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Methylene chloride is a high production chemical used in a variety of applications resulting in estimated occupational and consumer exposures of at least one million people per day. Results of previously reported chronic evaluations of inhaled methylene chloride indicated that it caused mammary tumors in Fischer 344 rats and neoplasia in the lungs and liver of B6C3F1 mice. Mechanism(s) for methylene chloride-induced carcinogenesis have not been adequately elucidated. In this paper we describe the histologic evaluation of animals at a number of intermittent times for the purposes of assessing the progressive development of liver and lung neoplasia. Additionally, a series of stop-exposure treatments was conducted to evaluate the role of different methylene chloride exposure durations on the induction of hepatic and pulmonary neoplasia in female mice. Inhalation exposure to 2000 p.p.m. methylene chloride for 6 h per day, 5 days per week, for 104 weeks resulted in an 8-fold increase in the incidence of exposed animals having a lung adenoma or carcinoma (63 versus 7.5%; P < 0.01) and a 13-fold increase in the total number of pulmonary adenomas and carcinomas per animal at risk (0.97 versus 0.075; P < 0.01). This exposure also caused a 2.5-fold increase in the incidence of mice having liver tumors (69 versus 27%; P < 0.01) and a 3-fold increase in the total number of hepatic adenomas and carcinomas per animal at risk (1.34 versus 0.46; P < 0.01). Methylene chloride exposure hastened the first appearance of lung tumors (by 1 year) compared to that observed in control animals; chemical-induced and spontaneous liver tumors first occurred simultaneously. A shorter exposure duration was sufficient to attain maximal numbers of lung tumors than that needed for a maximal liver tumor burden. Lung tumor multiplicity was substantially increased by having additional time after cessation of the chemical treatment. This contrasts with the findings in liver, where additional post-exposure latency time did not effect tumor multiplicity compared to that of mice evaluated immediately after cessation of exposure. The incidence of lung alveolar hyperplasia in methylene chloride exposed animals was very low, even in tumor-bearing animals and the hyperplasias were not seen until at least 13 weeks after appearance of adenomas and carcinomas. Thus, the genesis of methylene chloride induced lung tumors in B6C3F1 mice is not preceded by overt cytotoxicity, enhanced cell proliferation nor observed hyperplasia.(ABSTRACT TRUNCATED AT 400 WORDS)

We have used methylene chloride as a model to study cellular and molecular processes responsible for liver tumor induction by chlorinated hydrocarbons. Because of current interest in the role of enhanced cell proliferation in tumor induction, measurement of S-phase hepatocytes was incorporated into recently conducted toxicity and carcinogenicity studies. In prechronic studies, female B6C3F1 mice were exposed to 0, 1000, 2000 or 8000 p.p.m. methylene chloride by inhalation, 5 days per week, for up to 4 weeks followed by a 1 and 2 week recovery period. Mice exposed to concentrations of 2000, 4000 or 8000 p.p.m. methylene chloride had sustained increased liver weight commencing after 1 week of exposure and returning to normal after the 1 or 2 week recovery period. The increased liver weight was attributed to hepatocellular hypertrophy secondary to intracellular glycogen accumulation. Tritiated thymidine was administered by osmotic minipumps to label S-phase hepatocytes over a 6 day period. At most intervals examined there was decreased hepatocyte labeling in mice exposed to methylene chloride. However, there was a transitory increased number of S-phase hepatocytes observed at the 2 week interval in the 1000, 4000 and 8000 p.p.m. methylene chloride groups. In a chronic study, female mice were exposed to 2000 p.p.m. methylene chloride for up to two years. Following labeling with BRDU using 6 day minipumps, a statistically significant decrease in S-phase hepatocytes was observed after 13 weeks of methylene chloride exposure. A minor increased labeling index (LI) observed at 52 weeks was not considered to be a methylene chloride treatment-related effect. Retrospective immunohistochemical staining for proliferating cell nuclear antigen (PCNA) in liver sections containing foci of cellular alteration allowed demonstration of S-phase hepatocytes in these clonally expanded preneoplastic lesions. While foci frequently had higher LI's than surrounding normal hepatocytes, there was no difference in the mean LI of foci from methylene chloride-treated mice versus foci occurring spontaneously in control mice. The absence of a sustained increase in S-phase hepatocytes in female B6C3F1 mice suggests that enhanced cell proliferation is not a major mechanistic factor associated with the observed hepatocarcinogenicity of methylene chloride.

The potential of the mouse hepatocarcinogen dichloromethane (DCM) to induce hepatocellular division, as monitored by increased DNA synthesis, has been evaluated using B6C3F1 mice--the strain in which it is carcinogenic but not apparently genotoxic. Male mice were exposed to DCM either by oral gavage in corn oil (1000 mg/kg) or by inhalation of an atmosphere containing 4000 p.p.m. DCM for 2 h. Cells undergoing DNA synthesis (S-phase) were radiolabelled by means of four consecutive i.p. injections of tritiated thymidine at hourly intervals prior to killing. No evidence of S-phase activity was observed in the gavage studies. The inhalation studies resulted in some weak, but statistically significant increases in S-phase incidence, but the biological significance was unclear due to similar increases being observed in some control groups. It is concluded that DCM does not share the mitogenic properties of such presumed non-genotoxic mouse liver carcinogens as trichloroethylene, polybrominated biphenyls and carbon tetrachloride, and as such its carcinogenicity to the mouse liver remains mechanistically obscure.