Linking indoor air and pharmacokinetic models to assess tetrachloroethylene risk.

Physiologically based pharmacokinetic (PBPK) models describing the uptake, metabolism, and excretion of xenobiotic compounds are now proposed for use in regulatory health-risk assessments. In this study we investigate the extent of PCE metabolism arising from domestic respiratory exposure to tetrachloroethylene (PCE) from ground water, as predicted using a PBPK model. Indoor exposure patterns we use as input to the PBPK model are realistic ones generated from a three-compartment model describing volatilization of PCE from domestic water into household air. Values we use for the metabolic parameters of the PBPK model are estimated from data on urinary metabolites in workers exposed to PCE. It is shown that for respiratory PCE exposure due to typical levels of PCE in ground water, use of time-weighted average air concentrations with a steady-state PBPK model yields estimates of total metabolized PCE similar to those obtained using completely dynamic modeling, despite considerable uncertainty in key exposure- and metabolic-model parameters. These findings suggest that, for PCE, risk estimation taking pharmacokinetics into account may be accomplished using a simple analytic approach.

[1]  A C Monster,et al.  Kinetics of tetrachloroethylene in volunteers; influence of exposure concentration and work load , 1979, International archives of occupational and environmental health.

[2]  M. Ikeda Metabolism of trichloroethylene and tetrachloroethylene in human subjects. , 1977, Environmental health perspectives.

[3]  P. Watanabe,et al.  Tetrachloroethylene: balance and tissue distribution in male Sprague-Dawley rats by drinking-water administration. , 1983, Toxicology and applied pharmacology.

[4]  P. Watanabe,et al.  Disposition of tetrachloro(14C)ethylene following oral and inhalation exposure in rats. , 1979, Toxicology and applied pharmacology.

[5]  F. A. Smith,et al.  Physiologically based pharmacokinetics and the risk assessment process for methylene chloride. , 1987, Toxicology and applied pharmacology.

[6]  H J Clewell,et al.  Metabolism of inhaled dihalomethanes in vivo: differentiation of kinetic constants for two independent pathways. , 1986, Toxicology and applied pharmacology.

[7]  A. Koizumi,et al.  Limited capacity of humans to metabolize tetrachloroethylene , 1983 .

[8]  Masayuki Ikeda,et al.  Urinary excretion of total trichloro-compounds, trichloroethanol, and trichloroacetic acid as a measure of exposure to trichloroethylene and tetrachloroethylene , 1972, British journal of industrial medicine.

[9]  M. Metzler,et al.  Identification of S-1,2,2-trichlorovinyl-N-acetylcysteine as a urinary metabolite of tetrachloroethylene: bioactivation through glutathione conjugation as a possible explanation of its nephrocarcinogenicity. , 1986, Journal of biochemical toxicology.

[10]  Thomas E. McKone,et al.  Human exposure to volatile organic compounds in household tap water: the indoor inhalation pathway , 1987 .

[11]  M E Andersen,et al.  A physiologically based description of the inhalation pharmacokinetics of styrene in rats and humans. , 1984, Toxicology and applied pharmacology.

[12]  T. McKone,et al.  Health risk assessment of trichloroethylene (TCE) in California drinking water , 1987 .

[13]  H. S. Brown,et al.  The role of skin absorption as a route of exposure for volatile organic compounds (VOCs) in drinking water. , 1984, American journal of public health.

[14]  C. Mitoma,et al.  Metabolic disposition study of chlorinated hydrocarbons in rats and mice. , 1985, Drug and chemical toxicology.

[15]  P. Watanabe,et al.  The pharmacokinetics and macromolecular interactions of perchloroethylene in mice and rats as related to oncogenicity. , 1980, Toxicology and applied pharmacology.

[16]  J. B. Andelman Human exposures to volatile halogenated organic chemicals in indoor and outdoor air. , 1985, Environmental health perspectives.

[17]  D. M. Hetrick,et al.  Pharmacokinetics of tetrachloroethylene. , 1988, Toxicology and applied pharmacology.

[18]  E. Gubéran,et al.  Experimental human exposures to tetrachloroethylene vapor and elimination in breath after inhalation. , 1976, American Industrial Hygiene Association journal.

[19]  G. Kerr Organ dose estimates for the Japanese atomic-bomb survivors. , 1979, Health physics.

[20]  Elizabeth L. Anderson,et al.  Quantitative Approaches in Use to Assess Cancer Risk , 1983 .