The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
calculated using this new tool are generally consistent with those calculated by<br />
Rodgers et al., while providing a convenient, approachable and high-throughput<br />
tool to estimate these measures for a large variety <strong>of</strong> xenobiotics.<br />
1810 A COMPUTATIONAL FRAMEWORK FOR<br />
CHARACTERIZING BIOMARKERS OF<br />
ORGANOPHOSPHORUS INSECTICIDE MIXTURE<br />
EXPOSURE.<br />
J. H. Ivy1, 2 , J. M. Wright2 , J. L. Rogers1, 2 , A. N. Mayeno1, 2 , M. A. Lyons1, 2<br />
and B. Reisfeld1, 2 . 1Department <strong>of</strong> Chemical and Biological Engineering, Colorado<br />
State University, Fort Collins, CO and 2Systems and Computational Biology Research<br />
Group, Colorado State University, Fort Collins, CO.<br />
<strong>The</strong> disposition and toxicological effects <strong>of</strong> organophosphorus insecticides (OPs)<br />
following human exposure are governed by complex absorption, distribution, metabolism,<br />
and elimination (ADME) and pharmacodynamic (PD) processes. Among<br />
the signatures <strong>of</strong> these processes are a variety <strong>of</strong> metabolites, some <strong>of</strong> which are<br />
common to many OPs and some <strong>of</strong> which are unique to a given OP. Characterizing<br />
these biomarkers <strong>of</strong> exposure and effect, and their quantitative relationship to the<br />
an individual’s ADME and PD, warrants the development and use <strong>of</strong> quantitative<br />
and computational modeling tools. Here we describe the development and usage <strong>of</strong><br />
such a modeling tool that can facilitate the analysis <strong>of</strong> tissue dosimetry based on<br />
given dosing scenarios and reconstruct dose from specific biomarker data. This s<strong>of</strong>tware<br />
framework, DoseSim:OP, is centered around a sophisticated differential equation<br />
solution and statistical simulation engine, allowing analyses that include<br />
Bayesian inference and Monte Carlo stochastic simulations. <strong>The</strong> modular architecture<br />
behind DoseSim:OP allows different models (ADME+PD) to be linked to the<br />
simulation engine, allowing great flexibility in the systems to be analyzed. <strong>The</strong> first<br />
<strong>of</strong> the models to be implemented is a physiologically-based pharmacokinetic model<br />
for a mixture <strong>of</strong> chlorpyrifos [O,O-diethyl O-(3,5,6-trichloro-2-pyridyl)phosphorothioate]<br />
and diazinon [O,O-diethyl O-(2-isopropyl-6-methyl-4pyrimidinyl)phosphorothioate]<br />
based upon the work <strong>of</strong> Timchalk et al. (2008). We<br />
have further refined this model using data from our own studies, coupled with optimizations<br />
and global sensitivity analyses. Predictions from DoseSim:OP for various<br />
exposure and dose reconstruction scenarios have shown good agreement with<br />
those from the literature and to our own experiments, and demonstrate the flexibility<br />
and utility <strong>of</strong> this methodology and framework. This project is supported by<br />
EPA STAR Grant #RE83345101.<br />
1811 QSAR ANALYSIS OF THE ATSDR DATABASE OF<br />
CHEMICAL HEALTH GUIDANCE VALUES.<br />
E. Demchuk 1 , Y. Tie 1 , T. Miller 2 and R. M. Garrett 2 . 1 Division <strong>of</strong> <strong>Toxicology</strong> &<br />
Environmental Medicine, ATSDR/CDC, Atlanta, GA and 2 Department <strong>of</strong> Defense,<br />
Washington, DC. Sponsor: B. Fowler.<br />
<strong>The</strong> ATSDR SEQUOIA (formerly HazDat) database contains information concerning<br />
thousands <strong>of</strong> chemicals collected at hazardous waste sites across the nation.<br />
However, less than 10% <strong>of</strong> them have been extensively reviewed to provide public<br />
health guidance. A goal <strong>of</strong> this project is to develop QSAR (Quantitative Structure<br />
Activity Relationship) models using these well-studied chemicals and apply the<br />
