Application of human epidemiological studies to pesticide risk assessment

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Workshop What does the future hold for harmonised human health risk assessment of plant protection products? Application of human epidemiological studies to pesticide risk assessment Antonio F. Hernández, MD, PhD. Full Professor of Toxicology University of Granada School of Medicine (Granada, Spain) Member of the EFSA-PPR Panel

EU Legislation EU Regulation No. 1107/2009 (placing of plant protection products on the market) Where available, and supported with data on levels and duration of exposure, and conducted in accordance with recognised standards, epidemiological studies are of particular value and must be submitted. EU Regulation No. 283/2013 (setting out data requirements for active substances) Relevant epidemiological studies shall be submitted, where available. EU Regulation No. 1141/2010 (renewal of a.s.) The dossiers submitted for renewal should include new data relevant to the active substance and new risk assessments.

Use of epidemiological studies for pesticide risk assessment Human data Case series, PCC, registries, surveillance programs Observational epidemiological studies External validity Pesticide exposure Human outcomes Hazard identification Internal validity Complexity of studying associations in the field of pesticide epidemiology: large number of active substances in the market difficulties to measure exposure frequent lack of quantitative (and qualitative) data on exposure to individual pesticides

Relevant significant associations were found. A number of limitations were also identified: Weak study designs Lack of detailed exposure assessment Deficiencies in outcomes assessment Deficiencies in reporting and analysis Selective reporting and bias Heterogeneity Inconsistency 1. The inherent weaknesses of the epidemiological studies assessed do not allow firm conclusions to be drawn on causal relationships. 2. A concern was raised about the suitability of regulatory studies to inform on specific and complex human health outcomes.

EFSA Scientific Opinion 2017

EFSA Scientific Opinion 2017 Epi studies can assist the peer-review process (renewal of a.s.) EFSA PPR Panel Scientific Opinion: Methodology for using epi data for risk assessment Recommendations to improve the quality and reliability of epi studies on pesticides Methodology for the integration of epi data with other lines of evidence Enhance the quality and relevance of future epi studies for R.A.: Adequate assessment of exposure Valid and reliable outcome assessment Account for potentially confounding variables Appropriate statistical analysis and reporting of results

Incorporation of epidemiological studies into risk assessment Challenge for scientists, risk assessors and risk managers Use of evidence synthesis techniques: Summary of data, statistical power and precision Cannot overcome methodological flaws of individual studies Systematic reviews impact on risk assessment as they strengthen the understanding of pesticide hazards, exposure, Study evaluation should be performed within a best evidence synthesis framework: Indication on the nature of potential biases Assessment of the overall confidence in the database Assessment of the reliability of individual epidemiological studies (methodological quality and the risk of bias)

Incorporation of epidemiological studies into risk assessment Study quality parameters and their associated weight: Parameter High Moderate Low Study design and conduct Population Exposure assessment Outcome Assessment Risk of bias Confounder control Statistical Analysis Reporting of results Data from epi studies are not currently used for pesticide risk assessment in a systematic and consistent manner No harmonised framework on how to assess epi studies

Study 1 Study 2 Study 3 Study n Summarize the data Assess risk of bias Unacceptable for risk assessment Low reliability Medium reliability High reliability Assess WoE Summary of OR/RR Meta-analysis Heterogeneity Meta-regression Presence of bias Hazard identification Dose-response assessment Identification of critical effects Setting reference values

Integrating epidemiological evidence with experimental toxicology data An integrated approach is needed to integrate data from epidemiology and toxicology Weight the different sources of evidence: Epidemiological studies In vivo studies In vitro / in silico studies Bradford-Hill Criteria Causative relationships Identification of biological plausibility (mechanistic approach) For each standalone line of evidence: Quality assessment of single studies Reliability Assess strength of (pooled) evidence Relevance Integrate the standalone LoE - Consistency

Streams of evidence Experimental In silico In vitro In vivo Provided that the same endpoint is covered by the distinct lines of evidence Precedence - Hazard identification - Hazard characterization Reliability (confidence) Acceptable Supplementary Unacceptable Concordant data Integration Synthesis of evidence: - Systematic Review - Meta-analysis Discordant data Human Account for this uncertainty Identify areas for further research In case of similar reliability/relevance Precedence to more robust evidence Precedence to data suggesting a hazard Precedence to data with lower safe level

Biological plausibility for the interpretation of epi evidence External exposure Epidemiological studies Complementary experimental research needed Clinical disease External exposure Absorbed dose Target organ dose Early biologic effect Altered function or structure Clinical disease AOP framework may be an appropriate tool Molecular initiating event Receptor binding DNA lesion Protein/Enzyme oxidation Cellular response Altered signaling Gene expression Protein synthesis Organ response Disturbed physiology Disturbed function Altered homeostasis Cancer Individual Clinical disease Impaired development Impaired reproduction

Conclusions Current epidemiological studies can be useful for hazard identification of pesticides (evidence synthesis) Better designed epi studies may improve quantitative risk assessment of pesticides Biological plausibility can lend support to the associations between pesticide exposure and complex diseases AOP and MoA data can be used to assess the findings of epi studies in order to weight their conclusions Integration of all lines of scientific evidence would benefit from moving to a mechanistic-based risk assessment

Questions?