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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 />

T4-D.4 Shatkin, JA; Vireo Advisors; jashatkin@gmail.com<br />

Life Cycle <strong>Risk</strong> Assessment of Nanocellulosic Materials<br />

As novel materials, cellulosic nanomaterials require proactive<br />

attention to ensure their environmental health and safety<br />

per<strong>for</strong>mance is addressed, and can be demonstrated. For novel<br />

nanoscale materials, limitations in the availability and reliability<br />

of data create challenges <strong>for</strong> measuring and assessing their<br />

potential risks to health and the environment in real world<br />

applications, particularly because of the dynamic nature of<br />

these materials in the environment. To date, studies of<br />

cellulosic nanomaterials have shown very little toxicity in the<br />

assays conducted. However, the emerging science on the<br />

behavior of nanoscale materials in the environment suggests a<br />

more thorough evaluation of safety to address occupational,<br />

consumer and environmental endpoints. In this talk, I will<br />

describe an analysis that broadly considered health and safety<br />

across the value chain <strong>for</strong> several anticipate product<br />

applications using cellulosic nanomaterials and outlines<br />

priorities <strong>for</strong> establishing safe management practices <strong>for</strong> the<br />

commercial use of nanocelluloses, including the status of<br />

standards. First, an assessment of the current state of<br />

knowledge and practice <strong>for</strong> managing EHS risks associated<br />

with nanocellulose throughout the product life cycle, during<br />

research and development, manufacturing, use in products, and<br />

environmental/end of life stages characterizes what is known,<br />

and what gaps exist regarding nanocellulose effects on health<br />

and environment, and what standards and guidelines already<br />

exist and what in<strong>for</strong>mation is needed to address the breadth of<br />

stakeholder concerns. The analysis in<strong>for</strong>ms a roadmap that<br />

prioritizes the development of protocols most critical to<br />

advance R&D, manufacturing, and market development.<br />

Finally, the current status of standards development regarding<br />

EHS <strong>for</strong> cellulosic nanomaterials is discussed.<br />

W2-C.3 Shereif, M*; Monshi , M; Alharbi , B; King Saud<br />

University; mshereif@ksu.edu.sa<br />

<strong>Analysis</strong> and Monitoring of Criteria Air Pollutants in<br />

Selected Areas of Riyadh City, Saudi Arabia<br />

The present investigation was aimed at characterizing levels of<br />

the criteria air pollutants nitrogen dioxide (NO2), sulfur dioxide<br />

(SO2), ozone (O3), carbon monoxide (CO), particulate matter<br />

(PM10), and lead (Pb) in Riyadh city in selected areas<br />

representing industrial (Al-Manakh), residential (Al-Malaz),<br />

recreational (Al-Rawda) and urban/road locations (Al-Bat’ha).<br />

The average concentration levels of NO2 in the industrial and<br />

urban/road areas, and SO2 in the industrial area, during the<br />

summer months of June through September of 2009 and 2010<br />

exceeded the Saudi Arabian Air Quality Standards (SAAAQS)<br />

and US National Ambient Air Quality Standards (NAAQS). The<br />

average CO concentrations in the four areas during 2009 were<br />

below the SAAQS and US NAAQS. However, the monthly<br />

averages of CO in the urban/road area exceeded the standards<br />

of both SAAAQS and the 8-h US NAAQS <strong>for</strong> CO (10,000 µg/m3)<br />

through the summer months of June, July, August, and<br />

September of 2010, which could be attributed to the emissions<br />

from excessive traffic and motor vehicles in this area. Ozone<br />

and lead concentrations at the four selected areas were below<br />

the SAAAQS and NAAQS. With the exception of the industrial<br />

area, the measured values of inhalable particulate matter<br />

(PM10) in the other areas were found to meet the SAAAQS<br />

M4-J.2 Sheriff, G; Maguire, K*; US Environmental Protection<br />

Agency; maguire.kelly@epa.gov<br />

Ranking Distributions of Environmental Outcomes Across<br />

Population Groups<br />

This paper examines the use of inequality indices <strong>for</strong> evaluating<br />

distributional impacts of alternative environmental policies<br />

across population groups defined by demographic variables<br />

such as race, ethnicity, or income. The rich literature devoted<br />

to the use of inequality indices <strong>for</strong> analyzing income<br />

distributions within and across countries provides a natural<br />

methodological toolbox <strong>for</strong> examining the distributional effects<br />

of environmental outcomes. We show that the most commonly<br />

used inequality indices, such as the Atkinson index have<br />

theoretical properties that make them inconvenient <strong>for</strong><br />

analyzing bads, like pollution, as opposed to goods like income.<br />

We develop a trans<strong>for</strong>mation of the Atkinson index that is<br />

suitable <strong>for</strong> analyzing bad outcomes. In addition, we show how<br />

the rarely used Kolm-Pollak index is particularly well-suited <strong>for</strong><br />

ranking distributions of adverse health and environmental<br />

outcomes. We provide an illustration of its potential use in the<br />

context of emissions standards affecting indoor air quality.<br />

M2-B.4 Shirley, SH*; Grant, RL; Honeycutt, M; Texas<br />

Commission on Environmental Quality;<br />

stephanie.shirley@tceq.texas.gov<br />

Integrating evidence: The importance of exposure and<br />

framing the question<br />

In 2009 the National Academies (NAS) emphasized the<br />

importance of problem <strong>for</strong>mulation and exposure assessment,<br />

among other best practices. Robust problem <strong>for</strong>mulation is<br />

helpful when incorporating biological relevance and chemical<br />

specific knowledge to meaningfully guide risk management<br />

options. As a first step, it is important to clarify the potential <strong>for</strong><br />

exposure to chemicals of concern (COC) in order to develop the<br />

most reasonable and useful risk assessments. Once a potential<br />

COC has been identified, it is crucial to characterize sources,<br />

pathways, receptors and temporal patterns of exposure. For<br />

evaluation of inhalation exposures, ambient air monitoring data<br />

becomes increasingly important, although uncertainty around<br />

how air monitoring data correspond to personal exposures and<br />

specific health endpoints often remains. Initial stages of an<br />

exposure assessment may identify discrepancies between<br />

concentrations of COCs described in epidemiological or<br />

toxicological studies and concentrations to which the general<br />

population may be exposed. For example, design values from<br />

centrally-located monitors may be used in observational<br />

epidemiology studies to identify statistical correlations between<br />

concentrations and health endpoints of interest. However, when<br />

exposures are characterized <strong>for</strong> populations of interest, it may<br />

become apparent that it is unlikely individuals were routinely<br />

exposed to these levels, and there<strong>for</strong>e it is improbable that a<br />

particular health effect is due to the concentrations described<br />

in the study (i.e., an association is shown, but not causation). In<br />

conclusion, regulatory agencies often utilize problem<br />

<strong>for</strong>mulation and exposure characterization along with weight of<br />

evidence criteria (such as the Hill criteria) to derive useful and<br />

robust risk assessments that can in<strong>for</strong>m risk management<br />

determinations. Exposure assessments and problem<br />

<strong>for</strong>mulation play major roles in these decisions.<br />

December 8-11, 2013 - Baltimore, MD

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