Dahl A R, Bechtold W E, Bond J A, Henderson R F, Mauderly J L, Muggenburg B A, Sun J D, Birnbaum L S
Inhalation Toxicology Research Institute, Lovelace Biomedical and Environmental Research Institute, Albuquerque, NM 87185.
Environ Health Perspect. 1990 Jun;86:65-9. doi: 10.1289/ehp.908665.
Species differences in sensitivity to carcinogenic effects from inhaled 1,3-butadiene might stem, at least in part, from differences in uptake, metabolism, and distribution of 1,3-butadiene. To examine this possibility, rats, mice, and monkeys were exposed to stepped concentrations of 14C-labeled 1,3-butadiene and the chemically related compound, isoprene. Respiratory data were collected during exposure and were used to determine fractional uptake. Rates and routes of excretion of retained radioactivity were also determined and blood levels of potentially toxic metabolites were measured. In some cases, the concentrations of hemoglobin adducts were determined. For rodents, the tissue distribution of metabolites was examined. Some results from these continuing studies to date are: a) mice achieve higher blood concentrations of reactive metabolites than do rats; b) blood levels of toxic metabolites are lower in monkeys than in rodents; c) uptake and retention of 1,3-butadiene is nonlinear in the range where long-term toxicity studies have been conducted; d) the efficiency of production of reactive metabolites decreases with increased inhaled concentrations of 1,3-butadiene; e) repeated exposure to 1,3-butadiene does not induce the metabolism of 1,3-butadiene in rodents; f) hemoglobin adducts of 1,3-butadiene are potential dosimeters of exposure; and g) rats inhaling isoprene produce reactive metabolites analogous to those produced during inhalation of 1,3-butadiene. The available data indicate that major differences in the biological fate of inhaled 1,3-butadiene occur among species, and these differences, at least in part, account for those in species sensitivity to the toxicity of inhaled 1,3-butadiene.
吸入1,3 - 丁二烯致癌效应的物种敏感性差异可能至少部分源于1,3 - 丁二烯摄取、代谢和分布的差异。为研究这种可能性,将大鼠、小鼠和猴子暴露于逐步增加浓度的14C标记的1,3 - 丁二烯以及化学相关化合物异戊二烯中。暴露期间收集呼吸数据并用于确定摄取分数。还确定了保留放射性的排泄速率和途径,并测量了潜在有毒代谢物的血液水平。在某些情况下,还测定了血红蛋白加合物的浓度。对于啮齿动物,检查了代谢物的组织分布。这些持续研究迄今的一些结果如下:a)小鼠体内活性代谢物的血液浓度高于大鼠;b)猴子体内有毒代谢物的血液水平低于啮齿动物;c)在进行长期毒性研究的浓度范围内,1,3 - 丁二烯的摄取和保留是非线性的;d)活性代谢物的产生效率随吸入的1,3 - 丁二烯浓度增加而降低;e)重复暴露于1,3 - 丁二烯不会诱导啮齿动物体内1,3 - 丁二烯的代谢;f)1,3 - 丁二烯的血红蛋白加合物是潜在的暴露剂量计;g)吸入异戊二烯的大鼠产生的活性代谢物与吸入1,3 - 丁二烯时产生的类似。现有数据表明,吸入的1,3 - 丁二烯的生物学转归在物种间存在主要差异,这些差异至少部分解释了物种对吸入1,3 - 丁二烯毒性的敏感性差异。