City of Barnum v. County of Carlton

386 N.W.2d 770
CourtCourt of Appeals of Minnesota
DecidedJuly 16, 1986
DocketC3-85-1419
StatusPublished
Cited by8 cases

This text of 386 N.W.2d 770 (City of Barnum v. County of Carlton) is published on Counsel Stack Legal Research, covering Court of Appeals of Minnesota primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
City of Barnum v. County of Carlton, 386 N.W.2d 770 (Mich. Ct. App. 1986).

Opinion

OPINION

WOZNIAK, Judge.

The City of Barnum appeals the district court’s decision denying its request for a writ of mandamus compelling Carlton County to issue a conditional use permit to build a new wastewater treatment facility. The City of Barnum contends that Carlton County acted arbitrarily and capriciously in denying its application for a conditional use permit. We agree, and reverse the order of the district court.

FACTS

The City of Barnum is a small community of about 490 located in Carlton County, Minnesota. The city’s annual operating budget is about $90,000. Bamum’s existing sewage treatment plant, built in 1963, is a mechanical plant called an activated sludge. The city has consistently failed to meet applicable state and federal pollution control standards.

In 1979 Barnum obtained a grant from the Minnesota Pollution Control Agency (MPCA) to prepare a study to come up with a solution to its sewage treatment problems. The study, called a Facility Plan, was completed in 1980. The plan identified the most cost-effective and safe plan to be the construction of stabilization ponds with a controlled discharge to a small stream called Gillespie Brook, which flows into the Kettle River. The proposed site for the plant lies about four miles outside Barnum city limits, but within Carlton County.

*772 A stabilization pond system consists of one or more primary ponds and one or more secondary ponds. It is basically a man-made facility in which the natural purification of wastewater occurs under controlled conditions. Wastewater is initially pumped into the primary cell, where most of the treatment occurs, and then periodically transferred in small amounts to the secondary cell, where additional treatment occurs.

The proposed Barnum system will consist of two primary cells and one secondary cell, each cell about 5.6 acres in size. The system is typical of those used by small communities like Barnum. The system will hold over 30,000,000 gallons of water at a depth of about six feet and treat an average daily flow of 110,000 gallons. The ponds will be sealed to prevent the possibility of groundwater contamination.

When a pond system becomes full of water, the water must be removed, either by discharging to a body of water or spraying on nearby land. The proposed Barnum ponds would discharge into Gillespie Brook only twice a year, once in the spring and once in the fall. No discharge can be made without MPCA approval, which is necessary to insure that the water meets applicable standards and that the discharge is necessary. Barnum will have to meet the most stringent effluent limits available before it will be permitted to discharge from its secondary pond.

Because the proposed plant will not be discharging into a downstream lake, no phosphorus limitation will be necessary. Phosphorus, which is found in all wastewa-ter, can act as a limiting nutrient causing accelerated vegetation growth in a lake. When this vegetation dies, it begins to decompose and actually fill in the lake, a process known as eutrophication. The MPCA has therefore imposed restrictions on the levels of phosphorus that can be discharged into a lake. However, when phosphorus is discharged into streams, the moving water prevents the phosphorus from causing accelerated plant growth in a particular area of water.

The existing plant’s effluent is discharged into the Moose Horn River upstream from Hanging Horn Lake. The plant is the only point source of phosphorus to the lake. According to the MPCA, the concentration of phosphorus in Hanging Horn Lake puts it in the eutrophic category. The MPCA has determined that a phosphorus limitation on the proposed plant’s discharge to Gillespie Brook will not be necessary because there are no downstream lakes along Gillespie Brook.

There are about 250 pond systems in Minnesota. About 50% of Minnesota’s municipalities use stabilization ponds. The ponds are generally inexpensive to build and cheaper to operate than mechanical plants.

One disadvantage of stabilization ponds is the possibility that odors may arise for a few days during the spring as the ice melts and the ponds go from an anaerobic to an aerobic condition. To address the concern about odors, the MPCA requires ponds to be located at least one-quarter mile from the nearest residence. In this case, the nearest residence to the proposed pond site is over one-quarter mile away, to the northwest along County Road 135.

The Facility Plan found that:

The environment is expected to continue to slowly deteriorate without the project. Normal development would continue in the planning area, imposing even more of a load to the now undercapacitated treatment facilities.
Without the project, the Moose Horn River would continue to receive an effluent discharge from Barnum’s wastewater treatment works which could not be of sufficient quality to consistently meet NPDES Permit requirements. Overloaded and shock conditions would continue and operational problems would increase in frequency thereby affecting environmental conditions. This could have *773 adverse effects on future land use, property value, development, and recreational potential of areas affected by such conditions.

When the facility plan was complete, the MPCA prepared an environmental assessment, which evaluates the environmental impact of the most cost-effective project and, to a lesser extent, the alternative projects. The environmental assessment on the Barnum project concluded that “[tjhere is no significant major difference in the environmental impacts of the various alternatives.”

After completion of the environmental assessment, the matter was referred to the EPA for their review of environmental impact. The EPA issued a Finding of No Significant Impact regarding the Barnum project.

Barnum requested that Carlton County issue a conditional use permit to enable the city to build the new plant. In 1980, the Carlton County Board issued a conditional use permit to Barnum. However, the permit expired because the city was unable to obtain a construction grant and was therefore unable to commence construction within one year.

In 1984, the MPCA placed Barnum on its Municipal Project List for a construction grant in the upcoming year. The city hoped to implement the same Facility Plan it had proposed in 1980 and applied for another conditional use permit. The Carlton County Zoning Officer approved the plan and recommended approval of the permit. He stated in his memorandum to the planning commission, “Due to the isolation of the ponds, I do not feel they should have an adverse effect on properties in the area nor the future development of the area.” The Carlton County Planning Commission unanimously recommended approval of the permit on January 2, 1985.

On January 30, 1985, the Carlton County Board held an informational meeting to hear public concerns surrounding the proposed treatment facility. The board kept no written record of what transpired at this meeting. Two individuals prepared written summaries from individual notes. Several property owners voiced fears about diminished property values, odor problems, contaminated shallow wells, phosphorous levels, and other effects of the discharge on neighboring streams and lakes.

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City of Barnum v. County of Carlton
389 N.W.2d 727 (Supreme Court of Minnesota, 1986)

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Bluebook (online)
386 N.W.2d 770, Counsel Stack Legal Research, https://law.counselstack.com/opinion/city-of-barnum-v-county-of-carlton-minnctapp-1986.