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The most prominent neoplastic lesions in mice in the 2-year studies of o-nitrotoluene and riddelliine were hemangiosarcomas. Fifteen o-nitrotoluene-induced hemangiosarcomas of the skeletal muscle, subcutaneous tissue, and mesentery; 12 riddelliine-induced hemangiosarcomas of the liver; and 15 spontaneous subcutaneous hemangiosarcomas were examined for genetic alterations in ras, p53, and beta-catenin genes. Mutations in at least one of these genes were identified in 13 of 15 (87%) of the o-nitrotoluene-induced hemangiosarcomas with missense mutations in p53 exons 5-8 detected in 11 of 15 (73%) of these neoplasms. Seven of 15 (47%) hemangiosarcomas from mice exposed to o-nitrotoluene had deletions at exon 2 splice sites or smaller deletions in the beta-catenin gene. K-ras mutation was detected in only 1 of the 15 (7%) o-nitrotoluene-induced hemangiosarcomas. In contrast to the o-nitrotoluene study, 7/12 (58%) riddelliine-induced hemangiosarcomas had K-ras codon 12 GTT mutations and, when screened by immunohistochemistry, 9/12 (75%) had strong staining for the p53 protein in malignant endothelial cells, the cells of origin of hemangiosarcomas. Riddelliine-induced hemangiosarcomas were negative for the beta-catenin protein. Spontaneous hemangiosarcomas from control mice lacked both p53 and beta-catenin protein expression and ras mutations. Our data indicated that p53 and beta-catenin mutations in the o-nitrotoluene-induced hemangiosarcomas and K-ras mutations and p53 protein expression in riddelliine-induced hemangiosarcomas most likely occurred as a result of the genotoxic effects of these chemicals. It also suggests that these mutations play a role in the pathogenesis of the respective hemangiosarcomas in B6C3F1(1) mice.

Lindane (gamma-1,2,3,4,5,6-hexachlorocyclohexane), a widely used insecticide, may be found at low concentrations in the human diet. Male B6C3F1 mice given lindane daily at doses of 20 and 40 mg/kg body wt by gavage in corn oil for 3 days had suppressed bone marrow cellularity, erythrocyte precursors, granulocyte-macrophage progenitor cells (CFU-GM), and residual progenitor cell damage, which could be demonstrated by two whole-body irradiations (WBI) at 200 rads. Lindane exposure for 10 consecutive days at doses of 0, 10, or 20 mg/kg did not cause clinical abnormality or changes in body weights, but there were dose-dependent decreases in marrow cellularity, in more pluripotent stem cells and in committed CFU-GMs, which returned to control values by 4 weeks. These mice were then subjected to two 100-rad exposures of WBI at 4 and 9 weeks following cessation of lindane treatment. This level of irradiation caused only a transient drop in number of marrow progenitor cells. Control and lindane-exposed mice were examined at 1 and 6 weeks following the last irradiation, which was 10 and 15 weeks following the final lindane exposure. The lindane-exposed mice had lower progenitor cell numbers and slower recovery from the irradiation. These results indicate that lindane has significant myelotoxicity in mice and short-term lindane exposure can induce residual progenitor cell damage that can be demonstrated by subsequent irradiation.

Arsine gas is a potent hemolytic agent. Concern about semiconductor workers prompted an in-depth study of arsine at the National Institute of Environmental Health Sciences to determine the hematopoietic effects of prolonged exposure to this gas. Female B6C3F1 mice were exposed by inhalation to 0, 0.5, 2.5, and 5 ppm arsine, 6 hr/day for 14 days. Body weights of exposed mice were comparable to those of controls, but a marked, concentration-related splenomegaly was observed. Higher level arsine exposure produced statistically significant decreases in red blood cells, hematocrit and hemoglobin, with increases in white blood cell counts and mean corpuscular volume of red blood cells. Erythropoiesis as measured by quantitation of erythroid precursors in culture revealed a marrow reduction of colony-forming unit erythroids/femur cells for all treated groups on Day 3 postexposure and only at the 5 ppm dose group on 24 days postexposure, while splenic erythropoiesis increased at higher concentrations of arsine. There was no alteration in bone marrow cellularity and a less significant effect on granulocyte-macrophage progenitors. A 12-week study of arsine at 0, 0.025, 0.5, and 2.5 ppm (6 hr/day) by inhalation showed similar effects on hematopoiesis in mice. In conclusion, arsine exposure at low concentrations produces a stress on the hematopoietic system characterized by hemolysis, which persists for a prolonged period following exposure.

