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. 2018 Mar 16;126(3):037005.
doi: 10.1289/EHP1994.

Within-Day, Between-Day, and Between-Week Variability of Urinary Concentrations of Phenol Biomarkers in Pregnant Women

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Within-Day, Between-Day, and Between-Week Variability of Urinary Concentrations of Phenol Biomarkers in Pregnant Women

Céline Vernet et al. Environ Health Perspect. .

Abstract

Background: Toxicology studies have shown adverse effects of developmental exposure to industrial phenols. Evaluation in humans is challenged by potentially marked within-subject variability of phenol biomarkers in pregnant women, which is poorly characterized.

Objectives: We aimed to characterize within-day, between-day, and between-week variability of phenol urinary biomarker concentrations during pregnancy.

Methods: In eight French pregnant women, we collected all urine voids over a 1-wk period (average, 60 samples per week per woman) at three occasions (15±2, 24±2, and 32±1 gestational weeks) in 2012-2013. Aliquots of each day and of the whole week were pooled within-subject. We assayed concentrations of 10 phenols in these pools, and, for two women, in all spot (unpooled) samples collected during a 1-wk period. We characterized variability using intraclass correlation coefficients (ICCs) with spot samples (within-day variability), daily pools (between-day variability), and weekly pools (between-week variability).

Results: For most biomarkers, the within-day variability was high (ICCs between 0.03 and 0.50). The between-day variability, based on samples pooled within each day, was much lower, with ICCs >0.60 except for bisphenol S (0.14, 95% confidence interval [CI]: 0.00, 0.39). The between-week variability differed between compounds, with triclosan and bisphenol S having the lowest ICCs (<0.3) and 2,5-dichlorophenol the highest (ICC >0.9).

Conclusion: During pregnancy, phenol biomarkers showed a strong within-day variability, while the variability between days of a given week was more limited. One biospecimen is not enough to efficiently characterize exposure; collecting biospecimens during a single week may be enough to represent well the whole pregnancy exposure for some but not all phenols. https://doi.org/10.1289/EHP1994.

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Figures

Timeline for urine collection. For collection week 1, the median was 13 gestational weeks; for collection week 2, the median was 23 weeks; and for collection week 3, the median was 32 weeks. Spot samples of all urine voids over study week 1 were assayed in week 1 for subgroup 1 (n equals 2 women). Daily pools of the study week 1 were assayed for all women (n equals 8 women). Weekly pool of the study week 1 assayed in weeks 1 to 3 for all women (n equals 8 women). One random spot sample in each study week was assayed for all women (n equals 8 women).
Figure 1.
Urine collection, pooling procedure, and biomarker assays in all the study population (N=8 women) and in the nested subgroup 1 (N=2 women).
Twelve graphical representations plotting urinary concentrations of ten phenols, namely, 2,4-dichlorophenol, 2,5-dichlorophenol, butyl paraben, ethyl paraben, methyl paraben, propyl paraben, benzophenone 3, bisphenol A, bisphenol S, and triclosan, in micrograms per liter; creatinine in milligrams per deciliter; and specific gravity (no unit) (y-axis) across days 1, 2, 3, 4, 5, 6, and 7 (x-axis) for woman 1 and woman 2.
Figure 2.
Within-day and within-week variability – urinary concentrations of 10 phenols (μg/L), creatinine concentration (mg/dL), and specific gravity in log10-scale in the unpooled spot samples from subgroup 1 (2 women, n=114 spot samples collected over the first week of collection). Note that to facilitate visualization, each biomarker is displayed on a specific scale.
Twelve graphical representations plotting daily urinary concentrations of ten phenols, namely, 2,4-dichlorophenol, 2,5-dichlorophenol, butyl paraben, ethyl paraben, methyl paraben, propyl paraben, benzophenone 3, bisphenol A, bisphenol S, and triclosan, in micrograms per liter; creatinine in milligrams per deciliter; and specific gravity (no unit) (y-axis) across days 1, 2, 3, 4, 5, 6, and 7 (x-axis) for eight women.
Figure 3.
Between-day (within a week) variability of pooled daily samples – urinary concentrations of 10 phenols (μg/L), creatinine concentration (mg/dL), and specific gravity in log10-scale in the within-woman daily pooled samples from subgroup 1 and subgroup 2 (8 women, n=56dailypools, one daily pool for each day of the first week of collection). Note that to facilitate visualization, each biomarker is displayed on a specific scale.
Twelve graphical representations plotting weekly urinary concentrations of ten phenols, namely, 2,4-dichlorophenol, 2,5-dichlorophenol, butyl paraben, ethyl paraben, methyl paraben, propyl paraben, benzophenone 3, bisphenol A, bisphenol S, and triclosan, in micrograms per liter; creatinine in milligrams per deciliter; and specific gravity (no unit) (y-axis) across weeks 1, 2, and 3 (x-axis) for eight women.
Figure 4.
Between-week variability of weekly samples – urinary concentrations of 10 phenols (μg/L), creatinine concentration (mg/dL), and specific gravity in log10-scale in the within-woman weekly pooled samples from subgroup 1 and subgroup 2 (8 women, n=24weeklypools, one weekly pool for each of the three weeks of collection). Note that to facilitate visualization, each biomarker is displayed on a specific scale.
Graph shows plots with 95 percent confidence intervals. Intraclass correlation coefficients are plotted on the y-axis across ten phenols, namely, 2,4-dichlorophenol, 2,5-dichlorophenol, butyl paraben, ethyl paraben, methyl paraben, propyl paraben, benzophenone 3, bisphenol A, bisphenol S, and triclosan; creatinine; and specific gravity on the x-axis for within-day ICC using spot samples, between-day ICC using daily pools, and between-week ICC using weekly pools.
Figure 5.
Intraclass correlation coefficients (error bars for 95% confidence intervals) for the within-day variability using the unpooled spot samples from subgroup 1 (2 women, n=114 spot samples collected over the first week of collection, triangle markers), the between-day variability using the within-woman daily pooled samples from subgroup 1 and subgroup 2 (8 women, n=56dailypools, one daily pool for each day of the first week of collection, square markers), and the between-week variability in the within-woman weekly pooled samples from subgroup 1 and subgroup 2 (8 women, n=24weeklypools, one weekly pool for each of the three weeks of collection, circle markers). For triclosan, we give only the confidence interval truncated to zero due to the negative estimate of between-week ICC.

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