Kania-Korwel Izabela, Garrison A Wayne, Avants Jimmy K, Hornbuckle Keri C, Robertson Larry W, Sulkowski Wieslaw W, Lehmler Hans-Joachim
Department of Occupational and Environmental Health, College of Public Health, University of Iowa, Iowa City, Iowa 52242, USA.
Environ Sci Technol. 2006 Jun 15;40(12):3704-10. doi: 10.1021/es0602086.
The enantiomeric enrichment of polychlorinated biphenyl (PCB) atropisomers has been reported in both wildlife and in humans. The biological processes causing this enrichment are only poorly investigated, a fact that limits the use of enantiomeric fractions (EFs) as a tool to study various processes of environmental relevance. To further understand these enantioselective processes, this study investigates the tissue distribution and EFs of some PCB atropisomers after administration of PCB mixtures to immature male Sprague-Dawley rats. The mixtures selected for this study, Aroclor 1254 and an environmental mixture extracted from Chlorofen-contaminated soil, are qualitatively different and are known to induce different groups of hepatic enzymes. Animals were sacrificed 6 days after dosing, PCBs were extracted, and, whenever possible, the EFs of PCBs 84, 91, 95, 149, 174, and 176 were determined by chiral gas chromatography. The EFs of PCB 95 (adipose tissue, liver, and skin) and PCB 149 (adipose tissue, liver, skin, and blood) in tissues from Aroclor 1254-treated animals differed significantly from EFs in the Aroclor standard, while only EFs of PCB 95 (blood) and PCB 174 (adipose tissue) in tissues from soil-extract-treated animals were different from those of the Chlorofen soil extract. PCB 149 in tissues from soil-extract-treated animals underwent no statistically significant enantiomeric enrichment. These differences in the EFs clearly suggest that the enantioselective enrichment of PCB atropisomers may correlate with exposure history, and with the induction of hepatic enzymes, and that EFs may be useful chemical markers of physiologic and biochemical changes following exposure to PCBs.
多氯联苯(PCB)阻转异构体的对映体富集现象已在野生动物和人类中被报道。然而,导致这种富集的生物学过程却鲜有研究,这一事实限制了对映体分数(EFs)作为研究各种环境相关过程工具的应用。为了进一步了解这些对映选择性过程,本研究调查了向未成熟雄性Sprague-Dawley大鼠施用PCB混合物后,某些PCB阻转异构体的组织分布和EFs。本研究选用的混合物,即Aroclor 1254和从受氯芬污染土壤中提取的环境混合物,在性质上有所不同,并且已知会诱导不同组别的肝酶。给药6天后处死动物,提取PCB,并尽可能通过手性气相色谱法测定PCB 84、91、95、149、174和176的EFs。Aroclor 1254处理动物组织中PCB 95(脂肪组织、肝脏和皮肤)和PCB 149(脂肪组织、肝脏、皮肤和血液)的EFs与Aroclor标准品中的EFs有显著差异,而土壤提取物处理动物组织中只有PCB 95(血液)和PCB 174(脂肪组织)的EFs与氯芬土壤提取物中的不同。土壤提取物处理动物组织中的PCB 149未发生统计学上显著的对映体富集。这些EFs的差异清楚地表明,PCB阻转异构体的对映选择性富集可能与暴露史以及肝酶的诱导有关,并且EFs可能是接触PCB后生理和生化变化的有用化学标志物。