27.07.2013 Views

The Toxicologist - Society of Toxicology

The Toxicologist - Society of Toxicology

The Toxicologist - Society of Toxicology

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

for integrating epidemiology and animal results from the published literature have<br />

become increasingly important to regulatory agencies as evidenced by recently proposed<br />

EPA draft guidance and science advisory panel reviews in 2010 on this subject.<br />

Of special importance are evaluations <strong>of</strong> developmental neurobehavioral data<br />

for children’s health RA. Chlorpyrifos (CPF) is used as a case study to illustrate a<br />

framework for systematic and transparent review <strong>of</strong> published neurobehavioral literature<br />

for human health RA. Steps include (1)identify human pesticide uses and<br />

exposure patterns so that relevance <strong>of</strong> duration,route and dose levels in animal studies<br />

can be determined;(2)evaluate exposure measures used in human studies relative<br />

to what is understood about mode <strong>of</strong> action, metabolism and pharmacokinetics;(3)define<br />

criteria for inclusion and utility <strong>of</strong> studies for RA;(4)tabulate both<br />

presence and absence <strong>of</strong> all findings, direction <strong>of</strong> change, key methods and exposure<br />

period from human and animal studies;(5)evaluate historical control data to assess<br />

reliability <strong>of</strong> methods and variability <strong>of</strong> control behavior especially when there is<br />

limited dose response data from one lab;(6)evaluate patterns <strong>of</strong> associations (or lack<br />

<strong>of</strong> associations) within and across different studies with respect to the following<br />

guideposts: consistency, dose-response, strength <strong>of</strong> association, temporality (taking<br />

into consideration frequency, intensity, timing and duration <strong>of</strong> exposure), as well as<br />

hypothesized modes <strong>of</strong> action. Based on this approach, we conclude that quantitative<br />

RA based on cholinesterase inhibition are adequately protective <strong>of</strong> developmental<br />

neurobehavioral effects reported in the literature for CPF.<br />

863 DEVELOPMENT OF SURFACE CLEAN UP LEVELS FOR<br />

ACUTE AND CHRONIC EXPOSURE TO TARGET<br />

CHEMICALS.<br />

J. M. Martinez 1 , S. A. Hines 2 and D. J. Chappie 2 . 1 Office <strong>of</strong> Emergency<br />

Management, U.S. EPA, Cincinnati, OH and 2 Battelle, Cincinnati, OH.<br />

Solid surface contamination, such as that resulting from indoor pesticide applications<br />

or residual contamination from releases <strong>of</strong> chemical weapons, is increasing<br />

recognized as a knowledge gap in the development <strong>of</strong> suitable decontamination<br />

strategies and standards to ensure appropriate clean-up. This is especially important<br />

when planning for reoccupation <strong>of</strong> a public facility contaminated with toxic agents<br />

that may persist in the environment for various lengths <strong>of</strong> time. Contaminated surfaces<br />

pose a challenge for assessment due to the lack <strong>of</strong> generally accepted dermal<br />

exposure methodologies as well as appropriate techniques to integrate surface wipe<br />

measurements with exposure point concentrations. Currently, there are no formal<br />

risk-based screening levels for chemical weapons or pesticides to determine if results<br />

from surface samples or wipe samples confirm the solid surfaces were successfully<br />

decontaminated or need to be re-evaluated before reoccupation. To develop surface<br />

clean up screening levels, we performed a careful evaluation <strong>of</strong> all surface contamination<br />

assessment methodologies proposed for the World Trade Center and home<br />

methamphetamine lab clean ups. Based on careful analysis <strong>of</strong> these methods and<br />

the chemical properties <strong>of</strong> toxicants, we present putative surface wipe screening levels<br />

for both chronic and acute exposures for a list <strong>of</strong> target chemicals.<br />

