Division of Laboratory Sciences, National Center for Environmental Health, Centers for Disease Control and Prevention , 4770 Buford Highway, Atlanta, Georgia 30341, United States.
Center for Environmental Research and Children's Health, School of Public Health, University of California , 1995 University Avenue, Berkeley, California 94720, United States.
Environ Sci Technol. 2018 Feb 20;52(4):2287-2294. doi: 10.1021/acs.est.7b05460. Epub 2018 Jan 31.
We report longitudinal serum concentrations of select persistent organic pollutants (POPs) in children at ages 7 and 9 years and in their mothers prenatally and again when the children were 9 years old. The participating families were enrolled in the Center for the Health Assessment of Mothers and Children of Salinas (CHAMACOS), a longitudinal birth cohort study of low-income Hispanic families residing in the Salinas Valley, California. We observed decreasing concentrations in the mothers with year of serum collection (2009 vs 2011) for six out of seven polybrominated diphenyl ether (PBDE) congeners and for 2,2',4,4',5-pentachlorobiphenyl (CB-99; p < 0.05). The 9-year-old children had similarly decreasing serum concentrations of all seven PBDE congeners, CB-99, and 2,2',3,4,4',5'- and 2,3,3',4,4',6-hexachlorobiphenyl (CB-138/158) with year of serum collection (2009 vs 2011; p < 0.05). In mixed effect models accounting for weight gain as the children aged from 7 to 9 years, we observed an annual decrease (-8.3% to -13.4%) in tri- to hexaBDE concentrations (p < 0.001), except for 2,2',3,4,4'-tetrabromodiphenyl ether (BDE-85) and 2,2',4,4',5,5'-hexabromodiphenyl ether (BDE-153). The concentrations of these congeners were not associated with time of serum collection and instead showed an -0.9% to -2.6% decrease per kilogram of weight gain during the study period (p < 0.05). In the case of tetra- to heptachlorobiphenyls, we observed -0.5% to -0.7% decrease in serum concentration per kilogram of weight gain (p < 0.05) and -3.0% to -3.7% decrease in serum concentration per year of aging (p < 0.05), except for 2,3',4,4',5-pentachlorobiphenyl (CB-118) and 2,2',4,4',5,5'-hexachlorobiphenyl (CB-153), which were not associated with time of serum draw. 2,2-Bis(4-chlorophenyl)-1,1-dichloroethene (p,p'-DDE) decreased -2.4%/kg of weight gain between the two sampling points (p < 0.001). These findings suggest that as children grow, dilution in a larger body size plays an important role in explaining reductions in body burden in the case of traditional POPs such as PCBs and p,p'-DDE. By contrast, in the case of PBDEs, reductions are likely explained by reduction in exposure, as illustrated by decreased concentrations in more recent years, possibly amplified by presumed shorter biological half-life than other POPs.
我们报告了儿童在 7 岁和 9 岁时以及母亲在产前和儿童 9 岁时的血清中选定的持久性有机污染物(POPs)的纵向血清浓度。参与的家庭参加了加利福尼亚州萨利纳斯山谷的母亲和儿童健康评估中心(CHAMACOS),这是一项针对居住在该地区的低收入西班牙裔家庭的纵向出生队列研究。我们观察到,随着血清采集年份的增加(2009 年与 2011 年相比),七溴二苯醚(PBDE)同系物中的六种和 2,2',4,4',5-五氯联苯(CB-99)的浓度呈下降趋势(p<0.05)。9 岁儿童的所有七溴二苯醚同系物、CB-99、2,2',3,4,4',5'-和 2,3,3',4,4',6-六氯联苯(CB-138/158)的血清浓度也呈类似的下降趋势,与血清采集年份有关(2009 年与 2011 年相比;p<0.05)。在考虑儿童从 7 岁到 9 岁体重增加的混合效应模型中,我们观察到三至六溴代 BDE 浓度每年下降(-8.3%至-13.4%)(p<0.001),除了 2,2',3,4,4'-四溴二苯醚(BDE-85)和 2,2',4,4',5,5'-六溴二苯醚(BDE-153)。这些同系物的浓度与血清采集时间无关,而是与研究期间每公斤体重增加的 -0.9%至-2.6%的下降有关(p<0.05)。在四氯至七氯联苯的情况下,我们观察到每公斤体重增加的血清浓度下降了 -0.5%至-0.7%(p<0.05),每年老化的血清浓度下降了 -3.0%至-3.7%(p<0.05),除了 2,3',4,4',5-五氯联苯(CB-118)和 2,2',4,4',5,5'-六氯联苯(CB-153),它们与血清抽取时间无关。2,2-双(4-氯苯基)-1,1-二氯乙烯(p,p'-DDE)在两次采样点之间下降了 2.4%/kg 的体重增加(p<0.001)。这些发现表明,随着儿童的成长,在更大的体型中稀释在解释传统 POPs(如 PCB 和 p,p'-DDE)的体内负荷减少方面起着重要作用。相比之下,在 PBDE 的情况下,由于近年来浓度下降,可能是由于假定的生物半衰期比其他 POP 短,因此浓度下降可能是由于暴露减少所致。