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Both sexes of F344 rats were gavaged with maximal tolerated doses of mercuric chloride for periods from 2 wk to up to 2 yr to investigate chronic nephrotoxicity and potential carcinogenicity. The toxicity of mercuric chloride was excessive after 2 wk of exposure to doses ranging from 1.25 to 20 mg/kg, compromising renal function by selectively destroying cells of the proximal tubules, and eliciting marked elevations in urinary biomarker enzymes diagnostic for acute renal tubule necrosis. In the 2-wk studies, urinary alkaline phosphatase and aspartate amino-transferase were most sensitive to renal mercury toxicity among a panel of six enzymes, exhibiting twofold increases above controls at the 5.0 mg/kg dose, before changes in the other enzymes occurred. Urinary lactate dehydrogenase was the most responsive enzyme, with up to 11-fold increases in activity above controls. In response to mercuric chloride exposure of 5.0 mg/kg for 2-6 mo, the greatest and most persistent increases in elevation of urinary enzyme activities were exhibited by alkaline phosphatase and gamma-glutamyl transferase, which increased two-to threefold above controls. At this interval, the maximal severity of the renal lesions in both sexes of rats was graded as minimal to mild. Beyond 6 mo none of the urinary enzymes measured in this study was adequate as biomarkers of nephrotoxicity, although the severity of the renal lesions had progressed. Mercury accumulated in a dose-related fashion primarily in the kidney, and to a lesser extent in the liver. The severity of the renal lesions was increased by continued exposure to mercuric chloride, as tissue concentrations of mercury rose in proportion to dose. Mercuric chloride treatment for 2 yr clearly exacerbated the severity of the spontaneous nephrotoxicity prevalent in aging F344 rats. The excessive mortality that occurred in the male rats was probably due to a combination of these factors. No renal tumors were detected in rats, possibly because the potential for their development was reduced; however, direct tissue contact with mercury induced squamous-cell papillomas of the forestomach in both sexes.

Telone II (technical grade, 1,3-dichloropropene), a soil fumigant, was evaluated in chronic toxicology/carcinogenicity studies using Fischer-344 (F344) rats and B6C3F1 mice of both sexes. Doses administered were 0, 25, or 50 mg/kg to rats and 0, 50, or 100 mg/kg to mice. Telone II was given in corn oil by gavage 3 times per week for 104 wk. Ancillary studies were conducted to determine time-related effects, in which dose groups containing 5 male and 5 females rats were killed after receiving Telone II for 9, 16, 21, 24, or 27 mo. The primary organs affected were the forestomach (rats and mice), urinary bladder (mice), lung (mice), and liver (rats). Compound-related non-neoplastic lesions included basal-cell or epithelial hyperplasia of the forestomach (rats and mice), epithelial hyperplasia of the urinary bladder (mice), and hydronephrosis (mice). Neoplastic lesions associated with administration of Telone II included squamous-cell papillomas of the forestomach (male and female rats, female mice), squamous-cell carcinomas of the forestomach (Male rats, female mice), transitional-cell carcinomas of the urinary bladder (female mice), alveolar/bronchiolar adenomas (female mice), and neoplastic nodules of the liver (male rats). Although cis- and trans-1,3-dichloropropene are the principal components of Telone II, the presence of 1% epichlorohydrin, a direct-acting mutagen and carcinogen added as stabilizer, may have influenced the development of forestomach lesions. The results of the ancillary studies supported the findings of the carcinogenesis studies and demonstrated the time-dependent development of lesions in the forestomach (basal-cell hyperplasia and squamous-cell papilloma). Under the conditions of these gavage studies, Telone II was shown to be carcinogenic in male and female F344 rats and female B6C3F1 mice. Although the study in male B6C3F1 mice was considered inadequate because of the low survival resulting from suppurative inflammation of the heart (myocarditis) in the control group, there was some indication of Telone II-related increases of transitional-cell carcinomas of the urinary bladder, squamous-cell papillomas of the forestomach, and alveolar/bronchiolar adenomas and carcinomas of the lung.

