovery Act (“RCRA”), and has led to the unpermitted discharge of
pollutants into navigable waters in violation of the Clean Water Act (“CWA”). [Id.] KU has
moved to dismiss the Complaint on the grounds that the plaintiffs do not have standing to bring
an RCRA claim, that the RCRA claim is barred by the abstention doctrine of Burford v. Sun
Oil, 319 U.S. 315 (1943). The defendant also contends that the plaintiff’s CWA claim fails as
a matter of law. [Record No. 16] For the reasons that follow, the motion to dismiss will be
granted.
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I.
The E.W. Brown Generating Station (“E.W. Brown”) is a three unit coal-fired power
plant owned and operated by KU. [Record No. 1, ¶¶ 36-37] It is located on the west side of
the Dix River, beside the hydroelectric dam that created Herrington Lake in Harrodsburg,
Kentucky. It has been in operation since the 1950s. [Id. ¶¶ 37-38] E.W. Brown generates
coal combustion residuals (“CCR”), consisting principally of fly ash (fine, powdery coal ash
particles that are carried up the smokestack by exhaust gases) and bottom ash (larger coal ash
particles that fall to the bottom of the furnace) as a result of the coal burning process. [Id. ¶
38] To dispose of the CCR waste, KU has historically transported it by water through a sluice
system to coal ash ponds known as “settling ponds” or “treatment ponds.” [Id. ¶ 40] The
heavier particles settle at the bottom of the ponds, while the more buoyant particles are
channeled out through permitted discharges into Herrington Lake. [Id.]
An unlined area known as the Main Ash Pond served as the primary settling pond for
many years. [Id. ¶ 40] It was built in the 1950s by damming a valley leading to Herrington
Lake, and was twice expanded to accommodate the growing mass of CCR. [Id.] It now has a
surface area of one hundred and fourteen acres and contains approximately six million cubic
yards of CCR. [Id.] KU switched the sluicing operation from the Main Ash Pond to an
Auxiliary Ash Pond in 2008, which was constructed as a lined temporary settling pond until
the Main Ash Pond could be expanded again. [Id.] The Auxiliary Ash Pond is expected to be
full by 2019. [Record No. 16, Exhibit 1, 1-1]
Due to surrounding land use, KU determined that further expansion of the CCR waste
disposal area would be undesirable. [Record No. 16, p. 3] Instead, KU sought to continue to
use the land occupied by the Main Ash Pond for CCR disposal by capping the pond and
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installing a special waste landfill located physically on top of it. [Record No. 1, ¶ 41] Newly
generated CCR waste would be dried and conditioned in a CCR treatment area and then
deposited in the landfill. [Id.; Record No. 16, Exhibit 1, 1-1]
KU submitted a landfill permit application to the Kentucky Division of Waste
Management (“KDWM”) in 2011, and was required to submit a groundwater assessment plan
(“GWAP”) as part of the application process. [Record No. 16, p. 3, Exhibit 1] The GWAP
was designed to provide a hydrogeologic characterization of the site, evaluate groundwater
quality conditions, and assess water quality in the surface water bodies receiving groundwater
discharges from the site. [Id. at Exhibit 1, 1-1]
The Sierra Club submitted public comments in opposition KU’s landfill application. It
argued that the GWAP revealed that the settling ponds were contaminating the groundwater at
E.W. Brown and represented a danger to human health and the environment. [Record No. 16,
Exhibit 5] The Sierra Club also believed that further study was necessary, in part, because the
settling ponds are located over a fractured and permeable karst region which makes the water
flow less predictable and the area more vulnerable to contamination. [Id. at 5-6] And despite
the limited data, the Sierra Club claimed that initial testing indicated that the groundwater was
likely contaminated with boron, sulfate, total dissolved solids (“TDS”), selenium, arsenic,
cadmium, lead, and other coal ash metals. [Id. at 7-8]
The Sierra Club also alleged that contaminated groundwater was discharging via a
network of springs into Herrington Lake, a major recreational and fishing area. [Id. at 3] As
a result, the Sierra Club asked the KDWM to: (i) deny the landfill permit application until the
existing contamination was more delineated and a corrective action plan was developed and
implemented; and (ii) require KU to construct the landfill elsewhere on-site or off-site. [Id. at
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1-2] KDWM reviewed the application, the GWAP, and the public comments, and issued a
permit to construct the landfill in July 2014. [Record No. 16, Exhibit 3] However, in response
to the Sierra Club’s comments, it required KU to submit a groundwater remedial action plan
(“GWRAP”) before it would issue a permit to operate the landfill. [Record No. 16, p. 4]
The GWRAP noted that groundwater flow through the watershed containing the CCR
ponds emerges in the Briar Patch and HQ Springs, which discharge into Herrington Lake at
HQ Inlet via HQ Stream. [Record No. 16, Exhibit 1, 2-3, 2-5] Arsenic was detected in Briar
Patch and HQ Springs, and concentrations of calcium, chloride, magnesium and sulfate were
generally higher in that area. [Id. at 2-7] However, according to the GWRAP, KU’s ongoing
modifications, including closing and dewatering the Main Ash Pond, capping it with low
permeability materials, and converting to dry CCR disposal in the special waste landfill, would
help to ameliorate this condition because they would “significantly reduce the amount of
contact between water and CCR, and therefore reduce the mobilization of CCR constituents in
water with the potential to be discharged to the environment.” [Id. at 2-9, 2-10]
Still, the GWRAP noted that “[s]ome flow of natural groundwater through the existing
CCR in the Main Pond is expected to continue over time, as the natural flow of water that
existed before the Pond was filled with CCR continues into the buried valley.” [Id. at 2-10]
As a result, KU stated that it would work with the Division of Water “to develop a
comprehensive approach to risk management that addresses the totality of surface water
impacts from both groundwater and surface water discharges.” [Id. at 3-1] In the meantime,
it proposed a series of interim remedial actions designed to reduce the total mass of CCR
constituents entering Herrington Lake via the groundwater flow system. [Id.]
