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Computational Toxicology: New Approaches for the 21st Century September 9 th , 2009 Session IV: ToxCast and the Comparative Toxicogenomics Database (CTD) David Dix, Acting Deputy Director of EPA/ORD’s National Center for Computational Toxicology Carolyn Mattingly, Mount Desert Island Biological Laboratory 1 September 9, 2009 1

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Page 1: Computational Toxicology: New Approaches for the 21st Century 09sept2009_v1bw... · Computational Toxicology: New Approaches for the 21st Century September 9th, 2009 Session IV: ToxCast

Computational Toxicology: New Approaches for the 21st Century

September 9th, 2009  Session IV: ToxCast and the Comparative ToxicogenomicsDatabase (CTD)

David Dix, Acting Deputy Director of EPA/ORD’s National Center for Computational Toxicology

Carolyn Mattingly, Mount Desert Island Biological Laboratory

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September 9, 2009

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Page 2: Computational Toxicology: New Approaches for the 21st Century 09sept2009_v1bw... · Computational Toxicology: New Approaches for the 21st Century September 9th, 2009 Session IV: ToxCast

David DixActing Deputy Director, EPAs National Center for Computational Toxicology

ToxCast- Screening and Prioritization of Environmental Chemicals Based on Bioactivity Profiling and Predictions of Toxicity

NIEHS Risk e Learning Sept 9, 2009

Office of Research and DevelopmentNational Center for Computational Toxicology

This work was reviewed by EPA and approved for presentation but does not necessarily reflect official Agency policy.

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September 9, 2009

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Office of Research and DevelopmentNational Center for Computational Toxicology

Predicting Toxicity Will Not Be Easy

Chemical

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Office of Research and DevelopmentNational Center for Computational Toxicology

Key Challenges Of Pathway Profiling

•Find the Toxicity Pathways•Hepato vs developmental nuerotoxicity

•Obtain HTS Assays for Them• Including metabolic capability

•Screen Chemical Libraries• Coverage of p-chem properties

•Link Results to in vivo Effects• Gold standard and dosimetry

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Office of Research and DevelopmentNational Center for Computational Toxicology

ToxCastTM Background

• Research program of EPA’s National Center for Computational Toxicology

• Addresses chemical screening and prioritization needs for pesticidal inerts, anti-microbials, CCLs, HPVs and MPVs

• Comprehensive use of HTS technologies

• Coordinated with NTP and NHGRI/NCGC via Tox21

• Committed to stakeholder involvement and public release of data

• Chemical Prioritization Community of Practice

• NCCT website- http://www.epa.gov/ncct/

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Office of Research and DevelopmentNational Center for Computational Toxicology

The ToxCast_320

Classes with > 3 chemicals

Misc MOA classes with3 or fewer representatives

Acetylcholine esterase inhibitorsconazole fungicidesSodium channel modulatorspyrethroid ester insecticidesorganothiophosphate acaricidesdinitroaniline herbicidespyridine herbicidesthiocarbamate herbicidesimidazolinone herbicidesorganophosphate insecticidesphenyl organothiophosphate insecticidesaliphatic organothiophosphate insecticidesamide herbicidesaromatic fungicideschloroacetanilide herbicideschlorotriazine herbicidesgrowth inhibitorsorganophosphate acaricidesoxime carbamate insecticidesphenylurea herbicidespyrethroid ester acaricidesstrobilurin fungicidesunclassified acaricidesunclassified herbicides

Misc

309 Unique Structures

Replicates for QC

291 Pesticide Actives9 Industrial Chemicals8 Metabolites

56/73 Proposed Tier 1 EDSP

53 of 80 with DNTs

122 in IRIS

14 HPV11 HPV Challenge

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Office of Research and DevelopmentNational Center for Computational Toxicology

ToxRefDB

• Relational phenotypic/toxicity database

• Provides in vivo anchor for ToxCast predictions

• Three study types• Chronic/Cancer Rat and Mouse (Martin, et al, EHP 2008)

• Rat multigenerational Reproduction (Martin, et al, 2009)

• Rat & Rabbit Developmental Toxicity (Knudsen, et al, 2009)

• Two types of synthesis• Supervised (common individual phenotypes)

• Unsupervised (machine based clustering of phenotype patterns)

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Office of Research and DevelopmentNational Center for Computational Toxicology SOURCE: Matt Martin, NCCT, 2009

A = Rat B = Mouse C = Rabbit

CHRONIC/CANCER (CHR)Martin et al. (2008) Environ Hlth Perspdoi:10.1289/ehp.0800074

