EPA/600/N-94/009 united states environmental protection agency Region II, New York, New York 10278 DATE: June 24» 1994 SUBJECT: Risk Assessment Review FROM: William J.^WSzyhsk^f P.E. Deputy Regional Administrator William Farland, Ph.D. Director Office of Health and Environmental Assessment Attached is a copy of the Risk Assessment Review, a bimonthly publication that is a cooperative effort between the Office of Research and Development and the Regional Risk Assessment Network. The Review serves as a focal point for information exchange among the EPA risk assessment community on both technical and policy issues related to' risk assessment. It is currently in its fourth year of publication and we are pleased at the positive feedback we've received on the Review's usefulness to staff across the Agency. Thanks to all of you who continue to contribute articles and are involved with production efforts. If you have an article to contribute or any suggestions for further issues, contact one of the Committee members listed on page 1 of the Review. Attachment ------- ssessme May 1994 mm** • FSTRAC Workshop on the Revision to the Human Health Criteria Methodology p. 1 • SAB Project to Identify Future Environmental Problems.............. p. 1 • IRIS Highlights p. 6 • Symposium on Values, Perceptions, and Ethics in Environmental Risk Decision Making p. 6 I. Special Features Federal-State Toxicology And Risk Analysis Committee (FSTRAC) Workshop on the Revision to the Human Health Criteria Methodology by Bob CantiUi, (202) 260-5546 Introduction A total of 49 representatives from 13 states, 4 EPA regions, EPA Headquarters, and academia gathered at the fall Federal-State Toxicology and Risk Analysis Committee (FSTRAC) meeting in Washington, D.C. EPA officials Risk Assessment Review Committee BUI Farland - ORD, (202) 260-7317 Maureen McClelland • Region I, (617) 565-4885 Maria Pavlova - Region II, (212) 264-7364 Marian Olsen - Region n, (212) 264-5682 Suzanne Wuerthele - Region VIII, (303) 293-1714 Dana Davoli - Region X, (206) 553-2135 began the meeting by updating FSTRAC members on pro- posed drinking and ambient water regulations and criteria. FSTRAC subcommittees met to review accomplishments over the past six months and to plan for the next six months, and, as usual, the group discussed several hot issues on the final day. The highlight of the meeting, however, was the workshop on the Revision to the Human Health Criteria Methodology, which proved to be a successful interactive forum for state and federal discussion on the proposed revisions to the national methodology. FSTRAC members were first presented with an overview of the methodology, and then extensive discussion ensued on non-cancer risk, microbiology, exposure, bioaccumulation, cancer risk, and, minimum data requirements. (see FSTRAC, p 2) II. Headquarters Science Advisory Board (SAB) Project to Identify Future Environmental Problems by Don Barnes, (202) 260-4126 The SAB is in the midst of a major, year-long effort to help the Agency develop methods for anticipating environmen- tal problems of the future. Too often the Agency is in the position of playing "catch up" in regard to significant environmental problems. One can list numerous examples: PCBs, dioxins, wetlands disappearance, contaminated sedi- ments, and others. In 1993 EPA Administrator Carol Browner endorsed a proposal from David Gardiner, the Assistant Administrator for the Office of Policy, Planning and Evaluation (OPPE), that the SAB focus its technical expertise on responding to two requests: • Recommend techniques that could be used by the Agency to better anticipate the environmental prob- lems of the future (5 and 20 years from now). • Illustrate the use of those techniques by generating a sample listing of problems that the SAB believes could have significant environmental consequences 5 and 20 years from now. The SAB accepted this assignment, seeing it as the next step beyond their 1990 Reducing Risk report that argued that it is possible, on technical grounds, to distinguish between greater and lesser environmental risks. Dr. Raymond Loehr, former SAB chair and former co-chair of the Reducing Risk Activity, accepted the invitation to lead what is now known as the SAB's Environmental Futures Project (EFP). The Environmental Futures Committee (EFQ has been meeting nearly monthly over the past nine months to re- ceive briefings from Agency experts and, more often, ex- perts from around the country who make it their business (see SAB, p .6) 1 ------- FSTRAC (continued from p. 1) At the fall FSTRAC workshop, the essential question being asked state members by EPA officials was, "Should EPA proceed with the revised methodology as proposed?" More specifically, EPA sought to learn whether state members thought modifications suggested by the Science Advisory Board (SAB) would make the revised methodology more or less "implementable" at the local level, and whether they found the proposed revision to be based on the best science. State officials responded to EPA's call for comments in workshop presentations and discussions that focused on the six principle topic areas of the revision. Some presenters made comments on the proposed revision of the 1980 methodology in relationship to