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The Toxicologist - Society of Toxicology

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pharmacokinetic and toxicological pr<strong>of</strong>ile optimization. During the development<br />

<strong>of</strong> a new lead compound, several in silico tools and models are normally used.<br />

<strong>The</strong>se are however built using compounds that may look quite different from conventional<br />

drug compounds and/or natural products and have a different distribution<br />

in their physicochemical properties. To understand how chemistry and pharmacokinetic<br />

and toxicological pr<strong>of</strong>iles compare between natural products and<br />

synthetic molecules and to determine the reliability <strong>of</strong> our current tools, we have<br />

analyzed and compared a number <strong>of</strong> data sets from different sources. <strong>The</strong>se were<br />

the Clinical candidate database (9 800 compounds) and the Natural Product database<br />

(121 600 compounds) from GVKBio, a set <strong>of</strong> 2 000 oral drugs and the KEGG<br />

set <strong>of</strong> 11 700 compounds. For all datasets, we computed physicochemical properties<br />

as well as standard DMPK and safety models such as Caco-2, Ames and hERG.<br />

We reviewed the structural space overlap between the different sets using Principal<br />

Component Analysis (PCA) and established usability <strong>of</strong> our current models for the<br />

natural drug compounds. Physicochemical property models can be validated<br />

against experimental data but safety models can mainly be assessed by space coverage<br />

and model domain applicability as experimental data is not generally available<br />

for natural products. When possible, validation against experimental data was<br />

done. <strong>The</strong> results show that there are some significant differences between the distributions<br />

<strong>of</strong> simple molecular properties and that the classes (synthetic drug/natural<br />

drug) can be partially separated using PCA. <strong>The</strong> reliability <strong>of</strong> our current models<br />

is also discussed in relation to these differences.<br />

480 A FLEXIBLE METHOD FOR BUILDING AND USING<br />

PREDICTIVE MODELS APPLIED TO SAFETY<br />

ENDPOINTS.<br />

O. Spjuth2 , L. Carlsson1 , M. Eklund2 , E. Ahlberg Helgee1 and S. Boyer1 .<br />

1Computational <strong>Toxicology</strong>, AstraZeneca, Mölndal, Sweden and 2Department <strong>of</strong><br />

Pharmaceutical Biosciences, Uppsala University, Uppsala, Sweden.<br />

We present a general method for building and using predictive in silico models. <strong>The</strong><br />

method can take any collection <strong>of</strong> compounds with activities as input, and automatically<br />

produces several different predictive models; (1) Similarity searches using<br />

InChI, signatures and fingerprints (exact matches and nearest neighbours) (2) A<br />

classification or regression QSAR model using a support vector machine (SVM)<br />

and interpretable signature descriptors (3) Discriminative signatures (structural<br />

alerts or toxicophores). All models can be run simultaneously for novel chemical<br />

structures and produce interpretable results with important substructures highlighted<br />

in a chemical editor or spreadsheet, with the possibility to generate hypothesis<br />

on how to avoid safety hazards by making changes to the chemical structure<br />

and watch how this change affects the predictions. <strong>The</strong> method is available from<br />

the Bioclipse workbench, can be run on desktop computers and does not necessarily<br />

require a network connection. We demonstrate our method on publicly available<br />

data for three endpoints: mutagenicity, carcinogenicity, and AhR inhibition.<br />

<strong>The</strong> results indicate that combining local data with established and well tested<br />

models together with interpretable results can aid scientists in making better informed<br />

decisions in safety assessment.<br />

481 ASSESSING DOSE-RESPONSE OF ENVIRONMENTAL<br />

CHEMICALS INTERACTION WITH DNA USING A<br />

SYSTEM BIOLOGY MODELING APPROACH.<br />

J. M. Gavina, Y. Feng and A. Nong. Environmental Health Science and Research<br />

Bureau, Health Canada, Ottawa, ON, Canada.<br />

Genotoxicity <strong>of</strong> environmental pollutants is investigated at the molecular level for<br />

DNA damage or instability, disruption <strong>of</strong> cellular metabolic processes, carcinogenicity,<br />

or mutagenic modifications. Chemical interaction with cellular DNA can<br />

be screened using genetic or proteomic assays, sensitive chromatography, or mass<br />

spectrometry techniques. <strong>The</strong> difficulty with the in-vitro chemical screens at the<br />

target receptor lies in the interpretation <strong>of</strong> these results for in-vivo or even human<br />

internal dose levels. System biology modeling approaches integrate genomic and<br />

proteomic data with biological mechanism <strong>of</strong> response. <strong>The</strong>se models provide understanding<br />

<strong>of</strong> the process as well for correlation in doses ranges <strong>of</strong> concern. In this<br />

pilot study, a biological model or system motif was developed to described the kinetic<br />

reaction <strong>of</strong> DNA adduct formation following exposure to different chemicals<br />

(tetrachlorohydroquinone, styrene-7,8-oxide, methyl methane sulfonate, PGE, and<br />

BPDE). A HPLC screening method was used to detect and quantify DNA products.<br />

A simple experiment was designed to expose double stranded DNA oligonucleotides<br />

under controlled conditions over time and various doses. DNA adducts<br />

were then separated and measured respectively by chromatography and spectrometry.<br />

<strong>The</strong> motif model parameters were then calibrated with the time series and validated<br />

with the dose-response relationship data. <strong>The</strong> estimated rate constants <strong>of</strong><br />

these reactions are chemical dependent. <strong>The</strong> dose-response behaviour is linear,<br />

where a Hill coefficient <strong>of</strong> 1 was estimated, for all chemicals except for tetrachlorohydroquinone.<br />

