Pesticides and fertilizers, as used in modern agriculture, contribute to the overall low-level co... more Pesticides and fertilizers, as used in modern agriculture, contribute to the overall low-level contamination of groundwater sources. In order to determine the potential of pesticide and fertilizer mixtures to produce reproductive or developmental toxicity at concentrations up to 100 x the median level found in groundwater, we prepared and studied two mixtures of pesticides and a fertilizer (ammonium nitrate). One mixture containing aldicarb, atrazine, dibromochloropropane, 1,2-dichloropropane, ethylene dibromide, and simazine plus ammonium nitrate was considered to be a representative of groundwater contamination in California (CAL). The other, containing alachlor, atrazine, cyanazine, metolachlor, metribuzin, and ammonium nitrate, simulated groundwater contamination in Iowa (IOWA). Each mixture was administered in the drinking water of either Swiss CD-1 mice during a Reproductive Assessment by Continuous Breeding study or pregnant Sprague-Dawley rats (gd 6-20) at three dose levels (1x, 10x, and 100x) where 1x was the median concentration of each pesticide component as determined in the groundwater surveys in California or Iowa. Unlike conventional toxicology studies, the purpose of this study was to evaluate the health effects of realistic human concentrations. Thus, the testing concentrations are probably well below the maximally tolerated dose. Propylene glycol was used as the solubilizer for the pesticides in drinking water formulations in both studies. In the reproductive study, neither mixture caused any clinical signs of toxicity, changes in food or water consumption, or body weight in either F0 or F1 mice at doses up to 100x the median groundwater concentrations. There were no treatment-related effects on fertility or any measures of reproductive performance of either the F0 or the F1 generation mice exposed to either CAL or IOWA at up to 100x. Similarly, measures of spermatogenesis, epididymal sperm concentration, percentage motile sperm, percentage abnormal sperm, and testicular and epididymal histology were normal. In the developmental study, CAL- or IOWA-exposed females did not exhibit any significant treatment-related clinical signs of toxicity. No adverse effects of CAL or IOWA were observed for measures of embryo/fetal toxicity, including resorptions per litter, live litter size, or fetal body weight. CAL or IOWA did not cause an increased incidence of fetal malformations or variations. In summary, administration of these pesticide/fertilizer mixtures at levels up to 100-fold greater than the median concentrations in groundwater supplies in California or Iowa did not cause any detectable reproductive (mice), general, or developmental toxicity (rats).
The potential reproductive toxicity of boric acid (BORA) in CD-1 mice (Swiss) was evaluated using... more The potential reproductive toxicity of boric acid (BORA) in CD-1 mice (Swiss) was evaluated using the Reproductive Assessment by Continuous Breeding (RACB) Protocol. BORA was administered in the feed for 27 weeks to male and female Swiss (CD-1) mice at concentrations of 0, 1000, 4500, or 9000 ppm. Estimated doses, based on feed consumption and body weight, averaged 152, 636, and 1262 mg/kg body wt during Week 1 for males for 1000, 4500, and 9000 ppm, respectively. During 14 weeks of cohabitation, fertility of F0 mice was partially reduced at 4500 ppm and totally eliminated at 9000 ppm. No litters, dead or alive, were produced by 9000 ppm cohabited pairs. Among the litters born at 4500 ppm, live litter size and body weight were significantly reduced. A crossover mating trial of control and 4500 ppm groups confirmed the male as the affected sex, with fertility rates and the mating index significantly lower in the 4500 male x 0 ppm female group. At necropsy, after 27 weeks of BORA exposure, dose-related changes were present in F0 males for reduced body and reproductive organ weights, increased incidence of abnormal sperm, decreased sperm concentration and motility, and seminiferous tubule degeneration. In the 4500 ppm females, dietary BORA for 27 weeks caused significantly decreased weights of kidney/adrenals and livers; kidney/adrenal weight was also reduced in 4500 ppm males. The last litters of the control and 1000 ppm females, born in the 14-week breeding phase, were reared to 74 days of age and then mated in nonsibling pairs within treatment groups. These F1 mice had normal fertility, but the adjusted mean body weight of F2 pups was decreased. These data establish the reproductive toxicity of BORA in CD-1 mice and demonstrate that the male is the most sensitive sex.