recommendations from EPA, the SAB, and participants at EPA's 1992 workshop, which involved more than 100 experts. Other presenters spoke more generally about recommended modifications to the proposed revision. The rest of this article summarizes the presentations and discussions that took place at the workshop. Noncancer Risk In his presentation on noncancer issues related to the pro- posed methodology, Scott Stoner of the New York State Department of Environmental Conservation generally sup- ported EPA and the 1992 workshop participants' recom- mendation to update the ambient water quality criteria using the reference dose (RfD) concept He added, how- ever, that he has questions about some of the uncertainty factors (UFs) and modifying factors (MFs) used to derive RfDs. The SAB did not specifically comment on use of the RfD concept Mr. Stoner reviewed the five factors for UFs and MFs endorsed by EPA and the 1992 workshop participants (the SAB did not specifically comment) and suggested that the MF and factor D, for an incomplete database, are redun- dant. Michael Dourson of the Systemic Toxicants Assess- ment Branch of EPA's Environmental Criteria and Assessment Office (ECAO) responded, saying that the MF is needed to account for the occasional uncertainty not covered by UFs. Dr. Dourson added that because the factors provided are default values, states should use specific data if they have them. Concerning whether severity of effect should be considered in developing the RfD, New York agrees with the 1992 workshop participants about the usefulness of this consider- ation and about the need for expanded guidelines. The SAB said that the scale needs further work and offered three scales for consideration. Joe Brown of the California EPA recommended that U.S. EPA list points to consider when developing an RfD rather than developing a restrictive quantitative methodology. This approach would give state officials an opportunity to exer- cise their professional judgment when using the methodol- ogy. On whether a plausible range of RfD values should be provided in the methodology, New York supports the ap- proach as long as the basis of the range is described, since the state's regulations require the derivation and implemen- tation of a single number. The SAB and the 1992 workshop participants also supported the range approach, and EPA's preliminary recommendation was to provide a more com- plete description of each RfD. In contrast Luanne Williams of the North Carolina Department of Environment Health, and Natural Resources said that risk managers in her state would prefer a single number that will protect the state's citizens from the majority of likely health effects. Deirdre Murphy of the Maryland Department of the Envi- ronment suggested that environmental groups likely would demand that states use the low end of a range, and industry likely would demand that the high end be used; as a result some states would be pressured toward the middle. She supported the range approach, however, because it would provide a basis for defending state-specific advisories. Gary Hurlburt of the Michigan Department of Natural Resources cautioned EPA to take into account situations where states share a common resource, as with the Great Lakes states, and use criteria within a region consistenly to avoid confu- sion. More generally, David Maschwitz of the Minnesota Pollution Control Agency pointed out that only larger states would be likely to have sufficient resources for officials to make the best use of a range. Margaret Stasikowski of the Ecological Criteria Division of EPA's Office of Water stated that presenting risk managers with a single RfD is not scientifically sound, since risk assessment produces a range rather than a precise value. Concerning the issue of whether EPA should establish ambient water quality criteria using new data or the estab- lished RfDs, New York supports using the most appropriate data and revising the RfDs as necessary. The position is essentially consistent with the one taken by EPA and the 1992 workshop participants. The SAB did not specifically address the issue. Mr. Brown said that most state officials would consult the Integrated Risk Information System (IRIS) first to check on the latest available data. On whether studies of less-than-lifetime duration should be used to derive criteria, Mr. Stoner said that New York places less reliance on 30-day studies, using these to derive a guidance value only. This position was consistent with the other panels' cautions about the use of studies that are of less than 90 days in duration. Gloria Post of the New Jersey Department of Environmental Protection and Energy said that her state depends on the endpoint and knowledge of how it is derived. 