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Abstracts (PDF file, 1.8MB) - Society for Risk Analysis

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SRA 2013 Annual Meeting <strong>Abstracts</strong><br />

M4-C.2 Pate-Cornell, ME; Stan<strong>for</strong>d University;<br />

mep@stan<strong>for</strong>d.edu<br />

On black swans and perfect storms<br />

I will discuss the origins of the terms "black swans" and<br />

"perfect storms", their relations to different types of<br />

uncertainties, and the way they have sometimes been used as<br />

excuses <strong>for</strong> bad decisions. I will then address some risk<br />

management strategies to deal with different classes of<br />

situations. These include monitoring (e.g. of signals of<br />

epidemics <strong>for</strong> the CDC) and gathering of in<strong>for</strong>mation about<br />

marginal and conditional probabilities (e.g. weather data) of<br />

events that in rare combinations, can have disastrous effects. In<br />

all cases, the use of systems analysis and probabilities (mostly<br />

Bayesian) is key to decision support.<br />

W4-A.4 Patel, M*; Owens, EO; Kirrane, E; Ross, M; National<br />

Center <strong>for</strong> Environmental Assessment, U.S. Environmental<br />

Protection Agency; patel.molini@epa.gov<br />

Transparently Implementing the Causal Framework in<br />

the EPA NAAQS Review<br />

For Integrated Science Assessments (ISAs), EPA assesses the<br />

body of relevant literature to draw conclusions on the causal<br />

relationships between relevant air pollutant exposures and<br />

health or environmental effects related to the review of the<br />

National Ambient Air Quality Standards (NAAQS). Causal<br />

determinations are made by applying EPA’s causal framework<br />

that describes consideration of the consistency of evidence<br />

from various scientific disciplines (e.g., epidemiologic,<br />

controlled human exposure, animal toxicological studies), as<br />

well as evidence <strong>for</strong> plausible modes of action <strong>for</strong> each of five<br />

causal determinations. A challenge in the ISAs is<br />

communicating the consistent application of the framework<br />

across the various evaluated outcomes <strong>for</strong> which the evidence<br />

may vary in quantity, consistency, and the relative<br />

contributions from the various scientific disciplines. In order to<br />

better communicate how EPA considers the supporting<br />

evidence, uncertainties, and coherence across disciplines in<br />

drawing causal determinations, EPA developed summary of<br />

evidence tables <strong>for</strong> use in the ISAs. With these tables, EPA<br />

concisely summarizes the available evidence across scientific<br />

disciplines and demonstrates how this evidence relates to the<br />

attributes described in the causal framework. To describe the<br />

nature of the available evidence, these tables summarize the<br />

types of study designs available, potential biases, the control<br />

<strong>for</strong> potential confounding factors, consistency of evidence, the<br />

relative contributions from various scientific disciplines, and<br />

the exposure or biomarker levels associated with outcomes.<br />

This session will describe how the causal framework used in the<br />

NAAQS review is implemented and transparently applied using<br />

the ISA <strong>for</strong> lead as an example. Disclaimer: The views<br />

expressed are those of the authors and do not necessarily<br />

reflect the views or policies of the US EPA.<br />

W2-F.4 Patterson, J*; Nance, P; Dourson, M; Toxicology<br />

Excellence <strong>for</strong> <strong>Risk</strong> Assessment; patterson@tera.org<br />

