W4-C.5 Sass J; jsass@nrdc.orgNatural Resources Defense Council (NRDC)NATURAL RESOURCES DEFENSE COUNCIL (NRDC) PERSPECTIVEON TRANSPARENCY, SPEED AND STAKEHOLDERS’ INVOLVE-MENT IN EPA’S CHEMICAL RISK ASSESSMENTThe EPA has a program <strong>for</strong> assessing the hazards of industrial chemicals in ourair, water, and soil. These scientific assessments are not regulations themselves, butthey are frequently used by regulators, at EPA, in the states, and around the world,to set the allowable levels of exposure to chemicals from different sources. UnderTSCA - chemicals are considered safe until they are proven to be harmful by regulatoryagencies. In most cases, the agency can’t prove that a chemical is harmful withoutcompleting an assessment. And, un<strong>for</strong>tunately, under the current law there is noen<strong>for</strong>ceable deadline <strong>for</strong> EPA to complete its chemical assessment, no ‘harmful untilproven safe’ interim standards to limit chemical exposures, and no consequences <strong>for</strong>the industry if EPA fails to (or is prevented from) completing an assessment. Combinedwith the “innocent until proven guilty” approach of the current law, industryhas every incentive to delay the completion of those assessments it thinks may leadto regulatory restrictions or liabilities. The recurring failure to complete risk assessmentsand set new legal limits on chemicals is so severe, that it became the focus ofan investigation and report by the Government Accountability Office (GAO) in 2008.This presentation presents three high-profile chemical assessments - <strong>for</strong>maldehyde,styrene, and TCE - to support regulatory re<strong>for</strong>ms. Re<strong>for</strong>ms should include: en<strong>for</strong>ceabledeadlines <strong>for</strong> completing chemical assessments, meaningful consequences <strong>for</strong> thefailure to complete a safety assessment, default interim health-protective standards(such as some protective fraction of the LD50) until the EPA can complete its assessment,restrictions on the expansion or new use of a chemical pending completion ofthe safety assessment, and shifting the burden of proof from the EPA to the chemicalindustry to show that chemicals are safe. EPA needs the authority to take action andprotect the public from unsafe chemicals without waiting <strong>for</strong> additional years of studyor surmounting endless hurdles thrown up by the regulated industry.M4-D.3 Scanlon KA, McDonald SM; scanlon30@yahoo.comConcurrent Technologies CorporationCLOSING THE LOOP: AN ASSESSMENT OF THE LIFE CYCLE OFBERYLLIUM-CONTAINING MATERIALS IN THE DEPARTMENT OFDEFENSEThe Department of Defense classifies beryllium as a strategic, critical material.It is used in a vast array of defense-related products, such as bearings <strong>for</strong> landing gear,electronic connectors, mast-mounted sights, hatch springs, and mirrors. Beryllium’sphysicochemical characteristics make it a valued metal <strong>for</strong> military aerospace applications.Despite these characteristics and its numerous uses beryllium compounds pose168significant human health hazards when the beryllium or the beryllium-containingcomponent is abraded, ground, or otherwise made respirable. Workplace activitiesand processes that generate aerosols are of particular concern. Exposure to aerosols(particulates, fumes, and dusts) of beryllium compounds (metal, alloys, oxide) is associatedwith beryllium sensitization and chronic beryllium disease. The U.S. EnvironmentalProtection Agency (USEPA), the National Toxicology <strong>Program</strong>, and theInternational Agency <strong>for</strong> Research on Cancer (IARC) support the conclusion thatberyllium is likely a human carcinogen. Because beryllium is a potential occupationalexposure hazard and a strategic, critical material, it is important to know where berylliumis used, how it is used, and how it is managed at end-of life. The main goal ofthis presentation is to provide the results of a life cycle study that tracked specificberyllium-containing materials used in the DoD through production, component fabrication,manufacture, storage, use, maintenance, and end-of-life management. Thepresentation will highlight existing policies, procedures, and practices concerning thesafe use and handling of beryllium, gaps in the life cycle of beryllium-containing materials,and risk management options to address these gaps.M4-E.1 Schaffner DW, Danyluk MD; schaffner@aesop.rutgers.eduRutgers UniversityLESSONS LEARNED FROM A PRELIMINARY QUANTITATIVE MI-CROBIAL RISK ASSESSMENT FOR LEAFY GREENSThis presentation will present findings from a project that was undertaken torelate what is known about the behavior of E. coli O157:H7 under laboratory conditions,and integrate this in<strong>for</strong>mation to what is known regarding the 2006 E. coliO157:H7 spinach outbreak in the context of a Quantitative Microbial <strong>Risk</strong> Assessment(QMRA). The QMRA explicitly assumes that all contamination arises fromexposure in the field, but the mechanism is unspecified. What can be specified are theprevalence per serving and the pathogen concentration per gram on product comingout of the field. Extracted data, models and user inputs were entered into an Excelspreadsheet and the modeling software @RISK was used to per<strong>for</strong>m Monte Carlosimulations. The model predicts that cut leafy greens that are temperature abused willsupport the growth of E. coli O157:H7, where concentrations of the organism mayincrease by as much a 1 log CFU per day under optimal temperature conditions. Whenthe risk model used a starting concentration of -1 log CFU/g, with 0.1% of incomingservings contaminated, the predicted cells per serving were within the range of bestavailable estimates of pathogen concentrations during the outbreak. The model predictsthat levels in the field of -1 log CFU/g and 0.1% prevalence could have resultedin an outbreak approximately the size of the 2006 E. coli O157:H7 outbreak. ThisQMRA model represents a preliminary framework that identifies available data andprovides initial risk estimates <strong>for</strong> pathogenic E. coli in leafy greens. Important datagaps that were identified include retail storage times, correlations between storage
