Trichloroethylene-induced mouse lung tumors: studies of the mode of action and comparisons between species.

CD-1 mice exposed to 450 ppm trichloroethylene, 6 hr/day, 5 days/week, for 2 weeks showed a marked vacuolation of lung Clara cells after the first exposure of each week and a marked increase in cell division after the last exposure of each week. The damage seen in mouse lung Clara cells is caused by an accumulation of chloral resulting from high rates of metabolism of trichloroethylene but poor clearance of chloral to trichloroethanol and its glucuronide. The activity and distribution of the key metabolizing enzymes in this pathway have been compared in mouse, rat, and human lung. While mouse lung microsomal fractions were able to metabolize trichloroethylene to chloral at significant rates, the rate in rat lung was 23-fold lower and a rate could not be detected in human lung microsomes at all. Immunolocalization of cytochrome P450IIE1 in lung sections revealed high concentrations in mouse lung Clara cells with lesser amounts in type II cells. Lower levels of enzyme could be detected in Clara cells of rat lung, but not at all in human lung sections. Western blots of lung tissues from the three species and of mouse lung Clara cells were entirely consistent with these observations. Consequently, it is highly unlikely that humans exposed to trichloroethylene are at risk from the lung damage/cell proliferation mechanism that is believed to lead to the development of tumors in the mouse lung.

The distribution of theta-class glutathione S-transferases in the liver and lung of mouse, rat and human.

Two murine Theta-class glutathione S-transferases (GSTs), mGSTT1 and mGSTT2, have been cloned and sequenced. The murine cDNAs, together with the published sequences of the rat and human enzymes, were used to design oligonucleotide probes in order to determine the distribution of mRNA for these enzymes in the liver and lung of rat, mouse and human. The mRNA distribution was compared with that of enzyme protein determined with an antibody to rat GSTT2-2. Both the antibody and the oligonucleotide probes gave the same distribution patterns. Both enzymes were present at significantly higher concentrations in mouse tissues than in rat or human tissues. In mouse liver, both enzymes were localized in specific cell types and in nuclei. Although the distribution of GSTT2-2 in rat liver was similar to that seen in the mouse, GSTT1-1 was not localized in a specific cell type or in the nuclei of either rat or human liver. In the lungs, very high concentrations of the Theta enzymes were present in mouse-lung Clara cells and ciliated cells, with much lower levels in the Clara cells only of rat lung. Low levels of human transferase GSTT1-1 were detected in a small number of Clara cells and ciliated cells at the alveolar/ bronchiolar junction. The relative activities between species, and the cellular and sub-cellular distribution within the liver and lungs of each species, provides an explanation for the species-specificity of methylene chloride, a mouse-specific carcinogen activated by glutathione S-transferase GSTT1-1.