Skip to main content
. Author manuscript; available in PMC: 2020 Sep 1.
Published in final edited form as: Environ Int. 2019 Jun 19;130:104890. doi: 10.1016/j.envint.2019.05.084

Table 2.

Distribution of urinary biomarker concentrations among the ancillary study sample of LIBCSP women.

Biomarker LOD n (%) <LOD Median uncorrected
urinary concentrations
(μg/L)a
Median creatinine-corrected
urinary concentrations
(μg/g creatinine)a
With
Breast
Cancer
(n=893)
No
Breast
Cancer
(n=650)
Pb With
Breast
Cancer
(n=711)
No
Breast
Cancer
(n=598)
Pb
2,5-dichlorophenol 0.2 3 (0.2) 7.50 8.30 0.55 9.95 10.4 0.26
Benzophenone-3 0.4 115 (7.5) 8.60 10.1 0.39 11.5 11.9 0.40
Bisphenol A 0.4 282 (18.3) 1.20 1.30 0.41 1.53 1.69 0.13
Triclosan 2.3 759 (49.2) 2.40 2.40 0.52 5.18 5.77 0.64
Methylparaben 1.0 7 (0.5) 104 100 0.24 160 150 0.37
Propylparaben 0.2 35 (2.3) 25.6 22.4 0.13 39.9 34.8 0.36
Butylparaben 0.2 779 (50.5) <LOD 0.200 0.31 0.440 0.551 0.06
Creatinine 76.4 71.2 0.57

Long Island Breast Cancer Study Project (LIBCSP) population-based women without breast cancer were frequency matched by age to women diagnosed with breast cancer between August 1, 1996 and July 31, 1997.

LOD, limit of detection (in μg/L)

a

Values <LOD were imputed as LOD/√2.

b

P-value for Wilcoxon rank-sum test.