21st Century Screening Assessment of Pesticides – A Regulatory View Vicki Dellarco, Ph.D. Senior Science Advisor Office of Pesticide Programs US Environmental Protection Agency Office of Pesticide Programs Managing Chemical Risks Gateway to Market National Pesticide Program ~1,100 active ingredients & 19,000 products • Reevaluate existing pesticides on a regular schedule • Safety evaluations required for human health & ecological risks – FIFRA, FFDCA, FQPA, ESA • Risk management decisions apply to – Antimicrobials, biochemical & conventional active ingredients and food-use & non-food use inert ingredients • Available information – Varies across chemical programs with extensive requirements for food use, conventional pesticide actives to minimal requirements for non-food use inert ingredients Office of Pesticide Programs 1 Managing Chemical Risks Common Challenges • Large Number of Chemicals to Review with Many Possible Adverse Outcomes • Finite Resources & Time • Science Increasingly Complex & Changing • Public Expectation Sound Science, Transparency & Timeliness for Environmental Health Protection Office of Pesticide Programs 2 Managing Chemical Risks Strategic Direction Transition toward new integrative & predictive 21st century techniques, to increase efficiency and effectiveness Animal Testing: Reduce, Refine, of testing & assessment Replace • 2005 OPPTS-ORD White Paper • 2007 NAS Report on Testing in the 21st Century • 2009 Agency’s Strategic Plan for Evaluating the Toxicity of Chemicals Office of Pesticide Programs Use of computational tools is not new to evaluate & assign priorities for follow-up actions 3 NRC 2007 “Toxicity Testing in the 21st Century: A Vision and A Strategy • Objective – Foster transformative paradigm shift based largely on increased use of in vitro & in silico systems that will: • broader coverage of chemicals, end points, life stages • reduce cost & time of testing, increase efficiency & flexibility • use fewer animals • more robust scientific basis by providing mode of action & dosimetry information Office of Pesticide Programs Current Data Paradigm in vivo testing Cancer Reproductive Toxicity Developmental Toxicity Neurotoxicity KidneyToxicity ImmunoTox $Millions Food Use, Conventional Pesticide Actives: Generates in vivo animal data for all possible outcomes to determine which of all possible effects are relevant. Office of Pesticide Programs 5 Cl Cl C C2Cl3 Cl OH Cl Cl Cl Cl Cl Cl OH Cl Cl Cl OH Cl Cl Cl Cl OH Cl Cl OH Cl C C2Cl3 Cl Cl Cl Cl Cl OH Cl Cl Cl Cl Cl Cl C C2Cl3 Cl Cl Cl Cl Cl Cl Cl Cl Cl OH Cl Cl O H C l C lC C2Cl C C C C l Cl C l C l C l lC C l C l l l l C l 3 O CH C l C l C COC l l HC l Cl CC C l lC l C l C l l l l O HC C C C C l Cl l C l C lC C l Cl l l l l C lC C2Cl CC ll 3 C l C C2Cl O H Cl Cl OH Cl Chemical Inventories Cl Cl Cl Cl Cl Cl Cl C C2Cl3 Cl Cl Cl Cl Cl Cl Cl Cl Cl Existing Knowledge, exposure use, toxicity data, SAR, QSAR O CH l C l 3 C lC C2Cl C l C l C C2Cl 3 C l 3 O H C l C Cl Cl C l l C C C C l lC l lC C l l l C l O CH l C l O CH l C l O CCH C C C C ll Cl l C l C lC C l Cl l l l l O CH l C Cl Cl C l l O H C l O CH l O O H H C l O C CH C C l Cl C l C l O C l lC C l HlC l l l C C C C l lC l lC C l l l C l O CH l O H C O l O CH CH l In Vitro Profiling: Molecular interactions, Cellular Responses Efficient Focused In Vivo Testing l Evaluation for Relevant Effects Office of Pesticide Programs Risk Assessment Priority Setting Process Research: Learn & Refine 6 Mapping Toxicity Pathways to Adverse Outcomes Structure Chemical 2-D Structure Structure Chemical 2-D Structure Structure Chemical 2-D Structure Structure Chemical 2-D Structure Structure Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Molecular 2-D Structure StructureChemical ER Binding Chemical 3-D Structure/ Properties Molecular Chemical Structure Molecular Chemical 2-D Structure 2-D Structure Structure Chemical 3-D Structure/ Properties ER Binding Receptor/Ligand Molecular Chemical 2-D Structure ER Binding Interaction Chemical 3-D Structure Chemical 2-D Structure Structure/ Properties Molecular ER Binding Chemical 3Chemical 3-D Structure/ Properties D Structure Molecular 2-D Structure Structure/ Chemical ER Binding Chemical 3-D Structure/ Properties Properties Structure Chemical 2-D Structure Structure Chemical 2-D Structure Structure Chemical 2-D Structure Structure Chemical 2-D Structure Structure Chemical 2-D