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. Author manuscript; available in PMC: 2022 Jul 1.
Published in final edited form as: Environ Pollut. 2021 Mar 22;280:117002. doi: 10.1016/j.envpol.2021.117002

Table 3.

Multivariable linear regression models between maternal urinary glyphosate or AMPA and female AGD measures (N=45)

AGD-AF AGD-AC
continuous exposure Beta SE p 95%CI Beta SE p 95%CI
Log SpG-adj glyphosatea 0.62 0.35 0.09 (−0.09, 1.33) 0.11 0.33 0.73 (−0.55, 0.77)
Log SpG-adj glyphosateb 0.47 0.35 0.18 (−0.23, 1.17) 0.10 0.33 0.76 (−0.56, 0.76)
Log SpG-adj AMPAa 0.39 0.30 0.20 (−0.22, 1.00) −0.18 0.27 0.52 (−0.73, 0.37)
Log SpG-adj AMPAb 0.40 0.29 0.17 (−0.18, 0.98) −0.11 0.27 0.70 (−0.65, 0.44)
categorical exposure Beta SE p 95%CI Beta SE p 95%CI
Glyphosate highc 1.16 0.85 0.18 (−0.55, 2.9) 1.48 0.74 0.05 (−0.01, 3.0)
Glyphosate highd 0.75 0.82 0.37 (−0.91, 2.4) 1.35 0.74 0.07 (−0.13, 2.8)
AMPA highc 2.06 0.80 0.01 (0.46, 3.7) 0.44 0.76 0.56 (−1.09, 2.0)
AMPA highd 1.96 0.75 0.01 (0.44, 3.5) 0.27 0.75 0.72 (−1.23, 1.8)

SE, standard error; Log, natural log; SpG-adj, specific gravity-adjusted

a

unadjusted continuous exposure models

b

continuous exposure models adjusted for infant age (weeks) and weight-for-length Z-score at AGD exam

c

unadjusted models (exposure dichotomized at the median)

d

models (exposure dichotomized at the median) adjusted for infant age (weeks) and weight-for-length Z-score at AGD exam