2 ------- New York agrees with the SAB that Health Advisory Doses (HADs) are not needed for the permit program. The 1992 workshop participants recommended providing HADs in- stead of ambient levels, and EPA supported the use of 1-day HADs. Both Mr. Stoner and Mr. Hurlburt contended that EPA should justify the public health need for short-term criteria. Concerning the use of other routes to derive RfDs if oral data are not available, New York generally agrees with EPA and the 1992 workshop participants that it is appropri- ate to use the inhalation route (and the dermal route should be explored) if a similar mechanism is involved and phar- macokinetic data can differentiate bioavailability. The SAB did not specifically address this issue. Similarly, New York was in general agreement with EPA and the 1992 workshop participants on the appropriateness of using developmental/reproductive, immunotoxicity, and/ or neurotoxicity studies for establishing criteria when a lifetime study is not available to serve as a general endpoint The SAB did not specifically address this issue. Also, New York agrees with the SAB and the 1992 work- shop participants that the methodology should endorse the use of physiologically based pharmacokinetic (PBPK) mod- els as needed to estimate tissue dose. EPA is urging caution in the use of pharmacokinetic data to encourage the use of adequate studies. On whether the methodology should allow for exceptions to assumed thresholds for noncarcinogens and teratogens, for example, New York agrees with EPA that the methodology should allow for such exceptions in cases where adequate justification is demonstrated. Mr. Stoner and Ms. Murphy noted that this would give the methodology the flexibility needed to accommodate developments in the science. Microbiology In his overview of current microbiological standards and major issues discussed at the 1992 workshop, Charles Haas, Professor of Environmental Engineering at Drexel Univer- sity in Philadelphia, said the workshop participants recog- nized the lack of a definitive methodology for performing a microbiological risk assessment Thus, participants recom- mended that a work group be assigned to outline procedures along with the rationale for performing such an assessment Mr. Haas contended that the current guidelines are inad- equate for several reasons, including their specificity to gastrointestinal illness and their exclusion of nonfecal patho- gens. Mr. Haas also pointed out that, according to the SAB, certain indicators used to make correlations between patho- gens and human illness at bathing beaches where microbial loadings are dominated by an outside source have been challenged. The SAB stated that current bacterial indicator levels do not uniformly provide adequate protection from gastrointestinal illnesses caused by pathogens found in bath- ing water. Mr. Haas recommended the development of a policy docu- ment on microbial risk assessment, since current method- ologies for establishing microbial water quality criteria are inadequate. He pointed out that EPA, the SAB, and the 1992 workshop participants have acknowledged the poten- tial utility of conducting formal microbial risk assessments that are based on dose-response and exposure information. Developing such a methodology would require generating additional data for defining duration of exposure relative to effects. Along with developing criteria for surface water, Mr. Haas recommended developing microbial criteria for drinking» water sources, reclaimed wastewater, shellfish waters, ground water, irrigation waters, and wedands-in that order. Mr. Haas closed by identifying further research needs: development of indicators that are more specific to human and nonhuman sources; development and validation of meth- ods for direct pathogen detection based on molecular meth- odologies; and extension and validation of databases on pathogen dose-response relationships and exposures. Exposure Human Health Exposure Issues In her presentation on human health issues relevant to the proposed methodology, Dr. Post discussed the recent work of New Jersey state officials in developing surface water quality standards. The major exposure issues addressed by state officials were the designated uses and pathways con- sidered, the selection of values for exposure assumptions, exposure concentrations for low bioconcentration factor contaminants, issues related to combining exposure path- ways, nonsurface exposure routes, and consistency with other regulatory programs. Dr. Post reviewed equations from the 1980 methodology that the state uses to calculate criteria for carcinogens and noncarcinogens in potable water, saying that the major exposure factors for such calculations are body weight drinking water consumption, fish consumption, and bioconcentration. For nonpotable uses, fish consumption would be the only exposure factor considered. In regard to the combining of exposure pathways for the revised methodology, Dr. Post said New Jersey favors combining criteria for such pathways as drinking water and fish consumption. The SAB recommended that separate criteria be used for such pathways. Also, Dr. Post emphasized the importance of consistency in exposure assumptions among regulatory programs—a sig- 3 ------- nificant problem for state officials working in areas involv- ing a variety of media and standards. Exposure Elements of the Great Lakes Water Qual- ity Initiative In his presentation on exposure assessment, Mr. Hurlburt discussed the recent work of officials of the Great Lakes states in developing the Great Lakes Water Quality Initia- tive (GLI). A primary goal of the GLI was to establish consistent water quality criteria using data specific to the region. Mr. Hurlburt