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The Sierra Club objected to the GWRAP, arguing that “the interim remedial measures
. . . while all appropriate and necessary, do very little to address the flow of contaminants from
the ash ponds into Lake Herrington and in all other directions from the ash ponds.” [Record
No. 16, Exhibit 10, Attachment 1, p. 11] In its view, KU should have been required to conduct
a more complete characterization of the groundwater contamination at the site, and then collect
and treat the contaminated water. [Id.] However, after reviewing the public comments, the
KDWM approved the GWRAP in October 2015. [Record No. 16, Exhibit 11]
Shortly thereafter, the plaintiffs sent a notice of intent to file a citizen suit under the
Clean Water Act (“CWA”) to KU, the United States Environmental Protection Agency
(“EPA”), and the Kentucky Department of Environmental Protection (“KDEP”), a division of
the Kentucky Energy and Environment Cabinet (the “Cabinet”). [Record No. 1, Exhibit A]
The notice alleged that KU has discharged and continues to discharge pollutants into the waters
of the United States without a permit in violation of the CWA. [Id. at 1] According to the
notice, these discharges originate from both the now-buried Main Ash Pond and the Auxiliary
Ash Pond, and migrate through groundwater which emerges in HQ and Briar Patch Springs
and discharges into HQ Stream, a jurisdictional surface water that flows into Herrington Lake
at HQ Inlet. [Id. at 2-3]
The plaintiffs also sent a notice of intent to file a citizen suit under the Resource
Conservation and Recovery Act (“RCRA”) on October 26, 2016. [Record No. 1, Exhibit C]
The RCRA notice alleged that KU’s handling, storage, treatment, transportation, and/or
disposal of CCR waste at E.W. Brown has resulted in contamination in the ground and surface
waters, presenting an imminent and substantial endangerment to human health and the
environment. [Id. at 2] It also alleged that KU’s remedial actions were inadequate to abate
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the risk of endangerment because they failed to characterize the full extent of contamination,
failed to adequately monitor ground and surface water quality, and failed to halt, abate, or
otherwise adequately address the ongoing contamination. [Id. at 4]
After receiving the RCRA notice, the Cabinet reviewed the available data regarding the
ground and surface water quality near E.W. Brown and conducted additional surface water
testing. [Record No. 16, Exhibit 15, ¶¶ 7-8] It determined that water samples collected from
HQ and Briar Patch Springs identified selenium levels above Kentucky’s selenium water
criterion, and fish samples collected from Herrington Lake adjacent to HQ Inlet contained
selenium in excess of Kentucky’s whole body fish tissue selenium criteria. [Record No. 16,
Exhibit 14] Based on these results, the Cabinet issued a notice of violation (“NOV”) to KU
alleging that E.W. Brown “directly or indirectly discharged, or caused or permitted to be
discharged, a pollutant or substance that has caused or contributed to pollution of a water of
the Commonwealth” in violation of Kentucky Revised Statutes (“KRS”) 224.70-110, and
aesthetically or otherwise degraded surface waters in violation of Kentucky Administrative
Regulations (“KAR”) Title 401, Chapter 10:031, Section 2. [Id.]
KU and the Cabinet entered into an Agreed Order on January 30, 2017, to resolve the
NOV and to “address any threat or potential threat to human health and the environment
associated with management and storage of CCR at [the] E.W. Brown Station.” [Record No.
16, Exhibit 15, ¶ 12] The Agreed Order required KU to continue to implement the GWAP,
the GWRAP, and the Main Ash Pond Closure Plan previously approved by the Cabinet, and
imposed a $25,000 civil penalty for the alleged violations. [Id. ¶¶ 13, 22] Additionally, KU
was required to submit two Corrective Action Plans (“CAPs”) “detailing the steps KU has
taken and will take to address the matters raised in this Agreed Order and the notice of violation
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dated January 11, 2017.” [Id. ¶¶ 13-15] The first CAP was to investigate the risks associated
with the contamination, its potential sources, and to consider additional remedial actions. [Id.
¶ 14] The second CAP was to address the discharge of ash transport water at the Auxiliary
Ash Pond. [Id.] The CAPs require the Cabinet’s approval, and are subject to a thirty day
public comment period. [Id. ¶¶ 16, 19]
KU submitted its CAP addressing the groundwater contamination on April 14, 2017,
which called for groundwater studies consisting of field sampling and site characterization, a
human health risk assessment, and an ecological risk assessment. [Record No. 16, Exhibit 16;
id. at p.12 n.7] The proposed studies may last through 2019, at which time KU would evaluate
and implement remedial actions as warranted. [Record No. 16, Exhibit 16, p. 40-42]
The plaintiffs filed this action on July 27, 2017, alleging violations of the CWA and the
RCRA. [Record No. 1] The plaintiffs’ CWA claim alleges that KU is discharging and has
discharged pollutants from the Main Ash Pond and the Auxiliary Ash Pond to HQ Stream, a
navigable water, without a permit, causing irreparable harm to the plaintiffs’ members and
their communities. [Id. ¶¶ 70-78] These pollutants allegedly include arsenic, lead, selenium,
and cadmium, which pose well-documented environmental and health risks. [Id. ¶ 43] The
plaintiffs’ RCRA claim contends that KU has contributed and is contributing to the handling,
storage, treatment, transportation, or disposal of solid waste at E.W. Brown that may present
an imminent and substantial endangerment to human health and the environment. [Id. ¶¶ 7985] The plaintiffs claim that the remedial steps taken by KU are inadequate, and that their
members will suffer irreparable harm unless KU eliminates the endangerment. [Id.]
