health consequences of an intentional food contamination scenario. Knowledgefrom published literature and subject matter expertise on agent stability, food processingtechnologies, and supply chain vulnerabilities are applied to evaluate the impact ofchemical, biological, and radiological threats on public health. Foodborne contaminationscenarios are mathematically simulated from the point of contamination (e.g.,a storage silo), through food processing (e.g., pasteurization), packaging or bottling,distribution to retail or quick service restaurant (QSR) outlets, to points of sales ofcontaminated product, consumer and QSR preparation methods (e.g., cooking), andconsumption patterns. A recall or public announcement component considers thetime to the appearance of illnesses or injuries, and applies a rate of in<strong>for</strong>mation diffusionto calculate the amount of contaminated product removed from retail outletsand consumer homes. Contaminant-specific data, such as that <strong>for</strong> dose-response, hydrolysisrate, temperature-dependent decay, and time to symptom onset, are utilizedto provide estimates of potential consequences in terms of deaths and injuries ofvarying severity. These modeling capabilities can be applied to prioritize investmentsin mitigating a food contamination event and have other potential applications inestablishing risk-based contaminant sampling programs <strong>for</strong> unintentional contaminationevents involving foods such as ground beef or lettuce.T2-C.3 Lynch MT, Hattis D, Greco S, Belova A; megkeaney@yahoo.comAbt Associates Inc.ESTIMATING NONCANCER HUMAN HEALTH RISKS ASSOCIATEDWITH ACROLEIN INHALATION USING THE STRAW MAN MODELWe estimated human health risks of nasal toxicity associated with acrolein inhalationusing the Hattis et al. 2002 “Straw Man” noncancer risk assessment approach.The Straw Man is a probabilistic risk assessment model that assigns distributions inplace of traditional point estimates <strong>for</strong> the point of departure and uncertainty factors.Specific uncertainty factor distributions are chosen from a preassembled database dependingon the toxicological in<strong>for</strong>mation available <strong>for</strong> a specific compound. For thefirst time, we evaluate how the Straw Man model might be applied to a highly reactiveair toxic such as acrolein. The model outputs are (1) a distribution of concentrationscorresponding to a specified risk level, and (2) uncertainty distributions of expectedrisks of harm at a specified level of severity as a function of chronic air concentrations.First we will present an overview of the available dose-response data <strong>for</strong> acroleinand a summary of the current approaches to regulating acrolein in the U.S. Wewill then describe our choice of input parameters <strong>for</strong> the Straw Man analysis, and willreport the results of the Straw Man evaluation of acrolein implementing our newlycreated Regional Gas Distribution Ratio (RGDR) distribution, necessary <strong>for</strong> this classof air toxics. Our analysis is intended to showcase how the Straw Man method mightbe employed to calculate noncancer risks <strong>for</strong> acrolein and other highly reactive air toxics.The results of this analysis should not be taken as final risk estimates, because the138RGDR distribution, as well as all the distributions that in<strong>for</strong>m the Straw Man analysis,could be expanded to include additional datasets and/or more sophisticated statisticaltechniques. These next steps will also be discussed.T2-D.4 MacDonell MM, Rypinski AD; macdonell@anl.govArgonne National LabRISK ASSESSMENT STRATEGIES FOR ADAPTATION AND SEA-LEV-EL RISEClimate change adaptation planning requires that policymakers decide onwhether to take action or follow a wait-and-see approach when confronted with arange of uncertain but significant local or regional climate impacts, such as sea-levelrise, changes in the frequency and intensity of precipitation and extreme weatherevents, availability of water resources, and increased temperatures. The uncertainpath of future climate change is compounded by uncertainties in making climatepredictions at regional scales. Despite these uncertainties, many decisions with longtermconsequences about land use, ecosystem protection, and long-lived infrastructuremust be made today. The Council on Environmental Quality explicitly counselsthe use of <strong>for</strong>mal risk assessment methods in adaptation planning. But what methodsought to be used? This paper surveys risk assessment methods described inthe evolving adaptation literature, describes how these methods have been applied inrecent U.S. practice, and considers the applicability of other approaches used by therisk assessment community.P.11 MacKenzie CA, Barker K; cmackenzie@ou.eduUniversity of OklahomaQUANTIFYING THE INTERDEPENDENT EFFECTS OF SUPPLYCHAIN DISRUPTIONS AND MITIGATION STRATEGIESSupply chain risk management has been a popular topic with both practitionersand researchers, and different models can help companies prepare and react to adisruption in their supply chain. Potential industry strategies <strong>for</strong> coping with thesedisruptions include maintaining inventory, buying from multiple suppliers, and substitutingone input <strong>for</strong> another. However, less attention has been given to exploring thebroader economic consequences that these strategies have on a region following a disruptiveevent. We deploy a risk-based interdependency model to analyze the broaderimpacts of supply chain disruptions. We find the equilibrium points as determined bythe disruption and a company’s optimal strategy and explore the dynamics of movingbetween equilibria. A risk-based input-output model quantifies the impacts of thisdynamic production model. The model is applied to a data-driven multiregional casestudy.
