Johanson G, Filser J G
Division of Work and Environmental Physiology, National Institute of Occupational Health, Solna, Sweden.
Arch Toxicol. 1993;67(3):151-63. doi: 10.1007/BF01973302.
The gas 1,3-butadiene (BU) is an important industrial chemical and an environmental air pollutant. BU has been shown to be a weak carcinogen in the rat but a potent carcinogen in the B6C3F1 mouse. This species difference makes risk extrapolation to humans difficult and the underlying mechanism should be clarified before meaningful risk extrapolation to humans can be made. One possible explanation for the species differences in cancer response is that there are quantitative species differences in the formation of genotoxic epoxides. To investigate this possibility a physiologically based pharmacokinetic (pbpk) model for BU together with its first reactive metabolite 1,2-epoxybutene-3 (butadiene monoxide, BMO) was developed. Previously reported values on hepatic glutathione (GSH) turnover, depletion of hepatic GSH in rodents exposed to BU, and in vitro metabolic data of BU and BMO were included in the model, which incorporates intrahepatic first-pass hydrolysis of BMO and the ordered sequential, ping-pong mechanism to describe the enzyme kinetics of BMO-GSH conjugation. In vitro studies were carried out to obtain tissue: air partition coefficients of BU and BMO in rat tissue homogenates. The simulated pharmacokinetics of BU, BMO, and GSH agreed with previously published experimental observations in rat and mouse obtained in closed and open chamber experiments. According to the model, the internal dose of BMO (expressed either as the concentration in mixed venous blood or as the area under the concentration-time curve) is approximately 1.6 times higher in the mouse than in the rat for exposure to BU below 1000 ppm. At higher exposure levels, GSH depletion occurs in the mouse, but not in the rat, after about 6-9 h. This GSH depletion results in up to 2-3 times higher internal doses in the mouse than in the rat. The clear but relatively small species differences in body burdens of BMO indicated from our model can only partly explain the marked species difference in cancer response between mice and rats exposed to BU.
气体1,3 - 丁二烯(BU)是一种重要的工业化学品,也是一种环境空气污染物。已表明BU在大鼠中是一种弱致癌物,但在B6C3F1小鼠中是一种强效致癌物。这种物种差异使得向人类进行风险推断变得困难,并且在能够对人类进行有意义的风险推断之前,其潜在机制应予以阐明。癌症反应中物种差异的一种可能解释是,在遗传毒性环氧化物的形成上存在数量上的物种差异。为了研究这种可能性,开发了一种基于生理的BU及其第一种反应性代谢物1,2 - 环氧丁烯 - 3(丁二烯 monoxide,BMO)的药代动力学(pbpk)模型。先前报道的关于肝脏谷胱甘肽(GSH)周转、暴露于BU的啮齿动物肝脏GSH消耗以及BU和BMO的体外代谢数据被纳入该模型,该模型纳入了BMO的肝内首过水解以及有序的顺序、乒乓机制来描述BMO - GSH共轭的酶动力学。进行了体外研究以获得大鼠组织匀浆中BU和BMO的组织:空气分配系数。BU、BMO和GSH的模拟药代动力学与先前在封闭和开放舱实验中在大鼠和小鼠中发表的实验观察结果一致。根据该模型,对于暴露于低于1000 ppm的BU,小鼠中BMO的内剂量(以混合静脉血中的浓度或浓度 - 时间曲线下面积表示)比大鼠高约1.6倍。在较高暴露水平下,约6 - 9小时后小鼠中会发生GSH消耗,但大鼠中不会。这种GSH消耗导致小鼠中的内剂量比大鼠高2 - 3倍。我们的模型表明,BMO体内负荷中明显但相对较小的物种差异只能部分解释暴露于BU的小鼠和大鼠之间癌症反应的显著物种差异。