864 USING PBPK/PD MODELS TO INCORPORATE<br />

CHEMICAL AND NON-CHEMICAL STRESSORS INTO<br />

CUMULATIVE RISK ASSESSMENT: A CASE STUDY OF<br />

PESTICIDE EXPOSURES.<br />

S. C. Wason 1, 2 , T. J. Smith 1 , M. J. Perry 1 and J. I. Levy 1 . 1 Environmental Health,<br />

Harvard School <strong>of</strong> Public Health, Boston, MA and 2 Gradient, Cambridge, MA.<br />

Sponsor: A. Lewis.<br />

Cumulative risk assessment has been proposed as an approach to evaluate health<br />

risks associated with simultaneous exposure to multiple chemical and non-chemical<br />

stressors. Physiologically based pharmacokinetic/pharmacodynamic (PBPK/PD)<br />

models can allow for inclusion and evaluation <strong>of</strong> multiple stressors, including nonchemical,<br />

but studies have not leveraged PBPK/PD models to jointly consider these<br />

disparate exposures in a cumulative risk context. In this study, we focused on exposures<br />

to organophosphate (OP) pesticides for children in urban low-income environments,<br />

where these children would be simultaneously exposed to other pesticides<br />

(e.g. pyrethroids) and non-chemical stressors that may modify the effects <strong>of</strong><br />

these exposures (e.g. diet). We developed a methodological framework to evaluate<br />

chemical and non-chemical stressor impacts on OPs, utilizing an existing<br />

PBPK/PD model for chlorpyrifos. We evaluated population-specific stressors that<br />

would influence OP doses or acetylcholinesterase (AChE) inhibition, the relevant<br />

PD outcome. We incorporated the impact <strong>of</strong> simultaneous exposure to pyrethroids<br />

and dietary factors on OP dose through the compartments <strong>of</strong> metabolism and PD<br />

outcome within the model, and simulated combinations <strong>of</strong> stressors across multiple<br />

exposure ranges and potential body weights. Our analyses demonstrated that both<br />

chemical and non-chemical stressors can influence the health implications <strong>of</strong> OP<br />

exposures, with up to 5-fold variability in AChE inhibition across combinations <strong>of</strong><br />

stressor values for a given OP dose. We demonstrate an approach for modeling OP<br />

risks in the presence <strong>of</strong> other population-specific environmental stressors, providing<br />

insight about co-exposures and variability factors that most affect OP health risks<br />

and contribute to children’s cumulative health risk from pesticides. This framework<br />

can be used to inform cumulative risk assessment for any compound affected by<br />

chemical and non-chemical stressors through metabolism or PD outcomes.<br />

865 ASSESSMENT OF AGGREGATE PERINATAL EXPOSURE<br />

TO BPA.<br />

D. A. Sarigiannis 1, 2 and S. Karakitsios 1 . 1 Institute for Health and Consumer<br />

Protection, European Commission - Joint Research Centre, Ispra, Varese, Italy and<br />

2 Chemical Engineering, Aristotle University <strong>of</strong> <strong>The</strong>ssaloniki, <strong>The</strong>ssaloniki, Greece.<br />

Sponsor: L. Birnbaum.<br />

<strong>The</strong> pharmacokinetic behavior <strong>of</strong> Bisphenol A, especially in the perinatal period is<br />

subject to large controversy. Recent epidemiological findings regarding inhaled<br />

BPA revealed that even at low levels <strong>of</strong> overall daily intake (0.5 μg/kg_bw) male sexual<br />

dysfunction was observed. This study aims to investigate (a) the exposure to<br />

BPA <strong>of</strong> the developing fetus during the perinatal period and reduce the uncertainty<br />

regarding internal dose determinants (fetus sulfation and BPA_Glu deconjugation<br />

by β-glucuronidase in the placenta; and (b) the effect <strong>of</strong> administration route on<br />

