Adler I D, Filser J, Gonda H, Schriever-Schwemmer G
GSF-Forschungszentrum für Umweltund Gesundheit GmbH, Institut für Säugetiergenetik, Neuherberg, Germany.
Mutat Res. 1998 Jan 16;397(1):85-92. doi: 10.1016/s0027-5107(97)00198-x.
Butadiene (BD) and its metabolites have extensively been studied in the EU sponsored research project "Multi-endpoint analysis of genetic damage induced by 1,3-butadiene and its major metabolites". Within this project a dominant lethal test and a heritable translocation test were performed with male mice to study the dose-response relationships for the respective endpoints. BD concentrations of 130 and 500 ppm were tested in the dominant lethal assay by exposing male mice on 6 h/day for five consecutive days resulting in doses of 3900 and 15,000 ppmh, respectively. Males were mated for four consecutive weeks at a ratio of 1:2 to untreated females. A positive dominant lethal effect was observed in the first mating week in the experiment with 15,000 ppmh but no dominant lethality was found with the lower dose of 3900 ppmh. The present dominant lethal data have to be viewed together with the data already published for a BD dose of 39,000 ppmh (1300 ppm at 6 h/day on 5 consecutive days) [1]. The main difference between results with the highest and the middle dose is that mating weeks one and two (sperm and late spermatids) showed an effect at 39,000 ppmh while only mating week one (sperm) showed an effect at 15,000 ppmh. In the heritable translocation assay, males mice were exposed with a BD dose of 15,000 ppmh and mated for one week to untreated females. Among 434 F1 offspring, we found 5 translocation carriers (1.15% vs. 0.05% in the historical control, p < 0.001). In the previous heritable translocation experiment with a BD dose of 39,000 ppmh of DB exposure, 2.7% of the offspring carried a reciprocal translocation [2]. These data can be used for quantification of genetic risk. The dose response for BD-induced heritable translocations in sperm and late spermatids of mice was linear (Y = 0.05 + 6.9 x 10(-5)X) and a doubling dose of 725 ppmh could be calculated.
在欧盟资助的研究项目“1,3 - 丁二烯及其主要代谢产物诱导的遗传损伤多终点分析”中,对丁二烯(BD)及其代谢产物进行了广泛研究。在该项目中,对雄性小鼠进行了显性致死试验和可遗传易位试验,以研究各个终点的剂量 - 反应关系。在显性致死试验中,通过让雄性小鼠连续5天每天暴露6小时,测试了130 ppm和500 ppm的BD浓度,分别产生3900 ppmh和15000 ppmh的剂量。雄性小鼠以1:2的比例与未处理的雌性小鼠连续交配4周。在15000 ppmh剂量的实验中,在第一次交配周观察到了阳性显性致死效应,但在3900 ppmh的较低剂量下未发现显性致死现象。当前的显性致死数据必须与已发表的关于39000 ppmh BD剂量(连续5天每天6小时暴露于1300 ppm)的数据一起看待[1]。最高剂量和中间剂量结果的主要差异在于,在39000 ppmh时,交配周1和2(精子和晚期精子细胞)出现了效应,而在15000 ppmh时,仅交配周1(精子)出现了效应。在可遗传易位试验中,雄性小鼠暴露于15000 ppmh的BD剂量,并与未处理的雌性小鼠交配1周。在434只F1后代中,我们发现了5只易位携带者(与历史对照中的0.05%相比为1.15%,p < 0.001)。在先前关于39000 ppmh BD剂量暴露的可遗传易位实验中,2.7%的后代携带相互易位[2]。这些数据可用于量化遗传风险。小鼠精子和晚期精子细胞中BD诱导的可遗传易位的剂量反应呈线性(Y = 0.05 + 6.9 x 10(-5)X),并且可以计算出加倍剂量为725 ppmh。