M2-D.4 MacKenzie CA, Barker K; cmackenzie@ou.eduUniversity of OklahomaOPTIMAL RESOURCE ALLOCATION FOR RECOVERY FROM MUL-TIMODAL TRANSPORTATION DISRUPTIONSThe American economy relies on the ability of businesses to move commoditiesand products efficiently around the nation. Companies can choose among highway,rail, waterway, air, or a combination of these modes to deliver products to theircustomers, and each of these modes has distinct advantages and disadvantages comparedto the other modes. However, if a disruptive event disables part of this network,companies may be <strong>for</strong>ced to scramble to find alternate transportation modesor routes to continue to deliver their commodities efficiently. These disruptions canlead to increased transportation costs and late deliveries. We develop a decision modelto determine the optimal resource allocation <strong>for</strong> a multimodal transportation networkrecovering from a disruption. Resources are distributed according to where themoney can provide the greatest help in easing transportation difficulties in terms ofcosts and transportation delays <strong>for</strong> companies. Necessary and sufficient conditionsare derived <strong>for</strong> both static and dynamic decision problems.M2-B.1 Maeda Y, Seo K; tymaeda1@ipc.shizuoka.ac.jpShizuoka University, Aoyama Gakuin UniversityDELPHI ANALYSIS OF ISSUES AFTER THE 2011 PACIFIC COAST OFTOHOKU EARTHQUAKEThe Pacific Coast of Tohoku earthquake on March 11, 2011 has catastrophicimpacts on Japan. Japan is currently on the way to recovery. However, as the damageon the country as well as society is so serious, Japanese society is urged to changesome systems including hazard management, energy policy, in<strong>for</strong>mation systems andcity planning. These changes are accompanied with social group realignments, thusnecessarily followed by various risks. In addition to these societal risks, Japan shouldbe prepared <strong>for</strong> the coming disaster risks in near future. In 2004, Indonesia experiencedmagnitude 9.1 earthquake, named “2004 Indian Ocean earthquake”. After thatevent, Indonesian society has suffered magnitude 7-8 class earthquakes every year.This could be the case with Japan because of plate movement mechanism: i.e., Japanmay have to brace <strong>for</strong> magnitude 8 class earthquakes again and again in the next severalyears. To cope with these risk issues, SRA-Japan established the special researchcommittee <strong>for</strong> the 2011 Pacific Coast of Tohoku earthquake. The aim of the committeeis, from viewpoints of risk analysts, to create and relate messages about riskissues in one year, in five years, in ten years and in thirty years from the earthquake.To do this, the committee garners SRA-Japan member’s opinions about possible risksin Japan by using Delphi method. In SRA-Japan, there are over 600 members in interdisciplinaryfields from various backgrounds, thus the messages are expected to behelpful <strong>for</strong> Japanese society to lower its risks and to optimize the resource allocation.The research is now underway. An interim report will be presented.P.36 Managaki S, Kotani K, Hondo H, Kobayashi T, Miyake A, Masunaga S;managaki@ynu.ac.jpYokohama National UniversitySUBSTANCE FLOW-BASED EXPOSURE ASSESSMENT FOR HBCDFROM A LIFE-CYCLE PERSPECTIVE IN JAPANThe present study aims to develop a risk reduction policy <strong>for</strong> chemicals, consideringa product life-cycle. Environmental emissions from end-products containingbrominated flame retardants (i.e., HBCD) <strong>for</strong> the period 1986-2030, which is currentlyundergoing a risk assessment has been estimated by substance flow analysis(SFA). Through the investigation of quantitative HBCD life cycle, estimated HBCDstock in&#12288;the use phase shows a continuous increase, indicating thatemissions from the materials containing HBCD will be potentially long-term sourcesof pollutants leaching to the environment. In Japan, 571 kg/year and 41 kg/year ofHBCD was calculated to emit to the atmospheric and aquatic environment in 2000,respectively. This corresponds to 0.03 % of the consumed HBCD quantity in Japan.These environmental emissions of HBCD were increasing rapidly until 2011. Usinga multimedia fate model, where the estimated HBCD emission were used <strong>for</strong> theinput parameter and a simple pharmacokinetic model, intakes of adults through lifecycle of HBCD were converted to predicted body burdens and compared with theresults observed from Japanese human milk. Predictions compared well with thoseobserved <strong>for</strong> HBCDs <strong>for</strong> the period 1986-2005. SFA focuses on the emission fromproduction to waste process (i.e., life cycle) of target chemicals and thus, this estimationmay cover whole exposure pathways. The present study gives an insight to obtainbasic in<strong>for</strong>mation <strong>for</strong> long term measures toward strategic chemical managementconsidering their life cycle.M4-G.3 Marenberg AA, Burch DF, Shatkin JA, Davis JM; amarenberg@icfi.comICF International, CLF Ventures, US EPASTATE OF THE SCIENCE AND INFORMATION GAPS REGARDINGA COMPREHENSIVE ENVIRONMENTAL ASSESSMENT OF AN AP-PLICATION OF A CARBON-BASED NANOMATERIALPart of EPA’s strategy <strong>for</strong> prioritizing research to in<strong>for</strong>m future assessments ofnanomaterials includes the development of case studies that describe what is knownand what needs to be known to assess the ecological and health implications of specificnanomaterial applications and uses. This presentation describes the scoping processused to select a candidate carbon-based nanomaterial application <strong>for</strong> the next ina series of these EPA case studies and summarizes preliminary findings of the casestudy. The process <strong>for</strong> selecting appropriate nanomaterial applications <strong>for</strong> case studydevelopment considered multiple criteria, including adequacy of available in<strong>for</strong>mation,relevance to EPA programs, evidence of general population and occupationalexposure potential, applicability to ecological and human health risk assessment, and139
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SECOND FLOOR Floor MapConvention Ce