PRENATAL DEVELOPMENTAL (DEV)Knudsen et al. (2009) Reprod Toxicoldoi: 10.1016/j.reprotox.2009.03.016

MULTIGENERATION REPRODUCTIVE (MGR)Martin et al. (2009) Toxicol Scidoi: 10.1093/toxsci/kfp080

ToxRefDB Endpoint Coveragedata evaluation records ToxRefDB

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Office of Research and DevelopmentNational Center for Computational Toxicology

Rat Chronic Bioassay Results

Martin, et al EHP, 2009September 9, 2009 9

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Office of Research and DevelopmentNational Center for Computational Toxicology

Digitizing Legacy in Vivo Data in ToxRefDB

Chronic/CancerMultigenationDevelopmental

Che

mic

als

30 years and more than $2B worth of data

Martin et al 2009a,bKnudsen et al 2009

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Office of Research and DevelopmentNational Center for Computational Toxicology

ToxRefDB in Predictive Modeling

STRENGTHS– Source data from >2,000 guideline studies– Puts >$2B worth of legacy data into a computable form– in vivo database anchoring HTS in vitro assays– Enables comparison of endpoint incidence between species– Searchable database will be public (www.epa.gov/ncct/toxrefdb/)

LIMITATIONS– Endpoints aggregated as independent features– Data largely qualitative (LELs, LOAELS)– Not all ToxCast™ chemicals represented in ToxRefDB– Not all ToxRefDB chemicals represented in ToxCast™– Species dimorphism may link to biology or study design–Limited mode of action information available in source DERs

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Office of Research and DevelopmentNational Center for Computational Toxicology

ToxCast Assays

• Cell lines– HepG2 human hepatoblastoma– A549 human lung carcinoma– HEK 293 human embryonic kidney

• Primary cells– Human endothelial cells– Human monocytes– Human keratinocytes– Human fibroblasts– Human proximal tubule kidney cells– Human small airway epithelial cells

• Biotransformation competent cells– Primary rat hepatocytes– Primary human hepatocytes

• Assay formats– Cytotoxicity– Reporter gene – Gene expression– Biomarker production– High-content imaging for cellular

phenotype

• Protein families– GPCR– NR– Kinase– Phosphatase– Protease– Other enzyme– Ion channel– Transporter

• Assay formats– Radioligand binding– Enzyme activity– Co-activator recruitment

Cellular AssaysBiochemical Assays

467 Endpoints

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Office of Research and DevelopmentNational Center for Computational Toxicology

Confidence Builders:Some Expected Results…

• Estrogen receptor (ER)–Bisphenol A, Methoxychlor, HPTE

• Androgen Receptor (AR)–Vinclozolin, Linuron, Prochloraz

• PPAR –PFOA, PFOS, Diethylhexyl Phthalate, Lactofen

• Mitochondrial Poisons–Azoxystrobin, Fluoxastrobin, Pyraclostrobin

• Acetylcholinesterase Inhibition–Multiple organophosphorus pesticides

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Office of Research and DevelopmentNational Center for Computational Toxicology

Confidence Builders (2):Multiple Assays and Technologies per Target

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Office of Research and DevelopmentNational Center for Computational Toxicology

Biologically Multiplexed Activity Profiling (BioMAP)

Cell-free HTS Assays

Cell-based HTS Assays

Multiplex Transcription Reporter Assay

High Content Cell Imaging Assays

Confidence Builders (3):Pathway Based Analysis

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Office of Research and DevelopmentNational Center for Computational Toxicology

Data Analysis:What is a hit?

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Office of Research and DevelopmentNational Center for Computational Toxicology

Biochemical HTS from Novascreen

hCYP 2C9 hERαrAdrRa2B

hLynAActivator

hM1hKATPase

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Office of Research and DevelopmentNational Center for Computational Toxicology

qHTS from the NCGC on NRs

ERα PPARγ

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Office of Research and DevelopmentNational Center for Computational Toxicology

trans: ERa

cis: ERE

Bisphenol A HPTE

Attagene: cis and trans Assays

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September 9, 2009

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Office of Research and DevelopmentNational Center for Computational Toxicology

CellzDirect: Data ExamplesCYP1A1-AhR CYP2B6-CARHMGCS2-PPARα

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Office of Research and DevelopmentNational Center for Computational Toxicology

ToxCast Phase I Assay Hits (n=624 measurements)

Judson et al, submitted

Cell Free HTSMultiplexed TFHuman BioMapHCSqNPAsXMEsImpedanceGenotoxicity

828 Assay-Chemical Pairshad AC50s of less than 1µM

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Office of Research and DevelopmentNational Center for Computational Toxicology

