To investigate the toxicity and carcinogenic potential of indole-3-carbinol (I3C), the National Toxicology Program has conducted 13-week subchronic studies in Fisher 344 rats and B6C3F1 mice, and chronic 2-year bioassays in Sprague-Dawley rats and B6C3F1 mice. While the chronic study results are not yet available, subchronic study results and short-term special evaluations of interim sacrifices in the 2-year rat bioassay are presented. F344 rats were orally gavaged ≤300 mg I3C/kg body weight 5 days a week for 13 weeks. Rats treated with ≥150 mg/kg demonstrated a dose-related dilation of lymphatics (lymphangiectasis) of the duodenum, jejunum, and mesenteric lymph nodes. Material within dilated lacteals stained positively for Oil Red O and Sudan Black, consistent with lipid. Electron microscopic evaluation confirmed extracellular lipid accumulation within the villar lamina propria, lacteals, and within villar macrophages. Analyses of hepatic and pulmonary CYP1A enzymes demonstrated dose-dependent I3C induction of CYP1A1 and 1A2. B6C3F1 mice orally gavaged ≤250 mg I3C/kg body weight did not demonstrate histopathological changes; however, hepatic CYP induction was similar to that in rats. The histopathologic changes of intestinal lymphangiectasis and lipidosis in this study share similarities with intestinal lymphangiectasia as observed in humans and dogs. However, the resultant clinical spectrum of protein-losing enteropathy was not present.

The heart is increasingly recognized as a target for toxicity. As studies in laboratory rodents are commonly used to investigate the potential toxicity of various agents, the identification and characterization of lesions of cardiotoxicity is of utmost importance. Although morphologic criteria have been established for degenerative myocardial lesions in rats and mice, differentiation of spontaneously occurring lesions from toxin-induced or toxin-related lesions remains difficult. A retrospective light microscopic evaluation was performed on the hearts of F344 rats and B6C3F(1) mice from National Toxicology Program (NTP) studies of six chemicals identified in the NTP database in which treatment-induced myocardial toxicity was present. Two previously defined myocardial lesions were observed: "cardiomyopathy" that occurred spontaneously or as a treatment-related effect and "myocardial degeneration" that occurred as a treatment-related effect. Both lesions consisted of the same basic elements, beginning with myofiber degeneration and necrosis, with varying amounts of inflammation, interstitial cell proliferation, and eventual fibrosis. This observation is indicative of the heart's limited repertoire of responses to myocardial injury, regardless of the nature of the inciting agent. A prominent differentiating factor between spontaneous and treatment-induced lesions was distribution and lesion onset. Once the respective lesions had undergone fibrosis, however, they generally appeared morphologically indistinguishable.

Exposure to dioxin and dioxin-like compounds (DLCs) has been connected to the induction of chloracne in humans and animals. 3,3',4,4'-Tetrachloroazobenzene (TCAB) is an environmental contaminant that induces chloracne in humans. TCAB has been studied only to a limited extent in laboratory animals. While performing a 2-year gavage study in B6C3F1 mice to evaluate the toxic and carcinogenic effects of TCAB, we also explored potential chloracnegenic properties. Groups of 50 male and 50 female B6C3F1 mice were exposed by gavage to TCAB at dose levels of 0, 3, 10 and 30 mg/kg for 5 days a week for 2 years. The animals developed treatment-related gross inflammatory skin lesions, which were characterized histologically by inflammation, fibrosis, hyperplasia, and ulcers. Additionally, many of the animals developed follicular dilatation and sebaceous gland atrophy, consistent with chloracne-like lesions. This current 2-year study supports recently published papers showing susceptibility to chloracne in mouse strains other than hairless mice. The chloracne-like lesions were not clinically evident; therefore, our study highlights the need for careful examination of the skin in order to identify subtle lesions consistent with chloracne-like changes in rodents exposed to dioxin and DLCs. Since previous short-term studies did not demonstrate any skin lesions, we suggest that reliable assessment of all safety issues involving dioxin and DLCs requires evaluation following chronic exposure. Such studies in animal models will help to elucidate the mechanisms of dioxin-related health hazards.

Induction of heart disease can be related to exposure to a number of agents, including environmental chemicals. Studies with laboratory rodents are commonly use to identify cardiotoxic agents and to investigate mechanisms of toxicity. This study was conducted to characterize spontaneous and chemically-induced rodent heart lesions. A retrospective light-microscopic evaluation was performed on the hearts of F344 rats and B6C3F1 mice from National Toxicology Program studies of six chemicals in which chemically-induced myocardial toxicity was present: oxymetholone, monochloroacetic acid, 3,3′–4,4′-tetrachoroazoxybenzene, diethanolamine, urethane, and methylbromide. Two myocardial lesions were observed: cardiomyopathy (multifocal myofiber degeneration that could occur spontaneously or as a treatment effect) and degeneration (diffuse myofiber degeneration that was clearly related to treatment). Oxymetholone produced cardiotoxicity that was apparent as an increase in the incidence and average severity of cardiomyopathy. The remaining five chemicals produced degeneration, which appeared morphologically similar with each of the chemicals. Based on available information concerning possible mechanisms by which each of these chemicals may induce cardiotoxicity, this evaluation indicated it may be possible to place the chemicals into two main categories: (1) those that primarily affected the coronary vasculature with secondary effects on the myocardium (oxymetholone), and (2) those that had a direct toxic effect on the myocardial cells (the remaining five chemicals). Beyond this, however, light-microscopic findings did not indicate any specific mechanisms. Additional morphologic evaluations, such as electron microscopy or special histochemical or immunostains, may help identify specific subcellular sites of toxic damage, which in turn can indicate appropriate types of molecular mechanistic studies.