Hawes v. State

125 P.3d 778, 203 Or. App. 255, 2005 Ore. App. LEXIS 1608
CourtCourt of Appeals of Oregon
DecidedDecember 14, 2005
Docket00-198; A120374
StatusPublished
Cited by6 cases

This text of 125 P.3d 778 (Hawes v. State) is published on Counsel Stack Legal Research, covering Court of Appeals of Oregon primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Hawes v. State, 125 P.3d 778, 203 Or. App. 255, 2005 Ore. App. LEXIS 1608 (Or. Ct. App. 2005).

Opinion

LINDER, J.

The dispositive issue in this case is whether a “memorandum of agreement” negotiated between the Oregon Department of Environmental Quality (DEQ) and the federal Environmental Protection Agency (EPA) constitutes a “final order” within the meaning of ORS 183.310(6)(b) of the Administrative Procedures Act. We conclude that it does not and that the circuit court therefore lacked jurisdiction over this proceeding. We accordingly vacate and remand with instructions to enter a judgment dismissing the action.

The memorandum of agreement between the DEQ and the EPA was the outgrowth of federal litigation brought by several environmental groups seeking to compel the EPA to enforce federal water quality standards in Oregon.1 In particular, the agreement concerned the coordinated development of water quality standards known as total maximum daily loads (“load limits”), which limit the maximum amount of a pollutant that can be discharged — or “loaded” — into certain waters from all combined sources.2 Under the federal Clean Water Act, load limits are to be established at levels “necessary to implement the applicable water quality standards.” 33 USC § 1313(d)(1)(C). As part of the settlement of the federal litigation, the DEQ agreed to develop and implement load limits for certain streams whose water quality was impaired.3 The agreement was memorialized in a “memorandum of agreement” that included both a list of impaired streams and a timetable by which the DEQ would create load limits for those streams. On the list of impaired streams was the Burnt River in Baker County.

Plaintiffs in this action are two Baker County ranchers, the Baker County Farm Bureau, and the Baker County [259]*259Livestock Association, all of whom anticipate that the DEQ will soon develop load limits for the Burnt River that will limit their agricultural activities on property adjoining the river. Accordingly, they brought this action under the APA challenging the DEQ’s authority to create load limits for so-called “nonpoint source streams,” which includes the Burnt River.4 More precisely, plaintiffs’ position is that the DEQ has the authority to create load limits for steams with “point sources” of pollution — that is, pipes, ditches, or other “points” from which pollutants are intentionally and legally discharged into a stream. But, according to plaintiffs, the DEQ lacks authority to create load limits for streams such as the Burnt River, which have only “nonpoint sources” of pollution — that is, pollutants that are the incidental result of runoff from, for example, timber operations, livestock grazing, and agricultural activities. The trial court agreed that the DEQ lacks the authority to create load limits for nonpoint source-only streams, and entered a judgment that, among other things, enjoined the DEQ from adopting load limits on those streams.

The DEQ and intervenors5 appeal, renewing the arguments that they made to the trial court. In addition to addressing the DEQ’s authority to develop and implement load limits for pollutants into nonpoint source-only streams, the DEQ and intervenors first raise a jurisdictional challenge. Specifically, they argue that the trial court lacked jurisdiction to review the memorandum under the APA because the agreement between the DEQ and the EPA was not a final order within the meaning of the pertinent judicial review provisions.6 As we explain below, we agree. We therefore do not reach the question of the DEQ’s authority.

[260]*260We begin with an overview of the agreement. The declared purpose of the agreement is to

“provide a framework, schedule, and strategy to restore the quality of impaired waters within the State of Oregon to achieve Water Quality Standards, and to describe the methods and processes that the State of Oregon will use to develop and implement the requisite Total Maximium Daily Loads for waters listed on the 1998 303(d) list of Water Quality Limited Waterbodies[.]”

The DEQ’s particular role is to establish the load limits for water quality impaired streams. In particular, the agreement provides that the

“DEQ will prioritize, schedule, scope, develop and submit Total Maximum Daily Loads (TMDLs [or load limits]) for water quality limited segments on the state’s 1998 303(d) list in accordance with the ‘Schedule for TMDL Submittal’ (Attachment A) by June 30, 2007. Submittal within one year of the date specified on the Schedule will be deemed timely.”

Water quality impaired streams are those that violate ambient water quality standards — that is, general water quality standards that do not distinguish between sources of pollution — developed by the DEQ pursuant to ORS 468B.048 and Section 303 of the Clean Water Act. Under the agreement, the DEQ must place streams that are currently impaired, as well as those that are expected to become impaired within a specified period of time, onto the “303(d) list.” Once that is done, in conformance with a schedule appended to the agreement, the DEQ must develop load limits for streams on the 303(d) list. The schedule calls for all load limits on the Burnt River to be developed by 2005, although load limits will be considered timely if the DEQ develops them within one year of the schedule’s target dates.

The agreement sets forth particular provisions governing streams with only nonpoint sources of pollution, such as the segments of the Burnt River that are the concern of [261]*261this case. With regard to the nonpoint source streams, the agreement calls for the DEQ to consult with an extensive listing of agencies, citizens, and interest groups to develop the applicable load limits. Specifically, the agreement provides that the “DEQ will work with federal and state agencies, watershed councils, communities, counties, [soil and water conservation districts], citizens’ groups, and others to identify data needs, collect, manage and analyze data and provide results to the public.” It further provides that “[a] local advisory group will be established to assist [the] DEQ in obtaining the maximum amount of local input to the [load limit] development process.” In conjunction with those various agencies and groups, the DEQ is to “conduct an assessment of the area characterizing the water quality problem, identifying potential causes and sources * * * and estimating relative contributions to the problem.” The DEQ is then to “tak[e] the lead in certain key technical decisions” affecting the load limits and to review, and ultimately make decisions regarding, recommendations made by advisory groups on other elements of the load limits. Under the agreement, once load limits are developed, the DEQ must develop plans to implement those limits. Those plans, which are to include implementation time lines by which the DEQ expects water quality standards to be attained, are then submitted to the EPA, along with the load limits themselves. Although it does not approve or disapprove the implementation plans so developed, the EPA does review and approve or disapprove the load limits set by the DEQ.

The process is more involved for nonpoint source streams where the pollution arises from forestry or farming practices.

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Cite This Page — Counsel Stack

Bluebook (online)
125 P.3d 778, 203 Or. App. 255, 2005 Ore. App. LEXIS 1608, Counsel Stack Legal Research, https://law.counselstack.com/opinion/hawes-v-state-orctapp-2005.