singled out fish consumption values as an example of the GLI approach. The GLI work group consid- ered the regulatory default value for Michigan to be low at 6.5 grams/day (g/day). After reviewing several region-specific studies on fish consumption, a determina- tion was made that a value of IS g/day was more reason- able. The work group then carried out an analysis that indicated only 11 percent of Michigan residents were likely to be exposed above the IS g/day value. The same analysis applied to Wisconsin yielded a comparable finding. The work group also found fish consumption values to be con- sistent in die region relative to body weight Michigan strongly recommends that incidental exposure be factored into exposure assessments. State officiate assume that a typical resident is subjected to one hour-long recre- ational exposure event per day during the four warm-weather months of the year, TTiis assumption yields 123 hours of potential water recreation exposure per year for a typical resident, an estimate that is consistent with other state data on recreational exposure. In regard to the proposed revision of the 1980 methodology, Mr. Hurlburt said that Michigan supports a single criterion for fish consumption and drinking water. Michigan recom- mends looking at water bodies as complete exposure routes and factoring in incidental exposure. Michigan also considers it appropriate and practical to use relative source contribution only in regard to chemical exposures that occur primarily through the surface water route (Le., fish consumption). Mr. Hurlburt contended that it is inappropriate to attempt to control total exposure to these contaminants via the surface water route until an equivalent level of control over contaminants from other environmental media is feasible. Mr. Maschwitz contended that using a separate relative source value would be appropriate for pesticides since high concentrations are found in food. Bioaccumulation In his presentation, Mr. Maschwitz said that Minnesota recommends that the revised methodology follow the same approach used in the GLI for determining bioaccumulation factors. The goal should be for EPA to recommend a single method for determining bioaccumulation factors that is flexible enough to accommodate local conditions and the availability of data. Mr. Maschwitz identified areas of agreement between the proposed revised methodology and the GLI. These include using bioaccumulation factors rather than bioconcentration factors to determine water quality criteria; relating bioaccumulation factors to the lipid content of fish; using log K^Cp) models to predict bioaccumulation factors; using a food chain multiplier to predict bioaccumulation from bioconcentration; recognizing the need for adequate quality assurance for both field and lab bioconcentration factors; and determining inorganic bioaccumulation factors on a chemical-specific basis. Moreover, the proposed methodol- ogy and the GLI are generally in agreement in regard to the hierarchy of preferred data for determining bioaccumulation factors. Mr. Maschwitz also outlined areas of potential disagree- ment These concerned metabolism and its impact on bioaccumulation; bioavailability and dissolved versus total concentrations; superlipophilic organic chemicals Cog > 6.5) (in regard to the use of a food chain multiplier, accounting for metabolism, and the use of log Km to predict a bioconcentration factor); and the use of mean or high values as a standard procedure for deriving bioaccumulation and bioconcentration factors and for percent lipid. Disagreeing with the SAB's recommendation that EPA return to an emphasis on bioconcentration, Mr. Maschwitz encouraged EPA to continue to develop the bioaccumulation factors approach. He noted that an SAB committee found the GLI's bioaccumulation approach to be an improvement over the bioconcentration approach, although the commit- tee contended that the Thomann model should not be used in a regulatory situation. The Thomann model, which was proposed for use in the GLI, is a biomagnification model used to determine the food chain multiplier. Cancer Risk In his presentation on cancer issues related to the proposed methodology, Mr. Brown stated that California would favor representing the criteria for carcinogens with a range of plausible estimates of chemical concentrations in surface water. The SAB has recommended expressing risk both as point estimates (with an indication of the uncertainty of the estimate) and as a collection of credible alternative esti- mates based on applicable models. EPA has suggested using a point estimate along with an indication of uncer- tainty. At the 1992 workshop, participants agreed with EPA but recommended expressing uncertainty as ranges and providing alternative procedures. 