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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 />

P.143 Schlosser, PM*; Isaacs, K; Sasso, AF; Gift, JS; U.S.<br />

Environmental Protection Agency; schlosser.paul@epa.gov<br />

A Probabilistic Model of U.S. Intra-Day Tap Water<br />

Exposure and Its Application in PBPK Modeling<br />

While the previously developed SHEDS model<br />

(http://www.epa.gov/heasd/research/sheds.html) provides<br />

probabilistic sampling <strong>for</strong> total daily water consumption, it does<br />

not provide in<strong>for</strong>mation on the intra-day distribution of that<br />

ingestion – the fraction of the total consumed in any hour of the<br />

day. For chemicals such as methanol or chloro<strong>for</strong>m which are<br />

rapidly absorbed, the peak blood concentration (Cmax) depends<br />

strongly on this distribution and is a determinant <strong>for</strong> key toxic<br />

effects. We analyzed 2003-2010 NHANES dietary recall data <strong>for</strong><br />

hourly ingestion, based on total moisture (g) in each food or<br />

beverage. (While the recall diaries allowed recording of events<br />

in 15-min intervals the data appeared biased to on-the-hour<br />

records, so consumption was summed into 1-h intervals.)<br />

Besides directly consumed tap water, a subset of NHANES<br />

foods and beverages assumed to be prepared with tap water<br />

was identified, and each was assigned an assumed fraction of<br />

total moisture attributed to tap water (e.g., 50% of canned soup<br />

prepared with water). Maximum-likelihood log-normal intake<br />

distributions were then fit <strong>for</strong> each 1-h interval. An assumed<br />

ingestion rate distribution (geometric mean, GM = 1 L/h) was<br />

applied allowing consumption to occur in less than an hour.<br />

18% of the diaries included “extended consumption” occasions<br />

(vs. “Breakfast,” “Lunch,” etc.) , assumed to be drinking from a<br />

large water bottle, coffee mug, etc., over longer periods; these<br />

observations were analyzed separately from the hourly<br />

distributions and simulated with appropriate probability. Since<br />

the length of the extended consumption events were not<br />

reported, a slower rate distribution was assumed (GM = 0.2<br />

L/h), with a minimum time of 1 h. With simulated distributions<br />

based on the NHANES diaries, most individuals appear to<br />

consume tap water less than 3 h each day. Use of these<br />

patterns as input to a PBPK model yields mean Cmax<br />

predictions 2x or more over an idealized pattern of 6 ingestion<br />

events per day.<br />

T1-G.5 Schweizer, PJ; University of Stuttgart;<br />

pia-johanna.schweizer@zirius.uni-stuttgart.de<br />

Requirements <strong>for</strong> climate change governance<br />

A global governance approach to tackle climate change seems<br />

now more out of reach than ever. One of the reasons <strong>for</strong> this<br />