KU argues that the Complaint should be dismissed because: (i) the Cabinet is already
redressing the harms alleged in the Complaint, depriving the plaintiffs of standing to bring an
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RCRA claim; (ii) Burford abstention applies because these matters are the subject of the
Cabinet’s ongoing regulatory proceedings; and (iii) the plaintiffs’ CWA claim fails as a matter
of law because the movement of contaminants from groundwater to surface water is not subject
to regulation under the CWA. [Record No. 16, p. 2]
II.
KU’s argument that the plaintiffs’ RCRA claim should be dismissed for lack of
standing contests this Court’s subject matter jurisdiction under Federal Rule of Civil Procedure
12(b)(1). Lyshe v. Levy, 854 F.3d 855, 857 (6th Cir. 2017) (citations omitted). A 12(b)(1)
motion “can either attack the claim of jurisdiction on its face, in which case all allegations of
the plaintiff must be considered as true, or it can attack the factual basis for jurisdiction, in
which case the trial court must weigh the evidence and the plaintiff bears the burden of proving
that jurisdiction exists.” DLX, Inc. v. Kentucky, 381 F.3d 511, 516 (6th Cir. 2004). KU’s
standing argument is based on administrative records that are not referenced in or attached to
the Complaint, but are attached to KU’s motion to dismiss. The Court may consider these
records to determine whether it has jurisdiction over this case. See Ohio Nat. Life Ins. Co. v.
United States, 922 F.22 320, 325 (6th Cir. 1990) (explaining that when a 12(b)(1) motion
hinges on facts outside of the Complaint, “a trial court has wide discretion to allow affidavits,
documents and even a limited evidentiary hearing to resolve disputed jurisdictional facts”).
KU’s argument that the plaintiffs’ CWA claim should be dismissed contests the
sufficiency of the Complaint under Federal Rule of Civil Procedure 12(b)(6). A 12(b)(6)
motion requires the Court to determine whether the Complaint alleges “sufficient factual
matter, accepted as true, to ‘state a claim to relief that is plausible on its face.’” Ashcroft v.
Iqbal, 556 U.S. 662, 678 (2009) (quoting Bell Atl. Corp. v. Twombly, 550 U.S. 544, 570
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(2007)). The plausibility standard is met “when the plaintiff pleads factual content that allows
the court to draw the reasonable inference that the defendant is liable for the misconduct
alleged.” Id. (citing Twombly, 550 U.S. at 556). Although the Complaint need not contain
“detailed factual allegations” to survive a motion to dismiss, the “plaintiff’s obligation to
provide the grounds of his entitlement to relief requires more than labels and conclusions, and
a formulaic recitation of the elements of a cause of action will not do.” Twombly, 550 U.S. at
555 (internal quotation marks and citation omitted); see also Iqbal, 556 U.S. at 678 (“[T]he
tenet that a court must accept as true all of the allegations contained in a complaint is
inapplicable to legal conclusions.”).
In general, where “matters outside the pleadings are presented to and not excluded by
the court, the motion will be treated as one for summary judgment under Rule 56” and the
“parties must be given a reasonable opportunity to present all the material that is pertinent to
the motion.” Fed. R. Civ. P. 12(d). However, a court may consider “exhibits attached to the
complaint, public records, items appearing in the record of the case and exhibits attached to
the defendant’s motion to dismiss so long as they are referred to in the complaint and are
central to the claims therein without converting the motion to one for summary judgment.”
Rondigo, L.L.C. v. Twp. of Richmond, 641 F.3d 673, 680-81 (6th Cir. 2011) (internal quotation
marks and citation omitted).
III.
The RCRA is “a comprehensive regulatory system designed to promote the safe
handling of solid and hazardous wastes.” Coal. for Health Concern v. LWD, Inc., 60 F.3d
1188, 1190 (6th Cir. 1995). Like similarly-structured environmental laws, the RCRA is “a
model of cooperative federalism.” Ellis v. Gallatin Steel Co., 390 F.3d 461 (6th Cir. 2004)
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(describing the Clean Air Act). “Chief responsibility for the implementation and enforcement
of [the] RCRA” rests with the EPA. Meghrig v. KFC Western, Inc., 516 U.S. 479, 483 (1996).
The EPA, in turn, may authorize states to administer their own RCRA hazardous waste
programs. Coal. for Health Concern, 60 F.3d at 1190 (citing 42 U.S.C. § 6926). Kentucky
has enacted an EPA-approved hazardous waste disposal program and implements the RCRA
through its program. Id. (citing Ky. Rev. Stat. Ann. §§ 224.01-010, et seq.).
In addition to state and federal enforcement, the RCRA’s citizen suit provision
provides that “any person” may commence a civil action against any person “who has
contributed or who is contributing to the past or present handling, storage, treatment,
transportation, or disposal of any solid or hazardous waste which may present an imminent
and substantial endangerment to health or the environment.” 42 U.S.C. § 6972(a)(1)(B). This
provision confers the Court with jurisdiction “to restrain any person who has contributed or
who is contributing to the past or present handling, storage, treatment, transportation, or
disposal of any solid or hazardous waste . . . , to order such person to take such other action as
may be necessary, or both . . . .” Id. § 6972(a).