BPA bioavailability. For this purpose, a dynamic lifetime PBTK model was developed,<br />

capable <strong>of</strong> estimating the BPA biologically effective dose throughout several<br />

developmental stages for different administration routes. <strong>The</strong> model integrates<br />

steady state and dynamic Markov chain Monte Carlo simulations for uncertainty<br />

assessment. <strong>The</strong> biologically effective dose <strong>of</strong> the fetus during gestation is linked to<br />

the levels <strong>of</strong> BPA in the mother blood due to its high lipophilicity and the relatively<br />

small molecular weight. Fetal BED was calculated to be only slightly lower than the<br />

one <strong>of</strong> the mother. Sensitivity analysis showed that this parameter is determining<br />

for placental concentration and affects the overall fetal exposure with a sensitivity<br />

coefficient <strong>of</strong> 0.67, much higher than the contribution <strong>of</strong> the fetal intrinsic clearance<br />

(sensitivity coefficient <strong>of</strong> 0.4), confirming thus the importance <strong>of</strong> de-conjugation.<br />

BPA bioavailability from inhalation exposure in adults is significantly higher<br />

than when BPA is orally administrated (6 times higher for the same intake rate) due<br />

to lack <strong>of</strong> first pass metabolism prior to systemic circulation entrance. Exposure to<br />

5 μg/m3 <strong>of</strong> BPA in the air corresponds to a steady state concentration in plasma<br />

equal to 0.22 μg/L. In neonates, whose overall clearance capability is limited to almost<br />

20% <strong>of</strong> adults, differences in BPA bioavailability for different administration<br />

routes are limited to 50%.<br />

866 USE OF A PBPK/PD MODEL TO DERIVE AGE-<br />

SPECIFIC INTERSPECIES (UF A ) AND<br />

INTERINDIVIDUAL (UF H ) UNCERTAINTY FACTORS<br />

FOR CHLORPYRIFOS.<br />

P. S. Price 1 , P. M. Hinderliter 2 and T. S. Poet 2 . 1 <strong>Toxicology</strong> & Environmental<br />

Research & Consulting, <strong>The</strong> Dow Chemical Company, Midland, MI and 2 Battelle<br />

Pacific Northwest Division, Richland, WA.<br />

Risk assessments <strong>of</strong> chemicals use uncertainty factors for establishing safe levels <strong>of</strong><br />

exposure. <strong>The</strong> default values for these factors do not necessarily reflect current<br />

knowledge <strong>of</strong> a chemical’s mechanism <strong>of</strong> action or our growing ability to quantitatively<br />

predict internal doses and responses in humans using physiologically based<br />

pharmacokinetic/dynamic (PBPK/PD) models. A PBPK/PD model <strong>of</strong> variability<br />

in response (RBC cholinesterase inhibition) to chlorpyrifos exposure in two age<br />

groups in humans (adults and three year olds) was developed. <strong>The</strong> model was used<br />

to derive complete values (including both kinetic and dynamic components) for the<br />

interspecies (UF A ) and interindividual (UF H ) uncertainty factors. <strong>The</strong> approach<br />

used to determine UF A is to design simulations <strong>of</strong> human populations that predict<br />

the dose levels in humans that are directly comparable to the animal BMD or<br />

BMDL. <strong>The</strong> approach used for UF H is to directly model the variation in human response,<br />

at relevant dose levels and regimens, and use the model results to determine<br />

the size <strong>of</strong> the interindividual uncertainty factor necessary to address the variation<br />

that occurs across different fractions <strong>of</strong> the population. Finally, data from age-appropriate<br />

animal studies and age-specific models <strong>of</strong> human sensitivity are used to<br />

derive separate values <strong>of</strong> UF A and UF H for each age group. <strong>The</strong>se age-specific values<br />

avoid the need for extrapolating from adults to children. Values <strong>of</strong> UF A and UF H<br />

were developed for cholinergic responses to chlorpyrifos based on a BMDL 10 determined<br />

in a recent acute oral study in rats. Values <strong>of</strong> UF A were calculated to be

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!