Larson J L, Wolf D C, Butterworth B E
Chemical Industry Institute of Toxicology, Research Triangle Park, North Carolina 27709.
Fundam Appl Toxicol. 1994 Jan;22(1):90-102. doi: 10.1006/faat.1994.1012.
Chloroform increases the incidence of liver tumors in B6C3F1 mice when administered in by gavage in corn oil, but not when given in the drinking water at similar daily doses. Since cytotoxicity and regenerative cell proliferation have been implicated in the tumorigenic process for this nongenotoxic agent, these effects of chloroform in corn oil and drinking water were evaluated under conditions similar to the two bioassays. Female B6C3F1 mice were administered oral doses of 0, 3, 10, 34, 90, 238, or 477 mg/kg chloroform dissolved in corn oil 5 days/week for periods of 4 days or 3 weeks, or were continually exposed to chloroform in the drinking water at concentrations of 0, 60, 200, 400, 900, or 1800 ppm for 4 days or 3 weeks, at which time they were necropsied. 5-Bromo-2'-deoxyuridine (BrdU) was delivered via osmotic pumps implanted 3.5 days prior to necropsy. Cell proliferation was evaluated as the percentage of hepatocytes that entered S-phase over 3.5 days (labeling index, LI), measured by immunohistochemical detection of BrdU incorporated into the DNA. Dose-dependent changes included centrilobular necrosis and markedly elevated LI in mice given 238 or 477 mg/kg chloroform in corn oil (the average daily doses that produced tumors in the cancer bioassay). The no-observed-effect level for histopathological changes was 10 mg/kg/day and for induced cell proliferation was 34 mg/kg/day for chloroform given in corn oil. Chloroform given in the drinking water did not increase the hepatic LI after either 4 days or 3 weeks in any of the dose groups, nor were any microscopic alterations observed in the livers, even though the cumulative daily amount of chloroform ingested in the 1800-ppm exposure group was 329 mg/kg/day. The sustained increase in LI in the livers of mice administered hepatocarcinogenic doses of chloroform in corn oil, but not for chloroform in drinking water, is evidence that chloroform-induced mouse liver cancer is secondary to events associated with induced cytolethality and cell proliferation. The triggering of these effects appears to be dependent on both the rate and duration of chloroform delivery to the target tissues. Thus, the most straightforward risk assessment for chloroform for this tissue would assign no increased cancer risk for dosing regimens that do not induce cytolethality and cell proliferation.
当通过玉米油灌胃给予B6C3F1小鼠氯仿时,会增加其肝脏肿瘤的发生率,但以类似日剂量经饮水给予时则不会。由于细胞毒性和再生细胞增殖与这种非遗传毒性剂的致癌过程有关,因此在与两种生物测定相似的条件下评估了氯仿在玉米油和饮水中的这些作用。给雌性B6C3F1小鼠口服溶解于玉米油中的氯仿,剂量分别为0、3、10、34、90、238或477mg/kg,每周5天,持续4天或3周;或者让小鼠持续饮用含氯仿的水,浓度分别为0、60、200、400、900或1800ppm,持续4天或3周,之后对它们进行尸检。在尸检前3.5天通过植入的渗透泵给予5-溴-2'-脱氧尿苷(BrdU)。通过免疫组织化学检测掺入DNA中的BrdU,将细胞增殖评估为在连续3.5天进入S期的肝细胞百分比(标记指数,LI)。剂量依赖性变化包括在给予238或477mg/kg氯仿(在癌症生物测定中产生肿瘤的平均日剂量)的玉米油组小鼠中出现的小叶中心坏死和显著升高的LI。对于玉米油中给予的氯仿,组织病理学变化的未观察到影响水平为10mg/kg/天,诱导细胞增殖的未观察到影响水平为34mg/kg/天。在任何剂量组中,经饮水给予氯仿4天或3周后均未增加肝脏LI,肝脏中也未观察到任何微观改变,尽管1800ppm暴露组摄入的氯仿累积日剂量为329mg/kg/天。在玉米油中给予致癌剂量氯仿的小鼠肝脏中LI持续升高,而饮水中的氯仿则未出现这种情况,这证明氯仿诱导的小鼠肝癌是由与诱导细胞毒性和细胞增殖相关的事件继发引起的。这些效应的触发似乎取决于氯仿输送到靶组织的速率和持续时间。因此,对于该组织而言,对氯仿最直接的风险评估是,对于不诱导细胞毒性和细胞增殖的给药方案,不会增加癌症风险。