“[T]o strike a balance between encouraging citizen enforcement of environmental
regulations and avoiding burdening the federal courts with excessive numbers of citizen suits,”
Congress limited the scope of the citizen suit provision. Hallstrom v. Tillamook Cnty., 493
U.S. 20, 29 (1989). A private party may not bring suit under § 6972(a)(1)(B) without giving
ninety days’ notice to the Administrator of the EPA, the State in which the alleged
endangerment may occur, and the potential defendants. Meghrig, 516 U.S. at 486 (citing 42
U.S.C. §§ 6972(b)(2)(A)(i)-(iii)). Further, no citizen suit can proceed if either the EPA or the
State has commenced, and is diligently prosecuting, a separate enforcement action. Id. (citing
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42 U.S.C. §§ 6972(b)(2)(B) and (C)). These limitations prevent unnecessary citizens’ suits by
allowing government agencies to take responsibility for enforcing environmental regulations,
and by giving the alleged violator an opportunity to comply with the RCRA. Hallstrom, 493
U.S. at 29 (quotation marks and citations omitted). As the Sixth Circuit has explained, “[t]he
notice provisions demonstrate that Congress has authorized citizen suits only when
environmental officials ‘fail to exercise their enforcement responsibility’ and has provided an
‘interstitial’ role for private parties in enforcing the statute.” Ellis, 390 F.3d at 475 (quoting
Gwaltney, 484 U.S. at 60-61).
As with every lawsuit filed in federal court, plaintiffs seeking to bring an RCRA citizen
suit must also satisfy Article III of the Constitution’s “case” or “controversy” limitation. See
Envtl. Conservation Org. v. City of Dallas, 529 F.3d 519, 526 (5th Cir. 2008). “The doctrine
of standing is one of several doctrines that reflect this fundamental limitation.” Summers v.
Earth Island Inst., 555 U.S. 488, 493 (2009). An association has standing to bring suit on
behalf of its members when: “[(i)] its members would otherwise have standing to sue in their
own right, [(ii)] the interests at stake are germane to the organization’s purpose, and [(iii)]
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. (TOC), Inc., 528
U.S. 167, 181 (2009) (citing Hunt v. Wash. State Apple Advert. Comm’n, 432 U.S. 333, 343
(1977)). An association member has standing to sue in its own right when it can demonstrate
that: “(1) it 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
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will be redressed by a favorable decision.” Id. at 180-81 (citing Lujan v. Defenders of Wildlife,
504 U.S. 555, 560-61 (1992)).
KU does not dispute that the plaintiffs provided ninety days’ notice to KU, the EPA,
and the KDEP, and that neither the EPA nor the KDEP has commenced, or is diligently
prosecuting, a separate enforcement action.
[Record No. 1, ¶¶ 13-15, Attachment C]
Likewise, KU does not contest the plaintiffs’ assertion that some of their members live near
and recreate in and around Herrington Lake, and that those members have suffered an “injury
in fact” that is “fairly traceable” to KU’s alleged conduct as KU’s alleged conduct may
endanger their health, that of their families and communities, and their environment (including
the fish, other aquatic life, and wildlife they observe, consume, and enjoy). [Id. ¶¶ 19-21;
Record No. 27, p. 16-17]
To redress these injuries, the plaintiffs ask the Court to declare that KU’s past and
present handling, storage, treatment, transportation or disposal of CCR at E.W. Brown may
present an imminent and substantial endangerment to health or the environment in violation of
the RCRA. [Record No. 1, p. 21 (Prayer for Relief (d))] They also seek an injunction ordering
KU to take all actions necessary to eliminate the endangerment to health and the environment,
including an order “to determine and implement the most expeditious, cost-effective, and
environmentally sound means to eliminate the ongoing migration of CCR pollutants into
groundwater, surface water, and sediments; and to fully abate the endangerment associated
with CCR pollutants that have already migrated into groundwater, surface water, and
sediments near the site.” [Id. (Prayer for Relief (e))] Although the plaintiffs decline to state
in advance of discovery exactly what injunctive relief would be appropriate, they suggest that
in addition to the studies and recommendations for remedial measures required by the Cabinet,
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the Court could redress their members’ injuries by ordering KU to excavate the six million
cubic yards of coal ash buried under the special waste landfill, or to clean up the contamination
in Herrington Lake. [Record No. 1, p. 21; Record No. 27, p. 20]
KU argues that the plaintiffs’ members’ alleged injuries are not “redressable” by this
Court because they “seek[] to remedy the same conditions the Cabinet and KU are addressing
in the [GWRAP], Agreed Order and the CAPs—impacts to groundwater and surface water at
and around E.W. Brown resulting from plant operations.” [Record No. 16, p. 15] In its view,
“[a] citizen suit plaintiff lacks standing to seek injunctive relief covering the same ground as
obligations imposed by a regulatory agency.” [Record No. 28, p. 2] The Agreed Order is
designed to “address any threat or potential threat to human health and the environment
associated with management and storage of CCR at [the] E.W. Brown Station,” and requires
KU to continue to implement the GWRAP, GWAP, and Main Ash Pond Closure Plan
previously approved by the Cabinet, and to pay a $25,000 civil penalty. [Id., Exhibit 15, ¶¶
12, 13, 22] In light of these agency-imposed remedial actions, KU argues that the Court cannot
award further injunctive relief. [Record No. 16, p. 15]
“[A] plaintiff must demonstrate standing separately for each form of relief sought.”
Laidlaw, 528 U.S. at 181. As a result, the plaintiffs bear the burden of demonstrating that the
Court could grant the relief requested and that doing so would remedy their members’ alleged
injuries. See Lujan, 504 U.S. at 561. Here, the plaintiffs seek declaratory and injunctive relief.