4 ------- Concerning use models other than the linearized multistage (LMS) model such as threshold approval, Mr. Brown ex- pressed concern about whether enough data are available on agents that produce chromosomal aberrations to use this threshold approach. EPA advocates use of the LMS model only when data suggest linearity or when available informa- tion does not establish a mechanism. Participants at the 1992 workshop agreed with EPA, and the SAB made no specific comment Mr. Brown joined EPA, the SAB, and the 1992 workshop participants in their support of the development of physi- ologically based pharmacokinetic (PBPK) and dosimetry modeling. Concerning Group C chemicals, Mr. Brown generally agreed with 1992 woikshop participants that the determination of whether to quantify cancer risk from animal studies should be based on the appropriateness of the data. He added, however, that establishing some guidelines would be use- ful. EPA prefers setting a criterion for this group of chemi- cals on the basis of noncancer endpoints with an uncertainty factor for the carcinogen of concern. The SAB recommends a case-by-case approach, given that Group C chemicals are extremely heterogeneous. Mr. Brown said that California joins the consensus concern- ing the proposal to use genotoxicity data more effectively when data to suggest evidence of carcinogenicity aie incon- clusive. Also, California generally agrees with EPA and the 1992 workshop participants that 2 liters/day should be used as a parameter when assessing cancer risk for adults. The SAB did not specifically address this issue. Mr. Brown commented, however, that emerging probabilistic approaches may ultimately be capable of providing a more precise value. Concerning the EPA-Food and Drug Administration con- sensus and 1992 workshop support regarding a proposed body weight of 3/4th power for cross-species scaling, Mr. Brown noted that another approach is receiving consider- able attention. This alternative involves use of a single default interspecies scaling power for cancer risk assess- ment to account for pharmacokinetic and pharmacodynamic (PD) differences between animals and humans. The SAB did not specifically comment on the EPA-FDA approach. In reference to the EPA recommendation that Agency-wide guidelines should be followed to assess the effects of mul- tiple carcinogenic chemicals and chemical interactions, Mr. Brown noted that novel PBPK/PD work on mixtures is being conducted. Researchers believe this work could yield a breakthrough in "non-additive" methodologies for certain mixtures. Minimum Data Derivation of Aquatic Life versus Human Health Criteria Deirdre Murphy of the Maryland Department of the Envi- ronment pointed out that minimum data requirements for deriving human health criteria are dependent on data qual- ity, in contrast to the development of aquatic life criteria, which requires that a specific number of tests be conducted. For human health criteria, an RfD can be based on a single study, if the data provide the Lowest Observed Adverse Effect Level (LOAEL). Ms. Murphy noted that the 1992 workshop participants recommended looking at the mini- mum data requirements on three levels when assessing a chemical. Providing a context for Mr. Hurlburt's presentation on minimum data requirements, Ms. Murphy also highlighted a number of other issues raised by the 1992 workshop participants, including whether guidelines should include specific data requirements. Recommendations for Minimum Data from the 1992 Workshop In his presentation, Mr. Hurlburt noted that the 1992 work- shop participants concluded that data can be categorized using a tiered approach, and he summarized the data re- quirements of the five tiers: • Tier I data, the highest quality data available, include mechanistic, pharmacoldnetic, and target organ toxicity data most predictive of human health effects. • Tier n data, which are of lesser quality in predict- ing human health effects, include data greater than, or of minimum quality, for establishing an RfD and/or data sufficient to meet the cancer risk guide- lines classification for Groups A and B and some Group C carcinogens of high concern. • Tier in data, which are of sufficient quality to develop interim toxicity values, include all avail- able data not sufficient to meet the quality/quantity requirements for RfD development • Tier IV data, which are data that do not meet minimum data requirements for Tier III, include acute toxicity, genetic toxicology, and structure-activity relationship data. • Tier V consists of no data. Mr. Hurlburt noted that Michigan prefers to use the avail- able data to make a scientific judgment rather than to leave a criterion at zero. According to Mr. Stoner, New York follows guidance values that are similar to those of Tier III 5 ------- (i.e., data of sufficient quality to develop interim toxicity values); however, if the data are not sufficient to meet a certain minimum criterion, the state will not promulgate a standard. Mr. Hurlburt explained that for the GLI, a two-tiered classi- fication system is used. The approach recommended by the 1992 workshop participants provides greater distinction between the quality and quantity of data than the GLI approach. The minimum data standard for the GLI requires that the best available toxicity data on adverse health effects be used. For carcinogens, all appropriate human epidemio- logical data and animal cancer bioassay data are considered. Mr. Hurlburt also described the specifics of the two GLI tiers. The next FSTRAC meeting is tentatively scheduled for the fall in Washington, DC. >- For more information about the next meeting or FSTRAC in general, call Bob Cantilli at (202) 260-5546 or Ed