Sierra Club v. United States Environmental Protection Agency

District Court, S.D. West Virginia·Decided August 1, 2024·No. 3:24-cv-00130·Unknown

Opinion

IN THE UNITED STATES DISTRICT COURT FOR THE SOUTHERN DISTRICT OF WEST VIRGINIA

HUNTINGTON DIVISION

SIERRA CLUB; WEST VIRGINIA HIGHLANDS CONSERVANCY, INC., and WEST VIRGINIA RIVERS COALITION, INC,

Plaintiffs,

v. CIVIL ACTION NO. 3:24-0130

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY; MICHAEL S. REGAN, Administrator, United States Environmental Protection Agency; and ADAM ORTIZ, Regional Administrator, United States Environmental Protection Agency, Region III,

Defendants.

MEMORANDUM OPINION & ORDER

Before the Court is West Virginia Coal Association’s Motion to Intervene as a Defendant. See ECF No. 17. The Court DENIES the Motion. BACKGROUND I The Clean Water Act aims to “restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.” 33 U.S.C. § 1251(a). To realize this goal, the Act requires EPA and States to participate in a “comprehensive” and “all-encompassing program” of water pollution regulation. Milwaukee v. Illinois, 451 U.S. 304, 317 (1981). This case implicates one part of this program—the total maximum daily load (“TMDL”) system. See Compl. ¶¶ 45–60, ECF No. 1. A States—subject to EPA’s approval—must establish “water quality standards” for navigable waters within their borders. See 33 U.S.C. § 1313(a). These standards “consist of the designated uses of the navigable waters involved and the water quality criteria for such waters based upon such uses.” Id. § 1313(c)(2)(A). States must regularly review their water quality standards and

modify them “as appropriate.” Id. § 1313(c)(1). To achieve water quality standards, the Clean Water Act imposes “effluent limitations.” See id. §§ 1311(b)(1)(A), (B). An “effluent limitation” is “any restriction . . . on quantities, rates, and concentrations of chemical, physical, biological, and other constituents which are discharged from point sources into” certain waters. Id. § 1362(11). A “point source” is “any discernible, confined and discrete conveyance . . . from which pollutants are or may be discharged.” Id. § 1362(14). See also Am. Farm Bureau Fed. v. U.S. E.P.A., 792 F.3d 281, 289 (3d Cir. 2015) (listing drainpipes at wastewater treatment plants as an example). The Clean Water Act anticipates point-source effluent limitations will be the “front line”

defense against water pollution. Id. But the Act is not naïve. It recognizes point-source effluent limitations may not protect all waters. To fill this gap, the Act requires States to “identify those waters within [their] boundaries for which the effluent limitations” of point sources are “not stringent enough to implement any water quality standard applicable to such waters.” 33 U.S.C. § 1313(d)(1)(A). These are called “impaired waters.” See, e.g., Ohio Valley Envtl. Coal., Inc. v. Pruitt, 893 F.3d 225, 227 (4th Cir. 2018) (using term). States must provide EPA with their list of impaired waters alongside a “total maximum daily load” for certain pollutants “from time to time.” 33 U.S.C. §§ 1313(c)(1)), (e)(2). A TMDL is “[t]he sum of the individual [waste load allocations] for point sources and [load allocations] for nonpoint sources and natural background.” 40 C.F.R. § 130.2(i). Said succinctly: a TMDL sets the maximum daily discharge of a particular pollutant into a water. See Pruitt, 893 F.3d at 227. When States provide their impaired water lists and TMDLs directly to EPA, they make an “actual submission.” Sometimes, however, States neglect or refuse to provide their information to EPA. If this apathy or defiance persists long enough, the State’s inaction may become a

“constructive submission” of “no TMDLs” to EPA. See id. at 229–230 (reviewing caselaw). Regardless of whether States actually or constructively submit their TMDLs to EPA, EPA must review them within thirty days. See 33 U.S.C. § 1313(d)(2). If it disapproves of a TMDL, EPA must issue its own TMDL within thirty days of the State’s submission. See id. Once issued, TMDLs are “not self-executing.” Am. Farm Bureau Fed., 792 F.3d at 291. Instead, they are “informational tools,” Pronsolino v. Nastri, 291 F.3d 1123, 1129 (9th Cir. 2002), and “cornerstones” for other pollution-reduction plans, Am. Farm Bureau Fed., 792 F.3d at 291. One of these other pollution-reduction plans is the National Pollution Discharge Elimination System. See 40 C.F.R. § 130.7(a) (explaining how to “incorporat[e]” a TMDL into a

state-NPDES permit system). Under this system, point-source operators must obtain a permit before discharging any pollutant into a body of water. See 33 U.S.C. §§ 1342(a), (b) (establishing federal and state systems); id. § 1362(12) (defining “discharge of a pollutant” as the “addition of any pollutant” into certain waters). These permits must be consistent with the wasteload allocations created in EPA-approved TMDLs. See 40 C.F.R. § 122.44(d)(1)(vii)(B). EPA—or by delegation, States—can issue NPDES permits. See Stewards v. A&G Coal Corp., 758 F.3d 560, 563 (4th Cir. 2014). Since 1982, EPA has delegated authority to issue NPDES permits to West Virginia. See State ex rel. Bell v. Cummings, 540 S.E.2d 917, 921 n.2 (W. Va. 1999). As a result, the Mountain State administers its own NPDES permit program through the West Virginia Department of Environmental Protection. See W. Va. Code § 22-11-4(a)(1). Despite this autonomy, WVDEP must provide advance notice to EPA before it issues any NPDES permit. See 33 U.S.C. § 1342(d)(1). If EPA objects to the permit as “outside the guidelines and requirements” of the Clean Water Act, “[n]o permit shall issue.” Id. § 1342(d)(2). See also 40 C.F.R. §§ 123.44 (“EPA review of and objections to State permits”); 123.29 (“State permit

programs shall provide that no permit shall be issued when the Regional Administrator has objected in writing under § 123.44.”). State-issued NPDES permits must be for “fixed terms not exceeding five years.” 33 U.S.C. § 1342(b)(1)(B). II West Virginia has “long resisted” the Clean Water Act. Pruitt, 893 F.3d at 227–28 (reviewing this history). This case is yet another chapter in this tortured tale. A Under state law, West Virginia identifies impaired waters based on narrative water quality standards—including measuring “[m]aterials in concentrations which are harmful . . . to man,

animal, or aquatic life.” Id. at 228 (quoting W. Va. Code § 47-2-3.2(e)). For years, WVDEP used the West Virginia Stream Condition Index to identify impaired waters. See id. Using this metric, WVDEP identified 573 impaired waters. See id. For some of these waters, WVDEP identified the “cause of impairment” as “ionic toxicity.” Id. In 2012, the West Virginia State Legislature changed course.

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