Best Practices <strong>for</strong> Independent Peer Reviews<br />

High quality peer review is very valuable to ensure that the<br />

science used to support regulatory and public health decisions<br />

is sound. Peer reviewers evaluate the adequacy of the scientific<br />

data to support the conclusions. They consider whether key<br />

data were identified and interpreted correctly, appropriate<br />

methodologies were used, analyses of data are appropriate,<br />

uncertainties have been clearly identified along with the<br />

attending implications of those uncertainties; and in<strong>for</strong>mation<br />

and conclusions are clearly communicated. Increasing attention<br />

has been given to selection of peer reviewers and determining<br />

whether particular individuals may have conflicts of interest.<br />

Ensuring the independence of the experts is an essential<br />

principle <strong>for</strong> high quality peer review. Other key principles and<br />

practices are also important: using a robust scientific approach<br />

to focus the experts on the key scientific issues and questions;<br />

selection of experts with appropriate discipline knowledge and<br />

contextual experience; and transparency in the process and<br />

communication of results to be most beneficial to in<strong>for</strong>ming<br />

public health decisions. Additional practices and activities have<br />

been suggested, such as instituting an independent evaluation<br />

of whether document authors addressed the recommendations<br />

of the peer reviewers in finalizing their documents. As peer<br />

review becomes more widely used by government agencies and<br />

others, the perspectives and thoughts of the experts themselves<br />

must also be considered.<br />

P.33 Patterson, J*; Becker, R; Borghoff, S; Casey, W; Dourson,<br />

M; Fowle, J; Hartung, T; Holsapple, M; Jones, B; Juberg, D,<br />

Kroner O, Lamb J, Marty S, Mihaich E, Rinckel L, Van Der<br />

Kraak G, Wade M, Willett C; 1,5,11 Toxicology Excellence <strong>for</strong><br />

<strong>Risk</strong> Assessment (TERA); 2 American Chemistry Council; 3, 9,<br />

15 Integrated Laboratory Systems (ILS); 4 National Institute of<br />

Environmental Health Sciences; 6 independent consultant; 7<br />

Center <strong>for</strong> Alternatives to Animal Testing, Johns Hopkins<br />

University; 8 Battelle;10 Dow AgroSciences; 12 Exponent, Inc.;<br />

13 The Dow Chemical Company; 14 ER2;16 University of<br />

Guelph; 17 Health Canada; 18 Humane <strong>Society</strong> of the United<br />

States; patterson@tera.org<br />

Workshop on lessons learned, challenges, and<br />

opportunities: The U.S. Endocrine Disruptor Screening<br />

Program<br />

Fifty-two chemicals were recently screened using 11 Endocrine Disruptor<br />

Screening Program (EDSP) Tier 1 assays and the data submitted to the EPA<br />

<strong>for</strong> review. Over 240 scientists participated in a workshop on the EDSP in<br />

April 2013 to share scientific learnings and experiences with the EDSP and<br />

identify opportunities to in<strong>for</strong>m ongoing and future ef<strong>for</strong>ts to evaluate the<br />

endocrine disruption potential of chemicals. The first session focused on the<br />

conduct and per<strong>for</strong>mance of the 11 Tier 1 assays. Speakers and workshop<br />

participants highlighted challenges in conducting the assays and solutions<br />

developed by the laboratories, as well as issues relevant to data<br />

interpretation. The second session focused on how to apply relevant<br />

in<strong>for</strong>mation from the current Tier 1 battery to identify potential modes of<br />

action and the value of a weight of evidence (WoE) assessment <strong>for</strong><br />

evaluating potential interactions with endocrine pathways. Presentations<br />

and discussions explored the development of critical systematic evaluation<br />

of existing data prior to implementation of Tier 2 testing, and application of<br />

alternative data to replace Tier 1 assays. The third session provided<br />

perspectives on the future of endocrine screening and the promise of in vitro<br />

high-throughput analyses, toxicity pathways, and prediction models. A<br />

number of common themes and suggestions emerged from the extensive<br />

discussions, including that a critical review and update of current Tier 1<br />

testing guidelines is needed, the use of biomonitoring data <strong>for</strong><br />

exposure-based prioritization, reducing the number of animals used in<br />

testing, and use of a robust WoE approach to align available Tier 1 data with<br />

potency and exposure in<strong>for</strong>mation to better in<strong>for</strong>m decisions on Tier 2<br />

testing.<br />

December 8-11, 2013 - Baltimore, MD

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