Harris J W, Anders M W
Environmental Health Sciences Center, University of Rochester School of Medicine, New York 14642.
Chem Res Toxicol. 1991 Mar-Apr;4(2):180-6. doi: 10.1021/tx00020a009.
1,2-Dichloro-1,1-difluoroethane (HCFC-132b) is a potential substitute for some ozone-depleting chlorofluorocarbons and a model for other 1,1,1,2-tetrahaloethanes under consideration as chlorofluorocarbon substitutes. Male Fischer 344 rats were given 10 mmol/kg HCFC-132b dissolved in corn oil by intraperitoneal injection. An NMR assay for covalent binding of HCFC-132b metabolites to liver proteins was negative, whereas binding was observed in halothane-treated rats. Total urinary metabolites excreted by rats given HCFC-132b during the first 24 h amounted to 1.8 +/- 0.1% of the injected dose, as determined by 19F NMR. During the first 6 h, metabolites of HCFC-132b corresponding to 2-chloro-2,2-difluoroethyl glucuronide, unknown metabolite A, chlorodifluoroacetic acid, and chlorodifluoroacetaldehyde hydrate [both free and conjugated (unknown metabolite B)] were excreted in urine in the approximate ratio 100:9:3:7, respectively. Metabolite A is apparently an O-conjugate of 2-chloro-2,2-difluoroethanol; unconjugated 2-chloro-2,2-difluoroethanol was not detected in urine. The 19F NMR spectrum of metabolite B indicates the formation of a hemiacetal of chlorodifluoroacetaldehyde. Repeated exposure of rats to HCFC-132b significantly increased both the rate of chlorodifluoroacetic acid excretion and the relative fraction of the HCFC-132b dose excreted as chlorodifluoroacetic acid in urine. Incubation of HCFC-132b with rat hepatic microsomes yielded chlorodifluoroacetaldehyde hydrate as the only fluorinated product. The in vitro metabolism of HCFC-132b was increased in microsomes from pyridine-treated rats as compared with control rats, and HCFC-132b metabolism was inhibited by p-nitrophenol, indicating that the cytochrome P-450 isoform IIE1 is largely responsible for the initial hydroxylation of HCFC-132b.
1,2 - 二氯 - 1,1 - 二氟乙烷(HCFC - 132b)是一些消耗臭氧层的氯氟烃的潜在替代品,也是其他正在考虑作为氯氟烃替代品的1,1,1,2 - 四卤乙烷的模型。通过腹腔注射给雄性Fischer 344大鼠注射溶解于玉米油中的10 mmol/kg HCFC - 132b。对HCFC - 132b代谢产物与肝脏蛋白质的共价结合进行的核磁共振分析结果为阴性,而在氟烷处理的大鼠中观察到了结合现象。通过19F核磁共振测定,给予HCFC - 132b的大鼠在最初24小时内排泄的总尿代谢产物量相当于注射剂量的1.8±0.1%。在最初6小时内,HCFC - 132b的代谢产物,即对应于2 - 氯 - 2,2 - 二氟乙基葡萄糖醛酸、未知代谢产物A、氯二氟乙酸和氯二氟乙醛水合物[游离和结合形式(未知代谢产物B)],分别以大约100:9:3:7的比例排泄到尿液中。代谢产物A显然是2 - 氯 - 2,2 - 二氟乙醇的O - 结合物;尿液中未检测到未结合的2 - 氯 - 2,2 - 二氟乙醇。代谢产物B的19F核磁共振谱表明形成了氯二氟乙醛的半缩醛。大鼠反复接触HCFC - 132b显著增加了氯二氟乙酸的排泄速率以及尿液中作为氯二氟乙酸排泄的HCFC - 132b剂量的相对比例。HCFC - 132b与大鼠肝微粒体孵育产生氯二氟乙醛水合物作为唯一的氟化产物。与对照大鼠相比,吡啶处理的大鼠的微粒体中HCFC - 132b的体外代谢增加,并且HCFC - 132b的代谢受到对硝基苯酚的抑制,这表明细胞色素P - 450同工酶IIE1在很大程度上负责HCFC - 132b的初始羟基化。