This in-vitro system motif provides as basis for more complex biological<br />

toxic response such as cellular DNA damage. Combined with internal<br />

dosimetry models (e.g. PBPK), system biology models can serve as a useful tools to<br />

predict the dose-response at the target receptor for environmental exposure risk assessment<br />

<strong>of</strong> contaminants.<br />

482 USING A MULTIPLE STAGE DECISION TREE TO MAKE<br />

ACTIVITY CALLS IN QUANTITATIVE HIGH-<br />

THROUGHPUT SCREENING (QHTS) DATA.<br />

K. R. Shockley 1 , G. E. Kissling 1 , R. Huang 2 , M. Xia 2 , C.P.Austin 2 and R. R.<br />

Tice 1 . 1 National <strong>Toxicology</strong> Program/National Inistitute <strong>of</strong> Environmental Health<br />

Sciences, Research Triangle Park, NC and 2 NIH Chemical Genomic Center,<br />

Bethesda, MD.<br />

<strong>The</strong> goals <strong>of</strong> the Tox21 collaboration are to identify mechanisms <strong>of</strong> toxicity, prioritize<br />

chemicals for in vivo testing and predict adverse responses to environmental<br />

chemicals in humans. Quantitative high throughput screening (qHTS) assays provide<br />

an opportunity to meet these goals, holding the potential for wide chemical<br />

coverage, reduced cost <strong>of</strong> testing on a per-substance basis and minimal use <strong>of</strong> animals.<br />

Moreover, the ability <strong>of</strong> a substance to induce a toxicological response is better<br />

understood by analyzing the response pr<strong>of</strong>ile over a broad dose range than by<br />

evaluating effects at one or a few doses. Pharmaceutical applications <strong>of</strong> qHTS generally<br />

seek to minimize false positives in activity assessment and <strong>of</strong>ten rely on heuristic<br />

algorithms to make activity calls. In contrast, multiple questions must be asked<br />

to determine the toxicological relevance <strong>of</strong> a chemical and statistical testing should<br />

be used to minimize false negatives. Here, we developed a multiple-stage decision<br />

tree statistical model and applied it to qHTS data from nine cell-based nuclear receptor<br />

agonist assays (AR, ER, FXR, GR, PPARα, PPARλ, RXR,TRβ, VDR).<br />

Data were fit to a four-parameter Hill equation and an overall F-test comparing the<br />

best fit to the Hill equation and a horizontal line (no response) was calculated for<br />

each chemical. Substances with a robust dose-response were identified in the first<br />

stage. In the second stage, compounds not detected as active in the first stage were<br />

evaluated for a maximal response at the lowest dose by comparing the distribution<br />

<strong>of</strong> measured responses to a control value. Chemicals with a weak dose-response were<br />

identified in the third stage, and the final stage separated substances exhibiting a cytotoxic<br />

response at the lowest dose from inactive compounds. Our model identified<br />

more active compounds than a previously utilized heuristic approach.<br />

483 TESTING MULTIPLE AVAILABLE QSARS FOR<br />

REPRODUCTIVE TOXICITY AND CARCINOGENICITY<br />

TO DRINKING WATER CONTAMINANTS.<br />

M. Heringa 1 , A. Roncaglioni 2 , R. Benigni 3 and A. Worth 4 . 1 KWR Watercycle<br />

Research Institute, Nieuwegein, Netherlands, 2 Istituto di Ricerche Farmacologiche<br />

“Mario Negri”(IRFMN), Milan, Italy, 3 Istituto Superiore di Sanita (ISS), Rome,<br />

Italy and 4 European Commission - Joint Research Centre (JRC), Ispra, Italy.<br />

Within the REACH legislation in Europe, Quantitative or Qualitative Structure<br />

Activity Relationship- (QSAR-) toxicity predictions are an important alternative to<br />

animal testing. Also in the hazard identification <strong>of</strong> detected drinking water contaminants<br />

for which no experimental toxicity data can be found, QSARs are helpful.<br />

However, proper use <strong>of</strong> QSARs is not always straightforward, as there are many<br />

models available, each with its own specifications. To illustrate what a risk-assessor<br />

runs into when using QSARs, toxicity predictions were sought for 10 selected case<br />

compounds for the endpoints mutagenicity, carcinogenicity, and reproductive toxicity<br />

(here: developmental toxicity and estrogenicity). <strong>The</strong> models applied were:<br />

CASETOX, TOPKAT, Derek for Windows, PharmaAlgorithms, the OSIRIS<br />

IRFMN RBA model, HazardExpert, Toxtree, and lazar. Only two <strong>of</strong> these models<br />

could be judged as “scientifically valid”, a requirement posed by REACH, which is<br />

based on the five OECD principles. <strong>The</strong> other models were used as supportive information.<br />

For mutagenicity, for eight <strong>of</strong> the ten compounds all models (seven)<br />

agreed in their predictions, for carcinogenicity this was the case for one compound<br />

only, for developmental toxicity for three compounds and for estrogenicity for nine<br />

compounds. <strong>The</strong> application <strong>of</strong> multiple QSAR models has made apparent that it<br />

is unclear how conflicting predictions <strong>of</strong> multiple models should be evaluated. This<br />

indicates a strategy on the use <strong>of</strong> multiple QSAR models is necessary, for which<br />

some ideas are discussed.<br />

484 CONSENSUS MULTIPLE-POTENCY QSAR MODELING<br />

FOR PREDICTION OF RODENT CARCINOGENICITY.<br />

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

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

<strong>The</strong> performance <strong>of</strong> quantitative structure-activity relationship (QSAR) models depends<br />

extensively upon the quality <strong>of</strong> the data used to construct the models, and<br />

the methods employed to optimize model predictive performance. For rodent carcinogenicity<br />

models, the nature, location, prevalence, and extensiveness <strong>of</strong> tumors<br />

SOT 2011 ANNUAL MEETING 103

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