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Vol. 27, Issue 3, 351-359, March 1999
Department of Pharmacology, Wayne State University School of Medicine, Detroit, Michigan (L.H.L., D.A.P.); U.S. Air Force, Air Force Research Laboratory, Toxicology Branch, Wright-Patterson Air Force Base, Dayton, Ohio (J.C.L.); and National Center for Environmental Assessment, U.S. Environmental Protection Agency, Washington, D.C. (J.C.P.)
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Abstract |
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Isolated human hepatocytes exhibited time-, trichloroethylene (Tri) concentration-, and cell concentration-dependent formation of S-(1,2-dichlorovinyl)glutathione (DCVG) in incubations in sealed flasks with 25 to 10,000 ppm Tri in the headspace, corresponding to 0.011 to 4.4 mM in hepatocytes. Maximal formation of DCVG (22.5 ± 8.3 nmol/120 min per 106 cells) occurred with 500 ppm Tri. Time-, protein concentration-, and both Tri and GSH concentration-dependent formation of DCVG were observed in liver and kidney subcellular fractions. Two kinetically distinct systems were observed in both cytosol and microsomes from pooled liver samples, whereas only one system was observed in subcellular fractions from pooled kidney samples. Liver cytosol exhibited apparent Km values (µM Tri) of 333 and 22.7 and Vmax values (nmol DCVG formed/min per mg protein) of 8.77 and 4.27; liver microsomes exhibited apparent Km values of 250 and 29.4 and Vmax values of 3.10 and 1.42; kidney cytosol and microsomes exhibited apparent Km values of 26.3 and 167, respectively, and Vmax values of 0.81 and 6.29, respectively. DCVG formation in samples of liver cytosol and microsomes from 20 individual donors exhibited a 6.5-fold variation in microsomes but only a 2.4-fold variation in cytosol. In coincubations of pooled liver cytosol and microsomes, addition of an NADPH-regenerating system produced marked inhibition of DCVG formation, but addition of GSH had no effect on cytochrome P-450-catalyzed formation of chloral hydrate. These results indicate that both human kidney and liver have significant capacity to catalyze DCVG formation, indicating that the initial step of the GSH-dependent pathway is not limiting in the formation of nephrotoxic and nephrocarcinogenic metabolites.
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Introduction |
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Trichloroethene
(Tri)2
is a major environmental contaminant and is an
occupational concern because of its widespread industrial use (Davidson
and Beliles, 1991
). Tri is an established animal carcinogen that
produces tumors in a variety of tissues. Due to the possibility of
human exposure, Tri has been extensively evaluated in rodent cancer
bioassays, and the U.S. Environmental Protection Agency is currently
performing a new human health risk assessment for Tri (Maull and Lash,
1998
). A complicating factor in the evaluation of the risk of Tri
exposure for humans is that susceptibility and target organ specificity
for Tri exhibit marked species and sex dependence. For example, Tri
produces lung and liver tumors in mice (National Cancer Institute,
1976
; Fukuda et al., 1983
; National Toxicology Program, 1983
; Forkert
et al., 1985
) and nephrotoxicity and renal tumors in rats (National
Toxicology Program, 1983
, 1987
; Maltoni et al., 1988
), with males of
each species exhibiting greater susceptibility than females.
Epidemiological studies in occupationally or environmentally exposed
humans, however, have given conflicting results with regard to
susceptibility and target organ specificity. In spite of this, the
International Agency for Research on Cancer (IARC) has recently revised
their classification of Tri and have declared it a Class 2A carcinogen
("Probably Carcinogenic to Humans"; IARC, 1995
).
The toxicity of Tri is dependent on its metabolism, which occurs by
either cytochrome P-450 (P-450)-dependent oxidation or GSH conjugation.
Metabolites derived from P-450 metabolism, including chloral hydrate,
trichloroacetate, and dichloroacetate, have been associated with the
pulmonary and hepatic toxicity of Tri (Davidson and Beliles, 1991
). In
contrast, reactive metabolites derived from GSH conjugation of Tri,
with subsequent metabolism by
-glutamyltransferase (GGT),
dipeptidases, and cysteine conjugate
-lyase (
-lyase), are
associated with the nephrotoxicity of Tri (Anders et al., 1988
; Goeptar
et al., 1995
). The cysteine conjugate DCVC may also be
N-acetylated to form the mercapturate, which represents a
detoxification mechanism. The mercapturate is then either deacetylated
to reform DCVC or is excreted in the urine.
