Morbidity and mortality resulting from acute inhalation exposures to hydrogen fluoride and carbonyl fluoride in rats.

OBJECTIVE: Experiments were undertaken to compare morbidity and mortality from brief inhalation exposures to high levels of hydrogen fluoride (HF) and carbonyl fluoride (COF2). METHODS: Rats from both sexes were exposed for durations of 5 and 10 min to nominal concentrations of 10,000 to 57,000 ppm HF or 500 to 10,000 ppm COF2. Respiration was monitored before, during, and after exposure. Animals were observed up to 6 days post-exposure. Terminal blood samples were collected for routine clinical chemistry and hematology. Post-mortem lung fluoride concentrations and lung weights were measured, and gross pathology noted. RESULTS: Both gases produced respiratory depression independent of concentration or exposure duration with minute ventilation decreasing to approximately 50% of baseline. Estimated mixed-gender HF and COF2 10-min LC50's were 48,661 ppm and 1083 ppm, respectively. HF mortalities were generally delayed 3 to 4 days post-exposure, while COF2 mortalities occurred during or briefly after exposure. Lung fluoride levels increased with COF2 dose, though elevated lung weights occurred only at the mid-level exposures. Lung weights were unaffected in the HF-exposed animals, and their lung fluoride concentrations were variable. Clinical chemistry and hematology had few consistent trends with the exception of hemoconcentration primarily in HF-exposed males. These short-term exposure experiments conclude that COF2 is nearly 45 times more lethal than HF in rats. CONCLUSIONS: These experiments suggest that hydrolysis to HF cannot solely explain COF2 toxicity. Although HF and COF2 may have common injury mechanisms, they are expressed to markedly different degrees and temporal occurrence.

Developmental toxicity study of dimethylpiperidone.

The potential maternal and developmental toxicity of dimethylpiperidone (DMPD) was assessed in rats. Groups of 25 mated female Crl:CD (SD)IGS BR rats were exposed by inhalation (whole-body exposures) for approximately six hours per day over days 7-21 of gestation (G); day 1G was the day of copulation plug detection. The exposure levels were 0, 52, 260, or 340 (vapor plus aerosol) mg/m3 DMPD. During the in-life portion, body weights, food consumption, and clinical observation data were collected. On day 22G, the dams were euthanized and examined for gross external and internal alterations. The uterine contents were described and the fetuses were weighed and examined for external, visceral, and skeletal alterations. Maternal toxicity was seen at both 260 and 340 mg/m3. At 340 mg/m3, evidence of maternal toxicity included mortality, increased clinical observations, and decreased body weight and food consumption. At 260 mg/m3, maternal toxicity was limited to increased clinical observations and decreased food consumption. Developmental toxicity was also produced at 260 and 340 mg/m3. At 340 mg/m3, evidence of developmental toxicity included decreased fetal weight, increased embryofetal lethality with concomitant reductions in litter size, and increased fetal malformations and variations. At 260 mg/m3, effects in fetuses were limited to slightly decreased fetal weight and increased fetal variations; additionally, one litter from this level consisted entirely of resorptions. There were no compound-related effects in either dams or fetuses at 52 mg/m3. It was, therefore, concluded that DMPD was not selectively toxic to the rat conceptus.