models to estimate provisional health guidance values (pHGVs) for other toxic<br />
chemicals that have not yet been reviewed by ATSDR. <strong>The</strong> QSAR analysis was conducted<br />
on a set <strong>of</strong> 100 compounds with rat oral chronic LOAEL (lowest-observedadverse-effect-level)<br />
values; and a QSAR model with R2 and Q2 <strong>of</strong> 0.92 and 0.82,<br />
respectively, was developed. <strong>The</strong> model was applied to assess the toxicity <strong>of</strong> n-alkanes<br />
found in the 2010 BP Gulf oil spill, because limited toxicological information<br />
is available for long-chain alkanes and their mixtures. <strong>The</strong> LOAEL estimates obtained<br />
using our model were in fair agreement with those obtained using the TOP-<br />
KAT package, and they were in an excellent agreement with information on<br />
ADMET properties <strong>of</strong> n-alkanes found in the ATSDR toxicological pr<strong>of</strong>ile for<br />
Total Petroleum Hydrocarbons. Further validation <strong>of</strong> the model and expansion <strong>of</strong><br />
its chemical space domain are under way. In the future, a robust model for pHGVs<br />
may complement the risk assessment <strong>of</strong> pure chemicals and multi-component exposures<br />
carried out using conventional methods.<br />
1812 SUPPORTING SAFETY ASSESSMENT OF DRUG<br />
IMPURITIES THROUGH EXAMINATION OF AN AMES<br />
ASSAY QSAR MODEL.<br />
G. Myatt 1 , K. P. Cross 1 and L. G. Valerio 2 . 1 Leadscope Inc., Columbus, OH and<br />
2 CDER/OPS, U.S. FDA, Silver Spring, MD. Sponsor: N. Sadrieh.<br />
Drugs under development may contain multiple impurities with structural alerts<br />
portending to toxicity, and thus to public health. According to the FDA draft guidance<br />
to industry on genotoxic and carcinogenic impurities in drug products and<br />
388 SOT 2011 ANNUAL MEETING<br />
substances, impurities can be evaluated for genotoxicity based on structure-activity<br />
relationship (SAR) analysis. <strong>The</strong>se molecules if predicted positive may need to have<br />
their levels controlled or the impurity synthesized and qualified in the Ames assay.<br />
Given the importance <strong>of</strong> adequately qualifying genotoxic impurities, this study<br />
evaluated a quantitative SAR (QSAR) analysis model developed that predicts Ames<br />
assay outcomes based on a training dataset <strong>of</strong> over 3000 molecules. A drug-like external<br />
validation set <strong>of</strong> over 3000 molecules was used to characterize the QSAR<br />
model performance by structural class, therapeutic category, and domain-<strong>of</strong>-applicability.<br />
Preliminary predictive performance statistics for the external test set (79%<br />
sensitivity, 76% specificity, 77% accuracy) were comparable to the model cross-validation<br />
statistics (77% sensitivity, 88% specificity, 83% accuracy). Hundreds <strong>of</strong><br />
drug impurity molecules (proprietary and public) were examined at the FDA to assess<br />
the suitability <strong>of</strong> the chemical space <strong>of</strong> the Ames model for predicting drug<br />
molecules. <strong>The</strong> predominant molecular features contributing to Ames positive predictions<br />
<strong>of</strong> the drug impurities were elucidated through hierarchical classification <strong>of</strong><br />
discriminating model features. This analysis has led to an improvement for predicting<br />
the mutagenicity <strong>of</strong> drug impurities in the Salmonella assay and by extending<br />
our understanding <strong>of</strong> known and new structural alerts in the Ames assay. <strong>The</strong><br />
QSAR model is intended to help support decision-making during safety evaluations<br />
<strong>of</strong> the genotoxic potential <strong>of</strong> drug impurities.<br />
1813 ESTIMATING TOXICITY-RELATED BIOLOGICAL<br />
PATHWAY ALTERING DOSES FOR HIGH-<br />
THROUGHPUT CHEMICAL RISK ASSESSMENTS.<br />
