However the concept of framing is more extensive than its common treatment inthe field of risk communication. In an ef<strong>for</strong>t to enrich the theoretical foundations offraming within the field of risk communication it is the goal of this panel presentationto critically examine and differentiate the multiple conceptual foundations andmanifestations of framing. This presentation also features lesser known strategies offrame alignment employed by social movement organizations that may be used prescriptivelyby risk communicators to further their goals in supplying the public withneeded in<strong>for</strong>mation to make in<strong>for</strong>med and independent decisions about risk. Framealignment strategies including frame bridging, frame amplification, frame extension,and frame trans<strong>for</strong>mation are discussed as potential loci <strong>for</strong> furthering risk communicationef<strong>for</strong>ts.W3-D.4 Cura J, Occhialini J, Vorhees D; jjcura@gmail.comWoods Hole Group, Alpha Analytical, The Science Collaborative, North ShoreDIFFERENTIAL BODY BURDENS OF VARIOUS COMPOUNDS INCO-OCCURRING BIVALVESResearch over the past ten years has demonstrated that bioaccumulation ofchemicals depends variously on the chemical properties, the species of organism,temporal differences, environmental conditions, and the exposure history of an organism.There is ample evidence that under field and laboratory conditions, contaminantconcentrations in tissue are often species-specific. For example, investigatorshave observed species differences in bioaccumulation of: Zinc between two filterfeeding co-located epibenthic organisms (mussels and barnacles); PCBs between adeposit feeding and a filter feeding bivalve in laboratory uptake experiments; Variousmetals and PCBs between mussels and oysters observed in long term regional monitoringdata in San Francisco Bay; Cadmium and copper among grass shrimp, mussels,and quahogs in controlled muti-element laboratory exposures; PAHs among variousbenthic species. These authors comment upon the implications of differential uptakeand accumulation when selecting organisms <strong>for</strong> toxicity testing, bioaccumulationtesting, or monitoring. These differences pose an uncertainty of generally unknownmagnitude in ecological and human health risk assessments which often depend upona small number of representative species. <strong>Risk</strong> assessors commonly select representativespecies to represent various trophic levels or vulnerabilities (ecological risk assessors)or ingested food types (human health risk assessors) with uncertain knowledgeregarding the range of differences in bioaccumulation that may occur even amongspecies of the same feeding type or taxonomic family. This work measures the rangeof tissue concentrations <strong>for</strong> various metals and organic chemicals among co-locatedbivalves that are both prey <strong>for</strong> local animal species and a regular food source <strong>for</strong> recreationalshell fishers. We discuss the implications <strong>for</strong> selecting representative speciesin ecological risk assessment and selection of recreationally caught species in humanhealth risk assessment.84W4-F.2 Dagonneau JM, Prpich G, Rocks SA, Pollard SJT; j.m.dagonneau@cranfield.ac.ukCranfield UniversityEVALUATION OF DIFFERENT DATA SOURCES USED TO POPULATEENVIRONMENTAL STRATEGIC RISK APPRAISAL FRAMEWORKDifferent data sources (expert opinion and published data) are often used toin<strong>for</strong>m decisions. This work seeks to evaluate and compare these two data sourcesused to populate an environmental strategic risk assessment tool (SRA). Previousexamples of SRA assessments have used non peer-reviewed sources (i.e. low reliabilityevidence). However, the use of peer-reviewed inputs provides a more defensiblebody of evidence <strong>for</strong> assessments. The developed SRA framework has beenused <strong>for</strong> assessing and comparing thirteen environmental threats, including flooding,coastal erosion, avian influenza and genetically modified organism. The SRA frameworkwas populated using a comprehensive literature search of published literature(i.e. reviewed journal and governmental report) or through data produced by identifiedexperts (n > 3). In<strong>for</strong>mation was categorised by theme and the quality of thein<strong>for</strong>mation was assessed using a standard process. The data were selected based ontheir high level of scientific quality, as well as the importance given to it within theliterature (i.e. frequency of citation of the in<strong>for</strong>mation in the publications). The SRAoutcomes from the literature were compared to the expert assessment and the relativeimportance of attributes was considered. The initial results show that the two in<strong>for</strong>mationsources provided slightly different risk assessment outcomes. The differencecan be partially explained by the exposure of experts to unpublished data and reports.Additional variation may be due to individual bias and gaps in evidence selection,which will be explored in more depth. Further investigation is required to support thistheory. 1. Prpich et al. (submitted 2011) Env. Sci.Tech.,P.38 Dalaijamts C, Wu KY; kuenyuhwu@ntu.edu.twInstitute of Occupational Medicine and Industrial Hygiene, College of Public Health, NationalTaiwan UniversityYOUNG KIDS POTENTIALLY AT GREATEST RISK DUE TO EXPO-SURES TO PERFLUORINATED COMPOUNDS THROUGH WATERCONSUMPTIONThe human health risks derived from the exposure to perflourinated compounds(PFOS, PFOA and PFDA) through water consumption were assessed <strong>for</strong>different age groups of general population in Taiwan using probabilistic approach.Based on available data on concentrations of PFCs in river water, exposure to PFOS,PFOA and PFDA via water consumption <strong>for</strong> different age groups were calculatedusing deterministic and probabilistic risk assessment methods. The oral non-cancerrisks from PFOS, PFOA and their combination, expressed as a Hazard Index (HI),was determined by comparing oral exposure dose (through water intake) with the oral
