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