66 FR 157 pgs. 42659-42663 - Identification of Priority Data Needs for 10 Priority Hazardous Substances
Type: NOTICEVolume: 66Number: 157Pages: 42659 - 42663
Docket number: [ATSDR-172]
FR document: [FR Doc. 01-20373 Filed 8-13-01; 8:45 am]
Agency: Health and Human Services Department
Sub Agency: Agency for Toxic Substances and Disease Registry
Official PDF Version: PDF Version
DEPARTMENT OF HEALTH AND HUMAN SERVICES
Agency for Toxic Substances and Disease Registry
[ATSDR-172]
Identification of Priority Data Needs for 10 Priority Hazardous Substances
AGENCY:
Agency for Toxic Substances and Disease Registry (ATSDR), U.S. Department of Health and Human Services (HHS).
ACTION:
Request for public comments on the identification of priority data needs for 10 priority hazardous substances, and an ongoing call for voluntary research proposals.
SUMMARY:
This Notice makes available for public comment the priority data needs for 10 priority hazardous substances (see attached Table 1) as part of the continuing development and implementation of the ATSDR Substance-Specific Applied Research Program (SSARP). The Notice also serves as a continuous call for voluntary research proposals. The SSARP is authorized by the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (Superfund) or CERCLA, and amended by the Superfund Amendments and Reauthorization Act of 1986 (SARA) (42 U.S.C. 9604(i)). This research program was initiated on October 17, 1991. At that time, a list of priority data needs for 38 priority hazardous substances was announced in the Federal Register (56 FR 52178). The list was subsequently revised based on public comments and published in final form on November 16, 1992 (57 FR 54150). In 1997, ATSDR finalized the priority data needs for a second list of 12 substances that was subsequently announced in the Federal Register (62 FR 40820).
Ten substances constitute the third list of hazardous substances for which priority data needs have been identified by ATSDR. In developing this list, ATSDR solicited input from the Environmental Protection Agency (EPA) and the National Institute of Environmental Health Sciences (NIEHS). The priority data needs documents are available for review by requesting them in writing from ATSDR (see ADDRESSES section of this Notice).
The exposure and toxicity priority data needs in this Notice were distilled from data needs identified in the agency's toxicological profiles via a logical scientific approach described in a "Decision Guide published" in the Federal Register on September 11, 1989 (54 FR 37618). The priority data needs represent essential information to improve the database to conduct public health assessments. Research to address these data needs will help determine the types or levels of exposure that may present significant risks of adverse health effects in people exposed to the subject substances.
The priority data needs identified in this Notice reflect the opinion of the agency, in consultation with other federal programs, of the research needed pursuant to ATSDR's authority under CERCLA. They do not represent the priority data needs for any other program.
Consistent with Section 104(i)(12) of CERCLA as amended [42 U.S.C. 9604(i)(12)], nothing in this research program shall be construed to delay or otherwise affect or impair the authority of the President, the Administrator of ATSDR, or the Administrator of EPA to exercise any authority regarding any other provision of law, including the Toxic Substances Control Act of 1976 (TSCA) and the Federal Insecticide, Fungicide, and Rodenticide Act of 1972 (FIFRA), or the response and abatement authorities of CERCLA.
In developing this research program, ATSDR has worked with other federal programs to determine common substance-specific data needs, as well as mechanisms to implement research that may include authorities under TSCA and FIFRA, private-sector voluntarism, or the direct use of CERCLA funds.
When deciding the type of research that should be done, ATSDR considers the recommendations of the Interagency Testing Committee established under Section 4(e) of TSCA. Federally funded projects that collect information from 10 or more respondents and that are funded by cooperative agreements are subject to review by the Office of Management and Budget (OMB) under the Paperwork Reduction Act. If the proposed project involves research on human subjects, the applicants must comply with Department of Health and Human Services regulations (45 CFR part 46) regarding the protection of human subjects. Assurance must be provided that the project will be subject to initial and continuing review by the appropriate institutional review committees. Overall, data generated from this research program will lend support to others conducting human health assessments involving these 10 substances by providing additional scientific information for the risk assessment process.