One of the major controversies about human risk of Tri exposure
concerns the kidney as a target organ (Bloemen and Tomenson, 1995
;
Henschler et al., 1995a
,b
; Swaen, 1995
). Three observations that have
been interpreted to indicate that the nephrotoxicity and
nephrocarcinogenicity of Tri may not be relevant to humans are that: 1)
kidney tumors are most frequently observed in male rats but are rarely
seen in female rats or in males or females of other species, 2) kidney
toxicity or renal tumors are rarely observed in humans exposed to Tri,
and 3) flux through the GSH conjugation pathway is thought to represent
only a minor fraction of total Tri metabolism (Green et al., 1997
).
The initial step in the GSH conjugation pathway, which is catalyzed by
glutathione S-transferases (GSTs) found in the cytosol and
microsomes of most tissues, occurs predominantly in the liver (Lash et
al., 1988
). GSH S-conjugates formed in the liver are then
readily translocated into bile and small intestine or plasma. Biliary
or intestinal GSH S-conjugates then undergo subsequent metabolism to the corresponding cysteine S-conjugates or
mercapturates. Through interorgan pathways, these metabolites are
extracted by the kidneys and are metabolized further or excreted.
Plasma GSH S-conjugates are also delivered to the kidneys,
where they are metabolized further or excreted as mercapturates. The
selective tissue distribution of the different enzymes of the GSH
conjugation pathway and of plasma membrane transporters determines the
renal selectivity of GSH-derived metabolites of chemicals such as Tri (Lash et al., 1988
).
In addition to interorgan metabolism, Tri may undergo GSH conjugation
and subsequent reactions within the kidneys, representing an intraorgan
metabolic pathway (Lash et al., 1995
). Although male rats exhibit
markedly higher rates of both hepatic and renal GSH conjugation of Tri
than female rats (Lash et al., 1995
, 1998
), which agrees with the
higher susceptibility of male rats to Tri- or DCVC-induced
nephrotoxicity and nephrocarcinogenicity, male and female mice exhibit
markedly higher rates of GSH conjugation of Tri than either sex of rats
(Lash et al., 1998
). Although human kidney cytosol has
-lyase, its
activity is present at only about 10% of levels found in rats (Lash et
al., 1990
), suggesting that this step may be limiting in humans.
Furthermore, Green et al. (1997)
measured GSH conjugation of Tri and
reported rates that were severalfold lower than those in rats, and they
concluded that flux through the entire pathway in humans is minor
compared with that through the P-450 pathway.
In the present study, we quantitated activity and determined kinetics of GSH conjugation of Tri in isolated hepatocytes and liver and kidney cytosol and microsomes from human tissue donors. The method of analysis involved measurement of S-(1,2-dichlorovinyl) glutathione (DCVG) by HPLC, allowing direct confirmation of conjugate formation. The results showed that rates of GSH conjugation of Tri in human liver and kidney are comparable to those found in male rats, demonstrating that the initial step in the pathway is not limiting in the generation of potentially nephrotoxic metabolites.
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Experimental Procedures |
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Materials.
Tri (reported to be 99.9% pure, as judged by electron ionization mass
spectrometry), collagenase type IV,
L-(
S,5S)-
-amino-3-chloro-4,5-dihydro-5-isoxazoleacetic acid (acivicin), and
L-
-glutamyl-L-glutamate
were purchased from Sigma. DCVG was synthesized as previously described
(Elfarra et al., 1986
) and was a gift from Dr. Adnan A. Elfarra
(University of Wisconsin, Madison, WI). Purity (>95%) was determined
by HPLC analysis and identity was confirmed by proton nuclear magnetic resonance spectroscopy. All other chemicals were of the highest purity available and were obtained from commercial sources.
Preparation of Isolated Hepatocytes.
Human liver and kidney samples were purchased from the Human Cell
Culture Center, Inc. (Anatomic Gift Foundation, Folkston, GA).
