The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
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<strong>of</strong> radiolabeled Mn (carrier-free 54 MnCl 2<br />
). Model parameters governing dietary absorption<br />
and biliary elimination were calibrated to whole body retention and tracer<br />
fecal excretion data due to different dietary conditions. Simulation results accurately<br />
recapitulated the fast and slow phases <strong>of</strong> elimination for all exposure routes in<br />
monkeys. Model predictions for whole body retention in humans given an iv dose<br />
<strong>of</strong> 54 Mn (2.5 μCi) compared well with retention characteristics <strong>of</strong> people on normal<br />
(3 mg/day Mn) and reduced calorie (1 mg/day Mn) diets. <strong>The</strong> ability <strong>of</strong> the PBPK<br />
models to provide consistent multispecies descriptions <strong>of</strong> Mn tracer kinetics across<br />
multiple exposure routes indicates that the models can accurately predict conditions<br />
where exposures will increase free Mn in various tissues throughout the body.<br />
885 TARGET-TISSUE DOSIMETRY MODELING TO<br />
SUPPORT THE RISK ASSESSMENT OF MANGANESE.<br />
M. D. Taylor 1 , M. Yoon 2 , J. D. Schroeter 2 , D. C. Dorman 3 , M. E. Andersen 2<br />
and H. J. Clewell 2 . 1 Afton Chemical Corp, Richmond, VA, 2 <strong>The</strong> Hamner Institutes,<br />
Research Triangle Park, NC and 3 North Carolina State University, Raleigh, NC.<br />
Manganese (Mn) is a ubiquitous, essential element that can be neurotoxic upon<br />
overexposure. Although Mn neurotoxicity has most commonly been associated<br />
with inhalation <strong>of</strong> excessive amounts <strong>of</strong> Mn-containing fumes and dusts, it may<br />
occur upon over-exposure by other routes. Dose to target tissue, not exposure<br />
route, is the critical determinant in the development <strong>of</strong> Mn neurotoxicity. Recently,<br />
tissue Mn data from a series <strong>of</strong> pharmacokinetic studies have been used to develop<br />
physiologically based pharmacokinetic (PBPK) models for ingested and inhaled<br />
Mn in rats and non-human primates. <strong>The</strong> models demonstrated that dose-dependent<br />
transitions exist for tissue accumulation <strong>of</strong> inhaled Mn, due in part to homeostatic<br />
regulation. <strong>The</strong> purpose <strong>of</strong> this study was to use these PBPK models to improve<br />
on traditional human health risk assessment approaches for environmental<br />
exposures to Mn. <strong>The</strong> PBPK models were used to estimate chemical-specific adjustment<br />
factors (CSAFs) in lieu <strong>of</strong> relying on default uncertainty factors (UFs).<br />
CSAFs were calculated for pharmacokinetic differences among potentially susceptible<br />
subpopulations and life stages. <strong>The</strong>se comparisons included gender, and age, as<br />
well as fetal and neonatal life stages. <strong>The</strong> resulting CSAFs were then used to replace<br />
some <strong>of</strong> the default UFs that have been used in risk assessments for inhaled Mn<br />
based on neurological effects observed in occupational studies in the derivation <strong>of</strong><br />
an acceptable environmental exposure concentration. Monte Carlo analysis<br />
demonstrated that the variation in target tissue dose at the resulting environmental<br />
exposure concentration was less than that associated with normal dietary variation.<br />
This work shows how PBPK models can be used to produce more robust and biologically<br />
based risk assessments <strong>of</strong> essential elements such as Mn by accounting for<br />
innate homeostatic control processes, dose-dependent transitions for tissue accumulation,<br />
and population variability.<br />
886 APPLICATION OF A PHYSIOLOGICALLY-BASED<br />
PHARMACOKINETIC MODEL OF<br />
TRICHLOROETHYLENE IN RATS FOR ESTIMATION<br />