The 10 substances, which are included in the ATSDR Priority List of Hazardous Substances established by ATSDR and EPA (64 FR 56792, October 21, 1999), are:
• Asbestos
• Benzidine
• Chlorinated dibenzo-p-dioxins
• 1,2-dibromoethane
• 1,2-dichloroethane
• 1,1-dichloroethene
• Ethylbenzene
• Pentachlorophenol
• 1,1,2,2-tetrachloroethane
• Total xylenes
The priority data needs for these 10 substances are presented in Table 1. We invite comments from the public on individual data needs. After considering the comments, ATSDR will publish the final priority data needs for each substance. These priority data needs will be addressed by the mechanisms described in the "Implementation of Substance-Specific Applied Research Program" section of this Federal Register Notice.
This Notice also serves as a continuous call for voluntary research proposals. Private-sector organizations may volunteer to conduct research to address specific priority data needs in this Notice by indicating their interest through submission of a letter of intent to ATSDR (see ADDRESSES section of this Notice). A Tri-Agency Superfund Applied Research Committee (TASARC) comprised of scientists from ATSDR, the National Toxicology Program (NTP), and EPA will review all proposals.
The substance-specific priority data needs were based on, and determined from, information in corresponding ATSDR toxicological profiles. Background technical information and justification for the priority data needs in this Notice are in the priority data needs documents. These documents are available for review by requesting them in writing from ATSDR (see ADDRESSES section of this Notice).
DATES:
Comments concerning the priority data needs for the 10 substances must be received by November 13, 2001. Regarding ATSDR's call for voluntary research proposals, the agency considers the voluntary research effort to be crucial to the continuing development of the Substance-Specific Applied Research Program, and believes this effort should be an open and continuous one. Therefore, private-sector organizations are encouraged to volunteer to conduct research to address identified data needs, beginning with the publication of this Notice and until that time when ATSDR announces that other research has been initiated for a specific data need.
ADDRESSES:
Submit comments to Dr. William Cibulas, Chief, Research Implementation Branch, Division of Toxicology, ATSDR, 1600 Clifton Road, NE., Mailstop E-29, Atlanta, GA 30333. Use the same address for requests for priority data needs documents and submission of proposals to conduct voluntary research.
Comments on this Notice will be available for public inspection at ATSDR, Building 4, Suite 2400, Executive Park Drive, Atlanta, Georgia (not a mailing address), from 8 a.m. to 4:30 p.m., Monday through Friday, except for legal holidays.
FOR FURTHER INFORMATION CONTACT:
Dr. William Cibulas, Chief, Research Implementation Branch, Division of Toxicology, ATSDR, 1600 Clifton Road, NE., Mailstop E-29, Atlanta, GA 30333, telephone (404) 498-0140.
SUPPLEMENTARY INFORMATION:
Background
The Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (Superfund) or CERCLA, as amended by the Superfund Amendments and Reauthorization Act of 1986 (SARA) [42 U.S.C. 9604(i)], requires that ATSDR (1) develop jointly with EPA a list of hazardous substances found at National Priorities List (NPL) sites (in order of priority), (2) prepare toxicological profiles of these substances, and (3) assure the initiation of a research program to address identified priority data needs associated with the substances.
The Substance-Specific Applied Research Program (SSARP) was initiated on October 17, 1991. At that time, a list of priority data needs for 38 priority hazardous substances was announced in the Federal Register (56 FR 52178). The list was subsequently revised based on public comments and published in final form on November 16, 1992 (57 FR 54150). In 1997, ATSDR finalized the priority data needs for a second list of 12 substances and announced the list in the Federal Register (62 FR 40820). Currently, a total of 201 priority data needs have been identified for these 50 substances.
This ATSDR SSARP supplies necessary information to improve the database to conduct public health assessments. This link between research and public health assessments, and the process for distilling priority data needs for ranked hazardous substances from data needs identified in associated ATSDR toxicological profiles, are described in the ATSDR "Decision Guide for Identifying Substance-Specific Data Needs Related to Toxicological Profiles" (54 FR 37618, September 11, 1989).