Hepatocytes were isolated from six liver donors by collagenase perfusion (Dorko et al., 1994
; Strom et al., 1996
). After surgical isolation, the left hepatic lobe was prepared by cannulating the hepatic vein and warming to 37-39°C. The liver was initially
perfused with a calcium-free buffer to help separate intercellular
junctions. The second perfusion buffer contained calcium, collagenase,
and 0.5% (w/v) bovine serum albumin (Dorko et al., 1994
). Perfusion was typically initiated within 18 to 24 h of clinical death and isolated hepatocytes were immediately suspended and shipped on ice-cold
University of Wisconsin medium. Cells were used fresh without
cryopreservation and time from organ removal to in vitro experiment
was
36 h. Cell viability was assessed by trypan blue exclusion and cells were discarded if viability was <65%. Cells were
then centrifuged, resuspended, and incubated at a density of 0.25 to
2 × 106/ml in Chee's modified medium in
30-ml screw-capped Erlenmeyer flasks. Flasks were purged with 95%
O2/5% CO2. The volume of
each flask (38 to 42 ml) was gravimetrically determined with water and
the volume of the cell suspension (kept constant at 3.0 ml) used was
just enough to ensure that the bottom of the flask remained covered
when the flask was oscillated at 50 rpm.
Preparation of Liver and Kidney Subcellular Fractions.
Liver cytosol and microsomes (see Table 1
for donor table) and kidney cytosol and microsomes from pooled donors
were prepared from tissue homogenates by differential centrifugation
(Guengerich, 1989
). Both pooled samples and individual samples were
used for liver cytosol and microsomes. Information on human liver
cytosol and microsome donors are given in Table 1. The cause of death in all individuals was unrelated to liver function; the donor population exhibited a wide range of ages (24 to 63 years for cytosol,
26 to 65 years for microsomes) and ethnic groups and comprised both
males and females. Pooled samples were used for kidney cytosol and
microsomes. For measurement of GGT activity in human kidney and liver
subcellular fractions, kidney cytosol and microsomes and liver cytosol
were pooled from donor tissues and were obtained from the source
described above. Pooled human liver microsomes used for GGT assays were
a gift from Dr. Paul F. Hollenberg (University of Michigan, Ann Arbor,
MI).
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Incubations for Measurement of Metabolism of Tri by GSH
Conjugation.
For incubations with isolated hepatocytes, Tri was volatilized into
tedlar bags containing known volumes of
O2/CO2 and was diluted into
sealed flasks to yield headspace concentrations of 25 to 10,000 ppm.
Previous partitioning experiments (Lipscomb et al., 1998a
) demonstrated
that these concentrations of Tri in the headspace result in Tri
concentrations of 0.011 to 4.4 mM in isolated hepatocytes. Preliminary
studies indicated that this range of headspace concentrations produced
detectable quantities of metabolites at the low end while saturating
the initial GST- or P-450-catalyzed reaction at the high end, as
demonstrated by formation of DCVG or chloral hydrate, trichloroethanol,
and trichloroacetate, respectively. Tri concentrations in the headspace
were verified by manually injecting 0.1-ml samples of flask headspace
on a Hewlett-Packard model 5890 Series II gas chromatograph equipped
with a Supelco (Bellefonte, PA) 2-5320 Vocol capillary column (0.53 mm × 30 m) and interfaced with a flame ionization detector.
Tri concentrations in flasks were verified by comparing area counts
with those from an external standard curve of authentic Tri volatilized
in crimp-sealed serum vials and analyzed simultaneously by the same
system. Incubations were carried out for up to 2 h and were
quenched by addition of 0.1 ml of 70% (v/v) perchloric acid to 0.5-ml
aliquots of incubation samples. Quenched samples were rapidly frozen in
liquid nitrogen and stored at
80°C until analysis. No significant
loss of cell viability, as assessed by release of cytosolic enzymes
into extracellular medium, occurred from hepatocytes during the
incubations with Tri (data not shown).
80°C until analysis.
Kidney microsomes were first preincubated with 0.25 mM acivicin to
inhibit any GGT activity from contaminating brush-border membranes to
minimize further metabolism of DCVG. This concentration of acivicin
inhibits GGT activity in rat kidney plasma membranes (Lash and Jones,
1984Assay of DCVG Formation.
