Grandjean Philippe, Budtz-Jørgensen Esben, Barr Dana B, Needham Larry L, Weihe Pal, Heinzow Birger
Institute of Public Health, University of Southern Denmark, Winsløwparken 17, DK-5000 Odense, Denmark.
Environ Sci Technol. 2008 Sep 15;42(18):6991-6. doi: 10.1021/es800778q.
The elimination kinetics of polychlorinated biphenyls (PCBs) in humans is difficult to assess in observational studies, because PCB exposure is never completely abolished. In a community with high dietary PCB exposures from whale blubber, we examined two groups of children with increased body burdens from breast-feeding. Follow-up was from ages 4.5 to 7.5 years (99 subjects) and 7 to 14 years (101 subjects). The calculations were performed by the use of structural equation models, with adjustment for body weight and dietary blubber intake as the main source of postnatal exposure. As a likely result of background exposures, apparent elimination half-lives were unexpectedly long when based on results from all cohort members. Subjects with exposures above the median and in the highest quartile showed half-lives of about 3-4 years for CB-138 and 4.5-5.5 years for CB-105 and CB-118; 6.5-7.5 years for CB-156, CB-170, and CB-187; and 7-9 years for CB-153 and CB-180. The longest half-lives correspond to elimination of the parent PCB solely with a daily fat excretion rate of 1-2 g, whereas shorter half-lives assume metabolic break-down.
在观察性研究中,人体多氯联苯(PCBs)的消除动力学很难评估,因为多氯联苯暴露从未完全消除。在一个因食用鲸脂而多氯联苯膳食暴露水平较高的社区,我们对两组因母乳喂养导致体内负荷增加的儿童进行了研究。随访时间分别为4.5至7.5岁(99名受试者)和7至14岁(101名受试者)。计算采用结构方程模型进行,并将体重和膳食鲸脂摄入量作为产后暴露的主要来源进行调整。作为背景暴露的一个可能结果,基于所有队列成员的结果,表观消除半衰期出乎意料地长。暴露量高于中位数且处于最高四分位数的受试者,CB - 138的半衰期约为3 - 4年,CB - 105和CB - 118的半衰期为4.5 - 5.5年;CB - 156、CB - 170和CB - 187的半衰期为6.5 - 7.5年;CB - 153和CB - 180的半衰期为7 - 9年。最长的半衰期对应于仅以每日1 - 2克的脂肪排泄率消除母体多氯联苯,而较短的半衰期则假定存在代谢分解。