No abstract

DFMO, an irreversible inhibitor of ornithine decarboxylase (ODC), is under development as a chemopreventive drug against cancers with pronounced proliferative phases. In support of human clinical trials, preclinical developmental toxicity studies were conducted in pregnant rats and rabbits. Rats were treated during GD 6-17, and fetuses were obtained by C-section on GD 20. Rabbits were treated during GD 7-20, and fetuses were obtained by C-section on GD 29. The dose range-finding study in rats (5/group at 0, 50, 125, 300, 800, or 1000 mg/kg/day) revealed maternal toxicity at doses > or = 800 mg/kg/day (decreased body weights and food consumption) and developmental toxicity at doses > or = 300 mg/kg/day (increased early resorptions and reduced fetal body weights). In the main study, rats (25/group) received 0, 30, 80, or 200 mg/kg/day. Developmental toxicity in the absence of maternal toxicity was observed at 200 mg/kg/day as significantly decreased fetal weights and increased incidence of litters with skeletal variations of 14th rudimentary rib, 14th full rib, and/or 27th presacral vertebrae. There were no treatment-related fetal skeletal malformations or external or visceral anomalies at any dose level. The dose range-finding study in rabbits (5/group at 0, 30, 60, 120, 240, or 500 mg/kg/day) revealed developmental toxicity at doses > or = 60 mg/kg/day (increased resorptions and reduced fetal body weights) in the absence of maternal toxicity. In the main study, rabbits (20/group) received 0, 15, 45, or 135 mg/kg/day. Developmental toxicity in the absence of maternal toxicity was observed at 135 mg/kg/day as nonsignificantly increased early resorptions, decreased implantation sites, decreased viable fetuses, and reduced fetal weights. There were no external, visceral, or skeletal anomalies at any dose level. Thus, in the main developmental toxicity studies, DFMO produced developmental but not maternal toxicity at 200 and 135 mg/kg/day in rats and rabbits, respectively. Accordingly, in rats, the maternal no-observable-effect level (NOEL) was 200 mg/kg/day and the fetal NOEL was 80 mg/kg/day; while in rabbits the maternal NOEL was 135 mg/kg/day and the fetal NOEL was 45 mg/kg/day. These fetal NOELs are several-fold higher than the dose level currently used in Phase II and III clinical trials (approximately 13 mg/kg).

Based on these results, no evidence of maternal toxicity, developmental toxicity, or teratogenicity was observed in rats or rabbits treated with DBDPEthane at dosage levels up to 1,250 mg/kg-day.

No abstract

The U.S. Environmental Protection Agency (EPA) National Ambient Air Quality Standards for ozone and particulate matter are requiring urban nonattainment areas to implement pollution-reduction strategies for anthropogenic source emissions. A type of fuel shown to decrease combustion emissions components versus traditional diesel fuels is the diesel-water emulsion. The Lubrizol Corporation in conjunction with Lovelace Respiratory Research Institute and several subcontracting laboratories recently conducted a rodent health assessment of inhaled combustion emissions of PuriNO(x) diesel fuel emulsion. Combustion emissions from either of two 2001 model Cummins 5.9-L ISB engines were diluted with charcoal-filtered air to exposure concentrations of 100, 200, and 400 microg total particulate matter/m(3). The engines were operated on a continuously repeating, heavy-duty certification cycle (U.S. Code of Federal Regulations, Title 40, Chapter I) using Rotella-T 15W-40 engine oil. Nitrogen oxide and particulate matter were reduced when engines were operated on PuriNO(x) versus California Air Resources Board diesel fuel under these conditions. Male and female F344 rats were housed in Hazleton H2000 exposure chambers and exposed to exhaust atmospheres 6 h/day, 5 days/wk for the first 11 wk and 7 days/wk threafter. Exposures ranged from 58 to 70 days, depending on the treatment group. Indicators of general toxicity (body weight, organ weight, clinical pathology, and histopathology), neurotoxicity (glial fibrillary acidic protein assay), genotoxicity (Ames assay, micronucleus, sister chromatid exchange), and reproduction and development were measured. Overall, effects observed were mild. Emulsion combustion emissions were not associated with neurotoxicity, reproductive/developmental toxicity, or in vivo genotoxicity. Small decreases in serum cholesterol and small increases in platelet values in some groups of exposed animals were observed. Particulate matter accumulation within alveolar macrophages was evident in all exposure groups. These findings are consistent with normal physiological responses to particle inhalation. Other statistically significant effects were present in some measured parameters of other exposed groups but were not clearly attributed to emissions exposure. Positive mutagenic responses in several strains of Salmonella typhimurium were observed subsequent to treatment with emulsion emissions subfractions. Based on the cholesterol and platelet results, it can be concluded that the 100 microg/m(3) exposure level was the no-observed-effect level. In general, biological findings in diesel emulsion emission-exposed animals and bacteria were consistent with exposure to petroleum diesel exhaust in the F344 rat and Ames assays.