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. 2018 Mar:112:269-278.
doi: 10.1016/j.envint.2017.12.030. Epub 2018 Jan 6.

Polybrominated diphenyl ethers (PBDEs) and hydroxylated PBDE metabolites (OH-PBDEs) in maternal and fetal tissues, and associations with fetal cytochrome P450 gene expression

Affiliations

Polybrominated diphenyl ethers (PBDEs) and hydroxylated PBDE metabolites (OH-PBDEs) in maternal and fetal tissues, and associations with fetal cytochrome P450 gene expression

Ami R Zota et al. Environ Int. 2018 Mar.

Abstract

Background: Human fetal exposures to polybrominated diphenyl ethers (PBDEs) and their metabolites (OH-PBDEs) are unique from adults, and in combination with a different metabolic profile, may make fetal development more sensitive to adverse health outcomes from these exposures. However, we lack data to characterize human fetal PBDE exposures and the metabolic factors that can influence these exposures.

Objective: We examined differences between 2nd trimester maternal and fetal exposures to PBDEs and OH-PBDEs. We also characterized fetal cytochrome P450 (CYP) mRNA expression and its associations with PBDE exposures.

Methods: We collected paired samples of maternal serum and fetal liver (n=86) with a subset having matched placenta (n=50). We measured PBDEs, OH-PBDEs, and mRNA expression of CYP genes (e.g. CYP1A1, -2E1, -2J2, -2C9) in all samples. As a sensitivity analysis, we measured PBDEs and OH-PBDEs in umbilical cord serum from a subset (n=22).

Results: BDE-47 was detected in ≥96% of all tissues. Unadjusted ∑PBDEs concentrations were highest in fetal liver (geometric mean (GM)=0.72ng/g), whereas lipid-adjusted concentrations were highest in cord serum (111.12ng/g lipid). In both cases, fetal concentrations were approximately two times higher than maternal serum levels (GM=0.33ng/g or 48.75ng/g lipid). ΣOH-PBDEs were highest in maternal and cord sera and 20-200 times lower than PBDE concentrations. In regression models, maternal BDE-47 explained more of the model variance of liver than of placenta BDE-47 concentrations (adjusted R2=0.79 vs 0.48, respectively). In adjusted logistic regression models, ∑PBDEs were positively associated with expression of CYP2E1 and -2J2 (placenta), and -1A1 (liver) (p<0.05).

Conclusion: Our findings suggest that under normal conditions of mid-gestation, the human fetus is directly exposed to concentrations of PBDEs that may be higher than previously estimated based on maternal serum and that these exposures are associated with the expression of mRNAs coding for CYP enzymes. These results will help frame and interpret findings from studies that use maternal or cord blood as proxy measures of fetal exposures, and will inform the molecular pathways by which PBDEs affect human health.

Keywords: Brominated flame retardants; Cytochrome P-450 enzymes; Endocrine disrupters; Fetal metabolism; OH-PBDEs; Organohalogen chemicals; Placenta transport; Prenatal exposures.

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Figures

Figure 1
Figure 1
Boxplots of the ratios of PBDE levels between matrices, with and without lipid adjustment. Only values above the method detection limit (MDL) in both matrices were included in the ratios. The red dotted line indicates a ratio equal to 1.
Figure 2
Figure 2
A) Percent of metabolic products in each participant by tissue matrix, calculated using the following equation: (∑OH-PBDEtissue / (∑OH-PBDEtissue+ ∑PBDEtissue )). The grey dotted line indicates the median percent of metabolic products by tissue. B) Percent composition of ∑OH-PBDEs by matrix.
Figure 3
Figure 3
Correlations between individual PBDE and OH-PBDE analytes (wet weight; ng/ml) in maternal serum, fetal liver, placenta, and cord serum. Correlations were calculated using only values above the method detection limit in both matrices. Asterisks indicate p < 0.05.
Figure 4
Figure 4
Associations (ORs and 95% CIs) between CYP 450 mRNA expression in placenta (n=45) and fetal liver (n=81) and ∑PBDEs adjusted for gestational age, fetal sex, lipid content, smoking status, and cohort (fetal liver models only).

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