Skip to main content
. Author manuscript; available in PMC: 2020 Oct 1.
Published in final edited form as: Environ Int. 2019 Jul 6;131:104903. doi: 10.1016/j.envint.2019.104903

Table 3.

Adjusteda percent change (95% confidence interval) in urinary oxidative stress biomarker in association with an interquartile range difference in urinary phenol concentrationb.

8-OHdG
8-isoprostane
% Change (95% CI) P % Change (95% CI) P
2,4-DCP 9.16 (5.95, 12.5) < 0.01 8.47 (3.46, 13.7) < 0.01
2,5-DCP 15.2 (11.0, 19.6) < 0.01 16.7 (9.66, 24.2) < 0.01
BP3 10.0 (5.46, 14.8) < 0.01 9.00 (1.39, 17.2) 0.02
Butyl PB 3.32 (−1.21, 8.04) 0.17 9.92 (1.80, 18.7) 0.02
Ethyl PB 4.28 (−0.19, 8.95) 0.07 12.8 (5.01, 21.1) < 0.01
Methyl PB 9.30 (5.40, 13.3) < 0.01 9.50 (3.32, 16.1) < 0.01
Propyl PB 7.32 (3.55, 11.2) < 0.01 7.32 (1.27, 13.7) 0.01
Triclosan 6.12 (2.08, 10.3) < 0.01 7.02 (0.14, 14.4) 0.05
BPSb 6.18 (−0.27, 13.1) 0.06 18.5 (7.68, 30.5) < 0.01
Triclocarbanb 3.05 (−6.76, 13.9) 0.56 3.87 (−11.7, 22.2) 0.65

Abbreviations: DCP, dichlorophenols; BP3, benzophenone-3; BPS, bisphenol-S; PB, paraben; 8-OHdG, 8-hydroxydeoxyguanosine. Results from weighted linear mixed effects models including a random intercept for ID. N = 464 participants, 1555 samples.

a

Models adjusted for urinary specific gravity, gestational age at sample collection, maternal age, Race/Ethnicity, education level, pre-pregnancy body mass index, and smoking during pregnancy.

b

Bisphenol-S and triclocarban modeled as above vs. below the limit of detection.