Abstract

BackgroundIn epidemiological studies, it is often not possible to measure accurately exposures of participants even if their response variable can be measured without error. When there are several groups of subjects, occupational epidemiologists employ group-based strategy (GBS) for exposure assessment to reduce bias due to measurement errors: individuals of a group/job within study sample are assigned commonly to the sample mean of exposure measurements from their group in evaluating the effect of exposure on the response. Therefore, exposure is estimated on an ecological level while health outcomes are ascertained for each subject. Such study design leads to negligible bias in risk estimates when group means are estimated from ‘large’ samples. However, in many cases, only a small number of observations are available to estimate the group means, and this causes bias in the observed exposure-disease association. Also, the analysis in a semi-ecological design may involve exposure data with the majority missing and the rest observed with measurement errors and complete response data collected with ascertainment.MethodsIn workplaces groups/jobs are naturally ordered and this could be incorporated in estimation procedure by constrained estimation methods together with the expectation and maximization (EM) algorithms for regression models having measurement error and missing values. Four methods were compared by a simulation study: naive complete-case analysis, GBS, the constrained GBS (CGBS), and the constrained expectation and maximization (CEM). We illustrated the methods in the analysis of decline in lung function due to exposures to carbon black.ResultsNaive and GBS approaches were shown to be inadequate when the number of exposure measurements is too small to accurately estimate group means. The CEM method appears to be best among them when within each exposure group at least a ’moderate’ number of individuals have their exposures observed with error. However, compared with CEM, CGBS is easier to implement and has more desirable bias-reducing properties in the presence of substantial proportions of missing exposure data.ConclusionThe CGBS approach could be useful for estimating exposure-disease association in semi-ecological studies when the true group means are ordered and the number of measured exposures in each group is small. These findings have important implication for cost-effective design of semi-ecological studies because they enable investigators to more reliably estimate exposure-disease associations with smaller exposure measurement campaign than with the analytical methods that were historically employed.

Highlights

  • In epidemiological studies, it is often not possible to measure accurately exposures of participants even if their response variable can be measured without error

  • In epidemiological cohort studies of occupational and environmental exposures, individual exposures are measured with errors and often not available for all members of the study, while health outcome measures are obtained for all individuals without measurement error

  • Where Wgi represents the observed exposure on the ith subject in the gth group, Xgi represents the true exposure on the subject; μg is the gth group mean exposure, g = 1, · · ·, G; γgi ∼ N (0, σb2) is a random effect due to subject i, i = 1, · · ·, ng in group g; ηgi ∼ N (0, ση2) is a measurement error occurring when evaluating the amount of exposure

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Summary

Introduction

It is often not possible to measure accurately exposures of participants even if their response variable can be measured without error. In epidemiological cohort studies of occupational and environmental exposures, individual exposures are measured with errors and often not available for all members of the study, while health outcome measures are obtained for all individuals without measurement error In such settings, a commonly employed approach is to derive exposure estimates via a group-based strategy (GBS, known as semi-individual or semi-ecological study design). Individuals are grouped according to shared attributes, such as job title or work area, and assigned an exposure score, usually the mean of some concentration measurements made on samples drawn from the group This amounts to single imputation of missing value, and is commonly used for all the individuals in the group [3]

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