Anderson D
TNO BIBRA International Ltd., Woodmansterne Road, Carshalton, Surrey SM5 4DS, UK.
Chem Biol Interact. 2001 Jun 1;135-136:65-80. doi: 10.1016/s0009-2797(01)00171-5.
Butadiene (BD) and its 2-methyl analogue, isoprene, have been extensively studied in animals and BD in population studies. Both chemicals are metabolised by liver cytochrome P450 dependent monogenases to monoepoxide and diepoxide intermediates. The diepoxide intermediates of both compounds were mutagenic in Salmonella typhimurium. However, unlike the monoepoxide of BD, the monoepoxides of isoprene were not mutagenic. It appears that they have no alkylating capacity. BD did not induce somatic cell mutation and recombination or sex-linked recessive lethal mutation in Drosophila melanogaster and isoprene produced no increase in chromosomal aberrations in CHO cells in vitro. Comparative concentrations of haemoglobin adducts in the blood of mice and rats after exposure to BD indicated that reaction with blood may decrease the levels of reactive intermediates available to tissues in rats, but not in mice contributing to greater potency of BD in the mouse. For isoprene, the adducts reach approximately the same concentrations in both species. DNA adducts have also been detected in testicular and lung cells of mice after BD exposure. The level of epoxybutene haemoglobin adducts was significantly elevated in BD-exposed workers, but lower than in rats and mice. In conjunction with the toxicology and carcinogenesis studies for BD and isoprene, additional mice were included for the evaluation of cytogenetic effects. Both chemicals produced increases in sister chromatid exchanges in bone marrow cells and in the frequency of micronuclei in normochromatic and polychromatic erythrocytes, but only BD produced an increase in the percent of bone marrow cells with chromosomal aberrations. At similar doses, the effects with BD were 2-3 times larger than with isoprene. There were also increased hprt mutation frequencies in rats and mice after BD exposure. Biomonitoring studies with hprt mutations in lymphocytes showed conflicting results, with both positive and negative findings. BD has been shown to be positive in one human cytogenetic biomonitoring study and not in three others, but chromosomal aberrations were increased in BD-exposed workers after challenge with gamma rays. Re-analysis of GSTTI null individuals showed positive results. There was an increase in spermatid micronuclei in mice by BD and its metabolites and in rats only by its metabolites. The cytotoxic response of germ cells in mice is greater than in rats. Dominant lethal mutations have been induced by BD and diepoxybutane, but not by epoxybutene. There was some evidence of congenital malformations in mice after BD exposure and there was a linear concentration-related induction of heritable translocations in mice. There was no induction of dominant lethal mutations or congenital malformations in rats. Using the heritable translocation data in mice, it has been determined that if a worker is continually exposed over 5 or 6 weeks to 20-25 ppm of BD, the risk of producing a child with a balanced reciprocal translocation is twice as high as the background risk. Since genetic damage cannot be measured directly in human germ cells, risk to such cells can also be estimated from germ cells and somatic cells of the mouse and human somatic cells using the parallelogram approach. Using doubling doses, the fourth corner of the parallelogram was calculated as a doubling dose for human germ cells of 4390 ppm/h. However, it is still questioned if man is more like rat than mouse in terms of sensitivity to exposure. Similar germ cell data do not exist for isoprene. In conventional developmental studies, where rats and mice were exposed to BD, maternal toxicity was shown in rats but there was no evidence of developmental toxicity or teratogenic effects and there was a small effect on sperm morphology. After exposure to isoprene, there was no adverse effect on rat dams or other reproductive indices. In mice, there was reduced foetal body weight and decreased maternal weight gain and isoprene also affected ovarian follicles. There was a reduction in testicular function parameters such as testicular weight and sperm motility.
丁二烯(BD)及其2 - 甲基类似物异戊二烯已在动物实验中得到广泛研究,BD也有相关人群研究。这两种化学物质均通过肝细胞色素P450依赖性单加氧酶代谢为单环氧化物和双环氧化物中间体。两种化合物的双环氧化物中间体在鼠伤寒沙门氏菌中具有致突变性。然而,与BD的单环氧化物不同,异戊二烯的单环氧化物没有致突变性。似乎它们没有烷基化能力。BD在黑腹果蝇中未诱导体细胞突变、重组或性连锁隐性致死突变,异戊二烯在体外对中国仓鼠卵巢(CHO)细胞的染色体畸变没有增加作用。小鼠和大鼠暴露于BD后血液中血红蛋白加合物的比较浓度表明,与血液的反应可能会降低大鼠组织中可用的活性中间体水平,但对小鼠没有影响,这导致BD在小鼠中的毒性更强。对于异戊二烯,两种物种中的加合物浓度大致相同。BD暴露后,在小鼠的睾丸和肺细胞中也检测到了DNA加合物。BD暴露工人的环氧丁烯血红蛋白加合物水平显著升高,但低于大鼠和小鼠。结合BD和异戊二烯的毒理学和致癌作用研究,额外纳入了一些小鼠用于评估细胞遗传学效应。两种化学物质均使骨髓细胞中的姐妹染色单体交换增加,以及正常染色和多染红细胞中的微核频率增加,但只有BD使具有染色体畸变的骨髓细胞百分比增加。在相似剂量下,BD的效应比异戊二烯大2 - 3倍。BD暴露后大鼠和小鼠的次黄嘌呤 - 鸟嘌呤磷酸核糖转移酶(hprt)突变频率也增加。淋巴细胞hprt突变的生物监测研究结果相互矛盾,既有阳性结果也有阴性结果。BD在一项人类细胞遗传学生物监测研究中显示为阳性,在其他三项研究中则不是,但BD暴露工人在接受γ射线刺激后染色体畸变增加。对谷胱甘肽S - 转移酶T1(GSTT1)基因缺失个体的重新分析显示为阳性结果。BD及其代谢产物使小鼠精子细胞微核增加,而仅其代谢产物使大鼠精子细胞微核增加。小鼠生殖细胞的细胞毒性反应大于大鼠。BD和1,4 - 丁二醇二缩水甘油醚(diepoxybutane)可诱导显性致死突变,但环氧丁烯不能。有证据表明BD暴露后小鼠出现先天性畸形,并且在小鼠中存在与浓度呈线性相关的可遗传易位诱导。大鼠未诱导显性致死突变或先天性畸形。利用小鼠的可遗传易位数据已确定,如果一名工人持续5或6周暴露于20 - 25 ppm的BD,生出具有平衡相互易位孩子的风险是背景风险的两倍。由于无法直接测量人类生殖细胞中的遗传损伤,也可以使用平行四边形方法从小鼠的生殖细胞和体细胞以及人类体细胞来估计此类细胞的风险。使用加倍剂量,计算出平行四边形的第四个角即人类生殖细胞的加倍剂量为4390 ppm/h。然而,在对暴露的敏感性方面,人类是否更像大鼠而非小鼠仍存在疑问。异戊二烯没有类似的生殖细胞数据。在常规发育研究中,大鼠和小鼠暴露于BD后,大鼠表现出母体毒性,但没有发育毒性或致畸作用的证据,对精子形态有轻微影响。异戊二烯暴露后,对大鼠母鼠或其他生殖指标没有不良影响。在小鼠中,胎儿体重减轻,母鼠体重增加减少,异戊二烯还影响卵巢卵泡。睾丸功能参数如睾丸重量和精子活力降低。