Structure Structure Chemical 2-D Structure Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Molecular Chemical 3-D Structure/ Properties ER Binding Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular Cellular ER Transctivation Organ Individual Organ Altered Vitellogenin Induction Reproduction/ VTG mRNA VTG mRNA VTG mRNA VTG mRNA VTG mRNA •GeneVTG mRNA Cellular Activation ER Transctivation VTG mRNA •Protein Cellular Production ER Transctivation VTG mRNA Sex Steroids Sex Steroids Sex Steroids Sex Steroids Sex Steroids Reproduction/ Development Reproduction/ Development Reproduction/ Development Reproduction/ Development Reproduction/ Development Development Sex Steroids •Gonad DevelopmentIndividual Organ Altered Vitellogenin Induction Development Sex Steroids Hormone Reproduction/ •Altered Individual Organ Levels Altered Vitellogenin Induction Sex Steroids Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered Cellular ER Transctivation Organ Vitellogenin Induction Individual Altered VTG mRNA VTG mRNA VTG mRNA VTG mRNA VTG mRNA VTG mRNA Sex Steroids Sex Steroids Sex Steroids Sex Steroids Sex Steroids Sex Steroids Sex Steroids Impaired Reproduction Reproduction/ Development Cellular ER Transctivation VTG mRNA Individual Reproduction/ Development Reproduction/ Development Reproduction/ Development Reproduction/ Development Reproduction/ Development Reproduction/ Development Reproduction/ Development Libraries of Toxicological Pathways Managing Chemical Risks Challenge: Assessing Data-Limited Chemicals • Near Term (≤5 years) Goal –Integrated Approaches to Testing & Assessment • “Enhance Tool Box” - Create means to efficiently & credibly predict toxic potency & exposure levels and to focus information needs –Situations • e.g., pesticide inerts, certain antimicrobials, metabolites & degradates of pesticide actives Office of Pesticide Programs 8 Managing Chemical Risks Challenge: Reducing Uncertainty • Long Term (~15 years) – Develop means to move, in a credible & transparent manner to hypothesis & mechanismdriven, risk-based approaches that focus on effects most relevant to risk assessment & risk management • “omics” technology in identifying toxicity pathways • PDPK modeling • Improved human exposure modeling Office of Pesticide Programs 9 Integrated Approaches to Testing & Assessment Example Activities Existing Knowledge, exposure use, toxicity data, SAR, QSAR (Q)SAR-Based System to Predict ER Binding Affinity In Vitro Profiling: Molecular interactions, Cellular Responses ToxCast HTP Research Program Efficient Focused In Vivo Testing New F1 Extended Reproductive Study Office of Pesticide Programs Partnerships Agencies & International Organizations • Collaborate on development & application of predictive computational models • Promote development of common databases • Harmonize frameworks/guidance • Build a common application tool box –OECD QSAR Tool Box Office of Pesticide Programs International Partnerships • Collaborate on development & application of predictive computational models – OECD Workshop (Dec 07, Wash DC) - Integrative Approaches to Testing & Assessment • Build a common application tool box – OECD QSAR Tool Box • Harmonize frameworks/guidance Office of Pesticide Programs Stakeholder Engagement • Pesticide Program Dialogue Committee (PPDC) – Workgroup on 21st Century Toxicology/New Integrated Testing Strategies – Purpose is to advise on communication & transition • Improve understanding of the perspectives of all stakeholders regarding new testing paradigm • Ensure input on key science & regulatory products • Develop common understanding for use of new tools Office of Pesticide Programs 13 US EPA EDSP Implementation Assay Validation Priority Setting Procedures Selecting chemicals to be screened Office of Pesticide Programs 14 OECD Endocrine Testing & Assessment Conceptual Framework • Level 1 - Sorting & prioritizing with existing data and/or (Q)SARs • Level 2 - In vitro assays to provide mechanistic data • Level 3 - In vivo assays providing data about single endocrine mechanisms & effects • Level 4 - In vivo assays providing data about multiple endocrine mechanisms & effects • Level 5 - In vivo assays providing data about endocrine & other effects Office of Pesticide Programs (OECD, 2004) USEPA Endocrine Disruptor Screening & Assessment Program • Sorting & Prioritizing Chemicals • Tier 1 Screening –Data to determine