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

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

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

W3-A.3 Fiorino, D ; American University;<br />

dfiorino@american.edu<br />

Policy Learning, Chemicals, and <strong>Risk</strong>: Can Policy<br />

Innovation Keep Up with Technology Change?<br />

The context <strong>for</strong> safe management of chemicals has changed<br />

dramatically in the last four decades, since the passage of the<br />

Toxic Substances Control Act of 1976. For example, the<br />

development of nanotechnologies and synthetic biology have<br />

dramatically changed the regulatory contexts, as have other<br />

technology changes. The focus of this presentation is on the<br />

need <strong>for</strong> new models of regulation or complements to<br />

regulation <strong>for</strong> responding to these changes in technologies. The<br />

rapid changes in the regulatory context mean that the old<br />

model of regulation increasingly is poorly-suited to chemical<br />

risk management issues. This presentation suggests "policy<br />

innovations" that offer ways of managing this new chemicals<br />

challenges effectively. Among them are collaborative<br />

governance models, new regulatory frameworks, combinations<br />

of regulatory and voluntary programs, and third-party codes<br />

and certifications. Each of these are linked conceptually by<br />

their focus on flexibility, adaptive management, and policy<br />

learning. This presentation builds upon the presenter's previous<br />

work on oversight of nanotechnology issues and on the need <strong>for</strong><br />

new models of environmental regulation.<br />

T1-K.1 Fitzpatrick, JW*; Schoeny, R; Gallagher, K; Ohanian,<br />

EV; U.S Environmental Protection Agency;<br />

fitzpatrick.julie@epa.gov<br />

EPA’s Framework <strong>for</strong> Human Health <strong>Risk</strong> Assessment to<br />

In<strong>for</strong>m Decision Making<br />

The Framework <strong>for</strong> Human Health <strong>Risk</strong> Assessment to In<strong>for</strong>m<br />

Decision Making was developed by a technical panel of the<br />

EPA’s <strong>Risk</strong> Assessment Forum to be responsive to the decision<br />

making needs of the agency. Most importantly, it addresses the<br />

recommendations presented in NRC’s Science and Decisions<br />

(2009) relative to the design of risk assessments, including<br />

planning, scoping, and problem <strong>for</strong>mulation. This Framework<br />

will be instrumental in facilitating the implementation of<br />

existing and future EPA guidance <strong>for</strong> conducting human health<br />

risk assessments and in improving the utility of risk assessment<br />

in in<strong>for</strong>med risk management decision-making process. In<br />

accordance with longstanding agency policy, it also emphasizes<br />

the importance of scientific review and public, stakeholder and<br />

community involvement. This presentation will discuss details<br />

of the Framework and associated implementation plans by the<br />

agency.<br />

W2-J.1 Fitzpatrick, BG*; Angelis, E; Polidan, EJ; Tempest<br />

Technologies; fitzpatrick@tempest-tech.com<br />

Estimating The <strong>Risk</strong> of Rabies Entry into The State of<br />

Hawaii<br />

Considered one of the oldest documented infectious diseases,<br />

rabies remains a dangerous zoonotic disease threat today<br />

exhibiting a global geographic spread, a broad spectrum of<br />

mammalian reservoirs and vectors, and possesses the highest<br />

case fatality rate of any disease-causing agent. Transmitted via<br />

the saliva of an infected mammal, the rabies virus aggressively<br />

attacks the central nervous system and if left untreated is<br />

almost always fatal. Health care costs associated with the<br />

detection, prevention and control of rabies in the U.S. are<br />

estimated to exceed $300M annually. Distinguishing itself from<br />

all other U.S. states, Hawaii maintains a rabies-free status and<br />

has never reported an indigenous rabies case (animal or<br />

human). The state has upheld this status due to a quarantine<br />

law enacted in 1912 that requires a post-arrival confinement<br />

period of 120 days <strong>for</strong> imported dogs and cats. Beginning in<br />

1996, the state has conducted a series of risk assessments to<br />

identify new alternatives and modifications to the 120-day<br />

confinement law, with current law maintaining the 120-day<br />

quarantine and providing a very rigorous 5-day quarantine. In<br />

this paper, we examine some additional quarantines of interest<br />

to the state, including 30-, 60- and 90-day confinements. The<br />

procedure we employ uses scenario trees that structure the<br />

individual risk components involved in bringing an animal into<br />

Hawaii. Using data from a number of rabies epidemiology<br />

studies, we estimate parameters <strong>for</strong> a Bayesian model <strong>for</strong> risk<br />

probabilities, and we present a number of comparisons of<br />

rabies introduction likelihoods.<br />

M4-A.1 Fitzpatrick, S*; Carrington, C; US Food and Drug<br />

Administration; Clark.Carrington@fda.hhs.gov<br />

Dietary exposure to inorganic arsenic from food in<br />

general and rice in particular.<br />

Given its widely appreciated toxic properties, arsenic in food<br />

has always been an important topic in food safety. It has also<br />

long been known that the organic species of arsenic in seafood<br />

is far less toxic than inorganic arsenic in food or water.<br />

However, modern chemical analytical methodology has led to<br />

the realization that there are many different <strong>for</strong>ms of arsenic in<br />

food that a different toxicological properties. At the very least,<br />

there are three major categories of arsenic; inorganic arsenic<br />

species that are the most toxic, methylated arsenic species that<br />

are moderately toxic, and arsenic complexes that are practically<br />

nontoxic. While arsenic complexes are the predominant <strong>for</strong>m in<br />

fish, and inorganic arsenic is the predominant <strong>for</strong>m in drinking<br />

water, arsenic in most foods are comprised of a combination of<br />

inorganic and methylated species. Recent survey work<br />

conducted by the USFDA as well as other agencies indicates<br />

that while most foods have some inorganic arsenic at a<br />

relatively constant level, most of the variation in total arsenic<br />

concentrations is attributable to the presence of methylated<br />

arsenic species in highly varying amounts. In addition to<br />

considering the chemical <strong>for</strong>m of arsenic in food, dietary<br />

exposure assessments must be tailored to the temporal<br />

component of the toxicological evaluation and to the individuals<br />

or populations that consume a particular food. Thus, while per<br />

capita averages of lifetime intake may serve well as<br />

characterizations of public health <strong>for</strong> some health endpoints<br />

(e.g. lifetime cancer risk), risk estimates intended to in<strong>for</strong>m<br />

individual consumers are better served by the use of exposure<br />

estimates that are based on frequency of consumption.<br />

Although drinking water and smoking can also be dominant<br />

sources of exposure <strong>for</strong> some people, the major source of<br />

exposure to inorganic arsenic in the United States in the diet.<br />

In particular, rice can be the principle source of exposure in<br />

individuals and populations who are frequent consumers.<br />

December 8-11, 2013 - Baltimore, MD

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