Ohanian at (202) 260-7571 in the Office of Water's Office of Science and Technology. SAB (continued from p. 1) to look into the future, identifying problems/opportunities for businesses and institutions. The focus has been on the techniques that are used in these various situations. In addition, most of the the SAB's 10 standing committees have joined the effort by "looking over the horizon" from their specialized perspectives of drinking water, air, ecologi- cal effects, etc. The EFP has enlisted Tom Super of the Office of Policy, Planning and Evaluation (OPPE) to help draft the report this summer. If you've ever wondered (or worried) about the environ- mental problems of the future but were afraid to ask (or never had the time to think about it!), keep your eyes open for die the SAB's Environmental Futures Report—coming to an INTERNET node near you this fall. Integrated Risk Information System Highlights by Patricia Daunt, (513) 569-7596 Summarized below are the Integrated Risk Information System (IRIS) highlights for the months of April, May, and June. More detailed NEWS is available for IRIS-2 users on the first screen of the system. April 1994 Update Oral RfD Added to IRIS: Aroclor 1248 CASRN 12672-29-6 May 1994 Update Inhalation RfC Added to IRIS: Methylene diphenyl isocyanate (MDI) CASRN 101-68-8 June 1994 Update Oral RfD Added to IRIS: Chlorine CASRN 7782-50-5 Inhalation RfC Added to IRIS: Dichlarvos CASRN 62-73-7 Carcinogenicity Assessment Noted as Pending Change: Arsenic CASRN 7440-38-2 As of June 1, 1994, IRIS contained 520 chemicals. This included 348 RfDs, 88 inhalation reference concentrations, and 218 carcinogenicity assessments, bringing the total number of risk information assessments to 654. In addition, IRIS contained 73 Drinking Water Health Advisories and 388 EPA regulatory action sections. >- For additional information, contact Patricia A. Daunt, IRIS Database Manager, at (513) 569-7596. Solicitation for Hot Chemicals and Key Risk Assessment Issues by Pat Daunt, (513) 569-7596 The EPA ECAO in Cincinnati, Ohio, is engaged in restruc- turing into several self-directed work teams. An outgrowth of ECAO's restructuring was the inception of the 'Technol- ogy Transfer Team." The teams' main objectives include identifying ECAO's key customers, responding to their needs, and identifying needs for improved risk assessment methods. The current function of this team is to manage existing projects such as IRIS, Superfund Health Risk Tech- nical Support Cento*, and the Health and Environmental Assessment Summary Table (HEAST). The Technology Transfer Team is soliciting input from EPA's risk assessors on specific human health risk assess- ment needs. We are also interested in your specific needs for new or improved risk assessment methods. Please FAX your suggestions to the Technology Transfer Team at (513) 569-7916, no later than September 22, 1994. We look forward to hearing from you. Please note: Responses will be accepted from EPA stafT only. Symposium on Values, Perceptions, and Ethics in Environmental Risk Decision Making by C. Richard Coihern, (202) 260-2734 The Center for Environmental Statistics Development Staff in EPA's OPPE will host the "Symposium on Values, 6 ------- Perceptions and Ethics in Environmental Risk Decision Making." The symposium will be part of the National Meeting of the American Chemical Society scheduled for August 21-25,1994, at the Washington Convention Center. The tentative date for the symposium is August 24,1994. The symposium will discuss different approaches to mak- ing risk decisions and the impacts of different values, perceptions, and ethics on these decisions. This symposium will involve discussions of current risk analysis and deci- sion processes as well as "how to" methods for directly involving value judgements and biases in the process. Some example judgments that will be discussed include safety, equity, fairness, justice, quality of life, health, stewardship, simplicity, fear, lack of trust, and doing the right thing. Speakers with varied institutional perspectives will partici- pate: industry spokespeople, government and academic risk decision makers, policy makers, social scientists, ethicists, philosophers, value researchers, journalists, theologians, and regulators. > For further information on the meeting contact C. Richard Cothem, Senior Scientist and Analyst, Center for Environmental Statistics Development Staff, Office of Policy, Planning and Evaluation, U.S. EPA, 401 M Street, S.W., Washington, D.C. 20460. The phone num- ber is (202) 260-2734 and the FAX is (202) 260-4968. in. Regions Region II Following are a few publications of interest: • The 1992 Toxics Release Inventory: Public.Data Releases, (EPA 745-R-94-001) and the 1992 Tox- ics Release Inventory: Public Data Release: State Fact Sheets (EPA 745-F-94-001) are available by contacting the EPCRA Hotline at (800) 535-0202 or (703) 412-9877. • The Office of Pollution Prevention and Toxics (OPPT) announced the availability of ECOS AR, a software program for estimating the toxicity of industrial chemicals to aquatic organisms. ECOSAR is a computerized version of the Structure-Activity Relationships (SAR) methods currently practiced by staff scientists in OPPT. ECOSAJt: Computer