Bisphenol A (BPA) was evaluated at concentrations of 0, 0.015, 0.3, 4.5, 75, 750, and 7500 ppm ( approximately 0.001, 0.02, 0.3, 5, 50, and 500 mg/kg/day of BPA) administered in the diet ad libitum to 30 CD((R)) Sprague-Dawley rats/sex/dose for 3 offspring generations, 1 litter/generation, through F3 adults. Adult systemic toxicity at 750 and 7500 ppm in all generations included: reduced body weights and body weight gains, reduced absolute and increased relative weanling and adult organ weights (liver, kidneys, adrenals, spleen, pituitary, and brain), and female slight/mild renal and hepatic pathology at 7500 ppm. Reproductive organ histopathology and function were unaffected. Ovarian weights as well as total pups and live pups/litter on postnatal day (PND) 0 were decreased at 7500 ppm, which exceeded the adult maximum tolerated dose (MTD). Mating, fertility, gestational indices; ovarian primordial follicle counts; estrous cyclicity; precoital interval; gestational length; offspring sex ratios; postnatal survival; nipple/areolae retention in preweanling males; epididymal sperm number, motility, morphology; daily sperm production (DSP), and efficiency of DSP were all unaffected. At 7500 ppm, vaginal patency (VP) and preputial separation (PPS) were delayed in F1, F2, and F3 offspring, associated with reduced body weights. Anogenital distance (AGD) on PND 0 was unaffected for F2 and F3 males and F3 females (F2 female AGD was increased at some doses, not at 7500 ppm, and was considered not biologically or toxicologically relevant). Adult systemic no observed adverse effect level (NOAEL) = 75 ppm (5 mg/kg/day); reproductive and postnatal NOAELs = 750 ppm (50 mg/kg/day). There were no treatment-related effects in the low-dose region (0.001-5 mg/kg/day) on any parameters and no evidence of nonmonotonic dose-response curves across generations for either sex. BPA should not be considered a selective reproductive toxicant, based on the results of this study.
A comparative study was done in women and men of the effects of delta 9-tetrahydrocannabinol (delta 9-THC), intravenously or orally, on dynamic activity, metabolism, excretion, and kinetics. In general no differences between the two sexes were observed. delta 9-THC is converted by microsomal hydroxylation to 11-hydroxy-delta 9-THC (11-OH-delta 9-THC), which is both a key intermediate for further metabolism to 11-nor-delta 9-THC-9-carboxylic acid (11-nor-acid) by liver alcohol-dehydrogenase enzymes and a potent psychoactive metabolite. Major differences in the ratio of the concentration of 11-OH-delta 9-THC to that of delta 9-THC in plasma were found after intravenous dosing (ratio 1:10 to 20) compared with oral administration (ratio 0.5 to 1:1). The final metabolic products are the 11-nor-acids and the related, more polar acids. Urinary excretion of delta 9-THC is restricted to acidic nonconjugated and conjugated metabolites. After 72 hr mean cumulative urinary excretion, noted for both routes and for both sexes, ranged from 13% to 17% of the total dose. After 72 hr the cumulative fecal excretion for both sexes after intravenous administration ranged from 25% to 30%; after oral administration the range was 48% to 53%. Metabolites were found in the feces in large concentration in the nonconjugated form; concentrations of 11-OH-delta 9-THC were particularly noteworthy. Kinetics of delta 9-THC and metabolites were much the same for female and male subjects. For delta 9-THC, terminal-phase t1/2s for both sexes, irrespective of the route, ranged from 25 to 36 hr. A comparison of the results for AUC/dose (delta 9-THC) after oral dosing with comparable data from intravenous administration indicated bioavailability of the order of 10% to 20% for both sexes. After intravenous delta 9-THC, large apparent volumes of distribution were noted (about 10 l/kg for both sexes).
The 11-hydroxy metabolites of Delta(8).- and Delta(9)-tetrahydrocannabinol are more active than the parent compounds when administered to mice by either the intravenous or intracerebral route. Both Delta(8)- and Delta(9)-tetrahydrocannabinol are rapidly and extensively metabolized by the liver and not by the brain. The hypothesis that the 11-hydroxy metabolites may be the active form of tetrahydrocannabinol is discussed
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