Reproductive and developmental toxicity of inhaled 2,3-dichloro-1,3-butadiene in rats.

Inhalation developmental and reproductive toxicity studies were conducted with 2,3-dichloro-1,3-butadiene (DCBD), a monomer used in the production of synthetic rubber. In the reproductive toxicity study, Crl:CD(SD)IGS BR rats (24/sex/group) were exposed whole body by inhalation to 0, 1, 5, or 50 ppm DCBD (6 h/day) for approximately 10-11 weeks total, through premating (8 weeks; 5 days/week), cohabitation of mating pairs (up to 2 weeks, 7 days/week), post-cohabitation for males (approximately 7 days) and from conception to implantation (gestation days 0-7 [GD 0-7]), followed by a recovery period (GD 8-21) for presumed pregnant females. Estrous cyclicity was evaluated during premating (last 3 weeks) and cohabitation. Reproductive organs and potential target organs, sperm parameters, and GD 21 fetuses (viability, weight, external alterations) were evaluated. In the developmental study, pregnant Crl:CD(SD)IGS BR rats (22/group) were exposed whole body by inhalation to 0, 1, 10, or 50 ppm DCBD (6 h/day) on GD 6-20; dams were necropsied on GD 21 (gross post-mortem only) and fetuses were evaluated (viability, weight, and external, visceral and skeletal exams). During the in-life portion of the studies, body weight, food consumption, and clinical observation data were collected. At 50 ppm, gasping and labored breathing occurred in both studies during the first few exposures; body weight and food consumption parameters were affected in parental animals from both studies, but were more severely affected in the developmental study. Fetal weight was decreased in the developmental study at 50 ppm. Degeneration of the nasal olfactory epithelium was observed in the reproduction study at 50 ppm. There were no effects on reproductive function, embryo-fetal viability, or increases in fetal structural alterations in either study. The no-observed-adverse-effect level (NOAEL) for reproductive toxicity was 50 ppm. The NOAEL for systemic toxicity in the reproduction study was 5 ppm based on adverse effects on body weight and food consumption parameters and nasal olfactory epithelial toxicity at 50 ppm in parental rats. The NOAEL for maternal and developmental toxicity was 10 ppm based on reduced maternal weight gain and food consumption and reduced fetal weight at 50 ppm in the developmental toxicity study.

Testicular degeneration and spermatid retention in young male rats.

The incidence of spontaneous testicular atrophy and its morphological changes in relation to stage-specific spermatogenesis were investigated in young Crl:CD/BR male rats at 10-12 wk of age used as controls for toxicity screening during 1983-1990. The incidence of testicular degeneration was 2.5% (5/197) in control rats used for oral toxicity studies and 9.4% (31/327) in rats used for inhalation studies. The epididymal tubules of rats with testicular degeneration had exfoliated germ cells and low sperm density. The high incidence of testicular degeneration observed in the control rats used in inhalation studies may be related to the stress associated with immobilization in the restrainer during nose-only exposure conditions. The severity of testicular degeneration in the inhalation studies was mostly minimal. In these minimally affected testes, mature spermatids (step 19) were retained within normal-appearing germinal epithelium at spermatogenic stages IX-XIV. Also, eosinophilic globular bodies (EGBs) were formed with elongated or mature spermatids throughout all spermatogenic stages, but the general architecture of germinal epithelium was normal in appearance. By electron microscopy, EGBs were sequestered necrotic spermatids, and the germ cell degeneration was associated with cytoplasmic vacuolation of Sertoli cells. In moderate testicular degeneration, markedly decreased maturing spermatids (steps 15-19) and a slight depletion of round spermatids were observed in stages I-VIII. In severe testicular degeneration, seminiferous tubules were lined with 1-2 layers of round spermatids and spermatocytes with giant cell formation. The round spermatids served as a marker to identify spermatogenic stages (I-VIII) of the atrophic tubules. Also, in severe testicular degeneration, tubules in spermatogenic stages X-XIV had no elongated spermatids, and spermatocytes were exfoliated with occasional giant cell formation. Many seminiferous tubules were lined with only 1-2 layers of spermatocytes, and specific germ cell markers were not present.

Subchronic inhalation study with vinyl fluoride: effects on hepatic cell proliferation and urinary fluoride excretion.

Vinyl fluoride is used widely in the manufacture of fluoropolymers. Based in part on the structural similarity of vinyl fluoride to the hepatocarcinogens vinyl chloride and vinyl bromide, a TSCA Section 4 test rule mandated the testing of vinyl fluoride for oncogenicity. This report presents the results of a 90-day inhalation study in rats and mice with vinyl fluoride designed to set test concentrations for a subsequent oncogenicity study. Groups of 15 male and female rats and mice were exposed 6 hr per day, 5 days per week for approximately 90 days to target concentrations of 0, 200, 2000, or 20,000 ppm vinyl fluoride. Clinical chemical, hematological, and urine analyses were performed on rats after 45 and 90 days of exposure. A hematological evaluation was performed on mice following 45 and 90 days of exposure. A complete gross and microscopic evaluation was conducted at the end of the study. After 93 days on test, groups of five rats and five mice per sex were implanted with osmotic minipumps containing [3H]thymidine and were exposed for an additional 5 days to measure cell proliferation in liver, kidney, lung, and nasal cavity tissues. Results of the histopathological, clinical chemical, and hematological evaluations showed no significant effects of vinyl fluoride exposure at any concentration following either 45 or 90 days of exposure. A concentration-related increase in fluoride ion in urine was observed in rats at 45 and 90 days of exposure. A plateau in urinary fluoride excretion was observed at approximately 2000 ppm, suggesting saturation of vinyl fluoride metabolism. Vinyl fluoride-related cell proliferation effects were largely restricted to liver. Hepatic cell proliferation in male and female rats and mice was elevated at all concentrations. The response was similar at concentrations of either 2000 or 20,000 ppm and was consistent with concentration-response relationships for other haloethylenes. Taken together, the urinary fluoride excretion and hepatic cell proliferation data suggest a mechanistic link between the two effects. On the basis of these findings and experience with other haloethylenes, concentrations of vinyl fluoride to be tested for oncogenicity should be chosen such that the full linear range of the concentration-response curve is evaluated. The present study demonstrates through example the value of incorporating cell proliferation studies in standard testing protocols.

Retrovirus-like particles associated with myeloproliferative disease in the dog.

A case of granulocytic myeloproliferative disease with hypercalcaemia of malignancy in a 6-year-old Golden Retriever dog is described. Numerous retrovirus-like budding particles were observed at the cell surface of the neoplastic granulocytes, suggesting the presence of a new oncogenic virus. Several attempts by other workers to demonstrate the presence of an oncogenic retrovirus in canine lymphosarcoma have produced minimal results. This study suggests that non-lymphoid canine myeloproliferative disorders warrant further investigation.

Canine intestinal carcinoids.

Intestinal carcinoids were diagnosed in three aged dogs. Two of the neoplasms occurred in the rectum and one at the cecocolic junction. Judged by histologic criteria, all three carcinoids were considered to be malignant. Amyloid was present in both rectal tumors. In each tumor the diagnosis was confirmed by the finding of electron-dense intracytoplasmic secretory granules in the neoplastic cells.