60 Chem. Res. Toxicol., Vol. 14, No. 1, 2001
Cai and Guengerich
kidney cells in rats exposed to halogenated anaesthetics. Mutat.
Res. 413, 1-6.
(6) Crebelli, R., and Carere, A. (1989) Genetic toxicology of 1,1,2-
trichloroethylene. Mutat. Res. 221, 11-37.
(7) Dekant, W., Berthold, K., Vamvakas, S., Henschler, D., and
Anders, M. W. (1988) Thioacylating intermediates as metabolites
of S-(1,2-dichlorovinyl)-L-cysteine and S-(1,2,2-trichlorovinyl)-L-
cysteine formed by cysteine conjugate â-lyase. Chem. Res. Toxicol.
1, 175-178.
(8) Elcombe, C. R., Rose, M. S., and Pratt, I. S. (1985) Biochemical,
histological, and ultrastructural changes in rat and mouse liver
following the administration of trichloroethylene: possible rel-
evance to species differences in hepatocarcinogenicity. Toxicol.
Appl. Pharmacol. 79, 365-376.
(9) Bull, R. J ., Templin, M., Larson, J . L., and Stevens, D. K. (1993)
The role of dichloroacetate in the hepatocarcinogenicity of trichlo-
roethylene. Toxicol. Lett. 68, 203-211.
(10) J untunen, J ., Kinnunen, E., Antti-Poika, M., and Koskenvuo, M.
(1989) Multiple sclerosis and occupational exposure to chemi-
cals: a co-twin control study of a nationwide series of twins. Br.
J . Ind. Med. 46, 417-419.
(11) Noseworthy, J . H., and Rice, G. P. (1988) Trichloroethylene
poisoning mimicking multiple sclerosis. Can. J . Neurol. Sci. 15,
87-88.
(12) Kilburn, K. H., and Warshaw, R. H. (1992) Prevalence of
symptoms of systemic lupus erythematosus (SLE) and of fluo-
rescent antinuclear antibodies associated with chromic exposure
to trichloroethylene and other chemicals in well water. Environ.
Res. 57, 1-9.
(13) Moore, M. M., and Harrington-Brock, K. (2000) Mutagenicity of
trichloroethylene and its metabolites: implications for the risk
assessment of trichloroethylene. Environ. Health Perspect. 108
(Suppl. 2), 1-9.
(14) Lash, L. H., Fisher, J . W., Lipscomb, J . C., and Parker, J . C. (2000)
Metabolism of trichloroethylene. Environ. Health Perspect. 108,
177-200.
(15) Lash, L. H., Parker, J . C., and Scott, C. S. (2000) Modes of action
of trichloroethylene for kidney tumorigenesis. Environ. Health
Perspect. 108, 225-240.
(16) Clewell, H. J ., III, Gentry, P. R., Covington, T. R., and Gearhart,
J . M. (2000) Development of a physiologically based pharmaco-
kinetic model of trichloroethylene and its metabolites for use in
risk assessment. Environ. Health Perspect. 108, 283-305.
(17) Boyes, W. K., Bushnell, P. J ., Crofton, K. M., Evans, M., and
Simmons, J . E. (2000) Neurotoxic and pharmacokinetic responses
to trichloroethylene as a function of exposure scenario. Environ.
Health Perspect. 108, 317-322.
radiocarbon with attomole sensitivity, the detection of
DNA adducts at the level of 1 adduct/1011 nucleosides was
reported (28). However, identification of any TCE-DNA
adducts has not been performed. In the work presented
here, we directly observed formation of an 8-mer oligo-
nucleotide adduct (with two formyl groups attached)
using HPLC/MS (Figure 5). The formyl groups were most
likely attached to the two dGuo residues of the 8-mer
oligonucleotide because only dGuo adducts (∼2% yield)
were detected during the reaction of TCE oxide with the
four individual nucleosides. The 8-mer oligonucleotide
adducts were unstable (Figure 6), which may explain the
low level of DNA adducts observed previously in the
literature.
Con clu sion s. Direct mass spectrometric analysis of
proteins and oligonucleotides treated with TCE oxide
indicates that a large fraction of the adducts are unstable,
presumably because of the instability of ester/thioester
products derived from the acyl chlorides (26). The exist-
ence of a large fraction of unstable adducts raises new
questions about protein adducts. One view might be that
toxicological risk from TCE is low because the recovery
of many modified proteins is rapid (Figure 4). An opposite
conclusion regarding risk assessment could be that TCE
is more likely to inactivate important proteins tran-
siently, because the level of protein binding is much
higher than estimated previously and presumably most
studies with [14C]TCE have underestimated the amount
of initial binding. Ultimately, answers to the dilemna will
need to involve measurement of levels of not only adducts
in surrogate (or total) protein fractions but also critical
targets, because of the diversity of recovery of function
(Figure 4). Nevertheless, these results and our previous
work (26) suggest that relatively high concentrations of
TCE oxide must be generated to inactivate proteins and
that TCE oxide is probably only weakly genotoxic,
possibly because of adduct instability (Figure 6). The
methods used for these analyses may be applied to other
electrophiles to study their modification of macromol-
ecules.
