Table 3.
Exposure | Exposure family | Transformation | IQR | ICC | Interaction P-value | Sex | Estimate (95% CI)a | P-value |
---|---|---|---|---|---|---|---|---|
Ethyl-paraben | Phenols | Log2 | 3.7 | 0.44 | 0.0060 | Female | −43 (−135; 49) | 0.36 |
Male | 112 (31; 193) | 0.007 | ||||||
Propyl-paraben | Phenols | Log2 | 3.0 | 0.44 | 0.0062 | Female | −61 (−142; 20) | 0.14 |
Male | 92 (11; 173) | 0.026 | ||||||
Molybdenum | Metals and essential elements | Log2 | 0.4 | b | 0.046 | Female | −19 (47; 8.2) | 0.15 |
Male | 24 (−8.6; 56) | 0.17 | ||||||
N-Butyl-paraben | Phenols | Log2 | 4.3 | 0.51 | 0.055 | Female | −14 (−114; 86) | 0.78 |
Male | 100 (5.6; 195) | 0.038 | ||||||
Cadmiumb | Metals and essential elements | Log2 | 0.7 | 0.78 | 0.060 | Female | 1.0 (−57; 59) | 0.97 |
Male | −55 (−107; 3.6) | 0.036 | ||||||
Lead b | Metals and essential elements | Log2 | 0.5 | 0.73 | 0.092 | Female | −6.0 (−73; 61) | 0.86 |
Male | −76 (−128; −24) | 0.0041 | ||||||
Arsenic | Metals and essential elements | Log2 | 2.3 | 0.42 | 0.11 | Female | −133 (−258; −6.6) | 0.039 |
Male | −24 (−149; 101) | 0.71 | ||||||
PFOSb | Per- and poly-fluoroalkyl substances | Log2 | 0.7 | b | 0.14 | Female | −54 (−98; −10) | 0.015 |
Male | −15 (−57; 28) | 0.50 | ||||||
PM2.5 absorbance in 3rd trimester of pregnancy | Atmospheric pollutants | Ln | 0.4 | b | 0.38 | Female | −35 (−91; 20) | 0.21 |
Male | −62 (−114; −10) | 0.019 | ||||||
DDTb | Organochlorine compounds | Log2 | 1.4 | b | 0.31 | Female | −15 (−66; 36) | 0.56 |
Male | −46 (−90; −2.8) | 0.037 |
CI, Confidence interval of the coefficient estimate; DDT, dichlorodiphenyltrichloroethane; IQR, inter-quartile range of the (normalized and corrected for measurement error) exposure variable; PFOS, perfluorooctane sulfonate.
Estimates are given as a change in mean birth weight (g) for each inter-quartile range (defined over all observations) increase in (normalized and corrected for measurement error) exposure. Only exposures with an uncorrected sex interaction or sex-specific P-value < 5% are reported. Associations were adjusted for gestational duration (simple and quadratic terms), sex of the newborn, parity, maternal height, maternal weight before pregnancy (using a broken stick model with a knot at 60 kg), maternal smoking during the second trimester of pregnancy, maternal education, season of conception and cohort (fixed effect variable).
Atmospheric pollutants were not assumed to suffer from classical-type measurement error; for biomarker-based exposures, no ICC was available in the literature.