Physiologically based pharmacokinetic (PBPK) modeling was used to -m the low-dose exposure of patients to the carcinogen 2,4-toluenediamine (2,4-TDA) rdeased from the adation ofthe polyester urethane foam (PU) used in Meme silicone breast implants. The tissues are represnted as five compartments: liver, Idney, gasrointestinal tract, slowly perfused tissues (e.g., fat), and richly perfused tissues (e.g., muscle). The PBPK model w tted to the plasma and urine concentrations of 2,4-TDA and its metabolite 4-AAT (4-N-aetyl-2-amino toluene) in rats given low doses of 2,4-TDA intravenously and subcutaeously. The rat modaldwas extrapolated to simulate oral and implant routes in rats. After adjusting for human physiological parmeters, the model was then used to predict the bioavailability of 2,4-TDA released from a typical 4. Polyurethanes have been used in breast implant covers, pacemaker leads, hemodialyzer potting material, and other medical applications. The degradation of polyurethanes in vivo has long been a concern due to both the release of potentially harmful materials as well as mechanical failure. The composition of the polyurethane degradation products depends on the original formulation of the polymer. The polyester urethane (PU) foam cover of the Meme breast implant (or Replicon; Surgitek Corporation, Racine, WI) was made from a polyester resin and a 80:20 mixture of 2,4-toluene diisocynate and 2,6-toluene diisocyanate (2,4-TDI, 2,6-TDI) (1). One of the degradation products of TDI is 2,4-toluenediamine (2,4-TDA). Data in experimental animals showed that the PU foam cover degraded within 6-12 months of implantation (2). This result was consistent with the clinical observations in patients with Meme breast implants (3,4). Our own in vitro studies indicated that 2,4-TDA was slowly released over time by hydrolytic degradation when PU foam samples were incubated under mild physiological conditions (5,6). The amount and rate of 2,4-TDA production observed in vitro varied with the conditions of PU foam exposure (7-9). The carcinogenicity of 2,4-TDA was studied extensively in mice, rats, and other species (10)(11)(12)(13)(14)(15)(16)(17)(18)(19) (25). The kinetic behavior of 2,4-TDA and its metabolite were derived from the implant PBPK model for both rats and humans. The simulated results were compared to the available independent data for validation (10-13,22,2,) with an experimentally determined value of 88 ng 2,4-TDA/g foam/day as previously reported (5,6). The degradation of the PU foam in vivo was assumed to produce only one product, 2,4-TDA (29). The PBPK model for 2,4-TDA accounts for hepatic metabolism, which is known to produce an active metabolite (18,19). Although there were at least eight known metabolites of 2,4-TDA in the liver, 2,4-TDA was assumed only to have one metabolite, 4-acetylamino-2-aminotoluene (4-AAT), in this model for simplicity (19,29). The rate of production of 4-AAT was controlled by an adjustable selectivity in the model (19). The selectivity was defined as the fraction of metabolite...