(18) Chen, C. W. (2000) Biologically based dose-response model for
liver tumors induced by trichloroethylene. Environ. Health Per-
spect. 108, 335-342.
(19) Fisher, J . W., Gargas, M. L., Allen, B. C., and Andersen, M. E.
(1991) Physiologically based pharmacokinetic modeling with
trichloroethylene and its metabolite, trichloroacetic acid, in the
rat mouse. Toxicol. Appl. Pharmacol. 109, 183-195.
(20) Lipscomb, J . C., Fisher, J . W., Confer, P. D., and Byczkowski, J .
Z. (1998) In vitro to in vivo extrapolation for trichloroethylene
metabolism in humans. Toxicol. Appl. Pharmacol. 152, 376-387.
(21) Henschler, D., Hoos, W. R., Fetz, H., Dallmeier, E., and Metzler,
M. (1979) Reactions of trichloroethylene epoxide in aqueous
systems. Biochem. Pharmacol. 28, 543-548.
(22) Uehleke, H., Poplawski, S., Bonse, G., and Henschler, D. (1977)
Spectral evidence for 2,2,3-trichloro-oxirane formation during
microsomal trichloroethylene oxidation. Xenobiotica 7, 94-95.
(23) Miller, R. E., and Guengerich, F. P. (1982) Oxidation of trichlo-
roethylene by liver microsomal cytochrome P-450: evidence for
chlorine migration in a transition state not involving trichloro-
ethylene oxide. Biochemistry 21, 1090-1097.
(24) Prout, M. S., Provan, W. M., and Green, T. (1985) Species
differences in response to trichloroethylene. I. Pharmacokinetics
in rats and mice. Toxicol. Appl. Pharmacol. 79, 389-400.
(25) Cai, H., and Guengerich, F. P. (1999) Mechanism of aqueous
decomposition of trichloroethylene oxide. J . Am. Chem. Soc. 121,
11656-11663.
(26) Cai, H., and Guengerich, F. P. (2000) Acylation of protein lysines
by trichloroethylene oxide. Chem. Res. Toxicol. 13, 327-335.
(27) Miller, R. E., and Guengerich, F. P. (1983) Metabolism of
trichloroethylene in isolated hepatocytes, microsomes, and re-
constituted enzyme systems containing cytochrome P-450. Cancer
Res. 43, 1145-1152.
Ack n ow led gm en t. We thank Prof. D. Hachey for
helpful suggestions regarding the HPLC/MS analyses.
This work was supported in part by U.S. Public Health
Service Grants R35 CA44353 and P30 ES00267. H.C. was
supported in part by U.S. Public Health Service Post-
doctoral Fellowship F32 ES05919.
Su p p or tin g In for m a tion Ava ila ble: UV spectrum of the
TCE oxide-dGuo adduct and comparison to that of dGuo and
tables of m/z assignments of peaks observed in Figures 1 and
2. This material is available free of charge via the Internet at
http://pubs.acs.org.
Refer en ces
(1) Gist, G. L., and Burg, J . R. (1995) Trichloroethylene: A review
of the literature from a health effects perspective. Toxicol. Ind.
Health 11, 253-307.
(2) Westrick, J . J ., Mello, J . W., and Thomas, R. F. (1984) The ground
water supply survey. J . Am. Water Works Assoc. 76, 52-59.
(3) Toxicological Profile for Trichloroethylene (1988) Oak Ridge
National Laboratory, Oak Ridge, TN.
(4) Goeptar, A. R., Commandeur, J . N. M., van Ommen, B., van
Bladeren, P. J ., and Vermeulen, N. P. E. (1995) Metabolism and
kinetics of trichloroethylene in relation to toxicity and carcino-
genicity. Relevance to the mercapturic acid pathway. Chem. Res.
Toxicol. 8, 3-21.
(28) Kautianinen, A., Vogel, J . S., and Turteltaub, K. W. (1997) Dose-
dependent binding of trichloroethylene to helpatic DNA and
protein at low doses in mice. Chem.-Biol. Interact. 106, 109-121.
(5) Robbiano, L., Mereto, E., Morando, A. M., Pastore, P., and
Brambilla, G. (1998) Increased frequency of micronucleated