Conservation Law Foundation v. Burke

645 A.2d 495, 162 Vt. 115, 1993 Vt. LEXIS 190
CourtSupreme Court of Vermont
DecidedSeptember 17, 1993
Docket92-358
StatusPublished
Cited by50 cases

This text of 645 A.2d 495 (Conservation Law Foundation v. Burke) is published on Counsel Stack Legal Research, covering Supreme Court of Vermont primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Conservation Law Foundation v. Burke, 645 A.2d 495, 162 Vt. 115, 1993 Vt. LEXIS 190 (Vt. 1993).

Opinion

Dooley, J.

Safety Medical Systems, Inc. (SMS) appeals from a decision of the Chittenden Superior Court denying it an air pollution *118 control permit to operate a medical waste incinerator because the operation will emit excessive levels of certain toxic substances. The parties opposing the permit are Conservation Law Foundation (CLF), Raymond Gonda, Timothy Fasten, Coca-Cola Bottling Company of New England, Inc., Seventh Generation, Inc., Little Red Wagon Daycare, Inc. and the City of Winooski. 1 Safety Medical Systems argues that the action of the Vermont Agency of Natural Resources (ANR), which granted the permit, was supported by the record and the applicable regulations and should have been affirmed. 2 Specifically, SMS argues that the ANR decision must be affirmed on theories of “de minimis” impact or offsetting benefits. 3 We affirm in part, and reverse in part.

In September 1989, Safety Medical Systems applied for an air pollution control permit to operate a medical waste incineration facility in Colchester. The facility includes two incinerators, each capable of incinerating 1,000 pounds of medical waste per hour. After further submissions, the application was deemed complete in July 1990. After a public hearing, ANR granted Safety Medical Systems’ •application and issued a permit.

The ANR decision was subsequently appealed to the superior court. While the appeal was pending, Safety Medical Systems completed the facility and gained all other required approvals. Because the permit contained a ninety-day waiting period between the time the facility was ready to operate and the date of first operation, Safety Medical Systems requested a remand to ANR to seek a permit modification. The remand was granted, and ANR held another public hearing, primarily on modifications to the permit. ANR reaffirmed its original decision but made three amendments to the permit, including elimination of the ninety-day waiting period. The matter again went to superior court, which, on Conservation Law Foundation’s motion for summary judgment, held that ANR acted in violation of the applicable regulations in granting the permit.

*119 I.

A.

The case is controlled by air pollution control regulations adopted by ANR pursuant to 10 V.SA,. § 554(2). 4 These regulations employ a three-step process to determine whether the emission of hazardous air contaminants will be authorized. For each hazardous air contaminant, ANR must first determine whether the emission rate will exceed the action level specified in the regulations for that contaminant. Vermont Agency of Natural Resources, Environmental Protection Regulations (EPR) § 5-261(1). If the emission does not exceed the action level, there is no further regulation of that contaminant. Id. If the emission does exceed the action level, the second regulatory step requires the source, in this case Safety Medical Systems, to use control technologies “to achieve the hazardous most stringent emission rate (HMSER).” Id § 5-261(2). Finally, even if the second step is met, ANR may not issue a permit allowing the discharge of hazardous air contaminants “which cause or contribute to ambient air concentrations in excess of any Hazard Limiting Value.” Id § 5-261(3). The regulations contain hazard limiting values for each of the hazardous air contaminants. Id Ch. 5 Appendix C.

B.

According to the data supplied by Safety Medical Systems, the medical waste incinerator will emit cadmium, chromium, dioxin and nitric oxide at a rate that exceeds the action level for each contaminant. For example, the action level for chromium is 0.0000071 pounds per eight-hour period; the SMS incinerator will emit 0.000018 pounds of chromium in the same period. Because the SMS incinerator met the first step for regulation, ANR then found that Safety Medical Systems must use control technologies to achieve the most stringent emission rate (HMSER) for each of the contaminants. It further found that Safety Medical Systems proposed to use sufficient control technologies to meet this requirement.

C.

The issue in this case arises with respect to ANR’s handling of the final regulatory step dealing with the impact of the SMS incinerator *120 output on ambient air concentrations of cadmium, chromium, dioxin and nitric oxide. As authorized by its regulations, ANR gave Safety Medical Systems the option of determining the actual ambient air concentrations at the site through a year of testing or of using preexisting data generated off-site for the four contaminants. Safety Medical Systems chose the latter option.

The only data for cadmium and chromium were collected at Randolph, Vermont between 1980 and 1985. For each contaminant, the data showed that the average level in the air exceeded the applicable hazard limiting value (HLV). No data were available for levels of dioxin or nitric oxide in the air in Vermont. The nearest place surveyed to determine ambient air levels of dioxin was in Connecticut. The Connecticut data registered levels of dioxin above the Vermont hazard limiting value. As for the lack of data on nitric oxide, ANR assumed that nitric oxide converts rapidly to nitrogen dioxide, so that existing levels of nitric oxide should be considered to be negligible.

ANR discounted the ambient air level findings for the four contaminants and issued the permit to Safety Medical Systems despite indications from the available data that the SMS incinerator would emit contaminants in excess of ANR’s hazard limiting values. ANR did so because it found the amount of the emissions to be de minimis and because the addition of contaminants from the SMS incinerator would be offset by a greater reduction in emissions of those contaminants in other incinerator facilities. On remand, it added that the Randolph and Connecticut data were unreliable. The superior court rejected each reason. We agree with respect to the first two reasons but conclude that analysis of the third reason is flawed because of inadequacies in the record. We now treat these three points of contention in succession.

II.

The superior court first found fault with ANR’s application of a “de minimis” test when judging the impact of the increased ambient air concentration of the four contaminants against each contaminant’s hazard limiting value. As part of the permitting process, ANR required Safety Medical Systems to show the extent to which its discharge would increase the ambient air level for each of the pollutants within 200 meters of the point of discharge. The results *121 showed that the SMS incinerator discharges would increase the ambient air level of cadmium 3.3%; of chromium, 1.4%; of dioxin, 3.6%; and of nitric oxide, 0.6%. As noted previously, these increases were over and above existing concentrations which the data used showed to be in excess of the hazard limiting values.

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Bluebook (online)
645 A.2d 495, 162 Vt. 115, 1993 Vt. LEXIS 190, Counsel Stack Legal Research, https://law.counselstack.com/opinion/conservation-law-foundation-v-burke-vt-1993.