City of East Peoria v. Pollution Control Board

452 N.E.2d 1378, 117 Ill. App. 3d 673, 72 Ill. Dec. 682, 1983 Ill. App. LEXIS 2228
CourtAppellate Court of Illinois
DecidedAugust 23, 1983
Docket82-596, 82-635, 82-648 cons.
StatusPublished
Cited by16 cases

This text of 452 N.E.2d 1378 (City of East Peoria v. Pollution Control Board) is published on Counsel Stack Legal Research, covering Appellate Court of Illinois primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
City of East Peoria v. Pollution Control Board, 452 N.E.2d 1378, 117 Ill. App. 3d 673, 72 Ill. Dec. 682, 1983 Ill. App. LEXIS 2228 (Ill. Ct. App. 1983).

Opinion

JUSTICE SCOTT

delivered the opinion of the court:

Waste Management of Illinois, Inc., petitioned pursuant to the Environmental Protection Act (Ill. Rev. Stat. 1981, ch. 111½, par. 1001 et seq.) for approval to locate a regional pollution control facility, i.e., sanitary landfill, in an unincorporated area of Tazewell County, Illinois. The Tazewell County Board of Supervisors first considered the petition and denied it. A review of that decision was conducted by the Illinois Pollution Control Board, and the Board reversed the Tazewell County decision and approved the petition. We are asked to consider the Pollution Control Board’s reversal order under administrative review procedures set forth in section 41 of the Environmental Protection Act (Ill. Rev. Stat. 1981, ch. 111½, par. 1041). The administrative review provided for therein is afforded directly in the appellate court and not in the circuit court.

According to the Illinois Environmental Protection Act,

“*** no permit for the development or construction of a new regional pollution control facility (sanitary landfill) may be granted *** unless the applicant submits proof *** that the location of said facility has been approved by the County Board of the county if in an unincorporated area, or the governing body of the municipality when in an incorporated area in which the facility is to be located ***.” (Ill. Rev. Stat. 1981, ch. 111½, par. 1039(c).)

The Act further provides:

“[T]he County Board *** shall approve the site location suitability for such new regional pollution control facility only in accordance with the following criteria:
(i) the facility is necessary to accommodate the waste needs of the area it is intended to serve;
(ii) the facility is so designed, located and proposed to be operated that the public health, safety and welfare will be protected;
(iii) the facility is located so as to minimize incompatability with the character of the surrounding area and to minimize the effect on the value of the surrounding property;
(iv) the facility is located outside the boundary of the 100 year flood plain as determined by the Illinois Department of Transportation, or the site is flood-proofed to meet the standards and requirements of the Illinois Department of Transportation and is approved by that Department;
(v) the plan of operations for the facility is designed to minimize the danger to the surrounding area from fire, spills, or other operational accidents; and
(vi) the traffic patterns to or from the facility are so designed as to minimize the impact on existing traffic flows.” (Ill. Rev. Stat., 1982 Supp., ch. 111½, par. 1039.2(a).)

Finally, the Act provides that in determining the suitability of the landfill site, the county board must hold at least one public hearing, with notice of such hearing published in a newspaper of general circulation and directed to all members of the General Assembly from the district in which the proposed site is located. Ill. Rev. Stat., 1982 Supp., ch. 111½, par. 1039.2(d).

On December 21, 1981, Waste Management of Illinois, Inc., filed its application for approval of the landfill site. On February 18, 1982, the county board held the mandated hearing and granted site approval finding that Waste Management had met its burden of proof on each of the six criteria set forth in the Act. Subsequently, on February 24, 1982, the city of East Peoria filed a petition with the county board requesting that the previous decision be set aside and that the public hearing be reopened, alleging as a basis for its petition certain misstatements of a Waste Management witness at the first hearing. In response to East Peoria’s petition, the County Board set aside its February 18 decision and reopened the public hearing on March 24, 1982. Following this reopened hearing, on April 19, 1982, the Tazewell County Board denied Waste Management’s petition for site location finding that the landfill facility was not so designed, located and proposed to be operated so that the public health, safety and welfare was adequately protected.

It is undisputed that the evidence before the county board demonstrated that the proposed landfill site was directly over the Sankoty Aquifer. An aquifer is a water-bearing underground layer of sand or gravel; such a layer is a source of ground water tapped when a well is dug. (Crookston Cattle Co. v. Minnesota Department of Natural Resources (Minn. 1981), 300 N.W.2d 769.) The evidence also demonstrated that the village of Washington, the city of Peoria, the village of Morton, the North Tazewell Public Water District, and the city of East Peoria all draw water for public water supplies from the Sankoty Aquifer. The proximity of landfill wastes and public water was the basis of the county board’s public health concern and of the site location denial.

To prevent potential contamination of the aquifer, Waste Management proposed to design and construct the landfill facility with a clay liner. According to Waste Management’s application, inspections and borings of the sides and bottoms of the landfill would be made to insure that a minimum of 10 feet of undisturbed clay would exist under the landfill and around the sides. Where clay seals were not naturally found, man-made clay seals would be compacted to a thickness of 12 feet. According to Waste Management’s application, it would require pollutants 50 years to penetrate the 10-foot clay liner which it proposed for the landfill, and it would take an additional 90 years to penetrate the 90 feet of soil separating the clay liner from the Sankoty Aquifer. As the contents of the landfill gradually leak through the 10 feet of clay and 90 feet of soil below the clay layer, attenuation and cationic exchange would tend to clean the leaching materials. According to one expert, a two-foot layer of clay would be adequate to clean the leachate.

Testimony presented at the hearing before the county board tended to show that the time necessary for materials to leak from the landfill as estimated in Waste Management’s application was incorrect. The estimates contained in the application were based on certain assumptions made prior to the formulation of precise design plans for the landfill. Calculating the rate of leakage using the final design plans, Waste Management’s own expert shortened the time period necessary to penetrate the 10-foot clay layer from 50 years to 33 years. It was also revealed in the county board’s hearing that the application’s estimate of 90 years to penetrate the soil layer between the clay liner and the Sankoty Aquifer was based upon the assumption that the average depth of this soil layer was 90 feet. The least depth of this second strata of soil was estimated at 50 feet, and the time required for material from the landfill to leak through this second layer into the Aquifer at the point of least depth would be proportionately reduced.

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Bluebook (online)
452 N.E.2d 1378, 117 Ill. App. 3d 673, 72 Ill. Dec. 682, 1983 Ill. App. LEXIS 2228, Counsel Stack Legal Research, https://law.counselstack.com/opinion/city-of-east-peoria-v-pollution-control-board-illappct-1983.