Implementation of Substance-Specific Applied Research Program
In Section 104(i)(5)(D), CERCLA states that it is the sense of Congress that the costs for conducting this research program be borne by the manufacturers and processors of the hazardous substances under the Toxic Substances Control Act of 1976 (TSCA) and by registrants under the Federal Insecticide, Fungicide, and Rodenticide Act of 1972 (FIFRA), or by cost recovery from responsible parties under CERCLA. To execute this statutory intent, ATSDR developed a plan whereby parts of the SSARP are being conducted via regulatory mechanisms (TSCA/FIFRA), private-sector voluntarism, and through the direct use of CERCLA funds.
CERCLA also requires that ATSDR consider recommendations of the Interagency Testing Committee (ITC), established under Section 4(e) of TSCA, on the types of research to be done. ATSDR actively participates on this committee; however, none of the proposed 10 substances are now on the ITC priority testing list.
The mechanisms for implementing the SSARP are discussed next. The status of the SSARP in addressing priority data needs of the first 50 priority hazardous substances via these mechanisms was described in a Federal Register Notice on January 15, 1999 (64 FR 2760).
A. TSCA/FIFRA
In developing and implementing the SSARP, ATSDR and EPA established procedures to identify those priority data needs of common interest to multiple federal programs. Where practicable, these data needs will be addressed through a program of toxicologic testing under TSCA or FIFRA. This part of the research will be conducted according to established TSCA/FIFRA procedures and guidelines.
B. Private-Sector Voluntarism
As part of the SSARP, on February 7, 1992, ATSDR announced a set of proposed procedures for conducting voluntary research (57 FR 4758). Revisions based on public comments were published on November 16, 1992 (57 FR 54160). ATSDR strongly encourages private-sector organizations to propose research to address data needs at any time until ATSDR announces that research has already been initiated for a specific data need. Private-sector organizations may volunteer to conduct research to address specific priority data needs identified in this Notice by indicating their interest through submission of a letter of intent.
The letter of intent should be a brief statement (1-2 pages) that identifies the priority data need(s) to be filled, and the methods to be used. The Tri-Agency Superfund Applied Research Committee (TASARC) will review these proposals and make recommendations to ATSDR regarding which specific voluntary research projects should be pursued and how they should be conducted with the volunteer organizations. ATSDR will enter into only those voluntary research projects that lead to high quality, peer-reviewed scientific work. Additional details regarding the process for voluntary research are in the Federal Register notices cited in this section.
C. CERCLA
Those priority data needs that are not addressed by TSCA/FIFRA or initial voluntarism will be considered for funding by ATSDR through its CERCLA budget. A large part of this research program is envisioned to be unique to CERCLA, for example, research on substances not regulated by other programs or research needs specific to public health assessments. Current examples of the direct use of CERCLA funds include interagency agreements with other federal agencies and cooperative agreements and grants with academic institutions.
Mechanisms to address these priority data needs may include a second call for voluntarism. Again, scientific peer review of study protocols and results would occur for all research conducted under this auspice.
Substance-Specific Priority Data Needs
The priority data needs are identified in Table 1. Unique identification numbers (37A through 46G) are assigned to the priority data needs for this list of 10 priority hazardous substances; the initial list of 38 substances has identification numbers 1A through 24C (64 FR 2760), and the second list of 12 substances has identification numbers 25A through 36G (64 FR 2760).
As previously stated, segments of the proposed research are unique to CERCLA and may be most appropriately addressed by ATSDR programs as follows.
ATSDR's responsibility as a public health agency addressing environmental health issues is, when appropriate, to collect human data to validate substance-specific exposure and toxicity assumptions. ATSDR will obtain this information by conducting exposure and health effects studies, and by establishing and using substance-specific subregistries of people enrolled in the agency's National Exposure Registry who are potentially exposed to these substances. When a subregistry or a human exposure study is identified as a priority data need, the responsible ATSDR program will determine its feasibility, which depends on identifying appropriate populations and funding.