Federal courts have explicitly held that “declaratory relief is not an appropriate basis to
support citizen suit standing,” Little v. Louisville Gas & Elec. Co., 33 F. Supp. 3d 791, 802
(W.D. Ky. 2014), except in “special circumstances . . . such as when a plaintiff is threatened
with potential enforcement action.” WildEarth Guardians v. Pub. Serv. Co. of Colo., 690 F.3d
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1174, 1191 (10th Cir. 2012). See also Nguyen ex rel. United States v. City of Cleveland, 1:09cv-452, 2016 WL 1031096 (N.D. Ohio March 15, 2016). As a result, the plaintiffs’ claim for
declaratory relief cannot establish standing to bring an RCRA citizen suit.
The plaintiffs’ claim for injunctive relief is also insufficient to confer standing in this
matter. In Ellis, the Sixth Circuit held that the district court committed reversible error by
awarding injunctive relief when consent decrees between the defendant and the EPA were
already addressing the injuries alleged in the complaint. Ellis, 390 F.3d 476. The court noted
that “the decrees were just three months old when the district court entered its injunction,
meaning that the remedial requirements imposed by the decrees either had just been completed
or had not yet been completed at all.” Id. Further, the court was rightly concerned that the
plaintiffs “not only sought to obtain an injunction on the same terms as the consent decrees,
but they also sought to obtain relief on ‘more stringent terms than those worked out by the
EPA.’” Id. at 477 (quoting EPA v. City of Green Forest, Arkansas, 921 F.2d 1394, 1403-04
(8th Cir. 1990)). As the Sixth Circuit explained,
[s]uch second-guessing of the EPA’s assessment of an appropriate remedy—a
mere three months after the entry of the decrees—fails to respect the statute’s
careful distribution of enforcement authority among the federal EPA, the States
and private citizens, all of which permit citizens to act where the EPA has
‘failed’ to do so, not where the EPA has acted but has not acted aggressively
enough in the citizen’s view.
Id. (quoting Gwaltney, 484 U.S. at 376). Courts in this circuit have applied Ellis in the standing
context. See Little, 33 F. Supp. 3d at 803. When injunctive relief is not available under Ellis,
the redressability requirement is not satisfied, and the plaintiff cannot demonstrate that it has
standing to seek that form of relief. Id.; see also Laidlaw, 528 U.S. at 181.
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All of the factors that made injunctive relief inappropriate in Ellis are present in this
case. The plaintiffs brought the same concerns that form the basis of this action before the
Cabinet during state regulatory proceedings. [See Record No. 1, Exhibits A-C; Record No.
16, Exhibits 5 and 10.] The Cabinet addressed the plaintiffs’ concerns, in part, by requiring
KU to submit a GWRAP and two CAPs, and to pay a $25,000 penalty. [See Record No. 16,
Exhibits 1, 15, 16, 19.] After receiving the plaintiffs’ RCRA notice, KU and the Cabinet
entered into an Agreed Order which was based on the same groundwater studies that underlie
this action and was designed to “address any threat or potential threat to human health and the
environment associated with management and storage of CCR at [the] CCR Brown Station.”
[Record No. 16, Exhibit 15, ¶¶ 4-12] In line with the plaintiffs’ previous demands for further
study, the CAPs call for extensive groundwater studies and require KU to recommend remedial
actions when the studies are complete. [See Record No. 16, Exhibits 5, 10, 16, 19.]
The plaintiffs filed this action just three months after the Cabinet and KU entered into
the Agreed Order. [Compare Record No. 1 with Record No. 16, Exhibit 16.] The studies
required by the CAPs have not been completed, and KU has not yet made the required
recommendations of what remedial actions are warranted. [See Record No. 16, Exhibit 16.]
As a result, “the remedial requirements imposed by the [Agreed Order] either ha[ve] just been
completed or ha[ve] not yet been completed at all.” Ellis, 390 F.3d 476.
Nonetheless, the plaintiffs claim that the remedial actions required by the Cabinet are
“unnecessary, flawed, and unaccompanied by any commitment to implement effective
remedial action,” and that therefore the Court could redress their members’ injuries by issuing
more appropriate relief, such as ordering KU to excavate the buried coal ash or to clean up the
pollution in Herrington Lake. [Record No. 27, p. 19-20] This amounts to little more than an
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invitation to “second-guess[]” the state regulatory authority and to award relief on “more
stringent terms” than it has imposed. Id. at 477 (quotation omitted). Accepting this invitation
would “fail[] to respect the statute’s careful distribution of enforcement authority among the
federal EPA, the States and private citizens, all of which permit citizens to act where the EPA
has ‘failed’ to do so, not where the EPA has acted but has not acted aggressively enough in the
citizen’s view.” Id. (quotation omitted). As a result, the requested injunctive relief is not
available to redress the alleged injuries, and cannot support a finding of standing. Accordingly,
the plaintiffs’ RCRA claims will be dismissed for lack of jurisdiction, as the plaintiffs’
members’ lack standing to bring an RCRA citizen suit at this time.1
IV.
Congress enacted the CWA “to restore and maintain the chemical, physical, and
biological integrity of the Nation’s waters.” 33 U.S.C. § 1251(a). To further this goal, the
CWA provides that the “discharge of any pollutant by any person shall be unlawful,” unless
authorized by a permit under the National Pollutant Discharge Elimination System (“NPDES”)
or another statutory exception. 33 U.S.C. §§ 1311(a); 1342. The term “discharge of a
pollutant” means, as relevant here, “any addition of any pollutant to navigable waters from any
point source . . . .” 33 U.S.C. § 1362(12) (emphasis added). The term “pollutant” includes,
1
Because the Court finds that the plaintiffs lack standing to bring an RCRA claim, it need not
consider the defendant’s Burford abstention argument. However, the Court notes that the Ellis
court’s concerns regarding the distribution of enforcement authority among the EPA, states,
and citizens are similar to the considerations of federalism and comity that underlie the Burford
abstention doctrine, and courts in this circuit have abstained under Burford in circumstances
similar to those presented in this case. See, e.g., Coal. for Health Concern, 60 F. 3d at 1189;
Ellis, 390 F.3d at 480; Ohio Valley Envtl. Coal. v. River Cities Disposal, LLC, 15-cv-47, 2016
WL 1255717, at *5 (E.D. KY Mar. 29, 2016).
