ExpoCast : Exposure Science for Prioritization and …...ExpoCastTM: Exposure Science for...

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April 6, 2010 Office of Research and Development National Center for Computational Toxicology EPA Chemical Prioritization Community of Practice April 22, 2010 Elaine Cohen Hubal National Center for Computational Toxicology ExpoCast TM : Exposure Science for Prioritization and Toxicity Testing

Transcript of ExpoCast : Exposure Science for Prioritization and …...ExpoCastTM: Exposure Science for...

Page 1: ExpoCast : Exposure Science for Prioritization and …...ExpoCastTM: Exposure Science for Prioritization and Toxicity Testing 1 Office of Research and Development National Center for

April 6, 2010Office of Research and DevelopmentNational Center for Computational Toxicology

EPA Chemical Prioritization Community of PracticeApril 22, 2010

Elaine Cohen HubalNational Center for Computational Toxicology

ExpoCastTM: Exposure Science for Prioritization and Toxicity Testing

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Toxicity Testing in the Twenty-first Century

• Key aspect of the NRC vision is that new tools are available to examine toxicity pathways in a depth and breadth that has not been possible

• Efforts to apply high-throughput-screening (HTS) approaches for chemical prioritization and toxicity testing have been accelerated

• An explosion of HTS data for in vitro toxicity assays will become available over the next few years ---- Data are available now!

• How will this new toxicity information be translated to assess potential for real-world human health risk?

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2Office of Research and DevelopmentNational Center for Computational Toxicology NAS, June 2007.

Toxicity Testing in the Twenty-first Century: A Vision and a Strategy

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Exposure Science in NRC Vision - TRANSLATION

• Population-based data and human exposure information critical for guiding development and use of toxicity information

• Components include:– Use of information on host susceptibility and background exposures

to interpret and extrapolate in vitro test results.– Use of human exposure data to select doses for toxicity testing so

we develop hazard information on environmentally-relevanteffects.

– Use of biomonitoring data to relate real-world human exposures with concentrations that perturb toxicity pathways to identify potentially important (biologically-relevant) exposures.

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Source

Fate/Transport

Exposure

Tissue Dose

Biologic Interaction

Perturbation

BiologicInputs

NormalBiologicFunction

Morbidityand

Mortality

Cell Injury

Adaptive StressResponses

Early CellularChanges

Modified from NRC, 2007

Exposure Science in NRC Vision

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Will fundamental knowledge of toxicity pathways improve understanding of real-world human-health risk?

• Assessing complex human-health risks requires that hazard, susceptibility, and exposure are all reliably characterized.

• Currently, balance of efforts to improve measuring hazard and exposure less than ideal.

• Accurate assessment of many environmental exposures remains an outstanding and largely unmet challenge in toxicology and risk assessment.

• To realize the NRC vision, we face a critical need for advanced exposure science.

Adapted from Wild, 2005

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ExpoCastTM: Exposure Science for Prioritization and Toxicity Testing

• Recognizes critical need for exposure information to inform – Chemical design and evaluation– Health risk management

• Goal– Advance characterization of exposure required to translate findings in

computational toxicology to support exposure and risk assessment– Together with ToxCast™ help EPA determine priority chemicals

• Approach – Mine and apply scientific advances and tools in a broad range of fields– Develop novel approaches for evaluating chemicals based on potential

for biologically-relevant human exposure

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April 6, 2010Office of Research and DevelopmentNational Center for Computational Toxicology

Select doses for toxicity testing

Relate real-world exposures with toxicity pathway perturbations

Translate in vitro results for risk assessment

ExposureBackground Exposure

HumanEnvironment

Biomonitoring

Population

Uptake

N

N N

NH NH

Cl

Exposure Media

Contact

Products

Sources

Chemicals

HostSusceptibility

Biotransformation

Rapid Prioritization

ExposomeInformatics Approaches

Network Models

Knowledge Systems

Mechanistic Models

Data Repositories

TOOLSTOOLS

N

N N

NH NH

Cl

Toxicity endpoints

In vivo bioassays

HTS assays

Distribution/Fate

Ann Richard, NCCT

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New technologies must be applied to BOTH toxicology and exposure science if the ultimate goal of evaluating chemical safety is to be achieved.