In addition, the need to collect, evaluate, and interpret environmental data from contaminated media around hazardous waste sites remains a priority data need for all 10 priority hazardous substances ATSDR has identified for this third set. However, some of this information has already been collected through individual state programs and the EPA's CERCLA activities; therefore, ATSDR will evaluate the extant information from these programs to better characterize the need for additional site-specific information.
ATSDR acknowledges that the conduct of human studies to determine possible links between exposure to hazardous substances and human health effects may be accomplished through mechanisms other than agency programs. We encourage private-sector organizations and other governmental programs to use ATSDR's priority data needs to plan their research activities, including identifying appropriate populations and conducting studies to answer specific human health questions.
| Substance | PDN ID | Priority data needs |
|---|---|---|
| Asbestos | 37A | Epidemiologic studies of individuals occupationally exposed to asbestos levels lower than those experienced before the institution of current occupational standards governing the use of asbestos, but higher than current levels in the general population. These studies should be performed in conjunction with the immunotoxicity studies. |
| 37B | Immunotoxicity studies of individuals occupationally exposed to asbestos. | |
| 37C | Development of human and rat lung retention models to aid in extrapolating between rat and human data. | |
| 37D | Improved analytical methods for screening samples and determining the chemical structure of asbestos fibers. Also, techniques are needed to normalize studies in which different analytical methods were employed. | |
| 37E | Exposure levels, fiber size distribution, and asbestos fiber type in areas with natural geologic deposits of friable asbestos and at hazardous waste sites. Also, techniques for estimating air levels of asbestos from soil concentrations and activity scenarios. | |
| 37F | Exposure levels in humans living near hazardous waste sites and in other populations such as humans living in areas with naturally high levels of friable asbestos. | |
| 37G | Potential candidate for subregistry of exposed persons. | |
| Benzidine | 38A | Dose-response data for acute-and intermediate-duration exposure via the oral route (the study of subchronic-duration exposure should include evaluation of reproductive and endocrine organ histopathology, lymphoid tissues histopathology as well as examination of relevant blood components, and nervous system histopathology). |
| 38B | Exposure levels in humans living near hazardous waste sites. | |
| 38C | Exposure levels of children. | |
| 38D | Potential candidate for subregistry of exposed persons. | |
| Chlorinated dibenzo-p-dioxins | 39A | Studies via oral exposure designed to assess childhood susceptibility. |
| 39B | Comparative toxicokinetic studies examining the relative absorption of CDDs across exposure routes and the relative contribution of each exposure route to total body burdens. | |
| 39C | Exposure levels in humans living near hazardous waste sites. | |
| 39D | Exposure levels of children. | |
| 1,2-Dibromoethane | 40A | Dose-response data in animals for acute- and intermediate-duration exposure by the oral route (the study of intermediate-duration exposure should include neuropathology and observation for overt signs of neurotoxicity). |
| 40B | Multigeneration reproductive toxicity studies via oral exposure. | |
| 40C | Developmental toxicity studies via oral exposure. | |
| 40D | Immunotoxicity battery studies via oral exposure. | |
| 40E | Exposure levels in humans living near hazardous waste sites and in other populations such as workers exposed to 1,2-dibromoethane. | |
| 40F | Exposure levels of children. | |
| 40G | Potential candidate for subregistry of exposed persons. | |
| 1,2-Dichloroethane | 41A | Dose-response data in animals for acute-duration (14-day) exposure by the inhalation route, including a comparison of young and adult animals. |
| 41B | Dose-response data in animals for acute-duration (14-day) exposure by the oral route, including a comparison of young and adult animals. | |
| 41C | Dose-response data in animals for intermediate-duration exposure by the inhalation route (the study should be performed in conjunction with the neurotoxicology battery of tests). | |
