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ATSDR’s approach to site assessment and epidemiologic considerations for multisite studies. Steve Dearwent, PhD, MPH. Chief, Health Investigations Branch Division of Health Studies Agency for Toxic Substances and Disease Registry
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ATSDR’s approach to site assessment and epidemiologic considerations for multisite studies Steve Dearwent, PhD, MPH Chief, Health Investigations Branch Division of Health Studies Agency for Toxic Substances and Disease Registry NAS - Analysis of Cancer Risks in Populations near Nuclear Facilities May 23, 2011 Agency for Toxic Substances and Disease Registry Division of Health Studies
ATSDR – our mandate and approach • Enabling legislation in the 1980s (CERCLA/RCRA/SARA) • Our work is a combination of: • site specific applications • public health assessments and consultations • health studies, surveillance and registries • community involvement • general information dissemination • toxicological profiles • medical education • CERCLA exclusion for facilities licensed by the NRC
ATSDR’s site assessment process • Initial focus of evaluations are typically exposure centric • The Public Health Assessment • a risk assessment process with associated documentation that often include site specific evaluations of: • contaminant(s) of concern • their concentrations in various environmental media • exposure pathways • potentially exposed populations • process includes a heavy reliance on the use of: • preexisting environmental sampling data • screening or comparison values to estimate risk of both malignant and nonmalignant outcomes in likely exposed populations
Considerations for conducting exposure and/or health effects studies • For ecologic analyses, usually a positive response to the following questions (via the public health assessment process): • completed/potential exposure pathway? • determined exposure time frame? • quantified exposed population? • sufficient exposure levels and latency? • geographic unit similar? • data available for outcomes of interest? • For analytic studies: • above considerations plus available resources, adequate statistical power and a priority data gap
ATSDR’s history with multisite studies • Limited experience due to a heavy focus on evaluating sites independently • Ecologic analyses (with large geographical units of aggregation) • Libby, MT daughter sites (asbestosis, lung cancer, and mesothelioma incidence/mortality within zip codes, census tracts and/or city limits) • NY landfill sites with VOC soil gas migration (cancer incidence within zip codes) • Case-control studies (constrained by significant exposure misclassification potential) • childhood brain cancers and proximity to hazardous waste sites (concentric buffering around sources) • CA birth defects to minority women proximate to waste sites (census tracts)
Epidemiologic considerations for a multisite study – design options • Ecologic • an update to the 1990 NCI mortality study • a study of incidence with 15+ years of data across all sites • generates hypotheses, does not test hypotheses • Cohort • likely too resource intensive for these circumstances (i.e. very low doses, rare outcomes, geographically disparate populations) • Case/control • more efficient • adequate number of incident cases when combining 100+ sites over the last 15+ years • must focus on controlling exposure misclassification
Epidemiologic considerations for a multisite study – case/control design • Assessing outcomes is relatively easy due to broad cancer registry coverage and quality of this data • Two of the biggest concerns are selection of controls and exposure assessment for all participants • Many exposure misclassification concerns • low levels (i.e. typically within regulatory standards) • residential migration combined with lengthy latency for cancer outcomes (i.e. are you studying cases that were exposed?) • other anthropogenic and natural sources for exposure (e.g. radon)
Epidemiologic considerations for a multisite study – case/control design • Municipal parcel data and associated tax records • Strengths • available in most urban (and some rural) locations • identify and select controls • impose residential requirement criteria for all participants (control for exposure misclassification) • locate residences accurately if using proximity to source(s) as part of a participant’s exposure assessment • Limitations • “renters bias” - exclusion of lower SES residents (is there exposure differential when compared to long term home owners?) • initially enumerating households not individuals as controls - requires limited follow-up for actual control selection