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Vol. 53, Issue 2, 177-208, June 2001
Department of Pharmacology, Wayne State University School of
Medicine, Detroit, Michigan (L.H.L.); and National Center for
Environmental Assessment, U.S. Environmental Protection Agency,
Washington, DC (J.C.P.)
I. Introduction
II. Pathways of Perchloroethylene Metabolism
A. Cytochrome P450-Dependent Oxidation and Associated Enzymes
1. Overview of Cytochrome P450-Dependent
Pathway.
2. Role of Specific Cytochrome P450 Enzymes in Perchloroethylene
Metabolism.
3. Role of Genetic Polymorphisms in Cytochrome P450-Dependent
Metabolism of Perchloroethylene.
4. Species Differences in Cytochrome P450-Dependent Metabolism of
Perchloroethylene.
B. Glutathione Conjugation Pathway
1. Overview of Glutathione Conjugation Pathway.
2. Glutathione S-Transferases.
3.
-Glutamyltransferase.
4. Cysteine Conjugate
-Lyase.
5. Other Reactions of
S-(1,2,2-trichlorovinyl)-L-cysteine and Evaluation of
Relative Rates of Each Step of the Glutathione Conjugation
Pathway.
C. Relative Roles of P450 and Glutathione Conjugation Pathways in
Perchloroethylene Metabolism
III. Physiologically Based Pharmacokinetic Models for
Perchloroethylene
IV. Laboratory Animal Studies of Perchloroethylene Toxicity
V. Human Studies of Perchloroethylene Toxicity
A. Occupational Studies
B. Epidemiological Studies of the General Population Exposed to
Perchloroethylene
VI. Modes of Action for Perchloroethylene in Hepatic Toxicity
A. Overall Patterns and Metabolites Associated with Hepatic
Toxicity
B. Peroxisome Proliferation and Enzyme Induction
C. Oncogene Activation
D. Oxidative Stress and Genotoxicity
E. Cell Proliferation
VII. Modes of Action for Perchloroethylene in Renal Toxicity
A. Overall Patterns and Metabolites Associated with Renal Toxicity
B. Peroxisome Proliferation
C.
2u-Globulin Nephropathy
D. Genotoxicity
E. Acute Cytotoxicity and Cell Proliferation
VIII. Development of Reference Dose and Reference Concentration for
Perchloroethylene Exposure
IX. Summary and Research Needs
Acknowledgments
References
Metabolism of perchloroethylene (Perc) occurs by cytochrome
P450-dependent oxidation and glutathione (GSH) conjugation. The cytochrome P450 pathway generates tri- and dichloroacetate as metabolites of Perc, and these are associated with hepatic toxicity and
carcinogenicity. The GSH conjugation pathway is associated with
generation of reactive metabolites selectively in the kidneys and with
Perc-induced renal toxicity and carcinogenicity. Physiologically based
pharmacokinetic models have been developed for Perc in rodents and in
humans. We propose the addition of a submodel that incorporates the GSH
conjugation pathway and the kidneys as a target organ. Long-term
bioassays of Perc exposure in laboratory animals have identified liver
tumors in male and female mice, kidney tumors in male rats, and
mononuclear cell leukemia in male and female rats. Increases in
incidence of non-Hodgkin's lymphoma and of cervical, esophageal, and
urinary bladder cancer have been observed for workers exposed to Perc.
Limited, and not always consistent, evidence is available concerning
the kidneys as a target organ for Perc in humans. Three potential modes
of action for Perc-induced liver tumorigenesis are: 1) modification of
signaling pathways; 2) cytotoxicity, cell death, and reparative
hyperplasia; and 3) direct DNA damage. Four potential modes of action
for Perc-induced renal tumorigenesis are: 1) peroxisome proliferation,
2)
-2u-globulin nephropathy, 3) genotoxicity leading to somatic
mutation, and 4) acute cytotoxicity and necrosis leading to cell
proliferation. Finally, the epidemiological and experimental data are
assessed and use of toxicity information in the development of a
reference dose and a reference concentration for human Perc exposure
are presented.
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