The effect of chrysotile asbestos exposure on bone marrow and immune parameters was examined in mice at 2, 12, and 26 weeks following a 3-day inhalation exposure. Ultrastructural examination revealed that the fibers were deposited primarily at alveolar duct bifurcations within the centriacinar region of the lung. Histological pulmonary changes were minimal, but by 26 weeks early asbestosis characterized by clusters of macrophages and minimal fibrosis were present in the centriacinar region of the lung. Lymphoproliferative responses, antibody levels, and number of plaque forming cells were not significantly altered in exposed mice. Pulmonary macrophages, but not peritoneal macrophages, showed evidence of activation in the chrysotile-exposed mice at 26 weeks following exposure. The most striking change was the depression of the number of bone marrow pluripotent stem cells (CFU-S) and marrow granulocyte macrophage progenitors (CFU-GM) which were lower at all three postexposure examinations. It is felt that the depression of bone marrow progenitors in asbestos-exposed mice may have relevance to the leukopenia reported in workers with occupational history of asbestos exposure.

Six- to seven-week-old female B6C3F1 mice were administered a total of 0, 20, 40, or 80 mg/kg of ochratoxin A (OCT A) ip on alternate days over an 8-day period. Twenty-four hours following the final dose, histopathology, bone marrow, and macrophage parameters were assayed. There was a dramatic dose related decrease in thymic mass with the mean thymus weight of the high dose animals being only 33% of controls. Histologic evidence of nephrotoxicity was minimal and restricted to the inner cortex. Myelotoxicity was present as evidenced by bone marrow hypocellularity, decreased marrow pluripotent stem cells (CFU-S), granulocyte-macrophage progenitors (CFU-GMs), and decreased 59Fe uptake in marrows and spleens of exposed mice. Peritoneal macrophages from sc as well as ip injected mice demonstrated increased phagocytic capacities and increased capacity to inhibit tumor cell growth. These alterations in bone marrow cells and macrophages suggest myelotoxicity is an additional potential hazard of OCT A exposure.

There is continuing concern about the role of irritation in cancer development. Methyl bromide, a widely used fumigant and known irritant reported to cause forestomach carcinomas in rats, was dissolved in peanut oil and given by gavage at 50 mg/kg body wt to Wistar rats five times per week for 13 to 25 weeks. Starting at Week 13, methyl bromide administration was discontinued for half of the methyl bromide-treated rats (stop treatment group). After that, rats from both the continuous treatment and stop treatment groups were terminated at 4-week intervals to follow the progression of the stomach lesions. Forestomach lesions were not found in control rats receiving peanut oil and killed at 13 or 25 weeks. At 13 weeks the forestomachs from rats receiving methyl bromide were contracted and adherent to the liver and spleen. Inflammation, acanthosis, fibrosis, and a high incidence of pseudoepitheliomatous hyperplasia were found microscopically in treated animals. At 25 weeks, 100% of the rats receiving methyl bromide continuously had hyperplastic lesions of the forestomach which were more severe than those at 13 weeks. Evidence of malignancy was seen in one rat and the lesion was considered a very early carcinoma. In the stop treatment group that received methyl bromide for 13 weeks, there was regression of the stomach lesions, but at the 12-week final sacrifice, adhesions, fibrosis, and mild acanthosis remained. This study illustrates the need for regression experiments for complex forestomach lesions in rodents, especially when an irritating chemical is given by gavage.

Female B6C3F1 mice plus male and female Fischer 344/N rats were gavaged with allyl isovalerate (AIV) in corn oil at 0, 31, 62, or 125 (mice) and 0, 31, 62, 125, or 250 (rats) mg/kg body weight for five daily exposures per week for a 2-week period. Hematologic, immunologic, and histopathologic studies were performed 48 to 72 hr following the final treatment. AIV exposure had no effect on hematology or bone marrow cellularity in mice or rats. AIV exposure at 250 mg/kg was toxic to rats causing reduced weight gain and hepatotoxicity. In vivo and in vitro studies revealed that pluripotent hematopoietic stem cells (CFU-S) and granulocyte-macrophage progenitors (CFU-GM) in the bone marrow were decreased in the treated mice. Hematopoietic suppression was correlated with the reduction in the hexose monophosphate shunt metabolism of bone marrow cells but the Embden-Meyerhof pathway and tricarboxylic acid pathway enzymes did not appear to be affected. Examination of host resistance following Plasmodium and Listeria challenge did not demonstrate significant differences between treated and control mice, nor were there other effects on the immune system. This suggests that the myelotoxic effects were minimal and of a degree that would not alter host resistance.