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The Toxicologist - Society of Toxicology

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1815 MEASURING COMPOUND SELECTIVITY AND ITS<br />

LINK TO IN VIVO TOXICITY STUDY OUTCOME.<br />

X. Wang and N. Greene. Compound Safety Prediction, Pfizer, Groton, CT.<br />

In order to reduce drug attrition, it’s important to assess the safety liabilities <strong>of</strong> early<br />

leads. A common practice to assess compound toxicity is using pharmacologic pr<strong>of</strong>iling<br />

panels. Several methods for measuring compound selectivity were developed<br />

over the years, from simple hit rate (defined as the fraction <strong>of</strong> assays with inhibition<br />

values greater than certain threshold for each compound) to more sophisticated<br />

methods, such as Gini Coefficient or <strong>The</strong>rmodynamics-Based Partition Index. Gini<br />

Coefficient measures statistical dispersion and is scale-free with no units. It is originally<br />

used to measure inequality <strong>of</strong> income or wealth, and had been successfully applied<br />

to measure Kinase inhibitors selectivity. <strong>The</strong> partition indexed can be defined<br />

as a competition assay in which the compound is placed in a test tube, and then<br />

compete for binding to a pool <strong>of</strong> targets. At thermodynamic equilibrium, the fraction<br />

<strong>of</strong> bound compound for a particular target is the “partition” index.<br />

In this study, we compared these three methods: hit rate, Gini Coefficient, and partition<br />

index, based on a panel <strong>of</strong> 180 Bioprint (CEREP) inhibition assays. First, the<br />

impact <strong>of</strong> different assay selection on selectivity score was tested by randomized<br />

studies, and a panel <strong>of</strong> 15 assays was selected that best represent the overall assay selectivity<br />

pr<strong>of</strong>iles. Second, ~200 Pfizer compounds had gone through in vivo toxicity<br />

studies, and can be divided into two groups: clean@10uM and findings@10uM.<br />

<strong>The</strong> capability <strong>of</strong> each method to separate two groups <strong>of</strong> compounds based on<br />

those 15 assays was measured. <strong>The</strong> results show that each methods capture different<br />

nuances <strong>of</strong> the data. Hit rate is most intuitive; Gini Coefficient needs to be modified<br />

to deal with small panel <strong>of</strong> assay; while partition index is the most predictive.<br />

It’s possible that the three methods could be combined to generate the optimal selectivity<br />

index.<br />

1816 IDENTIFICATION AND CLASSIFICATION OF<br />

GENOTOXIC AND NON-GENOTOXIC SCAFFOLDS IN<br />

RODENT CARCINOGENICITY QSAR MODELS.<br />

K. P. Cross 1 and E. J. Matthews 2 . 1 Leadscope, Inc., Columbus, OH and 2 U.S.<br />

FDA/CFSAN/OFAS, College Park, MD. Sponsor: R. Tice.<br />

Quantitative structure-activity relationship (QSAR) models have been developed<br />

for predicting mutagenicity in Salmonella typhimurium and carcinogenicity in rodents<br />

using Leadscope s<strong>of</strong>tware. <strong>The</strong>se models identify structure-activity relationships<br />

(SARs) between molecular features and chemical toxicity, and the SARs can<br />

support plausible mechanism <strong>of</strong> action (MOA) hypotheses responsible for the toxicity.<br />

<strong>The</strong> molecular features can be represented as molecular substructures that discriminate<br />

for, or against, toxicity, and the features may be extracted as scaffolds. <strong>The</strong><br />

predictive performance <strong>of</strong> these scaffolds may be assessed for accuracy and precision<br />

independently <strong>of</strong> the model they were derived from. This study revealed that a relatively<br />

small number <strong>of</strong> primary scaffolds, alerts, and MOAs were associated with<br />

mutagenicity; conversely, a relatively large number <strong>of</strong> scaffolds were associated with<br />

carcinogenicity. We also extracted and compared the predominant scaffolds contributing<br />

to carcinogenicity and mutagenicity through hierarchical classification <strong>of</strong><br />

discriminating model features. Preliminary analysis <strong>of</strong> the salmonella QSAR model<br />

indicated that 58% <strong>of</strong> salmonella model scaffolds matched compounds predominantly<br />

positive for rodent carcinogenicity, while only 2% <strong>of</strong> the scaffolds matched<br />

compounds predominantly negative for rodent carcinogenicity (40% remained unclassified).<br />