Reference Dose (RfD). The average exposure to PFOS via water consumption <strong>for</strong>adults ranged from 0.16 to 220.15 ng/kg-bw/day and <strong>for</strong> children 0.13 to 354.3 ng/kg-bw/day. The average exposure to PFOA <strong>for</strong> adults varied from 0.43 to 12.5 and<strong>for</strong> children 0.35 to 20.17 ng/kg-bw/day. The average exposure to PFDA <strong>for</strong> adultsranged from 0.43 to 2.36 ng/kg-bw/day and <strong>for</strong> children 0.35 to 3.79 ng/kg-bw/day.Probabilistic values of hazard indexes (HIs) due to exposure to the contaminantsand their combination from water consumption <strong>for</strong> all age groups only reside nearto Keya River exceeded the threshold value 2.4 to 4.8 times, corresponding mainly toPFOS with a percentage of 97%. In conclusions, children aged 1 to 3 years old andthe residents reside near to Keya River are at the highest risk of exposure to PFCs viawater consumption.M4-B.4 Dana GV; gvdana@gmail.comDana & Sharpe <strong>Risk</strong> AssociatesCOMPREHENSIVE ENVIRONMENTAL ASSESSMENT OF SYNTHET-IC BIOLOGY APPLICATIONSThe Woodrow Wilson Center’s Synthetic Biology Project is piloting a ComprehensiveEnvironmental Assessment (CEA) tool to test its ability to identify keyresearch areas needed to support ecological risk assessments of synthetic biology applications.This could be an organism containing novel genetic material or a productcontaining the organism. CEA combines a life-cycle analysis approach with a riskassessment framework and is one tool used by the US EPA to evaluate nanomaterialrisks and identify research directions; it is also applicable to synthetic biology applicationsat early stages of research and development. We report on the first pilot exerciseof CEA (held in July 2011), where engineers and ecologists used the CEA frameworkto consider how a cyanobacterium engineered <strong>for</strong> use as a biofuel feedstock may enter,travel through and impact the environment at different life-cycle stages. Participantsworked through the steps necessary <strong>for</strong> the cyanobacterium to enter the environment(e.g., discharges from open pond systems), what it might come in contact with (e.g.,animals, plants, microorganisms), what the potential impacts may be (e.g., gene flow,disruption of ecological processes), and what factors influence these actions (e.g., pH,species behavior, biosafety protocols). We report on the CEA’s ability to systematicallyidentify areas of research to support future ecological risk assessments, as well as opportunities<strong>for</strong> improving existing (or design new) biosafety measures.M4-G.5 David RM; raymond.david@basf.comBASF CorporationMANAGING RISKS OF CNTS IN A LARGE COMPANYManaging risk <strong>for</strong> substances <strong>for</strong> which the hazards are not completely understoodtypically default to the most protective measures. BASF has developed a matrixthat helps drive decisions on risk management by illustrating the need <strong>for</strong> eithergreater hazard in<strong>for</strong>mation or exposure reduction. The company has also developedshort-term screening tests <strong>for</strong> substances such as CNTs that can provide insight intothe long-term systemic and pulmonary effects. These tools as they have been appliedto products that contain CNTs will be presented.W4-I.2 DeAngelo BJ, Gilmore EA, Sarofim MC, Waldhoff ST, Martinich J, CardamoneK, Ohrel S, Ragnauth S, Birnbaum R; deangelo.ben@epa.govUS Environmental Protection AgencyQUANTIFYING AND COMMUNICATING BENEFITS AND RISKS OFGHG EMISSION SCENARIOSThe Environmental Protection Agency’s Climate Change Division (CCD) isdeveloping a methodology that will provide policy-relevant analysis about the USdomestic benefits and risks from different climate change scenarios. The methodologyconsists of four main components: 1) Establishing a consistent set of socio-economicand climate scenarios that can be applied across models of differing temporaland spatial resolution; 2) Coordinating and integrating general and partial equilibriumand sectoral models; 3) Describing and quantifying uncertainty; and, 4) Presentingand communicating a range of impacts and risks through multiple metrics and indicators.Here, we describe our progress and planned future work on developing andimplementing this methodology <strong>for</strong> a benefits analysis that articulates the benefits ofalternate GHG mitigation targets. We start with developing scenarios of some of thefundamental drivers of GHG emissions: population, economic growth and technologyassumptions. These scenarios are run through integrated assessment (IA) modelsthat produce estimates of future temperature and sea level rise. We identify approachesto produce consistent input data across modeled impacts, including downscalingtools and adapting more detailed inputs to our scenarios. Recognizing that no onemodel will provide answers to all questions and that multiple modeling approacheswill often provide different insights, we describe the coordination of several modelsthrough these scenarios and how we maintain consistency and avoid double counting.<strong>Final</strong>ly, we present the structure <strong>for</strong> communication of results <strong>for</strong> a range of impactsand risks <strong>for</strong> different audiences, including descriptions of uncertainty. We concludeby presenting a preliminary description of the benefits and risks of climate scenariosand the long-term vision <strong>for</strong> this framework.P.100 de Marcellis-Warin N, Peignier I; nathalie.demarcellis-warin@polymtl.caCirano - Ecole PolytechniqueRISK PERCEPTION, PUBLIC OPINION AND THE ACCEPTABILITYOF PUBLIC DECISIONS IN QUEBEC (CANADA)Public risk perception can disrupt the completion of major government projects.Projects such as regulating the shale gas industry, reopening a nuclear powerplant, or implementing a vaccination program may create public concern, thus resultingin resistance or even rejection. <strong>Risk</strong> perception depends on many factors, makingit important to identify those that are most likely to incite resistance and thus inhibit85
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WK9: Eliciting Judgments to Inform
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These freely available tools apply
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SECOND FLOOR Floor MapConvention Ce