City of Arcadia v. United States Environmental Protection Agency

265 F. Supp. 2d 1142, 2003 U.S. Dist. LEXIS 9044, 2003 WL 21262022
CourtDistrict Court, N.D. California
DecidedMay 16, 2003
DocketC 02-5244 SBA
StatusPublished
Cited by18 cases

This text of 265 F. Supp. 2d 1142 (City of Arcadia v. United States Environmental Protection Agency) is published on Counsel Stack Legal Research, covering District Court, N.D. California primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
City of Arcadia v. United States Environmental Protection Agency, 265 F. Supp. 2d 1142, 2003 U.S. Dist. LEXIS 9044, 2003 WL 21262022 (N.D. Cal. 2003).

Opinion

ORDER GRANTING DEFENDANTS’ MOTION TO DISMISS, DENYING AS MOOT PLAINTIFFS’ MOTION FOR PARTIAL SUMMARY JUDGMENT, AND DISMISSING ACTION

ARMSTRONG, District Judge.

Plaintiffs City of Arcadia and other California cities (collectively, “Plaintiffs”) bring this action against defendants United States Environmental Protection Agency (“EPA”), the EPA Administrator, and the EPA Region IX Administrator (collectively, “Defendants”) for injunctive and declaratory relief. The Natural Resources Defense Council, Santa Monica BayKeeper, and Heal the Bay (collectively, “Interve-nors”) have intervened as defendants.

Now before the Court are Defendants’ Motion to Dismiss Second Amended Complaint (the “Motion to Dismiss”), in which Intervenors join, and Plaintiffs’ Motion for Summary Adjudication of Issues (the “Motion for Partial Summary Judgment”). Having read and considered the papers submitted and. being fully informed, the Court GRANTS the Motion to Dismiss, DENIES AS MOOT the Motion for Partial Summary Judgment, and DISMISSES this action. 1

I. BACKGROUND 2

A. Statutory and Regulatory Background

1. Water Pollution Control Under the Clean Water Act

The Clean Water Act (“CWA”), 33 U.S.C. §§ 1251-1387, utilizes two fundamental approaches to control water pollution: technology-based regulations and water quality standards. Technology-based *1144 regulations seek to reduce pollution by requiring a discharger to effectuate equipment or process changes, without reference to the effect on the receiving water; water quality standards fix the permissible level of pollution in a specific body of water regardless of the source of pollution.

The National Pollutant Discharge Elimination System (“NPDES”) permit program is a key means of implementing both technology-based requirements and water quality standards. 33 U.S.C. §§ 1311(b)(1)(C), 1342(a)(1); 40 C.F.R. § 122.44(a), (d)(1). An NPDES permit establishes specific limits of pollution for an individual discharger. A discharge of pollutants (other than dredged or fill material) from any “point source,” which is defined as “any discernible, confined and discrete conveyance ... from which pollutants are or may be discharged,” 33 U.S.C. § 1362(14), into the waters of the United States is prohibited unless that discharge complies with the discharge limits and other requirements of an NPDES permit. Id. §§ 1311(a), 1362(12). At present, 45 states, including California, are authorized to administer the NPDES permit program. State Program Status, at http://cfpub.epa.gov/npdes/states-tats.cfm?program_id=45 & view=general. In the remaining states, EPA issues the permits. 33 U.S.C. § 1342(a).

2. Total Maximum Daily Loads (“TMDLs”)

Section 303(d) of the CWA and EPA’s implementing regulations require states to identify and prioritize waterbodies where technology-based effluent limitations and other required controls are insufficiently stringent to attain water quality standards. See 33 U.S.C. § 1313(d); 40 C.F.R. § 130.7(b). States must develop a “total maximum daily load,” or “TMDL,” for each pollutant of concern in each water-body so identified. A TMDL represents the maximum amount of pollutant “loading” that a waterbody can receive from all combined sources without exceeding applicable state water quality standards. Although the term “total maximum daily load” is not expressly defined in the CWA, EPA’s regulations define a TMDL for a pollutant as the sum of: (1) the “wasteload allocations,” which is the amount of pollutant that can be discharged to a waterbody from point sources, (2) the “load allocations,” which represent the amount of a pollutant in a waterbody attributable to nonpoint sources or natural background, and (3) a margin of safety. 40 C.F.R. §§ 130.2(g)-(i), 130.7(c)(1).

Under CWA Section 303(d)(2), EPA is required to review and approve or disapprove TMDLs established by states for impaired waters within thirty days of submission. 33 U.S.C. § 1313(d)(2). If EPA disapproves a state TMDL submission, EPA must issue its own TMDL for that waterbody within thirty days. Id.

3. Implementation of TMDLs

TMDLs established under Section 303(d)(1) of the CWA function primarily as planning devices and are not self-executing. Pronsolino v. Nastri, 291 F.3d 1123, 1129 (9th Cir.2002) (“TMDLs are primarily informational tools that allow the states to proceed from the identification of waters requiring additional planning to the required plans.”) (citing Alaska Ctr. for the Env’t v. Browner, 20 F.3d 981, 984-85 (9th Cir.1994)). A TMDL does not, by itself, prohibit any conduct or require any actions. Instead, each TMDL represents a goal that may be implemented by adjusting pollutant discharge requirements in individual NPDES permits or establishing nonpoint source controls. See, e.g., Sierra Club v. Meiburg, 296 F.3d 1021, 1025 (11th Cir.2002) (“Each TMDL serves as the goal for the level of that pollutant in the water-body to which that TMDL applies.... The theory is that individual-discharge permits *1145 will be adjusted and other measures taken so that the sum of that pollutant in the waterbody is reduced to the level specified by the TMDL.”); Idaho Sportsmen’s Coalition v. Browner, 951 F.Supp. 962, 966 (W.D.Wash.1996) (“TMDL development in itself does not reduce pollution.... TMDLs inform the design and implementation of pollution control measures.”); Pronsolino, 291 F.3d at 1129 (“TMDLs serve as a link in an implementation chain that includes ... state or local plans for point and nonpoint source pollution reduction .... ”); Idaho Conservation League v. Thomas, 91 F.3d 1345, 1347 (9th Cir.1996) (noting that a TMDL sets a goal for reducing pollutants). Thus, a TMDL forms the basis for further administrative actions that may require or prohibit conduct with respect to particularized pollutant discharges and waterbodies.

Free access — add to your briefcase to read the full text and ask questions with AI

Related

Kimber v. Harker
S.D. California, 2024
Williams v. Alameda County
N.D. California, 2023
City of Kennett v. Envtl. Prot. Agency
887 F.3d 424 (Eighth Circuit, 2018)
Conway v. State Water Resources Control Board
235 Cal. App. 4th 671 (California Court of Appeal, 2015)
Sierra Club v. Patriot Mining Co.
West Virginia Supreme Court, 2014
Klamath-Siskiyou Wildlands Center v. Graham
899 F. Supp. 2d 948 (E.D. California, 2012)
City of Arcadia v. State Water Resources Control Board
38 Cal. Rptr. 3d 373 (California Court of Appeal, 2006)
Wyoming v. United States Department of the Interior
360 F. Supp. 2d 1214 (D. Wyoming, 2005)
Bravos v. Green
306 F. Supp. 2d 48 (District of Columbia, 2004)

Cite This Page — Counsel Stack

Bluebook (online)
265 F. Supp. 2d 1142, 2003 U.S. Dist. LEXIS 9044, 2003 WL 21262022, Counsel Stack Legal Research, https://law.counselstack.com/opinion/city-of-arcadia-v-united-states-environmental-protection-agency-cand-2003.