Penland v. Redwood Sanitary Sewer Service District

965 P.2d 433, 156 Or. App. 311, 1998 Ore. App. LEXIS 1568
CourtCourt of Appeals of Oregon
DecidedSeptember 30, 1998
Docket94-CV-0209; CA A90247
StatusPublished
Cited by3 cases

This text of 965 P.2d 433 (Penland v. Redwood Sanitary Sewer Service District) 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
Penland v. Redwood Sanitary Sewer Service District, 965 P.2d 433, 156 Or. App. 311, 1998 Ore. App. LEXIS 1568 (Or. Ct. App. 1998).

Opinion

*313 HASELTON, J.

This case is before us on remand from the Supreme Court, 327 Or 1, 956 P2d 964 (1998). In our original opinion, 146 Or App 225, 934 P2d 434 (1997), we held that, regardless of whether the defendant District’s operation of a composting facility constituted a nuisance, the operation was shielded by “discretionary function” immunity under the Oregon Tort Claims Act (OTCA), ORS 30.265(3)(c), and, thus, the trial court had erred in enjoining the facility’s operation. 146 Or App at 225-37. The Supreme Court reversed, concluding that discretionary function immunity under the OTCA “confers immunity on public bodies only from liability for damages and does not confer immunity from injunctive actions” including, particularly, an action to enjoin a nuisance. 327 Or at 8.

Thus, on remand, we must address two issues that we initially deferred: First, is the composting operation a nuisance? Second, if so, does the balance of equities warrant issuance of permanent injunctive relief? On de novo review, Jewett v. Dearhorn Enterprises, Inc., 281 Or 469, 473, 575 P2d 164 (1978), we answer both questions in the affirmative and, consequently, affirm.

To “reset the scene,” we reproduce the summary of undisputed facts from our first opinion:

“The District operates sewage-related facilities, including a sewage treatment plant, in rural Josephine County. As part of the sewage treatment process, the District reduces incoming raw sewage to sludge, or biosolids, a bacteria-laden condensed form of sewage, by draining the liquids from the solids. Before 1988, the District trucked the sludge to various sites for land application, which involved spreading the sludge over a large area for agricultural and disposal purposes.
“In 1988, the District’s manager, Weber, who was charged with day-to-day oversight of its operations, instituted a small-scale pilot composting operation at the treatment plant. In July 1990, the District instituted composting on a permanent basis.
*314 “In the initial stages of the composting process, sludge is solidified by being poured into an outdoor levee, or ‘drying ring,’ which is exposed to the open air. After about two weeks, the material loses enough moisture to be mixed with organic material for composting. The reduced sludge, or biosolids, is then mixed with organic materials, such as wood, animal bedding, including animal waste, and yard waste, provided by local residents and businesses. The bacteria in the sludge break down the mixture. In order for the bacteria to decompose the sludge, the mixture must be exposed to air. Thus, the mixture is placed in a large pile, approximately nine feet high, 20 feet wide, and 100 hundred feet long, and exposed to the open air. The composted material is first piled over a perforated pipe for aeration. After two to three weeks, the pile is removed from the pipe and is turned every two weeks for aeration. There are normally seven piles at one time, each in a different stage of the composting process. Defendant uses heavy equipment to move the piles as they decompose and to load the finished product.
“After approximately 90 days, the material becomes finished compost, which defendant sells to the public as mulch or soil amendment. The product, called Jo-Gro, contains no nutrients for fertilizing but is valuable for retaining moisture in soils.
“If the sludge mixture is not aerated, it becomes anaerobic and, as a result, generates hydrogen sulfide. Hydrogen sulfide can cause headaches, nausea, and throat problems, and its odor is akin to that of rotten eggs. Hydrogen sulfide is generally released whenever a compost pile or the sludge pool is disturbed, but some level of hydrogen sulfide is always present as a result of the composting operation.
“Plaintiffs are landowners and homeowners who live in rural Josephine County near the plant and composting operation. Many lived in the neighborhood before the District instituted the permanent composting operation. The closest plaintiffs, the Penlands, live about 180 feet from the property where the composting activities take place. Plaintiffs and other neighbors began to notice odor, noise, and dust, which they associated with the composting operation, in October 1991. Beginning in February 1992, plaintiffs and others complained to the District that, because of the odor and noise they ascribed to the plant, they were unable to enjoy outdoor activities, such as gardening, sitting on *315 their porches, and barbequing. In response to those complaints, the District undertook several measures, including placing sound deflection panels on the electric wood grinder. Plaintiffs apparently found those measures to be ineffective and their complaints continued.
* * * *
“[In the summer of 1994, after receiving the recommendation of an advisory committee, the District’s board of directors voted] to continue the composting operation at the sewage plant while implementing 21 of the ad hoc committee’s recommended mitigation measures. Those measures included using a quieter loader, constructing vegetation screens, adding sound mufflers to equipment, eliminating construction lumber demolition, applying a commercial deodorizer, mixing the sludge more rapidly and efficiently, using fly bait, and adding dust-reducing spray misters.
“In August 1994, plaintiffs filed this action, seeking to enjoin the continuation of the composting operation. Plaintiffs alleged that that operation created a nuisance in that it created excessive odor, noise, and dust and interfered with the reasonable use of their properties.”

146 Or App at 227-29 (footnote omitted).

In determining whether the composting operation constitutes a nuisance — i.e., whether it substantially and unreasonably interferes with the use and enjoyment of plaintiffs’ property — we must assess five factors: (1) the location of the claimed nuisance; (2) the character of the neighborhood; (3) the nature of the thing complained of; (4) the frequency of the intrusion; and (5) the effect upon the plaintiffs enjoyment of life, health and property. Jewett, 281 Or at 473. Whether a condition constitutes a nuisance depends on its effect on “an ordinarily reasonable [person], a normal person of ordinary habits and sensibilities.” Id. at 476. See also Smith v. Wallowa County, 145 Or App 341, 346, 929 P2d 1100 (1996).

The trial court, in oral remarks that comported with its ultimate written findings and conclusions, explained its application of those factors:

“I want to start out, first of all, before I go on to the issue of nuisance, I’d just like for the record — I know it’s not really evidence, but I was taken on a view of the property *316 and I think it’s important that the record reflect, as everyone agrees, that this is a residential area.

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Bluebook (online)
965 P.2d 433, 156 Or. App. 311, 1998 Ore. App. LEXIS 1568, Counsel Stack Legal Research, https://law.counselstack.com/opinion/penland-v-redwood-sanitary-sewer-service-district-orctapp-1998.