if a chemical has the potential to interact with the estrogen, androgen or thyroid systems • Tier 2 Testing –Data to determine if endocrine-mediated adverse effects occur and quantify dose-response • Hazard & Risk Assessment Office of Pesticide Programs (USEPA, 1998) Sorting Chemicals for Endocrine Disruptor Screening & Testing: Four Categories • Chemicals unlikely to interact with hormone systems (e.g., certain polymers, strong mineral acids/bases) • Chemicals without sufficient existing data to determine if Tier 2 testing required • Chemicals with sufficient existing data to determine if Tier 2 testing required • Chemicals with sufficient data to support a hazard assessment Office of Pesticide Programs (USEPA, 1998) Prioritizing Chemicals for Endocrine Disruptor Screening & Testing • Chemicals without sufficient existing data –Considered by the EDSTAC (USEPA 1998) to have the largest number of chemicals and the greatest need for prioritization –EDSTAC (USEPA, 1998) and the SAB/SAP (USEPA, 1999) strongly recommended a prioritization scheme that included an effects & exposure component Office of Pesticide Programs Prioritizing Chemicals for Endocrine Disruptor Tier 1 Screening: Effects • EDSTAC (USEPA, 1998) recommended the use of measured or predicted receptor binding and/or transcriptional activation data derived through in vitro assays/High Throughput (HTP) Screening and (Q)SARs, respectively • SAB/SAP (USEPA, 1999) concurred; however, concluded that HTP screening and (Q)SARs were not sufficiently developed at that time – encouraged continued research • As part of USEPA’s computational toxicology and endocrine disruptor research programs, the Office of Research and Development (ORD), in collaboration with OPP and OSCP, has been developing in vitro assays, HTPs applications & (Q)SARs Office of Pesticide Programs (Q)SAR-Based System to Predict Estrogen Receptor Binding Affinity • ORD/OPP Collaborative Effort • Application for use in a prioritization scheme in the context of EDSTAC & SAB/SAP recommendations • Development focused on chemicals without sufficient existing data to determine if Tier 2 testing required • Model’s applicability domain – Structures associated with pesticide inert ingredients & antimicrobial pesticides T 347 C E 353 H A OH R 394 H H Office of Pesticide Programs H 524 CH3 H HO B Adverse Outcome Pathway ER-mediated Reproductive Impairment QSAR focus area In vitro Assay focus area In vivo Inerts; Antimicrobial Chemicals MOLECULAR Target Receptor Binding ER Binding CELLULAR Response Liver Cell Protein Expression TISSUE/ORGAN Liver Altered proteins(Vtg) & hormones; Vitellogenin Gonad (egg protein transported to ovary) Ova-testis; Complete ovary in male POPULATION INDIVIDUAL Sex reversal; Altered behavior; Skewed Sex Ratios; Yr Class Repro. Toxicity Pathway Adverse Outcome Pathway Greater Toxicological Understanding Greater Risk Relevance (Q)SAR-Based System to Predict ER Binding Affinity • External peer-review by USEPA SAP, August 2009 – http://www.epa.gov/scipoly/sap/meetings/2009/082509meeting. html • Development benefited from EDTA VMG-NA and two OECD peer consultations – May, 2008 Structural Alert Workshop • http://www.olis.oecd.org/olis/2009doc.nsf/linkto/env-jm- mono(2009)4 – February, 2009 Expert Consultation to Evaluate an Estrogen Receptor Binding Affinity Model for Hazard Identification • http://www.olis.oecd.org/olis/2009doc.nsf/linkto/env-jm- mono(2009)33 Office of Pesticide Programs Future Prioritization for EDSP Tier 1 Screening • Inert ingredients & other chemicals –develop in vitro & in silico tools that are integrated with exposure-based metrics • Pesticide active ingredients –current plan is to use EPA’s schedule for reevaluating registered active ingredients in the Registration Review program (http://www.epa.gov/oppsrrd1/registration_review/) • Consistent with EDSTAC & SAB/SAP recommendations Office of Pesticide Programs Enhanced Integrated Testing & Assessment • Where we need to be in the near term –Accelerated/enhanced priority setting/screening & focused animal testing • Where we would like to be in the long term –Greater reliance on hypothesis & mechanism-based assessments • What needs to happen –Collaborative research to develop scientific basis –Partnerships, stakeholder input, peer review, consensus building, staff training, development of new polices, etc Office of Pesticide Programs 24