• Systems exposure science

• Biologically-relevant exposure metrics

• Environmental informatics and advanced computational models

Cohen Hubal, Tox Sci, 2009

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StressorBiological Receptor OutcomePerturbation Perturbation

Population

Individual

Tissue

Cell

Biological Molecules

Environmental Source

Ambient Exposure

Environmental Source Personal

Exposure

Internal Exposure (Tissue Dose)

Dose to Cell

Dose of Stressor Molecules

Disease Incidence/Prevalence

Disease State(Changes to Health Status)

Dynamic Tissue Changes(Tissue Injury)

Dynamic Cell Changes(Alteration in Cell Division,

Cell Death)

Dynamic Changes in Intracellular Processes

Figure 1Cohen Hubal, JESEE, 2008

Systems Biology: Exposure at All Levels of Biological Organization

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Systems Exposure Science : Extending Network Analysis

Consider coupled networks spanning multiple levels of biological organization

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Biologically-Relevant Exposure Metrics

Markers required that can be directly associated with key events in disease processes and with individual exposure profiles

– ‘Omic technologies showing potential to yield a new generation of exposure metrics (Wild, 2009)(Altered global gene expression associated with exposures to arsenic, cigarette smoke, benzene, metal fumes and air pollution)

– Better environmental biosensors required to study gene-environment interactions associated with complex disease (Collins 2007)(Nano-scale sensor arrays can be developed to detect specific sets of environmental agents (Andreescu et al, 2009))

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PAHs, VOCs, NO2

Indoor/Outdoor Air

PM, Air Toxics

Ambient Air

Markers of Exposure

Markers of Susceptibility

Health status, other risk factors: BMI, HDL, blood chemistry

Genotypes at Candidate SNPs(HLA-DRB1, HLA-DQB1, FCER1B, ADAM33, CD14, IL4, IL13, GSTM1, GSTP1, GSTT1, TNF-a)

Other Immune Markers: Total IgE, allergen specific

Markers of Effect

Nicotine, PAHs, etc.

ETS

Secreted Autoantibodies:Neutrophils, Eosinophils, Monocytes

Asthma

Respiratory Symptoms

Gene Expression

Lung Function,eNO,eVOC

Inflammatory Markers:Cytokines, Chemokines

Child

MICA Framework

Allergy

Metals, Molds, Endotoxin,Pesticides

House Dust

CotininePAH Metabolites1-OH PyreneNapthols, etc.

Metals:Lead, Mercury,Arsenic, etc.

Age, Gender, Race/ethnicity

Cardiovascular

Obesity

Gallagher, Cohen Hubal, et al.

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Exposure-Hazard Knowledge System

• Computational Techniques – Two Branches A combination of discovery and engineering (mechanistic)-based modeling approaches for hypothesis development and testing are required.

• Knowledge-discovery – Data-collection, mining, and analysis– Required to extract information from extant data on critical exposure

determinants, link exposure information with toxicity data, and identify limitations and gaps in exposure data.

• Mechanistic (dynamic) simulation– Mathematical modeling at various levels of detail – Required to model the human-environment system and to test our

understanding of this system.

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Exposure-Hazard Knowledge System

• Translation of HTP hazard information requires holistic risk assessment knowledge system – Include ontologies, databases, linkages – Facilitate computerized collection, organization, and retrieval of

exposure, hazard, and susceptibility information

• Standardized exposure ontologies required to – Define relationships, allow automated reasoning, facilitate meta

analyses – Develop biologically-relevant exposure metrics– Design in vitro toxicity tests to measure environmentally-relevant

hazard– Incorporate information on susceptibility and background

exposures to individual and population-level risks

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Schematic of ontologies, databases and ontology/database linkages needed for the efficient development of a Foods-for-Health Knowledge System

MC Lange, et al. (2007) A multi-ontology framework to guide agriculture and food towards diet and health. J Sci Food and Ag 87(8)1427-34.

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Priority Exposure Research for Computational Toxicology

• Accessible and linkable exposure databases

• Exposure screening tools for accelerated chemical prioritization

• Advanced computational approaches for interpreting in vitro toxicity data in the context of individual and population health

• Biologically-relevant exposure metrics (biomarkers reliably associated with exposure)

Human vulnerability and life-stage aspects are integral to each of these.

Sheldon and Cohen, EHP, 2009

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Incorporating Exposure Databases into ACToR

