San Francisco Baykeeper v. Whitman

287 F.3d 764, 2002 WL 574110
CourtCourt of Appeals for the Ninth Circuit
DecidedApril 15, 2002
DocketNo. 01-16111
StatusPublished
Cited by1 cases

This text of 287 F.3d 764 (San Francisco Baykeeper v. Whitman) is published on Counsel Stack Legal Research, covering Court of Appeals for the Ninth Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
San Francisco Baykeeper v. Whitman, 287 F.3d 764, 2002 WL 574110 (9th Cir. 2002).

Opinion

OPINION

HUG, Circuit Judge.

OVERVIEW

San Francisco BayKeeper, an environmental group, filed this action under the Clean Water Act (“CWA”), 33 U.S.C. § 1365(b), seeking a declaration that the State of California had failed to implement an adequate water pollution control program and failed to establish total maximum daily loads (“TMDL”) of pollutants which could be introduced into polluted waters. BayKeeper contended that California was years behind in implementing a TMDL program, and consequently the U.S. Environmental Protection Agency (“EPA”) had a non-discretionary duty to establish water pollution standards for California because the State had failed to make the required submissions. Bay-Keeper appeals the district court’s dismissal of this claim on partial summary judgment, certified pursuant to Fed. R.Civ.P. 54(b). BayKeeper also challenges the district court’s reliance on the EPA’s Program Review document. We affirm.

I. BACKGROUND

A. Statutory Background

In 1972, Congress passed the Clean Water Act (“CWA” or “Act”) to “restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.” 33 U.S.C. § 1251. In order to attain this objective, Congress sought to eliminate the discharge of pollutants into the navigable waters by 1985. Id.

The Act focuses on two possible sources of pollution: point sources and nonpoint sources. Congress dealt with the problem of point source pollution using the National Pollution Discharge Elimination System (“NPDES”) permit process. Under this approach, compliance rests on technology-based controls that limit, the discharge of pollutants from any point source into certain waters unless that discharge complies with the Act’s specific requirements. 33 U.S.C. §§ 1311(a), 1362(12).

When the NPDES system fails to adequately clean up certain rivers, streams or smaller water segments, the Act requires use of a water-quality based approach. States are required to identify such waters, which are to be designated as “water quality limited segments” (“WQLS”). The [767]*767states must then rank these waters in order of priority, and based on that ranking, calculate levels of permissible pollution called “total maximum daily loads” or “TMDLs.” 33 U.S.C. §§ 1313(d)(1)(A), (C). TMDLs are the maximum quantity of a pollutant the water body can receive on a daily basis without violating the water quality standard. The TMDL calculations are to ensure that the cumulative impacts of multiple point source discharges and nonpoint source pollution are accounted for. States may then institute whatever additional cleanup actions are necessary, which can include further controls on point and nonpoint pollution sources.

Under the Act, states are required to submit lists of WQLSs and TMDLs to the EPA at certain times; the first such submission was due by June 26, 1979. Sec. 303(d), 33 U.S.C. § 1313(d)(2).1 Once a state makes the required submission, certain mandatory duties by EPA are triggered. Within 30 days, EPA must review the state’s submissions. If approved by EPA, the submissions are incorporated by the state into its continuing planning process established under § 1313(e)(3). If EPA does not approve the submission, however, the EPA has 30 days after disapproval to make its own identification of waters and establish TMDLs necessary to implement the applicable water quality standards. 33 U.S.C. § 1313(d)(2). The Act is silent as to the nature of EPA’s obligations if a state, such as California here, fails to make any initial submission at all.

B. California’s TMDL Program

As this is a review of summary judgment, we must construe the facts in the light most favorable to BayKeeper, the non-moving party in this case. BayKeeper contends that California did not submit any TMDLs until 1994, which was over 15 years after the initial deadline for making a submission pursuant to § 303(d) of the Act.

Since that time, however, California has dedicated substantial resources to the development of its TMDL program. According to the May 2000 report of the EPA on California’s TMDL Program Review, the state has completed more than 46 TMDLs for waters on California’s lists. In addition, the report demonstrates that California has established a schedule for completing all TMDLs for waters on its 1998 § 303(d) lists within the next 12 years. Finally, the state has dedicated substantial resources to its TMDL program, allotting $7 million annually to TMDL funding.

II. STANDARDS OF REVIEW

This Court reviews a grant of summary judgment de novo. Weiner v. San Diego County, 210 F.3d 1025, 1028 (9th Cir.2000). We must determine, viewing the evidence in the light most favorable to the nonmoving party, whether there are any genuine issues of material fact and whether the district court correctly applied the relevant substantive law. Far Out Prods., Inc. v. Oskar, 247 F.3d 986, 992 (9th Cir.2001). This Court reviews a district court’s decision to consider a particular piece of evidence for abuse of discretion. Northcoast Envtl. Ctr. v. Glickman, 136 F.3d 660, 665 (9th Cir.1998).

III. DISCUSSION

A. Clean Water Act

BayKeeper argues that California’s failings under the CWA have triggered a duty on the part of the EPA to establish [768]*768TMDLs for the entire state. In order to prevail on this claim, BayKeeper must prove that EPA has a nondiscretionary duty to establish TMDLs for the State of California. See 33 U.S.C. § 1365(a)(2) (limiting citizen-suits against EPA to suits alleging EPA has failed to perform a duty “which is not discretionary”). In attempting to prove such a duty, BayKeeper relies upon § 303(d) of the CWA. That section reads as follows:

Each State shall submit to the Administrator from time to time, with the first such submission not later than one hundred and eighty days after the date of publication of the first identification of pollutants under section 1314(a)(2)(D) of this title, for his approval the waters identified and the loads established under paragraphs (1)(A), (1)(B), (1)(C), and (1)(D) of this subsection. The Administrator shall either approve or disapprove such identification and load not later than thirty days after the date of submission. If the Administrator approves such identification and load, such State shall incorporate them into its current plan under subsection (e) of this section.

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Related

San Francisco Baykeeper v. Whitman
287 F.3d 764 (Ninth Circuit, 2002)

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Bluebook (online)
287 F.3d 764, 2002 WL 574110, Counsel Stack Legal Research, https://law.counselstack.com/opinion/san-francisco-baykeeper-v-whitman-ca9-2002.