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among other things, “solid waste,” “chemical wastes,” and “industrial waste” discharged into
water. Id. § 1362(6). A “point source” is “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 discharge.” Id. § 1362(14). The term “navigable
waters” means “the waters of the United States, including the territorial seas.” Id. § 1362(7).
The plaintiffs contend that KU has violated the CWA by adding pollutants to HQ
Stream from the Main Ash Pond and the Auxiliary Ash Pond without an NPDES permit.
[Record No. 1, ¶¶ 70-78] KU possesses a permit authorizing it to make regulated discharges
from the Main Ash Pond and the Auxiliary Ash Pond through an external outfall designated
as Outfall 001. [Id. ¶¶ 44-47] However, the plaintiffs claim that, in addition to these permitted
discharges, KU has made and continues to make unpermitted discharges into HQ stream, a
surface water body within the jurisdiction of the CWA. [Id. ¶¶ 48-49] These discharges
allegedly result from naturally flowing groundwater, which is infiltrating the settling ponds
and transporting the CCR pollutants into HQ Stream by way of the hydrologically connected
HQ and Briar Patch Springs. [Id. ¶¶ 50-56, 61-67]
KU has moved to dismiss on the grounds that the plaintiffs have not alleged that
pollutants are conveyed directly from the Main or Auxiliary Ash Pond to HQ stream, and to
the extent that pollutants enter navigable waters after migrating through groundwater, the
pollution is non-point source pollution, which cannot form the basis of a CWA citizen suit.
[Record No. 16, p. 27] The plaintiffs respond that they have sufficiently alleged that the
groundwater is “hydrologically connected” to HQ Spring, and that “discharges of pollutants to
navigable waters via a discrete, hydrologically-connected conduit are governed by the CWA.”
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[Record No. 27, p. 32] Thus, the issue before the Court is whether discharges into groundwater
that is hydrologically connected to navigable waters constitute the “addition of any pollutant
to navigable waters from any point source” under the CWA. 33 U.S.C. § 1362(12). Other
district courts have split on this question. See, e.g., Tenn. Clean Water Network v. Tenn. Valley
Auth., 3:15-cv-424, 2017 WL 3476069, *42-43 (M.D. Tenn. August 4, 2017) (collecting
cases).
There are three distinct reasons that hydrologically connected groundwater might be
subject to regulation under the CWA. First, hydrologically connected groundwater could itself
constitute a “navigable water” under the CWA such that an adding a pollutant to hydrologically
connected groundwater would constitute the discharge of a pollutant “to navigable waters.”
Second, hydrologically connected groundwater could constitute a “point source” under the
CWA such that discharging a pollutant to a “navigable water” from hydrologically connected
groundwater would constitute a discharge “from any point source.” Third, hydrologically
connected groundwater could constitute a non-point source conveyance that falls within the
CWA even though it is itself neither a point source nor a navigable water.
The plaintiffs distance themselves from the view that hydrologically connected
groundwater itself constitutes a “navigable water.” [See Record No. 27, p. 36.] And for good
reason.
Courts have overwhelmingly found that groundwater, even if hydrologically
connected to navigable waters, is not itself a navigable water under the CWA. See, e.g., Rice
v. Harken Expl. Co., 250 F.3d 264, 269 (5th Cir. 2001) (“[G]round waters are not protected
waters under the CWA.”); Vill. of Oconomowoc Lake v. Dayton Hudson Corp., 24 F.3d 962,
965 (7th Cir. 1994) (“Neither the Clean Water Act nor the EPA’s definition asserts authority
over ground waters, just because these may be hydrologically connected with surface
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waters.”). (citations omitted); Cape Fear River Watch, Inc. v. Duke Energy Progress, Inc., 25
F. Supp. 3d 798, 810 (E.D.N.C. 2014) (“Congress did not intend for the CWA to extend federal
regulatory authority over groundwater, regardless of whether that ground water is eventually
or somehow ‘hydrologically connected’ to navigable surface waters.”); Copper Indus., Inc. v.
Abbott Labs., No. 93-CV-193, 1995 WL 17079612, *4 (W.D. Mich. May 5, 1995) (“[T]he fact
that these ground waters are hydrologically connected to some surface waters is insufficient to
transform this case to a [CWA] cause of action.”).
The reasons for this are three-fold. First, considering ground waters to be “navigable
waters” would strain the language of the CWA. See Vill. of Oconomowoc Lake, 24 F.3d at
965 (“[W]e are confident that the statute Congress enacted excludes some waters, and ground
waters are a logical candidate.”). Second, the legislative history of the CWA demonstrates
that Congress extensively considered whether to extend the CWA to groundwater, and decided
against it. See Exxon Corp. v. Train, 554 F.2d 1310, 1325-29 (5th Cir. 1977) (discussing the
legislative history). The Senate Committee on Public Works recognized “the essential link
between ground and surface waters and the artificial nature of any distinction.” Id. at 1325
(quoting S. Rep. No. 414, 92d Cong., 1st Sess. 73 (1971)). But after a “heated debate,”
Congress rejected an amendment that would have extended the CWA to groundwater. Id. at
1327-29. Instead, Congress determined that regulation of groundwater should be left to the
states. Id. at 1325-29; see also Kelley ex rel. Mich. v. United States, 618 F. Supp. 1103, 1107
(W.D. Mich. 1985).