| 41D | Neurotoxicology battery of tests following inhalation exposure. | |
| 41E | Neurotoxicology battery of tests following oral exposure. | |
| 41F | Dose-response data in animals for chronic-duration exposure by the oral route. | |
| 41G | Developmental toxicity data for inhalation exposure (assessment of developmental cardiotoxicity and neurotoxicity). | |
| 41H | Developmental toxicity data for oral exposure (assessment of developmental cardiotoxicity and neurotoxicity). | |
| 41I | Additional analyses and studies for comparative toxicokinetics across species, ages, routes, and durations. | |
| 41J | Children's susceptibility. | |
| 41K | Exposure levels in humans living near hazardous waste sites. | |
| 41L | Exposure levels of children. | |
| 41M | Potential candidate for subregistry of exposed persons. | |
| 1,1-Dichloroethene | 42A | Dose-response data in animals for acute-duration exposure by the inhalation route. |
| 42B | Dose-response data in animals for chronic-duration exposure by the inhalation route. | |
| 42C | Dose-response data in animals for acute-and intermediate-duration exposure by the oral route. | |
| 42D | Carcinogenicity studies in two species following inhalation exposure. | |
| 42E | Reproductive toxicity studies assessing male and female end points following inhalation exposure. | |
| 42F | Developmental toxicity studies following oral exposure. | |
| 42G | Immunotoxicology battery of tests following oral exposure. | |
| 42H | Battery of neurobehavioral tests following inhalation exposure. | |
| 42I | Children's susceptibility. | |
| 42J | Exposure levels in humans living near hazardous waste sites. | |
| 42K | Exposure levels of children. | |
| 42L | Potential candidate for subregistry of exposed persons. | |
| Ethylbenzene | 43A | Dose-response data for acute-duration exposure by the inhalation route. |
| 43B | Dose-response data for chronic-duration exposure by the inhalation route. | |
| 43C | Dose-response data for acute- and intermediate-duration exposure by the oral route; the study of intermediate-duration exposure should include an evaluation of clinical signs of neurotoxicity and histopathology of reproductive organs, endocrine glands, and nervous system. | |
| 43D | Multigeneration toxicity study examining reproductive end points and indicators of endocrine disruption following inhalation exposure. | |
| 43E | Two-species developmental study with continued assessment of offspring during postnatal development following oral exposure. | |
| 43F | Studies for comparative toxicokinetics. | |
| 43G | Exposure levels in humans living near hazardous waste sites. | |
| 43H | Exposure levels in children. | |
| 43I | Potential candidate for subregistry of exposed persons. | |
| Pentachlorophenol | 44A | In vivo endocrine disruptor studies via oral exposure. |
| 44B | Multigeneration reproduction study involving multiple matings and examining male and female fertility via oral exposure. | |
| 44C | Comparative toxicokinetic studies. | |
| 44D | Exposure levels in humans living near hazardous waste sites. | |
| 44E | Exposure levels of children through play activities near contaminated environmental media. | |
| 44F | Potential candidate for subregistry of exposed persons. | |
| 1,1,2,2-Tetrachloroethane | 45A | Two-species developmental toxicity study by the oral route. |
| 45B | Immunotoxicity battery following oral exposure. | |
| 45C | Mammalian in vivo genotoxicity assays. | |
| 45D | Exposure levels in humans living near hazardous waste sites. | |
| 45E | Exposure levels of children. | |
| 45F | Potential candidate for subregistry of exposed persons. | |
| Total xylenes | 46A | Dose-response data for chronic-duration exposure by the oral route. This study should be done in conjunction with the neurotoxicologybattery of tests. |
| 46B | Neurotoxicology battery of tests following oral exposure. | |
| 46C | Two-generation reproductive study following oral exposure. | |
| 46D | Developmental toxicity study that includes neurodevelopmental end points following oral exposure. | |
| 46E | Exposure levels in humans living near hazardous waste sites. | |
| 46F | Exposure levels of children. | |
| 46G | Potential candidate for subregistry of exposed persons. |
Dated: August 7, 2001.
Georgi Jones,
Director, Office of Policy and External Affairs, Agency for Toxic Substances and Disease Registry.
[FR Doc. 01-20373 Filed 8-13-01; 8:45 am]
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