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Re: Docket Control Number OEI-100004; Comments on the Addition of Diisononyl Phthalate Category to List of Toxic Chemicals; Proposed Rule (65 Fed. Reg. 53,681) Dear Sir or Madam: A. INTRODUCTION AND SUMMARY The Society of the Plastics Industry, Inc.1(SPI or Society), on behalf of its Vinyl Formulators Division, is pleased to provide the following comments on the U.S. Environmental Protection Agency's (EPA or Agency) proposal to amend the list of toxic chemicals under the Emergency Planning and Community-Right-to-Know Act (EPCRA) ( 42 U.S.C. § 11001 et seq.) and list diisononyl phthalate (DINP) as a reportable category of chemicals. 65 Fed. Reg. 53,681 (Sept. 5, 2000); 65 Fed. Reg. 69,888 (Nov. 21, 2000). Many SPI members, in particular those in the SPI Vinyl Formulators Division2, use DINP in the manufacture of a variety of products. If the rule is finalized as proposed, SPI members and others in industry will be required to evaluate the need for reporting DINP under the Toxic Release Inventory (TRI) provisions of section 313 of EPCRA for DINP. Thus, SPI and its members have a direct and substantial interest in this rulemaking. DINP is a member of the phthalate esters class of plasticizers, which are used as a manufacturing component in a wide variety of applications, including flooring, wire and cable, wall covering, packaging, and toys. Many SPI members are involved in these application processes and will be directly impacted by the rule as proposed. SPI's principal comments can be summarized as follows:
For these and other reasons discussed below, the agency should not list DINP as a reportable chemical under EPCRA. B. COMMENTS 1. The Objectives of EPCRA Are Not Met By Listing DINP TRI reporting exists for the express purpose of informing the community about toxic chemical releases. In EPA's words, "[t]he basic purpose of this provision [EPCRA § 313] is to make available to the public information about releases of certain toxic chemicals that result from operations of certain facilities in their community."3 This aptly expresses a necessary prerequisite to listing any chemical under EPCRA § 313(d). EPA must determine that the listing serves EPCRA's purpose of informing the public about releases. Congress intended to require annual TRI reporting for chemicals only when there was a reasonable expectation of releases in quantities or circumstances that could cause the anticipated harm. The monitoring data for DINP in air, drinking water, and surface and ground waters, albeit limited, suggests that little DINP is released as the concentration of DINP is below analytical detection limits.4 Thus, providing access to TRI reports that suggest zero releases is of little value to the community. If the EPA's goal is simply to make the community aware that DINP is used in manufacturing processes, that information is available from other reports and is not a basis for listing under EPCRA § 313. To suggest, as EPA will by requiring TRI reports, that DINP presents a risk to human health because it is reasonably anticipated to be released into the environment in proportions that could cause harm would be quite misleading. Such misinformation will not benefit the community and is likely to cause confusion. EPCRA's goals are not met by adding DINP to the list of chemicals subject to TRI reporting. 2. The Scientific Evidence Does Not Support the Listing of DINP as an EPCRA Toxic Chemical Section 313(d)(2) of EPCRA authorizes EPA to add chemicals to the toxic chemical list if the following criteria are met based on generally accepted scientific principles or laboratory tests: (A) The chemical is known to cause or can reasonably be anticipated to cause significant adverse acute human health effects at concentration levels that are reasonably likely to exist beyond facility site boundaries as result of continuous, or frequently recurring, releases. (B) The chemical is known to cause or can reasonably be anticipated to cause in humans (C) The chemical is known to cause or can reasonably be anticipated to cause a significant adverse effect on the environment because of its toxicity, its toxicity and persistence in the environment, or its toxicity and tendency to bioaccumulate in the environment. EPA is proposing to list DINP as a toxic chemical based on its hazard assessment that "preliminarily" suggests that DINP meets the chronic health effects criteria of section 313(d)(2)(B) because DINP theoretically caused developmental toxicity, chronic liver and kidney toxicity, and other effects in animal studies.5 The weight of scientific evidence, however, does not support the Agency's hazard assessment of DINP or listing DINP under section 313 of EPCRA. In fact, the weight of the evidence strongly supports the conclusion that the effects observed in rodents are highly unlikely to occur in humans. As detailed in the comments filed by the American Chemistry Council, which SPI fully endorses, there is a substantial body of research that provides compelling evidence that tumors in rodents are not relevant for human health assessment. DINP has been extensively tested to validate its safe use. A number of scientific bodies around the world have studied DINP and none has determined that there is any significant risk to humans associated with typical exposure levels to DINP. DINP has an extensive database that includes test results from toxicity studies that examined possible liver and kidney effects, cancer, reproduction, and development, as well as recent and ongoing research on endocrine modulations. We request that EPA include the premiere studies cited below in its evaluation of DINP. In contrast to EPA's hazard assessment, the following expert reports suggest that DINP does not present carcinogenicity or other chronic human health effects, nor does it present acute human health effects or significant adverse effects on the environment.
Other studies specific to the risk posed by DINP provide further evidence that DINP is not harmful under typical exposure scenarios. Specifically, in December 1998, the Consumer Product Safety Commission expressly stated that "generally, the amount [of DINP] ingested [from toys] does not even come close to a harmful level."9 3. Listing DINP May Cause Facilities to Switch to Alternatives That May Not Be As Safe Our comments support the view that DINP is well-studied, safe as currently used in polymeric products, and is not anticipated to be released in amounts that would trigger significant adverse effects. There is real concern that, if EPA moves forward and lists DINP as a toxic chemical under EPCRA § 313, covered facilities as well as product manufacturers and sellers will seeking to avoid DINP because it would be a "listed" hazardous chemical. Ironically, this may result in switching to alternatives that are not as well studied. Indeed, the Consumer Product Safety Commission specifically asked that toy manufacturers not replace DINP in children's products with chemicals that have not been adequately tested for toxicity. EPA simply should avoid creating a situation that may cause companies to switch from a well-studied low-risk chemical to ones that may cause unintentional harm. C. CONCLUSION Because the world's scientific literature does not support the conclusion that DINP presents the statutorily required adverse health effects for listing, and because the underlying goals of EPCRA would not be served by listing, EPA should withdraw its proposal to list DINP as a toxic chemical under section 313 of EPCRA. SPI thanks the Agency in advance for its consideration of these comments. Respectfully submitted, Maureen Healey Doug Caster Of Counsel:
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