Sierra Club MacKinac Chapter v. Department of Environmental Quality

747 N.W.2d 321, 277 Mich. App. 531, 38 Envtl. L. Rep. (Envtl. Law Inst.) 20025, 2008 Mich. App. LEXIS 142
CourtMichigan Court of Appeals
DecidedJanuary 15, 2008
DocketDocket 269181
StatusPublished
Cited by10 cases

This text of 747 N.W.2d 321 (Sierra Club MacKinac Chapter v. Department of Environmental Quality) is published on Counsel Stack Legal Research, covering Michigan Court of Appeals primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Sierra Club MacKinac Chapter v. Department of Environmental Quality, 747 N.W.2d 321, 277 Mich. App. 531, 38 Envtl. L. Rep. (Envtl. Law Inst.) 20025, 2008 Mich. App. LEXIS 142 (Mich. Ct. App. 2008).

Opinions

Whitbeck, C.J.

I. OVERVIEW

Petitioner Sierra Club Mackinac Chapter (the Sierra Club) appeals by leave granted the trial court’s order affirming a declaratory ruling issued by the Department of Environmental Quality (DEQ). The DEQ issued the declaratory ruling as a result of administrative proceedings brought by the Sierra Club challenging the [533]*533DEQ’s administration of certain elements of the Federal Water Pollution Control Act,1 commonly known as the Clean Water Act.

This case presents three issues for our consideration. First, we must consider whether the Sierra Club properly sought judicial review of the DEQ’s declaratory ruling in state court. Second, we must consider whether the discharge rates of a concentrated animal feeding operation’s (CAFO) nutrient management plan are “effluent limitations” as the Clean Water Act defines them. And third, if we conclude that such nutrient management plans are effluent limitations, then we must consider whether the DEQ must include the nutrient management plan in the terms of the general permit itself, subject to public review and comment before the DEQ approves the permit.

With respect to the first issue, we conclude that the Sierra Club properly sought judicial review of the DEQ’s ruling in state court. Under the circumstances here, state court, rather than federal court, is the proper forum for review of a state agency’s declaratory ruling. Regarding the second issue, we conclude that the discharge rates of a CAFO’s nutrient management plan are effluent limitations, as the Clean Water Act defines them. We conclude that such discharge rates are effluent limitations because they affect the rates of discharge from a point source into navigable waters. Therefore, in the interest of maintaining the biological integrity of the nation’s navigable waters, such discharge rates must be subject to the DEQ’s meaningful review. Regarding the third issue, because the Clean Water Act requires public participation in the development, revision, and enforcement of any effluent limitation, we conclude that the DEQ must include a CAFO’s [534]*534nutrient management plan in the terms of the general permit. Such CAFO nutrient management plans will therefore be subject to public review and comment before the DEQ approves the permit. Accordingly, we reverse and remand.

II. BASIC FACTS AND PROCEDURAL HISTORY

A. BACKGROUND

This case concerns the application and construction of § 301 of the Clean Water Act.2 The Clean Water Act is a federal regulatory statute that is designed “to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.”3 The Clean Water Act prohibits the “discharge of any pollutant” into “navigable waters” from any “point source,” except when authorized by a permit issued under the National Pollutant Discharge Elimination System (NPDES).4 The federal Environmental Protection Agency (EPA) or the states, pursuant to federally approved permit systems within their jurisdictions, issue NPDES permits for discharges into navigable waters.5 State discharge standards and limitations cannot be less stringent than the federal standards and limitations.6

The Clean Water Act defines “point source” as “any discernible, confined and discrete conveyance, including but not limited to any pipe, ditch, channel, tunnel, conduit, well, discrete fissure, container, rolling stock, concentrated animal feeding operation, vessel or other floating craft, from which pollutants are or may be [535]*535discharged.”7 The “point source” of pollutants at issue here is a concentrated animal feeding operation or “CAFO.”8 The Clean Water Act defines a CAFO by a prescribed number of animals that it stables or confines.9 A “large CAFO” houses hundreds or thousands of livestock.10 According to the Sierra Club, confined livestock and poultry operations in the United States— 198 in Michigan — generate millions of tons of manure and waste each year, more than three times the raw waste generated by humans in the United States.

In an effort to dispose of the enormous amounts of liquid and solid waste generated at CAFOs, many CAFO owners and operators apply manure as fertilizer to agricultural fields adjacent to the confinement facilities.11 Although nutrients in the manure can act as a fertilizer when CAFO owners or operators properly apply it, when such owners or operators excessively or improperly apply it, manure has a number of potentially harmful pollutants that can infiltrate surface and ground waters.12

In 1973, the EPA delegated authority to Michigan to administer its own NPDES program. Under the provisions of Michigan’s Natural Resources and Environmental Protection Act (NREPA) relating to protection of water resources,13 the DEQ is responsible for issuing [536]*536NPDES permits in Michigan and ensuring that those permits comply with applicable federal law and regulations. Every NPDES permit must set forth effluent (liquid waste) limitations, which are “restriction^] .... on quantities, rates, and concentrations of chemical, physical, biological, and other constituents which are discharged from point sources into navigable waters[.]”14

In 2003, to address water pollution associated with improper or excessive application of manure by CAFOs, the EPA promulgated the “CAFO Rule,”15 which required that all CAFO owners or operators either (1) apply for an individual NPDES permit or (2) submit a notice of intent for coverage under an NPDES general permit.16 To receive a permit, in addition to the generally applicable NPDES permit requirements, CAFOs must satisfy various specific conditions, including developing and implementing a nutrient management plan.17 A nutrient management plan is a plan to manage the nutrients, that is, manure, litter, and process waste-water, that a CAFO puts on its agricultural fields.

According to the DEQ, the federal CAFO Rule “set forth a framework for states and other permitting authorities to use as a baseline for the development of their own CAFO permitting programs.” In light of the changes to the federal scheme, Michigan promulgated its own administrative rules specific to the NPDES for CAFOs,18 which the EPA reviewed. Like its federal counterpart, Michigan’s Administrative Code requires [537]*537all CAFO owners or operators “to apply either for an individual NPDES permit, or a certificate of coverage under an NPDES general permit, unless the owner or operator has received a determination from the department, made after providing notice and opportunity for public comment, that the CAFO has ‘no potential to discharge .... ’ ”19 Like the federal system, the DEQ requires that Michigan CAFOs develop and implement comprehensive nutrient management plans.20

In February 2005, a federal court examined and partially vacated the federal CAFO Rule. In Waterkeeper Alliance Inc v United States Environmental Protection Agency,

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Sierra Club MacKinac Chapter v. Department of Environmental Quality
747 N.W.2d 321 (Michigan Court of Appeals, 2008)

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Bluebook (online)
747 N.W.2d 321, 277 Mich. App. 531, 38 Envtl. L. Rep. (Envtl. Law Inst.) 20025, 2008 Mich. App. LEXIS 142, Counsel Stack Legal Research, https://law.counselstack.com/opinion/sierra-club-mackinac-chapter-v-department-of-environmental-quality-michctapp-2008.