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. 2011 Mar;119(3):409-15.
doi: 10.1289/ehp.1002453.

Statistical methods to study timing of vulnerability with sparsely sampled data on environmental toxicants

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Statistical methods to study timing of vulnerability with sparsely sampled data on environmental toxicants

Brisa Ney Sánchez et al. Environ Health Perspect. 2011 Mar.

Abstract

Background: Identifying windows of vulnerability to environmental toxicants is an important area in children's health research.

Objective: We compared and contrasted statistical approaches that may help identify windows of vulnerability by formally testing differences in exposure effects across time of exposure, incorporating continuous time metrics for timing of exposure, and efficiently incorporating incomplete cases.

Methods: We considered four methods: 1) window-specific and simultaneously adjusted regression; 2) multiple informant models; 3) using features of individual exposure patterns to predict outcomes; and 4) models of population exposure patterns depending on the outcome. We illustrate them using a study of prenatal vulnerability to lead in relation to Bayley's Mental Development Index at 24 months of age (MDI24).

Results: The estimated change in MDI24 score with a 1-loge-unit increase in blood lead during the first trimester was -2.74 [95% confidence interval (CI), -5.78 to 0.29] based on a window-specific regression. The corresponding change in MDI24 was -4.13 (95% CI, -7.54 to -0.72) based on a multiple informant model; estimated effects were similar across trimesters (p = 0.23). Results from method 3 suggested that blood lead levels in early pregnancy were significantly associated with reduced MDI24, but decreasing blood leads over the course of pregnancy were not. Method 4 results indicated that blood lead levels before 17 weeks of gestation were lower among children with MDI24 scores in the 90th versus the 10th percentile (p = 0.08).

Conclusions: Method 2 is preferred over method 1 because it enables formal testing of differences in effects across a priori-defined windows (e.g., trimesters of pregnancy). Methods 3 and 4 are preferred over method 2 when there is large variability in the timing of exposure assessments among participants. Methods 3 and 4 yielded smaller p-values for tests of the hypothesis that not only level but also timing of lead exposure are relevant predictors of MDI24; systematic power comparisons are warranted.

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Figures

Figure 1
Figure 1
(A) Maternal blood lead pattern across gestational period (weeks) for children in the 10th percentile (solid) and 90th percentile (dashed) of the covariate-adjusted MDI24 distribution with 95% pointwise CIs. (B) Relative exposure comparing those in the 10th percentile of the MDI distribution with those in the 90th percentile, with 95% pointwise CIs.

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