Billy J. Chou

Toxicity and carcinogenicity study in F344 rats following 2 years of whole-body exposure to naphthalene vapors.

The toxicologic and carcinogenic potential of naphthalene was studied by exposing groups of 49 male and 49 female F344 rats to atmospheres containing 0, 10, 30, or 60 ppm of the chemical for 6 h daily, 5 days/wk for 2 yr. Mean body weights of exposed groups of male rats were less than for the control group throughout most of the study. Mean body weights of exposed female rats were generally similar to those of controls. Survival of exposed and control rats was similar. Under the conditions of this 2-yr inhalation study, naphthalene was carcinogenic to male and female F344/N rats, causing increased incidences of respiratory epithelial adenoma (males: control, 0%; low dose, 12%, mid dose, 17%; high dose, 31%; females: 0%; 0%; 8%; 4%) and olfactory epithelial neuroblastoma (males: control, 0%; low dose, 0%; mid dose, 8%; high dose, 6%; females: 0; 4%; 6%; 24%) of the nose. In both sexes of rats, exposure to naphthalene also caused significant increases in the incidences of nasal lesions including hyperplasia, atrophy, chronic inflammation, and hyaline degeneration of the olfactory epithelium and hyperplasia; squamous metaplasia, hyaline degeneration, and goblet-cell hyperplasia of the respiratory epithelium; and glandular hyperplasia and squamous metaplasia.The toxicologic and carcinogenic potential of naphthalene was studied by exposing groups of 49 male and 49 female F344 rats to atmospheres containing 0, 10, 30, or 60 ppm of the chemical for 6 h daily, 5 days/wk for 2 yr. Mean body weights of exposed groups of male rats were less than for the control group throughout most of the study. Mean body weights of exposed female rats were generally similar to those of controls. Survival of exposed and control rats was similar. Under the conditions of this 2-yr inhalation study, naphthalene was carcinogenic to male and female F344/N rats, causing increased incidences of respiratory epithelial adenoma (males: control, 0%; low dose, 12%, mid dose, 17%; high dose, 31%; females: 0%; 0%; 8%; 4%) and olfactory epithelial neuroblastoma (males: control, 0%; low dose, 0%; mid dose, 8%; high dose, 6%; females: 0; 4%; 6%; 24%) of the nose. In both sexes of rats, exposure to naphthalene also caused significant increases in the incidences of nasal lesions including hyperplasia, atrophy, chronic inflammation, and hyaline degeneration of the olfactory epithelium and hyperplasia; squamous metaplasia, hyaline degeneration, and goblet-cell hyperplasia of the respiratory epithelium; and glandular hyperplasia and squamous metaplasia.

Inhalation Toxicity Studies of Cobalt Sulfate in F344/N Rats and B6C3F1 Mice

Groups of 10 F344/N rats and B6C3F1 mice of each sex were exposed to cobalt sulfate heptahydrate aerosols of 0, 0.3, 1.0, 3.0, 10, or 30 mg/m3, 6 hr per day, 5 days per week, for 13 weeks. All rats and female mice and all but 2/10 male mice exposed at the top concentration survived to the end of the studies. Polycythemia was observed in exposed rats but not in mice. Sperm motility was decreased in mice exposed at 3 mg/m3 (the lowest concentration evaluated) and at higher concentrations, and increased numbers of abnormal sperm and decreased testis and epididymal weights occurred in mice exposed to 30 mg/m3. Cobalt content in the urine of rats increased with increasing atmospheric cobalt exposure. Primary histopathologic effects were limited to the respiratory tract. Lesions in rats and mice included degeneration of the olfactory epithelium, squamous metaplasia of the respiratory epithelium, and inflammation in the nose; inflammation, necrosis, squamous metaplasia, ulcers (rats), and inflammatory polyps (rats) of the larynx; metaplasia of the trachea (mice); and fibrosis, histiocytic infiltrates, bronchiolar epithelial regeneration, and epithelial hyperplasia in the alveoli of the lung. The most sensitive tissue was the larynx, with squamous metaplasia observed in rats and mice at the lowest exposure concentration of 0.3 mg/m3. Thus, a no-observed-adverse-effect level was not reached in these studies.