Third, in Rapanos v. United States, 547 U.S. 715 (2006), the Supreme Court “eschewed
a broad interpretation of ‘navigable waters’ and repeatedly cautioned against ‘attempting to
expand the definition of navigable waters to encompass virtually all water, regardless of its
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actual navigability, location, or consistency of flow.’” Upstate Forever v. Kinder Morgan
Energy Partners, L.P., 252 F. Supp. 3d 488, 497-98 (quoting Chevron U.S.A., Inc. v. Apex Oil
Co., 113 F. Supp. 3d 807, 817 (D. Md. 2015)).
Accordingly, the Court finds that
hydrologically connected groundwater does not itself constitute navigable waters. This
conclusion finds support in “both the language and legislative history of the CWA and in the
Supreme Court’s decision in Rapanos.” Cape Fear River Watch, 25 F. Supp. 3d at 810.
However, hydrologically connected groundwater could still be subject to regulation
under the CWA if the discharge of a pollutant from hydrologically connected groundwater into
navigable waters constituted a discharge from a “point source.” Congress “drew a distinct
line” between the discharge of pollutants from point sources and non-point sources in the
CWA. Or. Nat’l Res. Council v. United States Forest Serv., 834 F.2d 842, 849 (9th Cir. 1987).
Discharges from point sources are subject to regulation under the NPDES, whereas the
regulation of non-point sources is left the states. Id. The Court must respect the line drawn
by Congress, and cannot extend the CWA’s NPDES requirements to non-point source
pollution. “This is true even though non-point-source pollution is a major contributor to the
pollution of the nation’s waters.” 26 Crown Assocs., LLC v. Greater New Haven Reg’l Water
Pollution Control Auth., 2017 WL 2960506, at *8 (D. Conn. July 11, 2017) (citing Or. Nat’l
Res. Council, 834 F.2d at 849). Courts are divided on whether hydrologically connected
groundwater qualifies as a point source under the CWA. Compare id., with Hawai’i Wildlife
Fund v. Cty of Maui, 24 F. Supp. 3d 980, 995 (D. Haw. 2014). The undersigned concludes
that it is not.
The CWA defines a “point source” as “any discernible, confined and discrete
conveyance, including but not limited to any pipe, ditch, channel, tunnel, conduit, well,
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discrete fissure, container, rolling stock, concentrated animal feeding operation, or vessel or
other floating craft, from which pollutants are or may be discharge.” 33 U.S.C. § 1362(14).
Non-point source pollution, by contrast “does not result from a discharge at a specific, single
location (such as a single pipe) but generally results from land runoff, precipitation,
atmospheric deposition, or percolation.” Cordiano v. Metacon Gun Club, Inc., 575 F.3d 199,
220 (2d Cir. 2009) (quoting EPA Office of Water, Nonpoint Source Guidance 3 (1987)).
Groundwater is, by its nature, “a diffuse medium” and not the kind of discernible, confined
and discrete conveyance contemplated by the CWA’s definition of “point source.” See 26
Crown Assocs., 2017 WL 2960506, at *8 (“It is basic science that ground water is widely
diffused by saturation within the crevices of underground rocks and soil.”). As a result, the
discharge of a pollutant from hydrologically connected groundwater to a navigable water does
not constitute the discharge of a pollutant from a point source to a navigable water under the
CWA. See id.; Upstate Forever v. Kinder Morgan Energy Partners, L.P., 252 F. Supp. 3d
488, 494 (D.S.C. 2017) (“The migration of pollutants through soil and groundwater is nonpoint
source pollution that is not within the purview of the CWA.”).
The final rationale for subjecting hydrologically connected groundwater to the CWA’s
permitting requirement is that if there is a close hydrologic connection between groundwater
and a navigable water, then the discharge of a pollutant from a point source through the
hydrologically connected groundwater to a navigable water could constitute the addition of a
pollutant to a navigable water from a point source even though the groundwater itself is neither
a point source nor a navigable water. The EPA has sometimes expressed this view. See, e.g.,
Amendments to the Water Quality Standards Regulations that Pertain to Standards on Indian
Reservations, Final Rule, 56 Fed. Reg. 64876, 64892 (Dec. 12, 1991) (“[T]he affected ground
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waters are not considered ‘waters of the United States’ but discharges to them are regulated
because such discharges are effectively discharges to the directly connected surface waters.”).2
Additionally, some courts have held that coal ash ponds qualify as “point sources” and that the
discharge of pollutants from a point source ash pond to a navigable water via hydrologically
connected groundwater may be subject to the CWA’s permit requirements even if the
groundwater itself is neither a navigable water nor a point source, so long as there is a “direct”
hydrologic connection. See Tenn. Clean Water Network, 2017 WL 3476069, *42-43; Sierra
Club v. Va. Elec. & Power Co., 247 F. Supp. 3d 753 (E.D. Va. 2017).
Adopting this theory would be inconsistent with the text and structure of the CWA.
