Susceptibility of nonhuman primates to carcinogens of human relevance.

Nonhuman primates are a valuable experimental model for the evaluation of human carcinogenic risk but have not been widely used for various reasons, such as high cost and lack of availability. The present review discusses the findings from a long-term carcinogenesis study in nonhuman primates that was carried out under contract by the National Cancer Institute from 1961 to 1997. Among the classes of compounds investigated were model rodent carcinogens, food additives, food and environmental contaminants, heterocyclic amines, N-nitroso compounds, and antineoplastic and immunosuppressives. Of the model rodent carcinogens tested, only urethane was carcinogenic in monkeys. Long-term administration of saccharin or cyclamate did not result in toxicity or carcinogenicity in nonhuman primates, which is commonly seen in rodent models. Similar to rodent models and suspected in the human population, the fungal toxins, aflatoxin B1 and sterimatocystin, induced malignant liver tumors in monkeys. Relatively few animals administered DDT developed malignant tumors, however, hepatic and CNS toxicity was commonly observed. Hepatocellular carcinoma developed in a majority of monkeys administered the heterocyclic amine, IQ but not the structurally similar MeIQx. Resultant toxicity and carcinogenicity from N-nitroso compounds was variable. While diethylnitrosamine proved to be the most potent hepatocarcinogen tested, no malignant tumors were seen in animals administered N-methyl-N-nitro-N-nitrosoquanidine. Susceptibility of nonhuman primates to chemotherapeutic agents was also variable. Only procarbazine and N-methyl-N-nitrosourea were highly carcinogenic, whereas few tumors were seen as a result of cyclophosphamide, Adriamycin, melphalan, or azathioprine.

Organ weights and fat volume in rats as a function of strain and age.

The Fischer 344 (F344) rat and the Sprague-Dawley (SD) rat are used commonly to evaluate potential adverse health effects resulting from environmental exposure to chemicals. They are also the most common rat strain/stock used in physiologically based pharmacokinetic (PBPK) modeling. Accurate characterization of model input parameters will improve the usefulness of PBPK model predictions. Thus, organ (i.e., liver, kidneys, spleen, stomach, small intestine, large intestine, heart, lungs, brain) weights and body fat were measured in male SD rats of different ages (4 to 40 wk) and in young (9 to 10 wk) and old (22 to 23 mo) male F344 rats. Comparison of age-matched (9 to 10 wk) F344 and SD rats revealed that the SD rats weighed significantly more and had significantly higher absolute organ weights. These significant differences usually disappeared when organ weights were expressed as a percentage of body weight (relative organ weight). Percent body fat was significantly lower in the age-matched SD rats (6.48%) than in their F344 counterparts (8.67%). As expected, both body weight and absolute organ weights were significantly higher in old than in young F344 rats. However, these differences were largely reversed when relative organ weights were considered, with most relative organ weights significantly lower in the old F344 rats. Body fat as a percentage of body weight was 14.02% in the old F344 rats. When SD rats of various ages were examined, relative organ weights declined between the ages of 4 and 14 wk. In contrast, significant differences in percent body fat were not detected among the SD rats of different ages and weights examined in this study (4 to 40 wk, approximately 75 to approximately 450 g). In summary, values for physiological input parameters are provided that should prove useful in development and implementation of more accurate PBPK models.