Baeder C, Albrecht M
Berufsgenossenschaft der chemischen Industrie, Heidelberg, Federal Republic of Germany.
Int Arch Occup Environ Health. 1990;62(4):263-71. doi: 10.1007/BF00640832.
The embryotoxic/teratogenic potential of halothane was evaluated on the basis of available data obtained in an extensive literature search. It was found that halothane induced ultrastructural visible changes in the offspring of rats exposed to concentrations of 10 ppm during gestation. These consisted of degenerative changes in the cerebral cortex and, in particular, the weakening of cell membranes and the vacuolisation of the Golgi-complex. Macroscopically visible morphological changes were seen in rats only after exposure to concentrations equivalent to 320-fold (1600 ppm) the MAK value (maximum concentration value at the workplace). Furthermore, behavioural disorders were seen when exposure to concentrations greater than or equal to 10 ppm occurred during gestation and after parturition. In mice, only macroscopical investigations were performed. The first disturbances scored were only visible as retardation in the offspring, and occurred after exposure to concentrations of halothane 200-fold (1000 ppm) the MAK-value. In the rabbit, anaesthetic concentrations of 22000 ppm halothane did not result in an embryotoxic/teratogenic effect. The individual epidemiological findings in humans were discussed controversially. The studies are inconclusive in establishing an embryotoxic/teratogenic risk following sole exposure to halothane at the MAK level, since mixed exposures occurred and data on the concentrations of halothane in the inhaled air were missing. Therefore, the decision on whether halothane can impair intrauterine development is primarily based on the animal experimental findings. As long as a threshold value has not been established for the observed lesions, halothane should not be inhaled during pregnancy.
根据广泛文献检索获得的现有数据,对氟烷的胚胎毒性/致畸潜力进行了评估。结果发现,在妊娠期暴露于10 ppm浓度氟烷的大鼠后代中,氟烷引起了超微结构可见变化。这些变化包括大脑皮层的退行性改变,特别是细胞膜的弱化和高尔基体复合体的空泡化。仅在暴露于相当于职业接触限值(MAK)值320倍(1600 ppm)的浓度后,大鼠才出现宏观可见的形态学变化。此外,在妊娠期和分娩后暴露于大于或等于10 ppm浓度时,会出现行为障碍。在小鼠中,仅进行了宏观研究。首次记录到的干扰仅表现为后代发育迟缓,且在暴露于氟烷浓度为MAK值200倍(1000 ppm)后出现。在兔子中,22000 ppm氟烷的麻醉浓度未导致胚胎毒性/致畸作用。关于人类个体的流行病学研究结果存在争议。由于存在混合暴露且缺少吸入空气中氟烷浓度的数据,这些研究对于确定仅在MAK水平暴露于氟烷后的胚胎毒性/致畸风险尚无定论。因此,关于氟烷是否会损害子宫内发育的决定主要基于动物实验结果。只要尚未确定所观察到病变的阈值,孕期就不应吸入氟烷。