The primary problem with this rationale is that, if adopted, “any non-point-source pollution
(such as ordinary surface run-off from the land into navigable waters) could invariably be
reformulated as point-source pollution by going up the causal chain to identify the initial point
sources of the pollutants that eventually ended up through non-point sources to come to rest in
2
Although an agency’s interpretation of a statute that it administers is entitled to great
deference, see Chevron U.S.A. Inc. v. Nat. Res. Def. Council, 467 U.S. 837, 843–44 (1984),
Chevron deference does not apply in this case because the “EPA has offered no formal or
consistent interpretation of the CWA that would subject discharges to groundwater to the
NPDES permitting requirement.” Umatilla Waterquality Protective Ass’n, Inc. v. Smith
Frozen Foods, Inc., 962 F. Supp. 1312, 1319 (D. Or. 1997). Since Umatilla was decided, the
EPA has interpreted the CWA as applying to hydrologically connected groundwater in
proposed rules, manuals, and informal guidances. [See Record No. 27, p. 37 n. 129.] However,
interpretations such as these, “all of which lack the force of law—do not warrant Chevronstyle deference.” Christensen v. Harris Cty., 529 U.S. 576, 578 (2000). Instead, such
interpretations “are ‘entitled to respect,’ . . . but only to the extent that those interpretations
have the ‘power to persuade.’” Id. (citation omitted). For the reasons stated in this
Memorandum Opinion and Order, the Court does not find the position expressed in these
documents to be persuasive.
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navigable waters.” 26 Crown Assocs., 2017 WL 2960506, at *8.3 This would lead to the
extensive regulation of non-point source pollution and would “effectively read the ‘point
source’ requirement out of the Clean Water Act.” Id. at *9.
Extending the reach of the CWA in this way also would be inconsistent with its
federalist structure. The CWA “does not purport to regulate (or to require a permit for) every
act that involves the noxious pollution of clean water. Instead, consistent with long-established
principles of federalism, the Clean Water Act’s permitting requirements are limited to
regulating the discharge of pollutants into the navigable waters of the United States.” Id. at
*6. Regardless of the theory underlying the plaintiffs’ claims, it remains the case that
“Congress did not intend for the CWA to extend federal regulatory authority over groundwater,
regardless of whether that ground water is eventually or somehow ‘hydrologically connected’
to navigable surface waters.” Cape Fear River Watch, Inc. v. Duke Energy Progress, Inc., 25
F. Supp. 3d 798, 810 (E.D.N.C. 2014). Instead, Congress determined that the regulation of
groundwater pollution was to be left to the states. See Train, 554 F.2d at 1325-29; see also
Kelley, 618 F. Supp. at 1107; Or. Nat’l Res. Council, 834 F.2d at 849.
The courts that have found that hydrologically connected groundwater is subject to the
NPDES permit requirement have relied heavily on the purpose of the CWA. See, e.g., Va.
Elec. & Power Co., 247 F.3d at 762 (“Congress intended the CWA to protect the water quality
3
Courts have attempted to mitigate this result by stating that non-point source groundwater
pollution is only subject to the CWA when there is a “direct” hydrologic connection to
navigable waters. See, e.g., Tenn. Clean Water Network, 2017 WL 3476069, at *44. However,
because this requirement is not grounded in the text or legislative history of the CWA, the
standards courts have employed to determine when a hydrologic connection is sufficiently
“direct” to fall within this exception have varied. [See Record No. 28, p. 12 n.13 (collecting
standards adopted by different courts).]
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of the nation’s surface water. Where the facts show a direct hydrological connection between
ground and surface water, that goal would be defeated if the CWA’s jurisdiction did not extend
to discharges to groundwater.”); Tenn. Clean Water Network, 2017 WL 3476069, at *43
(quoting N. Cal. River Watch v. Mercer Fraser Co., No. C-04-4620, 2005 WL 2122052, at *2
(N.D. Cal. Sept. 1, 2005) (“[I]t would hardly make sense for the CWA to encompass a polluter
who discharges pollutants via a pipe running from the factory directly to the riverbank, but not
a polluter who dumps the same pollutants into a man-made settling basin some distance short
of the river and then allows the pollutants to seep into the river via the groundwater.”)).
However, the Supreme Court has “often criticized,” relying on the statute’s purpose to the
detriment of its text “noting that no law pursues its purpose at all costs, and that the textual
limitations upon a law’s scope are no less a part of its ‘purpose’ than its substantive
authorizations.” Rapanos, 547 U.S. at 752 (plurality opinion). Further, “clean water is not the
only purpose of the statute. So is the preservation of primary state responsibility for ordinary
land-use decisions.” Id. at 755-56 (plurality opinion). If the CWA pursued the goal of
protecting surface water quality at all costs, it would not make sense to exempt any
groundwater from the CWA given “the essential link between ground and surface waters and
the artificial nature of any distinction.” Train, 554 F.2d at 1325 (quoting S. Rep. No. 414, 92d
Cong., 1st Sess. 73 (1971)). Indeed, the distinction between point- and non-point sources
would appear untenable in light of this purpose, given that “non[-]point sources of pollution
constitute a major source of pollution in the nation’s waters.” Or. Nat’l Res. Council, 834 F.2d
at 849. However, Congress has decided to distinguish between ground and surface waters and
between point- and non-point source pollution, and to regulate them differently. The Court
declines to undermine these choices to effectuate the CWA’s supposed purpose.
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Accordingly, the Court finds that the discharge of pollutants to a navigable water via
hydrologically connected groundwater is not subject to the CWA’s NPDES permit
requirement. As a result, the plaintiffs’ allegations are insufficient to state a claim for the
unlawful “discharge of a pollutant” without a permit under the CWA, and the plaintiffs’ CWA
claim will be dismissed. 33 U.S.C. §§ 1311(a); 1362(12).
V.
For the foregoing reasons, it is hereby
ORDERED as follows:
1.
The defendant’s motion to dismiss [Record No. 16] is GRANTED.
2.
The plaintiffs’ RCRA claim is DISMISSED, without prejudice.
3.
The plaintiffs’ CWA claim is DISMISSED, with prejudice.
4.
A corresponding Judgment will be entered this date.
This 28th day of December, 2017.
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