DeAngelo A B, Daniel F B, Stober J A, Olson G R
Biochemical and Molecular Toxicology Branch, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268.
Fundam Appl Toxicol. 1991 Feb;16(2):337-47. doi: 10.1016/0272-0590(91)90118-n.
Groups of male B6C3F1 mice (N = 50) were provided drinking water containing 2 g/liter sodium chloride (control) and 0.05, 0.5, and 5 g/liter dichloroacetic acid (DCA). Treatment of 30 animals in each group was carried out to 60 or 75 weeks. In a separate experiment, mice exposed to 3.5 g/liter DCA and the corresponding acetic acid control group were killed at 60 weeks. Groups of 5 mice were killed at 4, 15, 30, and 45 weeks. Time-weighted mean daily doses of 7.6, 77, 410, and 486 mg/kg/day were calculated for 0.05, 0.5, 3.5, and 5 g/liter DCA treatments. Animals exposed to 3.5 and 5 g/liter DCA had final body weights that were 87 and 83%, respectively, of the control value. Relative liver weights of 136, 230, and 351% of the control value were measured for 0.5, 3.5, and 5 g/liter, respectively. At 60 weeks mice receiving 5.0 g/liter DCA had a 90% prevalence of liver neoplasia with a mean multiplicity of 4.50 tumors/animal. Exposure to 3.5 g/liter DCA for 60 weeks resulted in a 100% tumor prevalence with an average of 4.0 tumors/animal. The prevalence of liver neoplasia and tumor multiplicity at 60 and 75 weeks in the 0.05 g/liter DCA (24.1%; 0.31 tumors/animal) and in the 0.5 g/liter group (11.1%; 0.11 tumors/animal) did not differ significantly from the control value (7.1% and 0.07 tumors/animal). No liver tumors were found in the group treated with acetic acid. Hyperplastic nodules were seen in the 3.5 (58%; 0.92/animal) and 5 g/liter DCA groups (83%; 1.27/animal). There was a significant positive dose-related trend in the age-adjusted prevalence of liver tumors. These data confirm the hepatocarcinogenicity of DCA administered in the drinking water to male B6C3F1 mice for 60 weeks. The results together with those in an earlier report from this laboratory suggest, for the conditions under which these assays were conducted, a threshold concentration of at least 0.5 g/liter followed by a steep rise to a maximum tumor incidence at 2 g/liter DCA.
将雄性B6C3F1小鼠分成几组(每组50只),分别给予含2克/升氯化钠的饮用水(对照组)以及含0.05、0.5和5克/升二氯乙酸(DCA)的饮用水。每组30只动物接受处理,持续60周或75周。在另一项单独实验中,暴露于3.5克/升DCA的小鼠及其相应的乙酸对照组在60周时被处死。每组5只小鼠分别在4周、15周、30周和45周时被处死。对于0.05、0.5、3.5和5克/升DCA处理组,计算出的时间加权平均每日剂量分别为7.6、77、410和486毫克/千克/天。暴露于3.5和5克/升DCA的动物最终体重分别为对照组的87%和83%。对于0.5、3.5和5克/升处理组,测得的相对肝脏重量分别为对照组的136%、230%和351%。在60周时,接受5.0克/升DCA处理的小鼠肝脏肿瘤发生率为90%,平均每只动物有4.50个肿瘤。暴露于3.5克/升DCA 60周导致肿瘤发生率达100%,平均每只动物有4.0个肿瘤。0.05克/升DCA组(24.1%;0.31个肿瘤/动物)和0.5克/升DCA组(11.1%;0.11个肿瘤/动物)在60周和75周时的肝脏肿瘤发生率及肿瘤多发性与对照组(7.1%和0.07个肿瘤/动物)相比,差异无统计学意义。乙酸处理组未发现肝脏肿瘤。在3.5克/升(58%;0.92个/动物)和5克/升DCA组(83%;1.27个/动物)中可见增生性结节。肝脏肿瘤的年龄调整发生率存在显著的剂量相关正趋势。这些数据证实了通过饮用水给予雄性B6C3F1小鼠60周DCA具有肝癌致癌性。这些结果与本实验室早期报告中的结果共同表明,在这些实验条件下,阈值浓度至少为0.5克/升,随后在2克/升DCA时肿瘤发生率急剧上升至最高。