Program and User's Guide for Estimating the Ecotoxicity of Industrial Chemi- cals Based on Structure Activity Relationships is available from the National Center for Environ- mental Publications and Information at (513) 596-7985. The EPA number is EPA-748-R-93-002. The document is also available from the National Technical Information Service at (703) 487-4650; publication numbers are PB94-104668 and PB94-500485. The Program and User's Guide may also be downloaded from the Government Printing Office Bulletin Board at (202) 512-1524. • EPA recently announced model standards and tech- niques for radon in homes. The standards were developed under the 1988 Indoor Radon Abate- ment Act. For more information contact Dave Murane at (202) 260-9442. • The Association of State and Territorial Health Officials (ASTHO) published a final report on a Multicultural Public Health Capacity Building Pi- lot Project Copies of the report are available from Monica Perz, ASTHO, 415 Second Street, N.E., Suite 200, Washington, D.C. 20002. Ms. Perz's phone number is (202) 546-5400. >• Contact: Marian Olsen, (212) 264-5682 IV. Meetings Third Summer Institute in Environmental Law—July 11-15,1994 New Yoik University will offer the Third Summer Institute in Environmental Law July 11-15,1994, from 9:00 a.m. to 5:00 p.m. The course will address environmental laws concerning air and water quality and solid and hazardous waste. Toxic torts are covered from the perspectives of property transfers, liability, public disclosure, citizen suits, enforcement, the application of health and environmental standards, and other topics. Co-directors of the course are Michael B. Gerrard, Esq., of Berle, Kass, and Case and Professor Rae Zimmerman from New York University. > For further information contact Professor R. Zimmerman, Course Director/Wagner Graduate School of Public Service at New York University (4 Washing- ton Square North, New York, New Yoik 10003). The phone number is (212) 998-7432 or the Center for Management at (212) 998-7450. Graduate course cred- its are available ($1,660 plus $33.00 fee). For non-credit certificate the cost is approximately $900.00. Society for Risk Analysis Course "New Horizons in Risk Assessment"—August 29-30, 1994 The Society for Risk Analysis will hold its eighth annual course, "New Horizons in Risk Assessment," August 29-30, 1994, at the Hyatt Regency, Crystal City, Arlington, Vir- ginia. The intent of the course is to provide an introductory overview of methodologies, assumptions, and new research in risk assessment. Lecturers will show how to perform and interpret risk assessments and how to use them in risk management Special emphasis will be given to new devel- opments in the field. Anyone desiring to learn the basic 7 ------- principles of risk assessment from nationally recognized leaders in the field should profit from this course. Lecturers will be Dr. Elizabeth Anderson, President, Sciences Inter- national, Inc.; Dr. Mildred Christian, President and CEO, Argus International, Inc.; Dr. Max Costa, Director, Institute of Environmental Medicine, New York University; Dr. Barnard Goldstein, Director, Environmental and Occupa- tional Health Sciences Institute; Dr. Lester Lave, James H. Higgins, Professor of Economics and University Professor, Carnegie-Mellon University; Dr. Thomas McKone, Group Leader, Exposure Assessment, Lawrence Livermore Na- tional Laboratory; Dr. Susan Santos, Director, Center for Risk Communication, Columbia University School of Pub- lic Health; Dr. Curtis Travis, Director, Center for Risk Management, Oak Ridge National Laboratory, and Dr. Chris Whipple, Vice President, ICF/Kaiser. > For further information call Dr. Curtis C. Travis, Course Director at (61S) 576-2107 or Mary Oran, Course Coordinator, at (615) 376-6844. Workshop on Bioavailability and Oral Toxicity of Manganese—August 30-31,1994 EPA's ECAO will host a two-day workshop, "Bioavailability and Oral Toxicity of Manganese," August 30-31,1994. The workshop will be held at EPA's Andrew W. Breidenbach Environmental Research Center, 26 West Martin Luther King Drive, Cincinnati, Ohio. The speakers will include Carl Keen, Bo Lonnerdal, and Jeanne Freeland-Graves. >• For additional information concerning the meeting con- tact Sue Velazquez or Joan Dollarhide of EPA's ECAO. Sue can be reached at (513) 569-7571 or Joan at (513) 569-7539. Challenges in Risk Characterization Workshop—September 7-8,1994 A workshop entitled "Challenges in Risk Characterization" will be held on September 7-8,1994, at EPA's Andrew W. Breidenbach Environmental Research Center in Cincinnati, Ohio. The workshop, sponsored by EPA's ECAO, is for EPA regional and headquarters risk assessors. Topics for the workshop will include implementation of the 1992 Risk Characterization Guidance, EPA management perspective on the guidance, case studies on successful implementation, and scientific tools and research needs for risk characteriza- tion. »• For further information and workshop agenda contact Rebecca Madison, Acting Chief, Chemical Mixtures Assessment Branch, ECAO-Cin. at (513) 569-7257. There is no registration fee for the workshop. Joint Sixth Conference of the International Society for Environmental Epidemiology and Fourth Conference of the