time and temperature, determining the importance of E. coli O157:H7 in leafy greenslag time models, and validation of the importance of cross-contamination during thewashing process.M2-J.2 Schultz BD; schultz.brad@epa.govU.S. Environmental Protection AgencyCUMULATIVE RISK ASSESSMENT AND MULTIDIMENSIONAL IN-DICATORSMany community groups have asked <strong>for</strong> a cumulative risk assessment (CRA)or cumulative impact assessment <strong>for</strong> their communities; they believe that some traditionalrisk assessments have ove rlooked major issues facing their communities. In responseto this call, US EPA published its Framework <strong>for</strong> Cumulative <strong>Risk</strong> Assessmentin 2003 and has undertaken a number of other ef<strong>for</strong>ts; the US National ResearchCouncil published Science and Decisions; and many other activities have been andare being undertaken by governmental and non-governmental organizations. Progress,however, continues to be slow on this challenging problem and several differentapproaches have been taken. This presentation briefly breaks down these CRAapproaches into several categories and describes an approach of multidimensionalindicators <strong>for</strong> accelerating scientific advances and application to multiple real-worldcommunities. These multidimensional indicators allow <strong>for</strong> core advances which canbe used <strong>for</strong> a variety of CRA approaches and rely heavily on improved exposure estimationapproaches at community scales. It also holds promise <strong>for</strong> incorporating nonchemicalstressors into community-based cumulative risk assessments more widely.P.68 Schultz BD, Zartarian VG, Geller A, Barzyk T, O’Shea S; schultz.brad@epa.govUS Environmental Protection AgencyEXTENDING YOUR COMMUNITY-BASED RESEARCH TO OTHERCOMMUNITIES: US EPA’S C-FERST (COMMUNITY-FOCUSED EXPO-SURE AND RISK SCREENING TOOL)Community-based research on environmental exposures and risks has empoweredmany communities, reduced environmental injustices, and otherwise improvedmany communities. Gaps remain, however, in the development of readily-availabledata and tools critical to in<strong>for</strong>ming community activities. In order to provide toolsand in<strong>for</strong>mation to more communities, EPA is developing the Community-FocusedExposure and <strong>Risk</strong> Screening Tool (C-FERST) to assist with community assessmentsand lead toward actions to improve the health and well-being of communities. Forresearchers, C-FERST can provide a venue <strong>for</strong> extending their research beyond individualcommunities and expand the impact of scientific research. C-FERST focuseson research which can be used in any community in the U.S., such as ambientconcentration, human exposure, and health effects, from spatially-explicit modelingresults covering large geographic areas; also included are measurement methods andrisk reduction approaches which have broad geographic applicability. The intent ofC-FERST is to foster meaningful community-based cumulative risk assessments andcumulative impact assessments. Collaborative research opportunities and needs exist<strong>for</strong> exposure modeling ef<strong>for</strong>ts, model evaluation, measurement methods, source apportionmentapproaches, risk reduction ef<strong>for</strong>ts, community sustainability best practices,the effects of ecosystem services on human health and well-being, and otheractivities widely applicable across the U.S. and, sometimes, other countries. The presentationwill discuss how research activities in these areas could be part of EPA’sweb-based GIS decision support tool <strong>for</strong> conducting cumulative human exposureand risk screening assessments, to help build sustainable and healthy communities.This presentation will describe how previous research is being delivered to communitiesand a description of how future research could be delivered, including your currentor future research.M2-B.3 Schuver HJ; schuver.henry@epa.govUS Environmental Protection AgencyVAPOR INTRUSION: RISKS AND BENEFITS OF AN ALTERNATIVEAPPROACHA growing body of evidence indicates that recalcitrant chemical vapor intrusion(VI) is highly variable (spatially heterogeneous and temporally episodic). VI risks cannotbe reliably estimated (e.g., +/- 25%) without samples of the indoor air, and continuousor numerous indoor air samples over a long duration (e.g., 1 yr) are needed,from each building. Given the number of samples needed and disruptive and timeconsumingnature of chemical indoor air sampling, including ‘background’ sourceremoval/assessment and sampling, and the high analytical costs, the reliable assessmentof current and future chemical VI risk is often impractical. The cost <strong>for</strong> reliablyassessing chemical vapor intrusion approximates the cost of implementing vaporcontrols. Also, a fraction of the buildings where costs were expended <strong>for</strong> a reliable assessmentof VI will find unacceptable exposures, and also incur costs <strong>for</strong> vapor controlsto be installed, operated, and monitored <strong>for</strong> an extended period of time. <strong>Final</strong>ly,it is globally recognized that the risks of VI are dominated by the risks from Radonwhich can be easily measured in indoor air and can be found to present >100x thegenerically-estimated source-based risk <strong>for</strong> chemical VI. An approach is proposedwhere buildings overlying chemical VI sources are assessed by assisting public volunteersto continuously measure the naturally-occurring general tracer of soilgas VI,Radon, in their indoor air <strong>for</strong> a period of one year (unless risks are excessive). Whereradon levels are found to present risks >100x the potential generic chemical VI risk,Responsible Parties will be recommended to offer building occupants a pre-emptive‘>100:1 Radon Zone 2+’ vapor control system, as a more beneficial alternative tocontinued attempts at VI assessment <strong>for</strong> chemicals alone. Continuous post-mitigationmonitoring of indoor Radon levels can ensure the effectiveness of VI controls and169
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M2-C.1 Abraham IM, Henry S; abraham
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Fukushima nuclear accident coverage
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W1-C.1 Goble R, Hattis D; rgoble@cl
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