Five categories of evidence of carcinogenicity in rats and mice were used to group interpretative results on 86 chemicals studied in recent carcinogenicity tests carried out by the National Toxicology Program (NTP). Of these studies, 50% (43/86) were regarded as showing carcinogenic effects, 42% (36/86) gave no evidence of carcinogenicity, 6% (5/86) showed equivocal evidence of carcinogenicity, and 2% (2/86) were regarded as inadequate experiments. The liver was the most frequent site of cancer in male and female Fischer-344 rats and in male and female B6C3F1 mice. Male rats appeared more sensitive than female rats to the induction of neoplasia, while for mice the females seemed more responsive. The routes of administration yielding the highest percentage (80-83%) of positive studies were gavage and inhalation; approximately one-third of the feed, drinking water, and dermal studies showed carcinogenic effects. In feeding studies, overall survival in dosed and control groups were similar, while the majority of gavage studies showed significantly reduced survival in one or more dosed groups relative to the corresponding controls. The overall percentage of studies showing carcinogenic effects (50%) agrees closely with the rate reported by other investigators for nearly 200 earlier carcinogenicity experiments conducted by the National Cancer Institute.

Certain limitations on the flexibility of small-animal inhalation exposure systems are overcome by the machine control and monitoring of the concentration of the gas or vapor of interest. Computer assistance of chamber operation allows the user to simulate time-varying concentration profiles accurately and repeatedly. We exposed rats to seven different profiles in which the maximum concentration of carbon tetrachloride (CCl4) was 1500 ppm and the product of concentration times time (C X T) was 4500 ppm X h. The purpose was to determine the effects of systematically varying the shape of the concentration profile on the expression of hepatotoxicity of a chemical about which much was already known. All of the exposures were conducted within a span of 6 h. Examination of the severity of vacuolation and pattern of necrosis could be used to distinguish some of the exposure profiles from others. For example, vacuolation was less severe when two equal pulses were presented with an interval of 60 min, rather than 180-240 min. The indexes of necrosis varied in a more complex way, and the differences among the profiles that accounted for the differences in the patterns of the histopathological changes were not immediately apparent. We concluded that the characteristic of a time-related variation in concentration is one of the determinants of the inhalation hepatotoxicity of CCl4 and that the simple, time-weighted, average concentration may not always fairly represent the best model for the study of problems in inhalation toxicology.

Female B6C3F1 mice were exposed to graded doses of nickel sulfate to determine a threshold response for myelotoxicity and immunotoxicity, and to identify which of the populations of lymphoreticular cells were most sensitive to the toxic effects of nickel. Animals were given free access to the chemical in the drinking water at 0, 1, 5, or 10 g/l for 180 d. Water consumption, blood and tissue nickel concentrations, body and organ weights, histopathology, immune responses, bone marrow cellularity and proliferation, and cellular enzyme activities were evaluated. There was no mortality. Mice in the 5-g/l and 10-g/l dose groups drank less water than controls; the responses measured in the 10-g/l group may have been due to a combination of dehydration and chemical toxicity. Decreases in body and organ weights were confined to mice in the 10-g/l dose group, except for the dose-related reductions in thymus weights. Blood nickel was measured at 4, 8, 16, and 23 wk of exposure. The mean blood nickel values showed increases between 4 and 8 wk that were proportional to time and dose; thereafter there was no substantial increase in blood nickel in any of the dose groups, except for an increase in the mean blood concentration in the 10-g/l group at 23 wk. The kidney was the major organ of nickel accumulation. The primary toxic effects of nickel sulfate were expressed in the myeloid system. There were dose-related decreases in bone marrow cellularity, and in granulocyte-macrophage and pluripotent stem-cell proliferative responses. In unfractionated bone marrow cells glucose-6-phosphate dehydrogenase enzyme activity from the hexose monophosphate shunt was more sensitive to nickel sulfate than were representative glycolytic or Krebs cycle enzymes, with 25-35% maximum inhibition at 5 g/l and 10 g/l. Aliquots of bone marrow cells were separated into enriched bands of lymphocytes, granulocyte-macrophages, and erythrocytes; enzyme inhibition that occurred in unfractionated bone marrow cell aliquots was only expressed after cell separation in the enriched granulocyte-macrophage cell population, suggesting that these committed stem cells were a primary target of nickel sulfate toxicity. There was one example of systemic immunotoxicity, reduction in the lymphoproliferative response to lipopolysaccharide, and it was regarded as secondary to the primary effect of nickel sulfate on the myeloid system, since this was the only significant change among a panel of seven immune parameters that were evaluated.