Templin M V, Jamison K C, Sprankle C S, Wolf D C, Wong B A, Butterworth B E
Chemical Industry Institute of Toxicology, Research Triangle Park, NC 27709, USA.
Cancer Lett. 1996 Nov 29;108(2):225-31. doi: 10.1016/s0304-3835(96)04427-8.
In a 2-year chloroform inhalation bioassay, an increased incidence of tumors was observed in the kidneys of male BDF1 mice and the liver of female BDF1 mice exposed to the highest exposure concentration of 90 ppm. To investigate the role of cytotoxicity and regenerative cell proliferation in tumor formation, male and female BDF1 mice were exposed to chloroform vapor concentrations of 0, 0.3, 5, 30, or 90 ppm 6 h/day for 4 days. Bromodeoxyuridine (BrdU) was administered via osmotic pumps implanted 3.5 days prior to necropsy, and the labeling index (LI), or percentage of cells in S-phase, was quantified using BrdU immunohistochemistry. To assess longer-term responses, additional male mice were exposed 5 days/week for 2 weeks to 0, 30, or 90 ppm. Degenerative lesions and an increase in the LI of seven- to ten-fold over controls were observed in the kidneys of male but not female mice exposed to 30 or 90 ppm. Liver lesions and increased hepatocyte LI were observed in male mice exposed to 30 or 90 ppm and in female mice exposed to 90 ppm. In the 2-week exposure groups 40% of the 30 ppm group and 80% of the 90 ppm group died with severe kidney damage, indicating that both 30 and 90 ppm exceed a maximum tolerated dose. Thus, in the 2-year bioassay chloroform concentrations had to be stepped-up over a period of weeks in order for the male mice exposed to 30 or 90 ppm to survive. The extrapolation of tumor data from such an unusual procedure is questionable. These observations are consistent with a substantial database that indicates that tumor induction by chloroform occurs via a non-genotoxic-cytotoxic mode of action and is secondary to organ-specific toxicity. These data further support the premise that doses that do not induce regenerative cell proliferation do not present an increased risk of cancer.
在一项为期两年的氯仿吸入生物测定中,在暴露于最高暴露浓度90 ppm的雄性BDF1小鼠的肾脏和雌性BDF1小鼠的肝脏中观察到肿瘤发生率增加。为了研究细胞毒性和再生细胞增殖在肿瘤形成中的作用,将雄性和雌性BDF1小鼠每天暴露于0、0.3、5、30或90 ppm的氯仿蒸气浓度下6小时,持续4天。在尸检前3.5天通过植入的渗透泵给予溴脱氧尿苷(BrdU),并使用BrdU免疫组织化学对标记指数(LI)或S期细胞百分比进行定量。为了评估长期反应,将另外的雄性小鼠每周暴露5天,持续2周,暴露于0、30或90 ppm。在暴露于30或90 ppm的雄性而非雌性小鼠的肾脏中观察到退行性病变以及LI比对照增加七至十倍。在暴露于30或90 ppm的雄性小鼠以及暴露于90 ppm的雌性小鼠中观察到肝脏病变和肝细胞LI增加。在2周暴露组中,30 ppm组的40%和90 ppm组的80%因严重肾损伤死亡,表明30和90 ppm均超过了最大耐受剂量。因此,在两年生物测定中,氯仿浓度必须在数周内逐步提高,以使暴露于30或90 ppm的雄性小鼠存活。从这种不寻常程序得出的肿瘤数据外推存在疑问。这些观察结果与大量数据库一致,该数据库表明氯仿诱导肿瘤是通过非遗传毒性 - 细胞毒性作用模式发生的,并且是器官特异性毒性的继发结果。这些数据进一步支持了这样一个前提,即不诱导再生细胞增殖的剂量不会增加癌症风险。