Rsr Corporation v. Environmental Protection Agency

102 F.3d 1266, 322 U.S. App. D.C. 238, 27 Envtl. L. Rep. (Envtl. Law Inst.) 20497, 43 ERC (BNA) 1801, 1997 U.S. App. LEXIS 35
CourtCourt of Appeals for the D.C. Circuit
DecidedJanuary 3, 1997
Docket95-1559
StatusPublished
Cited by6 cases

This text of 102 F.3d 1266 (Rsr Corporation v. Environmental Protection Agency) is published on Counsel Stack Legal Research, covering Court of Appeals for the D.C. Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

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Rsr Corporation v. Environmental Protection Agency, 102 F.3d 1266, 322 U.S. App. D.C. 238, 27 Envtl. L. Rep. (Envtl. Law Inst.) 20497, 43 ERC (BNA) 1801, 1997 U.S. App. LEXIS 35 (D.C. Cir. 1997).

Opinion

Opinion of the Court filed by Chief Judge Edwards.

HARRY T. EDWARDS, Chief Judge:

Under the Comprehensive Environmental Response, Compensation, and Liability Act (“CERCLA”), the Environmental Protection Agency (“EPA”) lists sites that pose a danger to public health or the environment on the National Priorities List (“NPL”). EPA uses the Hazard Ranking System (“HRS”), a mathematical model, to determine which sites should be listed. EPA promulgated the HRS in 1982 and amended it in 1990.

For many hazardous substances, the HRS incorporates a Human Toxicity Factor (“HTF”) as one variable in the mathematical formula that results in the overall HRS score. For lead, the amended HRS assigns a HTF value of 10,000-the highest value—because EPA determined that lead is a highly toxic substance without a demonstrated threshold below which it causes no adverse health effects. On July 9, 1993, in response to a proposed listing of its site on the NPL, petitioner RSR Corporation (“RSR”) challenged the lead HTF value. RSR argued that “new studies” demonstrate that this value is inappropriate.

We hold that RSR’s challenge to the lead HTF valuéis untimely. Section 113(a) of CERCLA states that all CERCLA regulations must be challenged “within ninety days from the date of promulgation of such regulations.” 42 U.S.C. § 9613(a) (1994). Because RSR did not raise its challenge to the lead HTF value until nearly three years after EPA promulgated the amended HRS, its challenge is barred by section 113(a).

RSR argues that this case comes within the Geller v. FCC, 610 F.2d 973 (D.C.Cir. 1979) exception to the timeliness rule. It contends that, due to the “new studies,” an exception is justified in light of the “changed circumstances giving rise to a new cause of action beyond the statutory period for review,” Eagle-Picher Indus., Inc. v. EPA, 759 F.2d 905, 909 (D.C.Cir.1985) (“Eagle-Picher P’) (describing the Getter exception). We reject this contention, for the scope of the Getter exception is not as broad as petitioner would have it. If we were to allow petitioner to pursue a challenge based solely on “new studies” (whose meaning is in dispute), we would completely undermine the HRS as a means of listing sites on the NPL. See id. at 916-17 (“EPA would be forced, contrary to the will of Congress, to defend the HRS repeatedly, wasting both time and funds that would be better spent cleaning up hazardous wastes that threaten human health and the environment.”). The proper place for RSR to raise its “new studies” argument is in a petition for a rulemaking.

*1268 We also reject RSR’s other challenges: we conclude that EPA followed established procedures in calculating the background level of lead for the site, and that EPA did not act arbitrarily and capriciously in naming the site the “RSR Corporation Site.” Accordingly, we deny RSR’s petition.

I. Background

A.Statutory and Regulatory Background

CERCLA provides a comprehensive statutory scheme for cleaning up releases or threatened releases of hazardous substances. See 42 U.S.C. §§ 9601-9675 (1994). Under CERLCA, Congress directed EPA to establish criteria to prioritize the cleanup of those sites presenting the greatest danger to public health or the environment. See id. § 9605(a)(8)(A). Sites meeting the criteria are placed on the NPL. See id. § 9605(a)(8)(B).

The HRS is a mathematical model-first promulgated in 1982, see 47 Fed.Reg. 31,180 (1982), and amended in 1990, see 55 Fed.Reg. 51,532 (1990)-that serves as a screening device for evaluating relative risks to health or the environment posed by releases of hazardous substances. See 40 C.F.R. pt. 300 app. A (1995). EPA evaluates risks by assigning numeric values from tables or formulas in the HRS to represent the dangers posed by the different features of hazardous substances at the sites. Overall HRS scores range from 0 to 100. See id. § 2.1.1. A site with a HRS score of 28.5 or greater is eligible for placement on the NPL. See 55 Fed.Reg. at 51,-569.

•For many hazardous substances, the HRS incorporates a HTF as one variable in the mathematical formula that results in the overall HRS score. A HTF reflects a substance’s potential to cause cancer or other adverse health effects. Depending on the particular substance’s toxicity, a HTF may range in value from 0 to 10,000. For lead, the amended HRS assigns a HTF value of 10,000. See 40 C.F.R. pt. 300 app. A § 2.4.1.1. EPA determined that this value was appropriate because lead was found to be a highly toxic substance without a demonstrated threshold below which it causes no adverse health effects. See Memorandum from Larry J. Zaragoza to HRS Docket, “Toxicity Factor Value for Lead” (Nov. 9, 1990), reprinted in Joint Appendix (“J.A”) 90-92.

The HRS also requires EPA to determine, for soil exposure pathways, if “observed contamination” is present at a site. Observed contamination is present if a hazardous substance attributable to the site is present at a concentration that is at least three times higher than the “background level.” See 40 C.F.R. pt. 300 app. A tbl. 2-3, § 5.0.1.

B. The RSR Corporation Site

The site at issue in this ease is an abandoned secondary lead smelter in Dallas, Texas, and the approximately 13.6 surrounding square miles. A number of different companies operated the smelter from 1936 until 1984. RSR purchased the smelter in 1971.

In 1991 and 1992, EPA conducted extensive sampling at the RSR site. It then compared these samples with background data that the city of Dallas had gathered in 1983 and 1984 in a city-wide study of lead contamination in the soil. Because the on-site samples exceeded the background level by three times or more, EPA concluded that there was “observed contamination” at the site. As a result, it assigned a value of 550 for that variable, as called for by the HRS. See 40 C.F.R. pt. 300 app. A §§ 5.0.1, 5.1.1. EPA also assigned the site a HTF value of 10,000, as required by the HRS. See id. § 2.4.1.1 (setting the lead HTF value at 10,000). Inputting these two values into the HRS, EPA calculated a final HRS score of 50 for the site, a value above the 28.5 required for listing on the NPL, see 55 Fed.Reg. at 51,-569. On May 10,1993, EPA proposed listing the site on the NPL. See 58 Fed.Reg. 27,-507, 27,513 (1993).

On July 9,1993, RSR submitted comments-challenging the proposed listing of the site. RSR challenged the fact that EPA assigned the site a lead HTF value of 10,000. It argued that “[n]umerous recent studies published since February 1989” demonstrate that this value is inappropriate.

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102 F.3d 1266, 322 U.S. App. D.C. 238, 27 Envtl. L. Rep. (Envtl. Law Inst.) 20497, 43 ERC (BNA) 1801, 1997 U.S. App. LEXIS 35, Counsel Stack Legal Research, https://law.counselstack.com/opinion/rsr-corporation-v-environmental-protection-agency-cadc-1997.