National Public Health Institute, Finland Combining epidemiological and toxicological dose-responses: Dioxin-induced tooth lesions www.ktl.fi Jouni Tuomisto KTL Kuopio, Finland National Public Health Institute, Finland Acknowledgements www.ktl.fi • The working group in KTL – Marjo Niittynen, M.Sc. – Jouni T. Tuomisto, MD, PhD – Anne Karvonen, M.Sc. – Anna Karjalainen, PhD – Juha Pekkanen, MD. Prof. National Public Health Institute, Finland Current combining of epi and tox data www.ktl.fi • In hazard identification (qualitative): in use • In dose-response assessment (quantitative): trickier, no developed methods available ⇒ Need for a framework to quantitatively combine epi and tox data • A part of EU-projects Intarese and Beneris about developing tools for risk assessment National Public Health Institute, Finland Objective www.ktl.fi • To develop a systematic way of utilising epidemiological and toxicological data in dose-response estimation • The ultimate goal: More precise and transparent environmental health risk assessment National Public Health Institute, Finland The research questions: www.ktl.fi 1) What is the true dose-response relationship in humans for chemical X (its slope and shape)? 2) How do we know what the true dose-response relationship is? 3) What are the factors that affect our understanding of the uncertainties (size and direction) of the answer to question 1? National Public Health Institute, Finland Our approaches www.ktl.fi 1. Checklist of correction factors for the doseresponse relationship 2. A causal diagram describing the phenomenon as real-world objects and their causal links 3. A case study: TCDD-induced developmental dental defects: human vs. rat – – – Almost the same endpoint Similar exposure levels Exposure can be expressed in same metrics National Public Health Institute, Finland TCDD-induced developmental dental defects: human vs. rat www.ktl.fi • TCDD (2,3,7,8-tetrachlorodibenzo-p-dioxin) – Most toxic congener of dioxins • Ubiquitous, persistent environmental contaminants • Bioaccumulate: humans are exposed via food • Induce a wide array of adverse effects in animals/humans Cl O Cl Cl O Cl National Public Health Institute, Finland TCDD-induced dental defects in humans www.ktl.fi • A study on dental effects in humans exposed to TCDD in Seveso, Italy, 1976 (Alaluusua et al. 2004) Environ Health Perspect 112:1313–1318 (2004) – Exposed persons: • residents of the contaminated area • age < 5 years • serum TCDD level was measured – Controls • from the surrounding non-contaminated area – Teeth were examined in adulthood for enamel defects National Public Health Institute, Finland Dental lesions in Seveso children www.ktl.fi Alaluusua et al., 2004 National Public Health Institute, Finland TCDD-induced dental defects in rats • Kattainen et al. 2001 (Toxicology and Applied www.ktl.fi Pharmacology 174, 216–224 (2001)) – Pregnant rats were exposed intragastrically to low doses (0.03 – 1 µg/kg) of TCDD – Teeth of the offspring were examined at the age of 35 and 70 days • Missing molars • Smaller molars National Public Health Institute, Finland Dental lesions in rat www.ktl.fi • Kattainen et al., 2001 National Public Health Institute, Finland www.ktl.fi Results National Public Health Institute, Finland www.ktl.fi Causal diagram of dose-response (1) National Public Health Institute, Finland www.ktl.fi Causal diagram of dose-response (2) National Public Health Institute, Finland www.ktl.fi Causal diagram of dose-response (3) National Public Health Institute, Finland Dose-response curves Risk for dental defects 100 90 80 risk % 70 60 50 40 Seveso children Line C rats, limit 1.45 mm Line C rats, limit 1.5 mm 30 20 10 0 www.ktl.fi 0 2000 4000 6000 TCDD-concentration pg/g lipid National Public Health Institute, Finland Uncertainties in the human study (Seveso) Main • Exposure misclassification – Serum TCDD-levels of the controls not measured – Part of the exposed persons had overlapping TCDD concentrations with the background exposure – Time-point of collecting serum samples Other (less important here) • Selection bias www.ktl.fi – Randomly invited study population: not all participated • Confounders – Possibly e.g. medication National Public Health Institute, Finland www.ktl.fi Uncertainties in the rat study Main • Toxicodynamics (AHR activation – pathways leading to defects) • Differences in the exposure time-point relative to teeth development Other (less important here) • Toxicokinetics • Endpoint extrapolation • High-to-low-dose extrapolation The size and direction of the uncertainties in both studies are under analysis National Public Health Institute, Finland www.ktl.fi Conclusions • Similar sources of uncertainty in both epidemiologial and toxicological studies, magnitude of these uncertainties varies greatly • Necessary prerequisites for combining epidemiological and toxicological data: – Common metrics for the exposure – Common metrics for the uncertainties ⇒Common conceptual framework • More discussion: http://heande.pyrkilo.fi