OF INTERNAL DOSE.<br />
C. R. Eklund, M. V. Evans and J. Simmons. Integrated Systems <strong>Toxicology</strong><br />
Division, U.S. EPA, Research Triangle Park, NC.<br />
Potential human health risk from chemical exposure must <strong>of</strong>ten be assessed for conditions<br />
for which suitable human or animal data are not available, requiring extrapolation<br />
across duration and concentration. <strong>The</strong> default method for exposure-duration<br />
adjustment is based on Haber’s rule which states that a constant toxic effect (K)<br />
is a function <strong>of</strong> exposure concentration (C or C n ) and exposure duration (t), K = C<br />
(or C n )×t. This approach has been criticized for poor predictability, with errors increasing<br />
as the extrapolation interval increases. <strong>The</strong> purpose <strong>of</strong> the present work is<br />
estimation <strong>of</strong> the internal doses that result from various exposure concentrations<br />
and duration using a PBPK model developed in our laboratory for trichloroethylene<br />
(TCE) (Simmons et al., 2005). <strong>The</strong> model compartments are liver, brain, fat,<br />
richly-perfused and slowly-perfused tissues. TCE is a volatile organic compound<br />
and a common environmental pollutant <strong>of</strong> air, water and food. Mortality data from<br />
experimental animals are used in setting acute exposure guideline level-3 (AEGL-3)<br />
values as these represent air concentrations above which exposure could result in<br />
life-threatening adverse health effects or death (NRC, 2001). We compared results<br />
from simulations <strong>of</strong> two inhalation exposure scenarios reported to cause 50% mortality<br />
(LC 50<br />
) in rats, 26,000 ppm for one hour and 12,000 ppm for four hours.<br />
<strong>The</strong>se resulted in simulated arterial blood concentrations at the end <strong>of</strong> the exposure<br />
period <strong>of</strong> 888 and 733 mg/L, respectively. While there was a 4-fold difference in exposure<br />
duration and a 2.17 fold difference (percent difference, 74%) in external exposure<br />
concentration, there was only a 1.2-fold difference (percent difference,<br />
19%) in estimated arterial blood concentrations. This highlights the utility <strong>of</strong><br />
PBPK modeling for estimation <strong>of</strong> internal dose when considering the health implications<br />
<strong>of</strong> exposures <strong>of</strong> varying duration and concentration and for extrapolation<br />
from one concentration-duration to another. (This abstract may not reflect EPA<br />
policy.)<br />
887 MODELING THE IMPACT OF WORKLOAD ON THE<br />
BIOLOGICAL EXPOSURE INDICATORS OF STYRENE:<br />
COMPARISON BETWEEN SINGLE EXPOSURE AND<br />
BINARY EXPOSURE WITH ACETONE.<br />
A. Bérubé 1 , G. Truchon 2 , G. Charest-Tardif 1 and R. Tardif 1 . 1 Santé<br />
environnementale et santé au travail, Université de Montréal, Montréal, QC, Canada<br />
and 2 Institut de recherche Robert-Sauvé en santé et sécurité du travail, Montréal, QC,<br />
Canada.<br />
Workload has been recognized as a major determinant <strong>of</strong> the absorbed dose for<br />
many solvents. This study was undertaken to assess the impact <strong>of</strong> physical exertion<br />
(workload) on the biological levels <strong>of</strong> unchanged styrene (STYR) or STYR-metabolites<br />
used as biological exposure indices (BEIs). Physiologically based toxicokinetic<br />
models were adapted and validated in order to simulate a typical weekly occupational<br />
exposure (8 h/day, 5 days) to STYR alone and combined with acetone (ACE)<br />
at their current threshold limit values (ACGIH) <strong>of</strong> 20 ppm and 500 ppm, respectively.<br />
Simulations were then conducted under workload levels corresponding to<br />
rest (12.5W), 25W and 50W, and the impact on the levels <strong>of</strong> STYR in venous<br />
