Bisphenol A is a widely used industrial chemical with many potential sources of human exposure. Bisphenol A is a weak estrogen and has been implicated as an "endocrine disruptor". This term is used for a variety of chemicals encountered in the environment which have estrogenic activity. It has been postulated that human exposure to these chemicals may elicit unwanted estrogenic effects in humans such as reduced fertility, altered development and cancer. Up to now the body burden of bisphenol A in humans is unknown. Therefore, we investigated the metabolism and toxicokinetics of bisphenol A in humans exposed to low doses since systemic bioavailability has a major influence on possible estrogenic effects in vivo. Human subjects (three males and three females, and four males for detailed description of blood kinetics) were administered d(16)-bisphenol A (5 mg). Blood and urine samples were taken in intervals (up to 96 h), metabolites formed were identified by GC/MS and LC-MS/MS and quantified by GC/MS-NCI and LC-MS/MS. d(16)-Bisphenol A glucuronide was the only metabolite of d(16)-bisphenol A detected in urine and blood samples, and concentrations of free d(16)-bisphenol A were below the limit of detection both in urine (6 nM) and blood samples (10 nM). d(16)-Bisphenol A glucuronide was cleared from human blood and excreted with urine with terminal half-lives of less than 6 h; the applied doses were completely recovered in urine as d(16)-bisphenol A glucuronide. Maximum blood levels of d(16)-bisphenol A glucuronide (approximately 800 nM) were measured 80 min after oral administration of d(16)-bisphenol A (5 mg). The obtained data indicate major species differences in the disposition of bisphenol A. Enterohepatic circulation of bisphenol A glucuronide in rats results in a slow rate of excretion, whereas bisphenol A is rapidly conjugated and excreted by humans due to the absence of enterohepatic circulation. The efficient glucuronidation of bisphenol A and the rapid excretion of the formed glucuronide result in a low body burden of the estrogenic bisphenol A in humans following oral absorption of low doses.

1,3-Butadiene (BD), a widely used monomer in the production of synthetic rubber and other resins, is one of the 189 hazardous air pollutants identified in the 1990 Clean Air Act Amendments. BD induces tumors at multiple organ sites in B6C3F1 mice and Sprague-Dawley rats; mice are much more susceptible to the carcinogenic action of BD than are rats. Previous in vivo studies have indicated higher circulating blood levels of butadiene monoepoxide (BMO), a potential carcinogenic metabolite of BD, in mice compared to rats, suggesting that species differences in the metabolism of BD may be responsible for the observed differences in carcinogenic susceptibility. The metabolic fate of BD in humans is unknown. The objective of these studies was to quantitate in vitro species differences in the oxidation of BD and BMO by cytochrome P450-dependent monooxygenases and the inactivation of BMO by epoxide hydrolases and glutathione S-transferases using microsomal and cytosolic preparations of livers and lungs obtained from Sprague-Dawley rats, B6C3F1 mice and humans. Maximum rates for BD oxidation (Vmax) were highest for mouse liver microsomes (2.6 nmol/mg protein/min) compared to humans (1.2) and rats (0.6). The Vmax for BD oxidation by mouse lung microsomes was similar to that of mouse liver but greater than 10-fold higher than the Vmax for the reaction in human or rat lung microsomes. Correlation analysis revealed that P450 2E1 is the major P450 enzyme responsible for oxidation of BD to BMO. Only mouse liver microsomes displayed quantifiable rates for metabolism of BMO to butadiene diepoxide (Vmax = 0.2 nmol/mg protein/min), a known rodent carcinogen. Human liver microsomes displayed the highest rate of BMO hydrolysis by epoxide hydrolases. The Vmax in human liver microsomes ranged from 9 to 58 nmol/mg protein/min and was at least 2-fold higher than the Vmax observed in mouse and rat liver microsomes. The Vmax for glutathione S-transferase-catalyzed conjugation of BMO with glutathione was highest for mouse liver cytosol (500 nmol/mg protein/min) compared to human (45) or rat (241) liver cytosol. In general, the KMs for the detoxication reactions were 1000-fold higher than the KMs for the oxidation reaction. Because of the low solubility of the BD and the relatively high KM for oxidation, it is likely that the Vmax/KM ratio will be important for BD and BMO metabolism in vivo. In vivo clearance constants were calculated from in vitro data for BD oxidation and BMO oxidation, hydrolysis and GSH conjugation.(ABSTRACT TRUNCATED AT 400 WORDS)

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1,3-Butadiene (BD), a rodent carcinogen, is metabolized to mutagenic and potentially DNA-reactive epoxides, including butadiene monoepoxide (BMO) and butadiene diepoxide. A physiological model containing five tissue groups (liver, lung, fat, slowly perfused tissues and rapidly perfused tissues) and blood was developed to describe uptake and metabolism of inhaled BD and BMO. Maximal rates for hepatic and pulmonary metabolism of BD and hepatic metabolism of BMO incorporated into the model were extrapolated from in vitro data (Csanády et al., Carcinogenesis, 13, 1143-1153, 1992). Apparent enzyme affinities used in the model were identified to the values measured in vitro. Model stimulations for BD and BMO uptake were compared to results from experiments in which groups of male Sprague-Dawley rats and B6C3F1 mice were exposed to initial concentrations of 50-5000 p.p.m. BD in closed chamber experiments and published data on BMO uptake by rats and mice. Metabolic rate constants extrapolated from in vitro data stimulated both BMO and BD uptake from closed chambers. The Vmax for hepatic metabolism of BD extrapolated from in vitro studies was 62 mumol/kg/h for rats and 340 mumol/kg/h for mice, while the Vmax for pulmonary metabolism of BD was 1.0 and 22 for rats and mice, respectively. These results demonstrate the usefulness of data derived in vitro for predicting in vivo behavior. Model simulations were also conducted in which only hepatic metabolism of BD was incorporated. These simulations underestimated BD uptake for mice, but not rats. Inclusion of in vitro-derived rates of pulmonary metabolism of BD into the model improved the fit to the data for mice. Since mice, but not rats, develop lung tumors after exposure to BD, these results point to the need for further characterize the metabolic capacity and target cells in the lung for BD and its metabolites. Once characterized, these models can be extended to predict in vivo behavior of BD in humans.

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