Perchloric acid extracts of hepatocytes or liver and kidney subcellular
fractions were derivatized with iodoacetic acid and 1-fluoro-2,4-dinitrobenzene as described previously (Lash et al., 1995
)
and the N-dinitrophenyl derivative of DCVG was analyzed by
ion-exchange HPLC as described by Fariss and Reed (1987)
. DCVG content
in samples was quantitated with respect to authentic standard and was
adjusted according to the content of added
L-
-glutamyl-L-glutamate as HPLC internal standard. The limit of detection was 50 pmol, with a
linear detector response being obtained with samples containing from 50 pmol to 10 nmol. The efficiency of derivatization was estimated to be
85 to 110%, with a correction made for this variation by use of an
internal standard. Besides comparison of retention time with that of
the derivative of authentic DCVG standard, the identity of the DCVG
peak was confirmed as done previously (Lash and Jones, 1985
) by a
15-min treatment of selected samples with 1 U of a partially purified
preparation of GGT that also contains dipeptidase activity (data not
shown). As a consequence of this treatment, DCVG was converted to DCVC,
whose N-dinitrophenyl derivative is also detected by this
HPLC method (Lash and Anders, 1989
). Amounts of nonenzymatic DCVG
formation were approximately 25% of those in the presence of cells or
tissues and were subtracted from the latter to obtain enzyme-dependent
rates of DCVG formation.
Assay of Chloral Hydrate Formation.
Chloral hydrate formation was measured in incubations with pooled human
liver microsomes (0.5 mg protein/ml) and pooled liver cytosol (1 mg
protein/ml) in the presence of either an NADPH-regenerating system, 5 mM GSH, or both to assess the effect of GST activity on the metabolism
of Tri by P-450. Tri was dissolved in acetone (final concentration = 0.1%). This concentration of solvent was shown previously (Lipscomb
et al., 1997
, 1998b
) to have no effect on dimethylnitrosamine
demethylase activity, indicating that CYP2E1 was not inhibited under
these conditions. Gas chromatographic quantitation of chloral hydrate
formation was performed as described by Lipscomb et al. (1997)
.
Other Assays.
GGT activity was determined in cytosol and microsomes from pooled human
liver or kidney with
L-
-glutamyl-p-nitroanilide and glycylglycine
as substrates by measuring formation of p-nitroanilide as
the increase in absorbance at 410 nm (Orlowski and Meister, 1963
).
Protein content of samples was measured by the method of Read and
Northcote (1981)
using bovine serum albumin as standard.
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Results |
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GSH Conjugation of Tri in Human Hepatocytes. Suspensions of human hepatocytes were incubated with 50, 500, or 5000 ppm Tri in the headspace for up to 120 min and DCVG formation was measured (Fig. 1A). These concentrations of Tri in the headspace correspond to 0.022, 0.22, or 2.2 mM Tri, respectively, in the cell suspensions. With 50 ppm Tri, no detectable DCVG was measured until the 120-min time point, when 5.62 nmol of DCVG/106 cells was found. In contrast, incubations with both 500 and 5000 ppm Tri exhibited time-dependent increases in DCVG formation, with maximal content of DCVG detected being 21.2 nmol/106 cells with 500 ppm Tri and 18.9 nmol/106 cells with 5000 ppm Tri. A full concentration dependence profile was obtained by measuring DCVG formation after 120-min incubations with 25 to 10,000 ppm Tri (0.011 to 4.4 mM; Fig. 1B). The 120-min time point was chosen to obtain maximal detectable amounts of DCVG. Amounts of DCVG detected increased with increasing concentration of Tri up to 500 ppm Tri, to a maximum amount of 22.5 nmol DCVG/120 min per 106 cells. At concentrations of Tri of 1000 ppm and above, the amount of DCVG detected decreased.
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Time Course and Kinetics of GSH Conjugation of Tri in Human Liver and Kidney Subcellular Fractions. One of the limitations in the measurement of GSH conjugate formation in tissues that contain significant GGT activity is subsequent metabolism of DCVG by GGT and dipeptidases. GGT activity was measured in kidney and liver subcellular fractions (Table 2). As expected, the kidney microsomal fraction, which contains a significant amount of brush-border membranes, exhibited high GGT activity that was 73-fold higher than that in the kidney cytosolic fraction and 33-fold higher than that in the liver microsomal fraction. Hence, incubations to measure DCVG formation in kidney microsomes are the only ones in which subsequent degradation of DCVG must be considered to obtain accurate quantitation of rates of GSH conjugation of Tri. As described above, this problem was circumvented by pretreatment of kidney microsomes with acivicin.
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Individual Variation in Rates of GSH Conjugation of Tri in Human Liver. Analysis of rates of GSH conjugation of Tri in 20 individual liver cytosol and microsomal (Table 4) donors revealed considerable variation among individuals. The liver cytosol donors included 9 males and 11 females. Overall, rates of GSH conjugation varied 2.41-fold and exhibited a range of rates of 34.7 to 83.6 nmol DCVG formed/20 min per mg protein. There was no significant difference between males and females, with males exhibiting a rate of DCVG formation of 52.1 ± 5.3 (mean ± S.E.; n = 9; range 34.7 to 83.6; 2.41-fold variation) and females exhibiting a rate of DCVG formation of 58.1 ± 4.4 (mean ± S.E.; n = 11; range 41.2 to 80.2; 1.95-fold variation) nmol DCVG formed/20 min per mg protein.