Preliminary analysis <strong>of</strong> the rodent carcinogenicity QSAR model indicated<br />

that 43% <strong>of</strong> carcinogenicity model scaffolds matched compounds predominantly<br />

positive for salmonella (and classified as genotoxic), while 30% <strong>of</strong> the<br />

scaffolds matched compounds predominantly negative for salmonella (and classified<br />

as non-genotoxic). <strong>The</strong> remaining 27% <strong>of</strong> the scaffolds were classified as only<br />

partially responsible for genotoxicity. <strong>The</strong> analysis further classified scaffolds for<br />

each <strong>of</strong> the rodent carcinogenicity models (mouse, rat, rodent, and sex) and identified<br />

genotoxic and non-genotoxic scaffolds common across several different models.<br />

1817 EFFECTS OF ORAL DOSAGE REGIMEN ON FIRST-PASS<br />

ELIMINATION AND TOXICOKINETICS (TK) OF 1, 1, 1-<br />

TRICHLOROETHANE (TRI) AND<br />

TRICHLOROETHYLENE (TCE).<br />

V. Srivatsan, S. Muralidhara, J. V. Bruckner and C. A. White. Pharmacology and<br />

Biomedical Sciences, University <strong>of</strong> Georgia, Athens, GA.<br />

<strong>The</strong> objective <strong>of</strong> this investigation was to compare the TK <strong>of</strong> TRI and TCE under<br />

conditions representative <strong>of</strong> drinking water exposure, and to contrast these TK pr<strong>of</strong>iles<br />

with those when the halocarbons are given by gavage. Fasted male Sprague-<br />

Dawley rats were given 6 – 48 mg TRI/kg or 8 – 50 mg TCE/kg, as an aqueous<br />

emulsion ia, iv or by constant gastric infusion (gi) over 2 h. Serial micro-blood sam-<br />

ples were taken and analyzed by GC, while other rats were sacrificed serially for<br />

blood and tissue collection. Bioavailability <strong>of</strong> TRI exceeded 95% and was independent<br />

<strong>of</strong> dose and dosage regimen. This was not the case for TCE. First-pass<br />

elimination <strong>of</strong> the 8 mg TCE/kg gi dose was virtually complete. Rapid absorption<br />

<strong>of</strong> TRI ad TCE into blood and tissues was followed by relatively rapid elimination<br />

<strong>of</strong> TCE. In vivo TRI blood:tissue partition coefficients were consistently higher<br />

than corresponding values for TCE. First-pass pulmonary elimination <strong>of</strong> TRI was<br />

independent <strong>of</strong> dose and dosage regimen and exceeded that <strong>of</strong> TCE, while the converse<br />

was true for hepatic first-pass elimination. <strong>The</strong>se TK data may prove useful in<br />

physiological modeling and in assessment <strong>of</strong> health risks <strong>of</strong> these common drinking<br />

water contaminants. Supported by U.S. DOE DE-FC09-02CH11109.<br />

1818 IN VITRO METABOLISM OF BDE-99 IN HUMAN LIVER<br />

MICROSOMES.<br />

C. Erratico and S. Bandiera. Faculty <strong>of</strong> Pharmaceutical Sciences, <strong>The</strong> University <strong>of</strong><br />

British Columbia, Vancouver, BC, Canada.<br />

Polybrominated diphenyl ethers (PBDEs) are persistent, bioaccumulative, and toxic<br />

environmental pollutants frequently detected in human samples. Limited information<br />

is available for PBDE metabolism in humans. In this study, metabolism <strong>of</strong><br />

2,2′,4,4′,5-pentabromodiphenyl ether (BDE-99), the major component <strong>of</strong> a widely<br />

used commercial PBDE mixture (Penta-BDE), was investigated in vitro to determine<br />

the hydroxy metabolites formed, rates <strong>of</strong> metabolite formation, and the cytochrome<br />

P450 (CYP) enzymes involved. BDE-99 was incubated with human liver<br />

microsomal preparations. Hydroxy metabolites were liquid-to-liquid extracted and<br />

quantified using liquid chromatography/mass spectrometry. Incubation conditions<br />

were optimized for substrate, NADPH, protein concentration, and incubation<br />

time. BDE-99 was metabolized to two major (5′-OH-BDE-99 and 2,4,5-tribromophenol),<br />

one intermediate (4′-OH-BDE-101), and two minor (4-OH-BDE-90<br />

and 6′-OH-BDE-99) oxidative products by human liver microsomes. Rates <strong>of</strong> formation<br />

