Upper Gwynedd Towamencin Municipal Authority v. Department of Environmental Protection

9 A.3d 255, 2010 Pa. Commw. LEXIS 631
Commonwealth Court of Pennsylvania·Decided November 30, 2010·No. 54 C.D. 2010·Published·Cited by 10 cases

Opinion

OPINION BY

Judge BROBSON.

In these consolidated petitions for review, petitioners Upper Gwynedd Towam-encin Municipal Authority (UG) and Lower Salford Township Authority (LS) (collectively, where appropriate, “the Authorities”) challenge orders of the Environmental Hearing Board (EHB) relating to the Authorities’ applications for recovery of attorneys’ fees and costs (fee applications) from the Department of Environmental Protection (DEP). EHB (1) denied the Authorities’ fee applications under Section 307(b) of the Clean Streams Law (Law), 1 and (2) denied the Authorities’ request for reconsideration of EHB’s order denying their fee applications.

I. BACKGROUND

A. Statutory Background

This matter arises under Section 303(d) of the federal Clean Water Act (Act), 33 U.S.C. § 1313(d), which provides in pertinent part:

(d) Identification of areas with insufficient controls; maximum daily load; certain effluvient limitations revision.
(1)(A) Each State shall identify those waters within its boundaries for which the effluent limitations required by section 301(b)(1)(A) and section 301(b)(1)(B) are not stringent enough to implement any water quality standard applicable to such waters ...
(C) Each State shall establish for the waters identified in paragraph (1)(A) of this subsection, and in accordance with the priority ranking, the total maximum *258 daily load, for those pollutants which the Administrator identifies under section 304(a)(2) as suitable for such calculation. Such load shall be established at a level necessary to implement the applicable water quality standards with seasonal variations and a margin of safety which takes into account any lack of knowledge concerning the relationship between effluent limitations and water quality....
(2) 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 304(a)(2)(D), 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. If the Administrator disapproves such identification and load, he shall not later than thirty days after the date of such disapproval identify such waters in such State and establish such loads for such waters as he determines necessary to implement the water quality standards applicable to such waters and upon such identification and establishment the State shall incorporate them into its current plan under subsection (e) of this section.

(Emphasis added.)

Thus, the Act vests with each state numerous responsibilities, including the establishment of water quality standards for bodies of water within the boundaries of the state. The Act requires states first to evaluate the use of a body of water. Based upon the particular use of a body of water, such as recreation or consumption, the state must then determine the water quality standards the body of water must meet in order to serve the designated use. 2 Part of the evaluation of these standards involves determining the maximum amount of various pollutants the body of water may contain before its designated use is impaired. 3 The amount of permitted effluents is referred to as “total maximum daily load” or TMDLs.

Section 303(d) of the Act, which is at issue in this case, requires states to perform two key functions: (1) to create a list of bodies of water within a state that do not meet established water quality standards—a “303(d) list,” which the Environmental Protection Agency (EPA) may approve or disapprove; and (2) to establish, for each body of water on its 303(d) list, TMDLs. As with the 303(d) list, EPA has the power to approve or disapprove a state-established TMDL for a particular body of water. Under Section 303(d) of the Act, EPA must establish a TMDL if it disapproves a state-established TMDL.

B. Historical Background Regarding Pennsylvania’s Compliance with the Requirements of Section 303(d) of the Act

In January 1996, the American Littoral Society and the Public Interest Research Group of Pennsylvania filed a complaint in the United States District Court for the Eastern District of Pennsylvania. (See Consent Decree; Lower Salford Township Authority Reproduced Record (L.S.R.R.) at 295a-331a.) The lawsuit sought to chal *259 lenge the alleged failure of EPA to comply with its responsibilities under Section 303(d) of the Act. (Id.)

The parties in that case reached an agreement, the terms of which were incorporated into a Consent Decree. (Id.) The Consent Decree set forth a process by which EPA could ensure compliance with the Act’s directive for the identification of bodies of water for placement on the 303(d) list and the establishment of TMDLs for those water ways. (Id.) The Consent Decree appears to provide broad power to EPA to establish TMDLs when a state has been unable to or is incapable of establishing TMDLs. (Id.)

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Upper Gwynedd Towamencin Municipal Authority v. Department of Environmental Protection, 9 A.3d 255, 2010 Pa. Commw. LEXIS 631 (Pa. Ct. App. 2010).

9 A.3d 255 (Upper Gwynedd Towamencin Municipal Authority v. Department of Environmental Protection) — published by Counsel Stack Legal Research, free access to 12M+ legal documents.

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