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Competition between P-450 and GSH Conjugation Pathways. To assess the potential competition between P-450 and GSH conjugation for metabolism of Tri, pooled human liver cytosol and microsomes were coincubated for 20 min with 1.9 to 125 µM Tri and 5 mM GSH in the absence or presence of an NADPH-regenerating system and amounts of DCVG formation were measured (Fig. 9). In the absence of an NADPH-regenerating system, where the P-450 pathway is inactive, amounts of DCVG formation increased with Tri concentration to a maximum value of 145 nmol/20 min per mg protein with 15 µM Tri and decreased with concentrations of Tri above that. In contrast, in the presence of an NADPH-regenerating system, where the P-450 pathway is active, amounts of DCVG formation increased modestly with increasing concentrations of Tri from 30.2 to 63.9 nmol/20 min per mg protein. These results indicate that P-450s efficiently competed with GSTs and deceased GSH conjugation of Tri by as much as 60%.
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Discussion |
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The complexity of the metabolism of Tri makes human health risk
assessment difficult. This complexity involves the existence of
simultaneous, competing pathways for Tri metabolism and sex-, species-,
and tissue-dependent differences in rates and distribution of
metabolites. The U. S. Environmental Protection Agency is
currently reevaluating Tri (Maull and Lash, 1998
). A central point of
contention involves the biological significance of the GSH conjugation
pathway in the nephrotoxicity of Tri in humans exposed either
occupationally or environmentally to Tri. To help address this
question, the goal of this study was to determine kinetic parameters of
GSH conjugation of Tri in human liver and kidney. If indeed this
pathway does not contribute significantly to overall Tri metabolism in humans, then it would be expected that rates of DCVG formation in human
liver and kidney should be low relative to P-450-catalyzed oxidation of
Tri. Additionally, rates of DCVG formation in human tissue should be
low relative to those observed in corresponding tissues of male rats,
in whom the kidney is an established target organ for Tri (Anders et
al., 1988
; Davidson and Beliles, 1991
; Goeptar et al., 1995
).
The present results show that human hepatocytes and human liver and
kidney cytosol and microsomes catalyze GSH conjugation of Tri at rates
that are significantly higher than those measured previously in rats
and are comparable to those measured in mice (Lash et al., 1995
, 1998
).
One difference in incubation conditions with the isolated hepatocytes
between the present study and the previous ones that may contribute to
the observed differences is that Tri was added to the headspace in the
present study, whereas it was dissolved in acetone and added directly
into the liquid phase in the previous studies. Nonetheless, the present
results confirm that although the liver is the primary site of GSH
conjugation, the entire GSH conjugation pathway can also occur within
the kidneys. The kinetics of GSH conjugation in the two tissues were
different, however, in that only one process was found in kidney
subcellular fractions, whereas two distinct processes were identified
in liver subcellular fractions. Furthermore, total capacity for GSH
conjugation of Tri is markedly higher in human liver than in human
kidney, based on the markedly lower Vmax in
human kidney cytosol and the greater tissue mass for liver than for kidney.
Comment is necessary concerning some of the time courses and
concentration dependence profiles. For example, the formation of DCVG
in isolated hepatocytes incubated with 7.8 µM to 1 mM Tri for 120 min
(cf. Fig. 1B) reached a maximum at 500 ppm Tri and was decreased at
higher concentrations of Tri. There are two possibilities that may
explain this behavior; either the enzyme(s) involved in DCVG formation
may be inhibited by higher amounts of product or other enzymes may
catalyze further metabolism of DCVG only at higher substrate
concentrations. It should be noted that these same cells showed
similar behavior at higher Tri concentrations in measurements of P-450
activity (Lipscomb et al., 1998a
). In some of the time courses of DCVG
formation, [e.g., DCVG formation in liver microsomes (cf. Fig. 3B) or
kidney cytosol or microsomes (cf. Fig. 4)], the amount of DCVG
measured reached a maximum at 10 to 20 min and declined thereafter.