R. Judson, D. J. Dix, K. J. Robert, R. Setzer, E. A. Cohen Hubal and M. T.<br />
Martin. U.S. EPA, Research Triangle Park, NC.<br />
<strong>The</strong> doses at which toxicity-related biological pathways are altered, measured using<br />
in vitro assays, are analogs to regulatory values such as Reference Doses (RfD) derived<br />
from in vivo toxicity tests. <strong>The</strong>se biological pathway altering doses (BPADs)<br />
could be used in high throughput risk assessments <strong>of</strong> 1000s <strong>of</strong> data-poor environmental<br />
chemicals. Estimating a BPAD requires definition <strong>of</strong> biological pathways<br />
that can lead to toxicity, and development <strong>of</strong> in vitro assays for these pathways that<br />
can rapidly, efficiently and quantitatively test many chemicals. <strong>The</strong> ToxCast and<br />
Tox21 programs are providing data from 100s <strong>of</strong> in vitro assays, on 1000s <strong>of</strong> environmental<br />
chemicals. <strong>The</strong> first step is to estimate minimum chemical concentrations<br />
required to significantly alter toxicity-related biological pathways in vitro, i.e.,<br />
the Biological Pathway Altering Concentration (BPAC). Pharmacokinetic modeling<br />
is then used to estimate the in vivo oral dose required to achieve the BPAC in<br />
target species and tissues (e.g., human serum concentration). Uncertainties are incorporated<br />
in both the BPAC and the pharmacokinetic parameters, and these are<br />
combined to yield a probability distribution for the dose required to alter pathway<br />
function. <strong>The</strong> BPAD is defined as the lower, protective end <strong>of</strong> this pathway-altering<br />
confidence interval. We illustrate with two examples. In the first, BPADs corresponding<br />
to the lowest AC50 for CAR/PXR-related assays were compared to the<br />
No-Effect Level (NEL)/100 for chronic rodent liver pathology <strong>of</strong> 13 conazole<br />
fungicides. In most cases, CAR/PXR BPADs were lower than the NEL/100, providing<br />
a reasonable starting point for setting exposure limits if these were data poor<br />
chemicals. In the second case, the lowest BPADs for any pathway were compared<br />
with regulatory RfDs for 35 chemicals and, again, BPADs were mostly lower than<br />
RfDs. BPADs were significantly higher than RfDs (less protective) in a few cases,<br />
but most <strong>of</strong> these were cholinesterase inhibitors requiring bioactivation for toxicity.<br />
This abstract does not necessarily reflect U.S. EPA policy.<br />
1814 EVALUATION OF IN SILICO TOOLS FOR THE<br />
PREDICTION OF MUTAGENICITY.<br />
A. Hillebrecht, W. Muster, A. Brigo, M. Kansy, T. Weiser and T. Singer.<br />
Pharmacology Research Nonclinical Safety, F. H<strong>of</strong>fmann-La Roche Ltd., Basel,<br />
Switzerland.<br />
Four s<strong>of</strong>tware packages (DEREK for Windows, Leadscope Model Applier, MCASE<br />
MC4PC and Toxtree) were systematically evaluated for their ability to predict the<br />
outcome <strong>of</strong> the Ames assay. A large, high quality data set <strong>of</strong> 9861 compounds, comprising<br />
public as well as Roche proprietary data, was used to test the systems.<br />
Acceptable performances were observed with the publicly available data sets,<br />
whereas a significant deterioration was obtained when the assessment was performed<br />
on the proprietary data. In particular, the sensitivity values dropped below<br />
45 %. <strong>The</strong> relatively low amount <strong>of</strong> Ames positive compounds included in pharmaceutical<br />
industry data sets and the different coverage <strong>of</strong> the chemical space are<br />
the most likely explanations for the observed discrepancy between test sets. As a<br />
general trend, expert systems (DEREK, Toxtree) tend to exhibit higher sensitivities,<br />
but lower specificities compared to QSAR-based systems (MC4PC, Leadscope<br />
Model Applier).