Minimum Human Pathways in ToxCast Phase I

Judson et al, submitted

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Office of Research and DevelopmentNational Center for Computational Toxicology

“Hits” per ChemicalAs a Function of AC50/LEC Cutoff

Judson et al, submitted

9 Chemicals have at least 20 hits at an AC50 of <30µM

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Office of Research and DevelopmentNational Center for Computational Toxicology

“Hit” Distribution for Chemical Classes Against 33 Minimal Pathways

(at least 10 chemicals per class)

Judson et al, submitted

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Office of Research and DevelopmentNational Center for Computational Toxicology

Judson et al, submitted

Activity of ConazolesAgainst Minimal Pathway Set

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Office of Research and DevelopmentNational Center for Computational Toxicology

Rat Liver Histopathologyfrom Chronic Bioassays

68

37

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No PathologyProliferative LesionsPre-neoplastic LesionsNeoplastic Lesions

N = 248 Chemicals

Martin et al, 2009 26

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Office of Research and DevelopmentNational Center for Computational Toxicology

Rat Liver Tumor Correlations

Fisher’s Exact test, p<0.01 Judson, et al, submittedSeptember 9, 2009 27

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Office of Research and DevelopmentNational Center for Computational Toxicology

Gene Networks Associated with Progression of Rat Liver Tumor Endpoints

Judson et al, submittedSEVERITYSeptember 9, 2009 28

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Office of Research and DevelopmentNational Center for Computational Toxicology

Some Challenges Faced or to be Faced

• Organizing the chemical library• Quality control of the chemical library

– Acceptable purity, stability• Defining concentration response ranges to the assayed• Definition/Calculation of a hit

– Minimum fold change; minimum r-squared; limit on Hill function• Assay performance

– Replicates, artifacts• Sufficient coverage of biological pathways

– Including those that represent tissue level processes• Incorporation of metabolic competency• Establishment of target prediction

– Pathway perturbation– Rodent bioassay data– Rodent mechanistic studies– Human effects

• Sufficient representation of positives to predict against29

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Office of Research and DevelopmentNational Center for Computational Toxicology

FY08 FY09 FY10 FY11 FY12

Proof of Concept: ToxCastVerification/Extension

Reduce to Practice

Tox21

Prioritization Product Timeline

FY07

FY09 -10~$15 -20K>200PMN Nanomaterials>12IId

FY09~$20 -25k>400ExtrapolationKnown Human Toxicants>100IIb

FY09$10K166PilotNanomaterials15Ib

FY09~$20 -25k>400ValidationData Rich Chemicals>300IIa

>300

>400

552

Number of Assays

Data poor

Expanded Structure and Use Diversity

Data Rich(pesticides)

Chemical Criteria

FY11 -12

FY10

FY08

TargetDate

~$15 -20k

~$20 -25k

$20k

Cost per Chemical

Prediction and Prioritization

Extension

Signature Development

PurposeNumber of ChemicalsPhase

ThousandsIII

>300IIc

320I

FY -~$15 -20K>200PMN Nanomaterials>12IId

FY09-11~$20 -25k>400ExtrapolationKnown Human Toxicants>100IIb

FY09$10K166PilotNanomaterials15Ib

FY09-11~$20 -25k>400ValidationData Rich Chemicals>300IIa

>300

>400

552

Number of Assays

Data poor

Expanded Structure and Use Diversity

Data Rich(pesticides)

Chemical Criteria

FY11 -12

FY09-11

FY07-09

TargetDate

~$15 -20k

~$20 -25k

$20k

Cost per Chemical

Prediction and Prioritization

Extension

Signature Development

PurposeNumber of ChemicalsPhase

ThousandsIII

>300IIc

320Ia

FY09-11

FY10-11

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Office of Research and DevelopmentNational Center for Computational Toxicology

Phase II Plans• Done in conjunction with Tox21 10k Library

–Subset of 700 will seed Phase II• Chemical Diversity

–More food use pesticides –Failed pharmaceuticals (preclinical and clinical)– “Green” chemicals–HPV Categories–Liver toxicants –OECD Molecular Screening Group nominations

• Evaluation of Phase I Assays• Addition of new assays via competitive procurements• Timing

–Chemical procurement completed 4thQ FY09–Launch of Assays, 1st Q FY10–Results Available early FY11

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Carolyn J. MattinglyThe Mount Desert Island Biological Laboratory

Salisbury Cove, Maine

The Comparative Toxicogenomics Database (CTD)

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Helping scientists explore the etiologies of environmental diseases

• What diseases are associated with arsenic?