Two-Year and Lifetime Toxicity and Carcinogenicity Studies of Ozone in B6C3F1 Mice

To evaluate the toxicity and carcinogenic potential of long-term exposure to ozone, B6C3F1 mice were exposed by whole-body inhalation to 0, 0.12, 0.5, or 1.0 ppm and 0, 0.5, or 1.0 ppm ozone for 24 or 30 mo (lifetime), respectively. The incidence of alveolar/ bronchiolar adenomas and carcinomas (combined) increased (p < 0.05) in female mice exposed to 1.0 ppm for 24 or 30 mo and marginally increased (p > 0.05) in male mice exposed to concentrations of 0.5 or 1.0 ppm. An increased incidence of nonneoplastic lesions were observed in the nasal cavities and in the centriacinar region of the lung of mice exposed to 0.5 or 1.0 ppm for 24 and 30 mo. Nasal cavity lesions were mild and included hyaline degeneration, hyperplasia, squamous metaplasia, fibrosis and suppurative inflammation of the transitional and respiratory epithelium of the lateral wall, and atrophy of the olfactory epithelium. Lung lesions included replacement of the epithelium of the alveolar ducts and adjacent alveolar septa with epithelium similar to that normally found in terminal bronchioles (metaplasia) and associated alveolar histiocytosis. Based on the results of these studies, we conclude that inhalation exposure of B6C3F1 mice to ozone for 24 or 30 mo (a) is carcinogenic in female B6C3F1 mice exposed to 1.0 ppm of ozone based on an increased incidence of alveolar/bronchiolar adenoma or carcinoma and (b) results in mild, site-specific, nonneoplastic lesions in the nasal cavity and centriacinar lung of male and female mice exposed to 0.5 or 1.0 ppm of ozone for 2 yrs, which persist with continued exposure to 30 mo. It is uncertain whether or not the marginal increase (p > 0.05) of alveolar/bronchiolar neoplasms in male B6C3F1 mice resulted from exposure to ozone.

Toxicology and Carcinogenesis Studies of Ozone and Ozone 4-(N-Nitrosomethylamino)-1-(3-Pyridyl)-1-Butanone in Fischer-344/N Rats

The purpose of this study was to evaluate the toxicity and potential carcinogenicity or cocarcinogenicity of ozone exposure in rats. Fischer-344/N (F-344/N) rats were exposed 6 hr/day, 5 days/wk, to 0, 0.12, 0.5, or 1.0 ppm ozone by inhalation for 2-yr and lifetime exposures. The cocarcinogenicity study included subcutaneous administration of 0, 0.1, or 1.0 mg/kg body weight of 4-(N-nitrosomethylamino)-1-(3-pyridyl)-1-butanone (NNK) and inhalation of 0 or 0.5 ppm ozone to male rats. NNK was administered by subcutaneous injections 3 times per week for the first 20 wk with ozone inhalation exposure. The ozone inhalation exposure was for 2 yr (104 wk), including the first 20 wk of NNK treatment and continuing for 84 wk after the last NNK injection. Ozone exposure caused a concentration-related increase in inflammation of the centriacinar region of the lung. There was also increased fibrosis and an extension of the bronchiolar epithelium in these centriacinar regions to involve the proximal alveoli. There was no increased incidence of neoplasms at any site, including the lung, that was associated with ozone exposure. Rats administered 1.0 mg/kg body weight NNK alone had an increased incidence of bronchiolar/alveolar neoplasms, but this effect was not enhanced by ozone exposure. Ozone exposure for 2 yr and lifetime was associated with site-specific toxic alterations in the nasal passage and lung similar to those previously described for short-term exposures. While there was significant attenuation of the pulmonary lesions as compared to short-term exposures, lesions persisted in the lifetime study and there was evidence of a mild progressive fibrosis. We conclude that under the conditions of these studies: (a) ozone exposure is not carcinogenic to either male or female F-344/N rats, (b) ozone does not enhance the incidence of pulmonary neoplasms in F-344/N rats exposed to a known pulmonary carcinogen (NNK), and (c) mild site-specific toxic lesions characteristic of ozone exposure persist in the nasal passage and lung throughout the lifetime of the rat with continued ozone exposure.

