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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 />

M3-J.3 Gilmore, EA*; Hendrickson, P; University of Maryland;<br />

gilmore@umd.edu<br />

Evaluating Proliferation Resistance of Small Modular<br />

Nuclear Reactors<br />

Nuclear energy can make an important contribution to reducing<br />

greenhouse gas emissions. Small modular reactors (SMRs),<br />

defined as units with a generating capacity of less than 300 MW<br />

that are delivered to the site fully assembled, may represent a<br />

viable alternative to large reactors since they require smaller<br />

initial capitalization, better match existing demand <strong>for</strong> energy<br />

and capacity requirements, may be easier to site and may<br />

engender less public opposition. Thus, this configuration opens<br />

new opportunities <strong>for</strong> nuclear energy use, especially in<br />

developing countries. However, there has been little ef<strong>for</strong>t to<br />

evaluate SMR designs, manufacturing arrangements and fuel<br />

cycle practices on the risks <strong>for</strong> proliferation. Here, we evaluate<br />

the designs and fuel cycle arrangements, manufacturing and<br />

delivery systems, and policy regimes are most likely to result in<br />

proliferation resistant SMRs. We start by reviewing the<br />

characteristics of existing SMRs. We compare this to a notional<br />

SMR with sealed fuel compartment that would not give users<br />

access to nuclear materials. In addition, these SMRs would be<br />

produced in a “hub and spoke” arrangement with a small<br />

number of manufacturing facilities worldwide and end of life<br />

recovery of the modules <strong>for</strong> recycling and disposal. We then<br />

apply and adapt a number of existing methods used to evaluate<br />

the proliferation resistance <strong>for</strong> conventional light water<br />

reactors to assess the SMRs. Adapting these models, we find<br />

that the technological features of SMR systems can reduce the<br />

proliferation risks compared to light water reactors, although<br />

strong international regimes are required to support this<br />

outcome.<br />

P.10 Gilmore, J*; Martinez, C; Pagliarulo, M; Ontario Ministry<br />

of Environment; James.Gilmore@Ontario.ca<br />

Interim action values <strong>for</strong> management of contaminants in<br />

soils <strong>for</strong> protection of human health risks<br />

The Ontario Ministry of the Environment has developed interim<br />

action value (IAVs) <strong>for</strong> several contaminants as part of its Soil<br />

Assessment Protocol, which in<strong>for</strong>ms investigation, analysis and<br />

risk reduction measures (RRMs) to address contaminated soil.<br />

An IAV represents the upper limit beyond which interim risk<br />

reduction measures should be considered. As the name implies,<br />

IAVs are intended to in<strong>for</strong>m short-term risk management and<br />

mitigation decisions, which may need to be reconsidered over<br />

time as more in<strong>for</strong>mation becomes available on the exposure<br />

conditions or on the science underpinning the IAV. IAVs can be<br />

developed <strong>for</strong> various media including soil, groundwater, soil<br />

vapour and indoor air, as needed. Interim action values are<br />

generally developed from generic soil standards (GSS) by: a)<br />

Reviewing the relevant human health component values<br />

(HHCVs) underpinning the GSS (e.g., direct contact <strong>for</strong><br />

incidental ingestion and dermal contact); b) Adjusting the<br />

target risk levels <strong>for</strong> non-cancer and cancer effects to the<br />

selected range <strong>for</strong> risk management; c) Selecting the more<br />

stringent effect and ensure that risks posed by other effects<br />

(e.g., acute effects) are not exceeded. The IAV may be also<br />

refined by reviewing available data from biomonitoring or other<br />

studies, if available. Using arsenic as an example, an IAV of 200<br />

µg/g was developed. This value is within the range of soil<br />

concentrations studied that showed no significant elevated<br />

arsenic exposure, reflects a 2 in 10,000 (or 1 in 5,000)<br />

incremental cancer risk and is within the range of risks posed<br />

from total inorganic arsenic exposure in the general Canadian<br />

population (1 in 1,000 to 1 in 10,000), and is equivalent to<br />

approximately ten times an upper estimate of background soil<br />

concentrations of arsenic at 18 µg/g.<br />

P.36 Glynn, ME*; Pierce, JS; Williams, B; Johns, LE; Adhikari,<br />

R; Finley, BL; Cardno Chem<strong>Risk</strong>; Meghan.Glynn@cardno.com<br />

Residential and occupational exposure to wood treating<br />

operations and bladder cancer: A meta-analysis<br />

The wood treating industry has operated <strong>for</strong> over 100 years in<br />

the United States, with sites commonly operating <strong>for</strong> more than<br />

decades. Over time, concerns have been raised regarding the<br />

potential chronic health effects associated with wood<br />

treating-related exposures. In at least one case it has been<br />

suggested that there might be an association between risk of<br />

bladder cancer and exposure to chemicals associated with<br />

historical wood treating operations (e.g., creosote, coal tar and<br />

associated polycyclic aromatic hydrocarbons [PAHs], and<br />

pentachlorophenol [PCP]). A literature search was conducted to<br />

identify all published and unpublished analyses that reported<br />

risk estimates <strong>for</strong> bladder cancer in (1) residents of<br />

communities surrounding wood treating operations, (2) wood<br />

treating workers, and (3) non-wood treating workers who were<br />

exposed to chemicals associated with wood treating operations<br />

(e.g., creosote/coal tar/PAHs and PCP). A total of 18 studies,<br />

including independent cohort, record-linkage, and case-control<br />

studies, were included in the meta-analysis. Using a random<br />

effects model, meta-relative risks (meta-RRs) were calculated<br />

<strong>for</strong> each exposure group. The summary relative risk (meta-RR)<br />

<strong>for</strong> bladder cancer overall was 1.04 (95% confidence interval<br />

[CI]: 0.93, 1.17). No statistically significant meta-RRs were<br />

observed among residents of communities in the vicinity of<br />

wood treating operations (meta-RR=0.99; 95% CI: 0.73, 1.34);<br />

wood treating workers (meta-RR=1.11; 95% CI: 0.53, 2.04);<br />

workers exposed to coal tar, creosote, and associated PAHs<br />

(meta-RR=1.04; 95% CI: 0.86, 1.27); and workers exposed to<br />

PCP (meta-RR=1.00; 95% CI: 0.82, 1.23). In conclusion, the<br />

studies reviewed provided no evidence of an association<br />

between residential and occupational exposure to wood<br />

treating operations and an increased risk of bladder cancer.<br />

M4-D.2 Gombas, D; United Fresh; dgombas@unitedfresh.org<br />

Produce Industry Perspective: Predicting the<br />

Unpredictable<br />

Protecting consumers is the top priority of the fresh produce<br />

industry. But, without a “kill step”, produce food safety must<br />

rely on prevention of contamination at every point in the supply<br />

chain, from field to <strong>for</strong>k. Good Agricultural Practices(GAPs)<br />

have been successfully used to prevent large scale<br />

contamination events in the field. Yet recalls and outbreaks<br />

linked to fresh produce demonstrate that GAPs cannot be the<br />

entire answer. So how does the industry proceed? This session<br />

will explore the industry’s current path, how speculations can<br />

divert food safety resources from more effective practices, and<br />

how opportunities have been missed in developing better<br />

approaches to predict, prevent and detect sporadic<br />

contamination events.<br />

December 8-11, 2013 - Baltimore, MD

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