• Arsenic affects which genes and proteins?

• What biological processes are affected by arsenic?

• Which molecular pathways are affected by arsenic?

• Which other chemicals affect the same molecular pathways?

• Which diseases are implicated with other chemicals?

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DiseasesGenes

Chemicals

Curated Data

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DiseasesGenes

Chemicals

chemical-diseaserelationships

chemical-geneinteractions

gene-diseaserelationships

Curated Data

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DiseasesGenes

Chemicals

Curated Data

MeSH (modified)

Entrez-Gene MeSH/OMIM

CTD interactions

chemical-diseaserelationships

chemical-geneinteractions

gene-diseaserelationships

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DiseasesGenes

Chemicals

chemical-diseaserelationships

chemical-geneinteractions

gene-diseaserelationships

181,150

9,179

5,757

Curated Data

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Arsenates

HMOX1 AlzheimerDisease

HMOX1

Inferred chemical-disease relationships

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Arsenates

HMOX1 AlzheimerDisease

HMOX1

Inferred chemical-disease relationships

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Chem/Gene Comps

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Tools

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Tools

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Tools

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Tools: VennViewer

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Tools: VennViewerInteracting Genes/Proteins

Pathways

127 1357118

Folic acid Arsenicals

4 7621

Folic acid Arsenicals

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Tools

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Tools: MyGeneVenn

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0 10 100

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0 10 100

64 168920

Array data CTD data

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0 10 100

64 168920

Array data CTD data

Mattingly, C. J., T. Hampton, K. Brothers, N. E. Griffin and A. J. Planchart (2009). Perturbation of defense pathways by low-dose arsenic exposure in zebrafish embryos. Environ Health Perspect doi:10.1289/ehp.0900555.

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Gohlke, J., R. Thomas, Y. Zhang, M. D. Rosenstein, A. P. Davis, C. Murphy, C. J. Mattingly, K. G. Becker and C. J. Portier (2009). The Genetic And Environmental Pathways to Complex Diseases. BMC Syst Biol.May 5 3:46.

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2096Chemicals

213Genes

213Genes Autism

Environmental etiology of autistic disorders

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2096Chemicals

213Genes

213Genes Autism

Environmental etiology of autistic disorders

• What do these chemicals have in common?

– Structure

– Regulatory features(e.g., High production, Carcinogen)

– Function(e.g., Associated pathways)

– Other associated diseases(e.g., Neurological)

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Next

• Analysis tools and visualization capabilities

• Integration of additional data sets

• Text mining

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• Gohlke, J., R. Thomas, Y. Zhang, M. D. Rosenstein, A. P. Davis, C. Murphy, C. J. Mattingly, K. G. Becker and C. J. Portier (2009). The Genetic And Environmental Pathways to Complex Diseases. BMC Syst Biol.May 5 3:46.

• Mattingly, C. J., T. Hampton, K. Brothers, N. E. Griffin and A. J. Planchart (2009). Perturbation of defense pathways by low-dose arsenic exposure in zebrafish embryos. Environ Health Perspect doi:10.1289/ehp.0900555.

• Davis, A. P., C. G. Murphy, C. A. Saraceni-Richards, M. C. Rosenstein, T. C. Wiegersand C. J. Mattingly (2009). Comparative Toxicogenomics Database: a knowledgebase and discovery tool for chemical-gene-disease networks. Nucleic Acids Res 37(Database issue): D786-92.

• Mattingly, C. J. (2009). Chemical databases for environmental health and clinical research. Toxicol Lett. 186(1):62-5.

• Davis, A. P., C. G. Murphy, M. C. Rosenstein, T. C. Wiegers and C. J. Mattingly (2008). The Comparative Toxicogenomics Database facilitates identification and understanding of chemical-gene-disease associations: arsenic as a case study. BMC Med Genomics 1: 48.

Recent CTD references

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AcknowledgementsScientific Curators

Allan Peter Davis, PhDCindy Murphy, PhDCynthia Richards, PhD

Scientific Software Engineers

Michael C Rosenstein, JDThomas Wiegers

System Administrator

Roy McMorran

James L. Boyer, MD (Yale)

Thomas Hampton (Dartmouth)

http://ctd.mdibl.org/

Zebrafish workAntonio Planchart, PhD

Funding

NIEHS and NLM (ES014065 and ES003828)NCRR (RR016463)Contact Us!

[email protected]@mdibl.org 73

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