Emivirine (EMV), formerly known as MKC-442, is 6-benzyl-1-(ethoxymethyl)-5-isopropyl-uracil, a no... more Emivirine (EMV), formerly known as MKC-442, is 6-benzyl-1-(ethoxymethyl)-5-isopropyl-uracil, a novel nonnucleoside reverse transcriptase inhibitor that displays potent and selective anti-human immunodeficiency virus type 1 (HIV-1) activity in vivo. EMV showed little or no toxicity towards human mitochondria or human bone marrow progenitor cells. Pharmacokinetics were linear for both rats and monkeys, and oral absorption was 68% in rats. Whole-body autoradiography showed widespread distribution in tissue 30 min after rats were given an oral dose of [(14)C]EMV at 10 mg/kg of body weight. In rats given an oral dose of 250 mg/kg, there were equal levels of EMV in the plasma and the brain. In vitro experiments using liver microsomes demonstrated that the metabolism of EMV by human microsomes is approximately a third of that encountered with rat and monkey microsomes. In 1-month, 3-month, and chronic toxicology experiments (6 months with rats and 1 year with cynomolgus monkeys), toxicity was limited to readily reversible effects on the kidney consisting of vacuolation of kidney tubular epithelial cells and mild increases in blood urea nitrogen. Liver weights increased at the higher doses in rats and monkeys and were attributed to the induction of drug-metabolizing enzymes. EMV tested negative for genotoxic activity, and except for decreased feed consumption at the high dose (160 mg/kg/day), with resultant decreases in maternal and fetal body weights, EMV produced no adverse effects in a complete range of reproductive toxicology experiments performed on rats and rabbits. These results support the clinical development of EMV as a treatment for HIV-1 infection in adult and pediatric patient populations.
Pesticides and fertilizers, as used in modern agriculture, contribute to the overall low-level co... more Pesticides and fertilizers, as used in modern agriculture, contribute to the overall low-level contamination of groundwater sources. In order to determine the potential of pesticide and fertilizer mixtures to produce reproductive or developmental toxicity at concentrations up to 100 x the median level found in groundwater, we prepared and studied two mixtures of pesticides and a fertilizer (ammonium nitrate). One mixture containing aldicarb, atrazine, dibromochloropropane, 1,2-dichloropropane, ethylene dibromide, and simazine plus ammonium nitrate was considered to be a representative of groundwater contamination in California (CAL). The other, containing alachlor, atrazine, cyanazine, metolachlor, metribuzin, and ammonium nitrate, simulated groundwater contamination in Iowa (IOWA). Each mixture was administered in the drinking water of either Swiss CD-1 mice during a Reproductive Assessment by Continuous Breeding study or pregnant Sprague-Dawley rats (gd 6-20) at three dose levels (1x, 10x, and 100x) where 1x was the median concentration of each pesticide component as determined in the groundwater surveys in California or Iowa. Unlike conventional toxicology studies, the purpose of this study was to evaluate the health effects of realistic human concentrations. Thus, the testing concentrations are probably well below the maximally tolerated dose. Propylene glycol was used as the solubilizer for the pesticides in drinking water formulations in both studies. In the reproductive study, neither mixture caused any clinical signs of toxicity, changes in food or water consumption, or body weight in either F0 or F1 mice at doses up to 100x the median groundwater concentrations. There were no treatment-related effects on fertility or any measures of reproductive performance of either the F0 or the F1 generation mice exposed to either CAL or IOWA at up to 100x. Similarly, measures of spermatogenesis, epididymal sperm concentration, percentage motile sperm, percentage abnormal sperm, and testicular and epididymal histology were normal. In the developmental study, CAL- or IOWA-exposed females did not exhibit any significant treatment-related clinical signs of toxicity. No adverse effects of CAL or IOWA were observed for measures of embryo/fetal toxicity, including resorptions per litter, live litter size, or fetal body weight. CAL or IOWA did not cause an increased incidence of fetal malformations or variations. In summary, administration of these pesticide/fertilizer mixtures at levels up to 100-fold greater than the median concentrations in groundwater supplies in California or Iowa did not cause any detectable reproductive (mice), general, or developmental toxicity (rats).