Carcinogenesis Studies of Tetrahydrofuran Vapors in Rats and Mice

Tetrahydrofuran (THF) is a widely used industrial solvent and was selected for carcinogenesis studies by the National Toxicology Program (NTP) because of its potential for widespread occupational exposure in humans and a lack of information on animal toxicity and carcinogenicity. Groups of 50 male and 50 female F344/N rats and B6C3F1 mice were exposed to 0, 200, 600, or 1800 ppm THF by inhalation, 6 h per day, 5 days per week, for 105 weeks. Survival and mean body weights of male and female rats exposed to THF were comparable to that of the controls. No clinical findings or nonneoplastic lesions related to THF exposure were observed in male or female rats. The incidences of renal tubule epithelial adenoma or carcinoma (combined) in exposed male rats occurred with a positive trend, and in males exposed to 600 and 1800 ppm exceeded the historical range for controls in 2-year NTP inhalation studies. There were no other neoplastic lesions related to THF exposure observed in male or female rats. After week 36, the survival of male mice exposed to 1800 ppm was significantly lower than that of the controls. Mean body weights of male and female mice exposed to THF were similar to those of the controls throughout the study. Male mice exposed to 1800 ppm were observed in a state of narcosis during and up to 1 h after the exposure periods. Nonneoplastic lesions related to THF exposure were not observed in male or female mice. The neoplastic lesions related to THF exposure were seen in female mice only. In female mice exposed to 1800 ppm, the incidences of hepatocellular neoplasms were significantly greater than those in the controls. In conclusion, there was some evidence of carcinogenic activity of THF in male F344/N rats due to increased incidences of adenoma or carcinoma (combined) of the kidney at the 600 and 1800 ppm exposure levels. There was clear evidence of carcinogenic activity in female B6C3F1 mice based on increased incidences of hepatocellular neoplasms at the 1800 ppm exposure level. THF was not carcinogenic in female rats or male mice exposed at 200, 600, or 1800 ppm.

Toxicity of inhaled chloroprene (2-chloro-1,3-butadiene) in F344 rats and B6C3F1 mice

Chloroprene (2-chloro-1,3-butadiene) is a high production chemical used almost exclusively in the production of polychloroprene (neoprene) elastomer. Because of its structural similarity to isoprene (2-methyl-1,3-butadiene) and to 1,3-butadiene, a potent trans-species carcinogen, inhalation studies were performed on chloroprene to characterize its toxicological potential and to provide a basis for selecting exposure concentrations for chronic toxicity and carcinogenicity studies. Thirteen-week inhalation toxicology studies were conducted in male and female F344 rats and B6C3F(1) mice at exposure concentrations of 0, 5, 12, 32 or 80 ppm (6 h/day; 5 days/week). A 200 ppm exposure group was also included for rats only, because a previous study showed that this concentration of chloroprene is lethal to mice. In mice, exposure to 80 ppm chloroprene caused a marginal decrease in body weight gain in males and epithelial hyperplasia of the forestomach in males and females. This lesion has been observed in mice exposed to isoprene or 1,3-butadiene. In rats, exposure to 80 ppm chloroprene or higher concentrations caused degeneration and metaplasia of the olfactory epithelium and exposure to 200 ppm caused anemia, hepatocellular necrosis and reduced sperm motility. These lesions have not been observed in rats exposed to isoprene or 1,3-butadiene. The profile of toxic effects of chloroprene is considerably different from that of isoprene or 1,3-butadiene; this may be due to differences in exposure concentrations that were used in toxicology studies of these compounds and /or to the influence of the chlorine substitution on the toxicokinetics of these compounds, on their biotransformation, or on the reactivity of metabolic intermediates with tissue macromolecules.