International Society for Exposure Analysis—September 18-21, 1994, Research Triangle Park, North Carolina The joint Sixth Conference of the International Society for Environmental Epidemiology and Fourth Conference of the International Society for Exposure Analysis will be held September 18-21, 1994, in Research Triangle Park, North Carolina. The conference is being hosted by the University of North Carolina at Chapel Hill School of Public Health. Sponsors include the National Institute of Environmental Health Sciences, EPA, ATSDR, and the World Health Organization. The purpose of the joint conference is to bring together scientists from throughout the world to ex- change ideas, methods, and applications for cutting edge research on environmental health. >¦ To register contact Phylliss Woody, Registrar, Office of Continuing Education, University of North Carolina School of Public Health, CB #8165, Miller Hall, Chapel Hill, North Carolina 27599-8165. Phone registration is available by calling (919) 966-4032 or FAX (919) 966-5692. Hotel reservations are available through the Sheraton Imperial Hotel and Convention Center in Research Triangle Park, North Carolina (rate $72 for a single or double room). The phone number for reservations is 800-222-6503 or (919) 941-5050. Conference on Computing in Environmental Management—November 30-December 2,1994 A specialty conference co-sponsored by the U.S. EPA and the Air and Waste Management Association will be held November 30-December 2, 1994, at the North Raleigh Hilton, Raleigh, North Carolina. The EPA sponsors include the Office of Air Quality Planning and Standards from OAR, Atmospheric Research and Exposure Assessment Laboratory from ORD, and the National Data Processing Division from OARM. Training opportunities, including a short course on the National Library of Medicine's online databases, will precede the conference; there will be a hardware and software exhibit as well. Advance registration is $370 for non-AWMA members, $285 for members, and includes proceedings. Although computing and netwoik technology have become increasingly important as an integral part of environmental management, this aspect of the field has been given little emphasis in the literature. The purpose of this conference is to expand the scope of information commonly presented about the characterization and solution of environmental problems to include the analytical tools and technology strategy employed in order to identify and/or implement solutions. 8 ------- Following a keynote address on the impact of the informa- tion highway on environmental management, concurrent sessions will be held on modeling, visualization, and high performance computing; artificial intelligence and expat systems, Global Positioning Systems, and Geographic In- formation Systems; database management issues, including client-server systems; multiplane complex environmental assessments; advances in input/output; electronic data inter- change; and remote online access. >- For additional information on the meeting, contact Vandy Bradow, National Data Processing Division, MD-34, U.S. EPA, Research Triangle Park, North Caro- lina 27711. Vandy's phone number is (919) 541-3574. Or contact Adrian Corolla, AWMA, P.O. Box 2861, Pittsburgh, Pennsylvania 15230. Adrian's phone num- ber is (412) 232-3444. VII International Congress of Toxicology— July 2-6,1995 The VII International Congress of Toxicology (ICT VII) will be held in Seattle, Washington, July 2-6, 1995. The program will be based on the theme, "Horizons in Toxicol- ogy: Preparing for the 21st Century." The meeting will be hosted by the Society of Toxicology in conjunction with the International Union of Toxicology. >> For additional information contact ICT/VII, c/o Soci- ety of Toxicology, 110114th Street, N.W., Suite 1100, Washington, D.C. 20005-5601 or (202) 371-1393. The FAX number is (202) 371-1090. Risk and Decision-Making Course Schedule The following is the schedule for the Risk and Decision-Making Courses through August: August 2-4 Denver, Colorado August 9-11 New York City, New York The following is the schedule for the Risk Communication Workshops through August: June 20-27 New South Wales, Australia (offered by Region IX) August 16-18 San Francisco, California September 19-22 Washington, D.C. (offered by Region IX) >¦ Contacts: Jim Cole, (202) 260-2747 Marian Olsen, (212) 264-5682 Alvin Chun, (415) 744-1022 Contacts: Jerome Puskin OAR-RAD (202) 260-9640 Linda Tuxen ORD-OHEA (202) 260-5949 Dorothy Patton ORD-RAF (202) 260-6743 John Vandenberg ORD-HERL (919) 541-4527 Dick Hill OPTS (202) 260-2897 Don Barnes SAB (202) 260-4126 Dean Hill NEIC (202) 776-8138 Maureen McClelland Region I (617) 565-4885 Marian Olsen Region II (212) 264-5682 Jeffrey Burke Region III (215) 597-8327 Elmer Akin Region IV (404) 347-1586 Carole Braverman Region V (312) 886-29.10 Jon Rauscher Region VI (214) 655-8513 Mary Rouse Region VII (913) 551-7415 Suzanne Wuerthele Region VIII (303) 293-0961 Arnold Den Region IX (415) 744-1018 Dana Davoli Region X (206) 442-2135 <£RI Distribution 26 West Martin Luther King Drive Cincinnati, Ohio 45268 If you would like to receive additional copies of this and subsequent Reviews or to be added to the mailing list contact 9 ------- |