The potential reproductive toxicity of boric acid (BORA) in CD-1 mice (Swiss) was evaluated using... more The potential reproductive toxicity of boric acid (BORA) in CD-1 mice (Swiss) was evaluated using the Reproductive Assessment by Continuous Breeding (RACB) Protocol. BORA was administered in the feed for 27 weeks to male and female Swiss (CD-1) mice at concentrations of 0, 1000, 4500, or 9000 ppm. Estimated doses, based on feed consumption and body weight, averaged 152, 636, and 1262 mg/kg body wt during Week 1 for males for 1000, 4500, and 9000 ppm, respectively. During 14 weeks of cohabitation, fertility of F0 mice was partially reduced at 4500 ppm and totally eliminated at 9000 ppm. No litters, dead or alive, were produced by 9000 ppm cohabited pairs. Among the litters born at 4500 ppm, live litter size and body weight were significantly reduced. A crossover mating trial of control and 4500 ppm groups confirmed the male as the affected sex, with fertility rates and the mating index significantly lower in the 4500 male x 0 ppm female group. At necropsy, after 27 weeks of BORA exposure, dose-related changes were present in F0 males for reduced body and reproductive organ weights, increased incidence of abnormal sperm, decreased sperm concentration and motility, and seminiferous tubule degeneration. In the 4500 ppm females, dietary BORA for 27 weeks caused significantly decreased weights of kidney/adrenals and livers; kidney/adrenal weight was also reduced in 4500 ppm males. The last litters of the control and 1000 ppm females, born in the 14-week breeding phase, were reared to 74 days of age and then mated in nonsibling pairs within treatment groups. These F1 mice had normal fertility, but the adjusted mean body weight of F2 pups was decreased. These data establish the reproductive toxicity of BORA in CD-1 mice and demonstrate that the male is the most sensitive sex.
Emivirine (EMV), formerly known as MKC-442, is 6-benzyl-1-(ethoxymethyl)-5-isopropyl-uracil, a no... more Emivirine (EMV), formerly known as MKC-442, is 6-benzyl-1-(ethoxymethyl)-5-isopropyl-uracil, a novel nonnucleoside reverse transcriptase inhibitor that displays potent and selective anti-human immunodeficiency virus type 1 (HIV-1) activity in vivo. EMV showed little or no toxicity towards human mitochondria or human bone marrow progenitor cells. Pharmacokinetics were linear for both rats and monkeys, and oral absorption was 68% in rats. Whole-body autoradiography showed widespread distribution in tissue 30 min after rats were given an oral dose of [(14)C]EMV at 10 mg/kg of body weight. In rats given an oral dose of 250 mg/kg, there were equal levels of EMV in the plasma and the brain. In vitro experiments using liver microsomes demonstrated that the metabolism of EMV by human microsomes is approximately a third of that encountered with rat and monkey microsomes. In 1-month, 3-month, and chronic toxicology experiments (6 months with rats and 1 year with cynomolgus monkeys), toxicity was limited to readily reversible effects on the kidney consisting of vacuolation of kidney tubular epithelial cells and mild increases in blood urea nitrogen. Liver weights increased at the higher doses in rats and monkeys and were attributed to the induction of drug-metabolizing enzymes. EMV tested negative for genotoxic activity, and except for decreased feed consumption at the high dose (160 mg/kg/day), with resultant decreases in maternal and fetal body weights, EMV produced no adverse effects in a complete range of reproductive toxicology experiments performed on rats and rabbits. These results support the clinical development of EMV as a treatment for HIV-1 infection in adult and pediatric patient populations.
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