deficiency is the sheer complexity of the issue. Climate change<br />

governance has to deal with uncertain science, the complexity<br />

of international negotiations, and ambiguous ethical issues,<br />

such as sustainability and international as well as<br />

intergenerational justice. Another reason is the politics of<br />

climate change governance. Climate change governance has<br />

sparked societal controversies in almost all countries of the<br />

world and has become a global issue. Consequently, the role of<br />

social trust and the role of civil society and the media have to<br />

be seen in the context of international relations and the<br />

management of common pool resources. In this multifaceted<br />

interplay of governance obstacles, it is a challenge if not an<br />

impossible task to propose a harmonized global governance<br />

framework of climate change. The intention of this presentation<br />

is to show ways in which climate change governance can be<br />

improved by a bottom-up rather than a top-down approach.<br />

Special attention will be paid to the question of how the “hard”<br />

facts of climate change science can be enhanced by “soft”<br />

parameters such as social acceptability and ethical as well as<br />

moral issues.<br />

T2-I.2 Scott, RP*; Cullen, AC; University of Washington;<br />

ryscott5@uw.edu<br />

Applying multi-criteria decision analysis and life cycle<br />

approaches to direct engineering research regarding the<br />

selection of CZTS back-contacts <strong>for</strong> thin film solar<br />

photovoltaics<br />

Cu2ZnSnS4 (CZTS) thin film photovoltaics are currently in the<br />

research phase as a potential method of producing electricity<br />

<strong>for</strong> $0.50 per watt at terawatt scales of production using<br />

abundant earth materials. Many uncertainties have arisen in<br />

terms of scalable manufacturing methods, device materials, and<br />

social and economic feasibility. One area of uncertainty in the<br />

quest to scale up production results from current use of<br />

molybdenum as a back-contact material, due to concerns about<br />

price volatility. However, research on potential substitution<br />

materials, including graphite, graphene, and molybdenum on<br />

steel, is still in the earliest stages. Since the broader goals of<br />

photovoltaics involve producing energy in a manner that<br />

protects both the environment and human health, developing<br />

the new back contact material without first considering the<br />

long-term price feasibility and impacts to health and<br />

environment could derail the future commercial viability of the<br />

thin film technology. This case provides an empirically based<br />

analysis of using decision tools to in<strong>for</strong>m research directions in<br />

emerging technology so as to avoid negative consequences.<br />

First proposed by Linkov et al (2007), a combined approach of<br />

Multi Criteria Decision <strong>Analysis</strong>, <strong>Risk</strong> Assessment, and Life<br />

Cycle Assessment allows <strong>for</strong> the application of available risk<br />

assessment and life cycle data within a larger decision<br />

framework. This work assesses the limitations of MCDA-RA-LCA<br />

while providing valuable decision analytic in<strong>for</strong>mation to CZTS<br />

engineers. For the case of CZTS back contact selection, MCDA<br />

is used to assess the various material options with the goal of<br />

maximizing future device utility through optimizing across cost,<br />

environment, and health metrics. Application of utility theory<br />

and the use of Monte-Carlo simulation to partition significant<br />

sources of uncertainty allows the selection of materials to<br />

incorporate social responsibility and risk minimization<br />

alongside future technical promise.<br />

T2-F.1 Sellke, P*; Amlot, R; Rogers, B; Pearce, J; Rubin, J;<br />

Mowbray, F; Dialogik non-profit institute;<br />

sellke@dialogik-expert.de<br />

Public In<strong>for</strong>mation Responses After Terrorist Events<br />

The threat western societies face through terrorist attacks<br />

became much more apparent than ever be<strong>for</strong>e through the<br />

attacks of 9/11 (New York and Washington 2001), 11-M<br />

(Madrid, March 11, 2004) and 7/7 (London, July 7, 2005). The<br />

new quality of those attacks comprised the deliberate attempt<br />

to cause as many fatalities as possible and to disrupt economic<br />

and social life. Not least the ruthlessness and sophistication of<br />

the attacks carried out made the use of radiological or<br />

biological substances <strong>for</strong> attacks conceivable, if not likely. How<br />

the public reacts to biological or radiological terrorism will help<br />

to determine how extensive the attack's medical, economic and<br />

social impacts are. Yet our understanding of what the public is<br />

likely to do in case of a radiological and/or biological attack is<br />

limited. Will they spontaneously evacuate affected areas? Are<br />

they willing to attend mass treatment centers? Will unaffected<br />

people demand treatment and monitoring? Will people avoid<br />

affected areas even after clean-up operations have been<br />

completed? As yet, we do not know. While emergency plans and<br />

simulations dealing with these scenarios assume a relatively<br />

compliant public with easily understood behaviors, evidence<br />

from previous incidents suggests that the reality may be<br />

different. As such, a first step to preparing better plans to<br />

protect the public is to identify actions they intend to take in<br />

the event of one of these scenarios occurring, and to assess<br />

how prevalent such intentions are in society. In this<br />

presentation results from a two-year reseach project will be<br />

presented, adressing the questions outlined above and<br />

comparing them between Germany and the United Kingdom.<br />

The presentation will emphasize the question of whether<br />

behavioral intentions of the public can be influenced by tailored<br />

emergency communication and the satisfaction of public’s<br />

in<strong>for</strong>mation needs and what possible differences in the<br />

response to terrorist attacks exist between Germany and the<br />

United Kingdom.<br />

December 8-11, 2013 - Baltimore, MD

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