The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
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