blood (STY-B) and on urinary mandelic (MA) and phenylglyoxylic (PGA) acids at<br />
the end <strong>of</strong> the last work shift <strong>of</strong> a week was examined for a typical worker. <strong>The</strong> predicted<br />
values were compared to results <strong>of</strong> both experimental and field studies which<br />
supported the adoption <strong>of</strong> the current BEIs for STYR. For an exposure to 20 ppm,<br />
the end-<strong>of</strong>-shift values <strong>of</strong> STY-B for a workload <strong>of</strong> 50W showed a 3-fold increase<br />
compared to the value at rest (0.17 mg/L), whereas the sum <strong>of</strong> MA and PGA in<br />
urine was 2.7 times higher than at rest (144 mg/g creatinine). <strong>The</strong> model predicted<br />
slight effect <strong>of</strong> co-exposure to ACE on biological levels <strong>of</strong> STYR at these exposure<br />
levels. Based on the relation between physical activity and the values <strong>of</strong> BEIs predicted<br />
by the model, the average workload level in field studies was approximately<br />
50W. Overall, the model described well the impact <strong>of</strong> workload on biological levels<br />
<strong>of</strong> STYR and showed that workload needs to be taken into account to avoid underestimation<br />
<strong>of</strong> the internal exposure <strong>of</strong> workers and health risk. (Supported by<br />
Afsset, France and IRSST, Canada)<br />
888 MODELING THE TOXICOKINETICS OF 24-HOUR<br />
TOLUENE EXPOSURE IN RATS: IMPACT OF ACTIVITY<br />
PATTERNS AND ENZYME INDUCTION.<br />
E. Kenyon, W. Oshiro, C. Eklund, C. Gordon, T. Krantz and P. Bushnell.<br />
ORD/NHEERL/ISTD/PB, U.S. EPA, Research Triangle Park, NC.<br />
Toluene, a solvent used in numerous consumer and industrial applications, exerts<br />
its critical effects on the brain and nervous system following inhalation exposure.<br />
Our previously published PBPK model successfully predicted toluene concentrations<br />
in blood and brain over a range <strong>of</strong> conditions, but in recent experimental<br />
studies it over-predicted (by ~2-fold) concentrations in blood and brain after 24 hrs<br />
<strong>of</strong> continuous exposure to 775 or 1125 ppm toluene. <strong>The</strong> goal <strong>of</strong> this current modeling<br />
effort was to determine if changes in physical activity patterns (as measured by<br />
telemetry) and/or enzyme induction could explain toluene pharmacokinetics following<br />
24 hrs <strong>of</strong> continuous exposure to toluene. Compartments in the model are<br />
lung, slowly and rapidly-perfused tissue groups, fat, liver, GI tract and brain; tissue<br />
transport is blood-flow limited and metabolism occurs in the liver. Chemical-specific<br />
parameters and initial organ volumes and blood flow rates were obtained from<br />
the literature. Observed changes in motor activity and heart rate during the period<br />
<strong>of</strong> exposure were implemented in the model by increasing cardiac output and alveolar<br />
ventilation up to 10%, but this was insufficient to account for the observed<br />
pharamacokinetic behavior. Alternatively, incorporation <strong>of</strong> cytochrome P450-mediated<br />
enzyme induction (increasing VmaxC up to 5-fold) allowed successful prediction<br />
<strong>of</strong> the experimental data. <strong>The</strong> degree <strong>of</strong> enzyme induction tested was biologically<br />
plausible based on literature data for shorter term toluene exposure which<br />
report up to 8.3-fold induction. Our results suggest the need to consider the potential<br />
impact <strong>of</strong> enzyme induction when simulating chronic toxicity studies for purposes<br />
<strong>of</strong> risk analysis, i.e. when using a PBPK model to obtain estimates <strong>of</strong> internal<br />
dose for application to dose-response analysis. (This abstract does not necessarily<br />
reflect EPA policy.)<br />
SOT 2010 ANNUAL MEETING 189