Toxicity of Furfuryl Alcohol to F344 Rats and B6C3F1 Mice Exposed by Inhalation

Groups of F344 rats and B6C3F1 mice were exposed to furfuryl alcohol vapor for 6 hours per day, 5 days per week for 14 days (0, 16, 31, 63, 125, 250 ppm) or 13 weeks (0, 2, 4, 8, 16, 32 ppm). Reduced survival was observed in the 14‐day study at 250 ppm. Final mean body weights of rats and mice exposed to 125 ppm and of female mice exposed to 63 ppm were lower than controls at the end of the 14‐day study; there were no significant differences in mean body weight among chemical‐exposed and control groups in the 13‐week study. Exposure to furfuryl alcohol had no toxicologically significant effect on organ weights in either rats or mice, and did not cause any adverse changes in hematology or serum chemistry parameters evaluated in rats in the 13‐week study. Microscopic lesions associated with exposure to furfuryl alcohol were present in the nose of both rats and mice at all exposure concentrations in both the 14‐day and 13‐week studies. Lesions observed in the 14‐day study consisted of inflammation of the nasal turbinates accompanied by necrosis and squamous metaplasia of the respiratory epithelium and necrosis and degeneration of the olfactory epithelium. Similar lesions were observed in both rats and mice in the 13‐week study. In addition, squamous metaplasia and goblet cell hyperplasia of the respiratory epithelium, squamous metaplasia of the transitional epithelium and degeneration, hyperplasia and some respiratory metaplasia of the olfactory epithelium were also observed in rats in the 13‐week study, and hyaline droplets in the respiratory epithelium and chronic inflammation and respiratory metaplasia in the olfactory epithelium were observed in mice in the 13‐week study. In general the nasal passages of mice appeared less sensitive than those of rats at the concentrations used in the 13‐week study; a no‐observable‐effect level was not achieved in either the 14‐day or the 13‐week study. ©1997 by John Wiley & Sons, Ltd.

Inhalation toxicity and carcinogenicity of isoprene in rats and mice: comparisons with 1,3-butadiene

As with 1,3-butadiene (BD), inhalation exposure of B6C3F1 mice to isoprene (2-methyl-1,3-butadiene) caused a macrocytic anemia; induced increases in sister chromatid exchanges in bone marrow cells and in levels of micronucleated erythrocytes in peripheral blood; and produced degeneration of the olfactory epithelium, forestomach epithelial hyperplasia, and testicular atrophy. Most notable was the finding that like BD, isoprene induced neoplasms in the liver, lung, Harderian gland, and forestomach of mice. The carcinogenic effects of isoprene were observed after a 26-week exposure (6 h/day, 5 days/week) of male mice to 700 ppm or higher concentrations of isoprene followed by a 26-week recovery period. Unlike BD, isoprene did not induce lymphomas or hemangiosarcomas of the heart in mice under these conditions nor did it induce chromosomal aberrations in mouse bone marrow cells. No toxicological effects were evident in rats exposed for 13 weeks to either isoprene or BD at concentrations up to 7000 ppm or 8000 ppm, respectively. Interstitial cell hyperplasia of the testis was observed in male F344 rats exposed to 7000 ppm isoprene for 26 weeks, and following a 26-week recovery period, there was a marginal increase in benign testicular interstitial cell tumors.

Development of α2u-Globulin Nephropathy and Adrenal Medullary Pheochromocytomas in Male Rats Following Exposure to Stoddard Solvent IIC

Stoddard solvent IIC is widely used as a solvent in paints and varnishes, and for dry cleaning and other grease removal applications. Because concern exists regarding the long-term effects of occupational exposure in industrial settings, the toxicity and carcinogenicity of Stoddard solvent IIC were evaluated in male and female F344/N rats and B6C3F1 mice. Rats and mice were exposed to 0, 138, 275, 550, 1100, or 2200 mg/m3 Stoddard solvent IIC by whole-body inhalation for 3 mo, and to 0, 138 (male rats), 550, 1100, or 2200 (female rats and male and female mice) mg/m3 for 2 yr. The kidney, liver, and adrenal medulla were targets of Stoddard solvent IIC toxicity in rats. After 3 mo of exposure, male rats developed lesions characteristic of α2u-globulin nephropathy. Male and female rats displayed increased liver weights and/or clinical pathology changes suggestive of hepatic injury, although no accompanying histopathologic changes were observed. After 2 yr, increased incidences of adrenal medullary pheochromocytomas provided some evidence of carcinogenicity in male rats. Renal tubule adenomas were slightly increased in male rats after 2 yr, and may have been related to exposure. In mice, there was no chemical-related toxicity after 3 mo, with the exception of increased liver weights in male mice exposed to 2200 mg/m3. After 2 yr, the incidences of hepatocellular adenomas were increased in female mice exposed to 2200 mg/m3; however, these increases were marginal and associated with increases in body weight. There was no evidence of Stoddard solvent IIC carcinogenicity in female rats or male mice. In summary, inhalation exposures of Stoddard solvent IIC resulted in renal toxicity and adrenal medullary pheochromocytomas in male rats. The liver also appeared to be a site of toxicity in male and female rats and mice.