<strong>of</strong> major and minor metabolites ranged between 18 and 20 and between 0.6<br />

and 0.9 pmol/min/mg protein, respectively. No other hydroxy or di-hydroxy<br />

metabolite <strong>of</strong> BDE-99 was detected under the experimental conditions used.<br />

Structures <strong>of</strong> the major and minor BDE-99 metabolites produced by human liver<br />

microsomes are different from structures <strong>of</strong> the major and minor BDE-99 metabolites<br />

identified in a previous study using rat liver microsomes. Moreover, BDE-99<br />

undergoes more extensive metabolism in human than in rat liver microsomes (50 vs<br />

3.5 pmols/min/mg protein). Formation <strong>of</strong> BDE-99 hydroxy metabolites is <strong>of</strong> toxicological<br />

concern as in vitro studies have recently shown that hydroxy PBDEs affect<br />

steroidogenesis and are agonists <strong>of</strong> human estrogen and transthyretin receptors.<br />

Experiments are in progress to identify the CYP enzymes responsible for the formation<br />

<strong>of</strong> BDE-99 metabolites using a panel <strong>of</strong> human recombinant CYP enzymes.<br />

<strong>The</strong> same experimental design will be used to characterize the metabolism <strong>of</strong> the<br />

second major component <strong>of</strong> Penta-BDE mixture, BDE-47.<br />

1819 BIOTRANSFORMATION OF ETHANOL TO ETHYL<br />

GLUCURONIDE IN A RAT MODEL AFTER A SINGLE<br />

ORAL DOSAGE.<br />

T. Haupt and K. Ferslew. East Tennessee State University, Johnson City, TN.<br />

Ethyl glucuronide (EtG) is a minor ethanol (Et) metabolite that confirms the absorption<br />

and metabolism <strong>of</strong> Et after oral or dermal exposure. Human data suggest<br />

maximum blood EtG concentrations are reached between 3.5 - 5.5 hours post Et<br />

administration 1 . This study was undertaken to determine if the Sprague Dawley<br />

(SD) rat biotransforms Et to EtG after a single oral dose <strong>of</strong> Et. SD rats (male, n=6)<br />

were gavaged with a single Et dose (4g/kg) and urine was collected for 3 hours in<br />

metabolic cages, followed by euthanization and collection <strong>of</strong> heart blood. Blood<br />

and urine were analyzed for Et and EtG by gas chromatography and enzyme immunoassay.<br />

Blood and urine Et concentrations (BEt, UEt) were 195 ± 23 and 218<br />

± 19 mg/dL while blood and urine EtG concentrations (BEtG, UEtG) were 1363 ±<br />

98 ng/mL and 2.1 ± 0.29 mg/mL (mean ±SE). Sixty-six, male, SD rats were gavaged<br />

Et (4 g/kg) and placed in metabolic cages to determine the extent and duration<br />

<strong>of</strong> Et to EtG biotransformation and urinary excretion. Blood and urine were<br />

collected up to 24 hours post administration for Et and EtG analysis. Maximum<br />

BEt, UEt, and UEtG were reached within 4 hours while maximum BEtG was<br />

reached 6 hours post administration. Maximum concentrations were: BEt, 213 ±<br />

20 mg/dL; UEt, 308 ± 34 mg/dL; BEtG, 2683 ± 145 ng/mL; UEtG, 1.2 ±<br />

0.06mg/mL (mean ±SE). Areas under the concentration-time curve were: BEt,<br />

1632 hr*mg/dL; UEt, 2936 hr*mg/dL; BEtG, 11764 hr*ng/mL; UEtG, 8.5<br />

hr*mg/mL. BEt and BEtG were reduced to below limits <strong>of</strong> detection (LOD) within<br />

12 and 18 hours post Et administration. UEt’s were below LOD at 18 hours, but<br />

UEtG was still detectable at 24 hours post administration. Our data proves that the<br />

SD rat biotransforms Et to EtG and excretes both in the urine and suggests it is<br />

similar to that <strong>of</strong> the human.<br />

SOT 2011 ANNUAL MEETING 389

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