http://actor.epa.gov

Exposure

Source/StressorFormation

Transport/Fate

EnvironmentalConcentration

Production/ Import

Volumes

Chemicals in Consumer Products

EnvironmentalReleases

Product Usage

Information

Indoor Air Monitoring

Data

Human Exposure

Monitoring

Production/ Process

Information

Environmental Transformation

Outdoor Air Monitoring

Data

Exposure Limits

Activity Patterns

Information

Human Biological Monitoring

Data

EPA HPVIS

EPA IUR

EU ESIS

EPA TRI

DOE GHG

Household Products DB

Cosmetic Voluntary Reg. DB

EPA Pesticide Usage Data

UK Pharma-ceutical Usage

EPA HPVIS

ATSDR ToxProfiles

DEA NFLIS

Environmental Fate Simulator

ECOTOX DB

CESAR

DOE IndoorAir

NHEXAS

CTEPP

EPA NATA

EPA AIRS/AFS

UN IPCC GHG

NHEXAS

EUROPA Pest-Diet

EPA NHAPS

EPA CHAD

CDC NHANES

NHEXAS

CTEPP

NIOSH NOES

AIHA WEEL

OSHA PEL

Exposure

Source/StressorFormation

Transport/Fate

EnvironmentalConcentration

Production/ Import

Volumes

Chemicals in Consumer Products

EnvironmentalReleases

Product Usage

Information

Indoor Air Monitoring

Data

Human Exposure

Monitoring

Production/ Process

Information

Environmental Transformation

Outdoor Air Monitoring

Data

Exposure Limits

Activity Patterns

Information

Human Biological Monitoring

Data

EPA HPVIS

EPA IUR

EU ESIS

EPA TRI

DOE GHG

Household Products DB

Cosmetic Voluntary Reg. DB

EPA Pesticide Usage Data

UK Pharma-ceutical Usage

EPA HPVIS

ATSDR ToxProfiles

DEA NFLIS

Environmental Fate Simulator

ECOTOX DB

CESAR

DOE IndoorAir

NHEXAS

CTEPP

EPA NATA

EPA AIRS/AFS

UN IPCC GHG

NHEXAS

EUROPA Pest-Diet

EPA NHAPS

EPA CHAD

CDC NHANES

NHEXAS

CTEPP

NIOSH NOES

AIHA WEEL

OSHA PEL

Peter Egeghy, NERL

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DiseasesGenes

Chemicals

chemical-diseaserelationships

chemical-diseaserelationships

chemical‐geneinteractions

chemical‐geneinteractions

gene-diseaserelationships

gene-diseaserelationships

pathway data

functional annotations

Exposure Data (curated and public

sources)

Exposure Data (curated and public

sources)Carolyn Mattingly,

Mount Desert Island Biological Laboratory

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Integrated Chemical Prioritization Scheme

A numerical index that can be used for ranking (instead of absolute thresholds) is more flexible for different prioritization tasks.Can better accommodate new data, new chemicals, data adjustments, etc.

ToxPi (Toxicological Priority Index)• Integrate over multiple domains of information

• Extend to incorporate additional types of data

• Transparently derive and visualize

• Customize components for diverse prioritization tasks

Chemical properties

Pathways

In vitro assays

Exposure

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Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration

RTP, NC, April 6-7, 2010

http://epa.gov/ncct/expocast/workshop.html

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Workshop Highlights

Participants IncludedHealth CanadaRIVMEU JRCUS FDAUS CPSCUS EPA (OPPTS, ORD, GLNPO)Washington StateU OttawaU MichiganU TorontoEOHSI/UMDNJLBNLExxon Mobile

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Workshop Highlights – Mandates for Prioritization

Health Canada (Christine Norman)• Completing assessments for 500 high priorities• Focus on 3000 medium priority, complete by 2020

– 36% organic, 11% inorganic, 14% polymers, 27% UVCB– 58% zero data, another 23% data poor

US CPSC (Treye Thomas)• Thousands of products in and around the home• Challenges in exposure

– Product Ingredients, Consumer Use Information– Method Validation, Probabilistic Methods– International Cooperation– Nanotechnology

US EPA GLNPO (Ted Smith)• P&B screening not appropriate for important groups of chemicals in

commerce (e.g., ionic)• Surveillance strategy based on Adverse Outcome Pathway framework

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Workshop Highlights – Tools and Approaches

Benchmarking prioritization models (Olivier Jolliet)• Start with parsimonious model, develop and evaluate a suite of

consistent tools to assess same metrics, but at different levels and detail• Evaluate the relative importance of parameters and intermediary steps in

the screening results • USEtox development process (Model evaluation; Publication and expert

review; Approval by International Life Cycle Panel)• Intake Fraction (fraction emission taken in by population)

Ground truthing prioritization schemes (Bette Meek)• Broadly draw on existing experience on limited # chemicals to inform

efficient evaluation of the rest (e.g., use more important than volume)• Identify chemicals for quantitative anchoring of “surrogates”• Select simplest most discriminating determinants• “Design” to limit exposure

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Workshop Highlights – Tools and Approaches

Value of information (Michael Sohn)• Approach for comparing decisions/consequences where uncertainty is

important• Can be used to combine different types of limited data (e.g., biomarker,

monitoring, modeling)• Grade relative rankings• Extrapolate from known chemicals to unknown

Limits of persistance and bioaccumulation (Jon Arnot)• P & B categorization data should not be used for exposure-based priority

setting for humans and ecological receptors • Mass balance multimedia exposure models can provide alternative

“holistic” hypotheses linking emissions to exposures (e.g., RAIDAR)• Integrated testing strategies required for property data and QSAR

development to expand “domains” of knowledge and predictability

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Acknowledgements

• NCCT – Bob Kavlock• ExpoCastTM – Peter Egeghy, Richard Judson, Sumit Gangwal,

Bonnie Joubert, plus • ToxCast ™ - David Dix, Keith Houck, plus many• MICA Study - Jane Gallagher, Stephen Edwards, David Reif, plus

Disclaimer

Although this work was reviewed by EPA and approved for presentation, it may not necessarily reflect official Agency policy.