Possible explanations for this may be substrate or product inhibition
or additional metabolism of the formed DCVG. Indeed, substrate-based
inhibition of P-450 activity by Tri was observed in recent studies with
human hepatocytes (Lipscomb et al., 1998a
) and human liver microsomes
(Lipscomb et al., 1998b
) and the concentration of Tri at which
inhibition began to be observed was the same in those studies and the
present study.
There was also some degree of variation in the absolute activity of various pooled samples that were used in some of the assays. This should not be unexpected because different individual samples comprised the various pooled samples and these individual samples can exhibit severalfold variation in rates (cf. Table 4). It was necessary to use pooled samples for most of the studies (except, of course, those specifically assessing individual variability) because of limitations in the amount of the human tissue available. Additionally, use of pooled samples is preferable and makes more sense from the point of view of experimental design because the pooled samples will reflect general or average rates of metabolism in the population.
The position has been taken that the flux of Tri through the GSH
conjugation pathway is significantly smaller than that through the
P-450 pathway (Green et al., 1997
). Consequently, the conclusion is
made that the amount of reactive metabolites of Tri generated in human
kidney is not high enough to produce the biochemical effects that have
been described in male rats. The following observations support this
conclusion: 1) Ratios of oxidative metabolites to the mercapturate in
the urine of exposed humans of 100:1 to as high as 3000:1 have been
reported (Birner et al., 1993
; Bernauer et al., 1996
), 2)
nephrotoxicity or kidney tumors have rarely been observed in humans
(McLaughlin and Blot, 1997
), and 3) activity of the
-lyase in human
kidney cytosol is only about 10% of that in rat kidney cytosol (Lash
et al., 1990
).
Rates of GSH conjugation of Tri in human liver and kidney subcellular
fractions reported in the present study are up to an order of magnitude
greater than those reported by Green et al. (1997)
. In incubations with
1.9 mM Tri and 5 mM GSH, Green et al. (1997)
found rates of DCVG
formation of 2.5, 1.6, and 0.19 pmol/min per mg protein in liver
cytosols of male mice, rats, and humans, respectively. In contrast, in
incubations with 2 mM Tri and 5 mM GSH, we previously reported rates of
DCVG formation of 408 and 122 pmol/min per mg protein in liver cytosols
of male mice and rats, respectively (Lash et al., 1995
, 1998
) and in
the current work, we report a rate of DCVG formation of 5.77 nmol/min per mg protein in pooled human liver cytosol. Similarly, Green et al.
(1997)
were unable to detect net enzymatic formation of DCVG in
incubations with rat kidney subcellular fractions. In contrast, in
incubations with 2 mM Tri and 5 mM GSH we previously reported a rate of
DCVG formation in male rat kidney cytosol of 7.5 pmol/min per mg
protein (Lash et al., 1995
, 1998
) and in the current work, we report a
rate of 0.7 nmol/min per mg protein in pooled human kidney cytosol.
The controversy between our present and previous results and those of
Green et al. (1997)
has not been resolved. Differences in analytical
methods (radiolabeled substrate with HPLC separation versus
derivatization and HPLC separation) may contribute to the discrepancies
in measured rates. Beyond this, no other explanations have been found
to explain the discrepancies. Corrections were made in the present
studies for nonenzymatic DCVG formation and our analytical method
involved measurement of the N-dinitrophenyl derivative of
DCVG and quantitation with respect to authentic standard. Hence, we
were certain of the identity of the measured compound.
Hence, we report rates of GSH conjugation of Tri in human liver
and kidney tissue that are significantly higher than those in
corresponding tissue fractions from the rat. These results indicate
that the initial step in the GSH conjugation pathway is not limiting in
humans and is not responsible for the lower susceptibility of humans
(as compared with rats) to Tri-induced renal injury. Based on previous
results (Lash et al., 1990
; Green et al., 1997
), the
-lyase step and
not the N-acetylation reaction, is likely to be the primary
determinant of how much reactive and toxic species is formed. Results
from a recent study (Lash et al., 1999
), in which human volunteers were
exposed by inhalation for 4 h to 50 or 100 ppm Tri, support the
conclusions of this study that GSH conjugation of Tri occurs at
significant rates. In that study, micromolar concentrations of DCVG
were detected in the blood of human volunteers, indicating significant
activity, presumably predominantly in the liver, of the GSH conjugation pathway with Tri as substrate.
Individual variation in rates of GSH conjugation of Tri were also
found. They are similar in magnitude to those previously reported by
Green et al. (1997)
and are similar to the degree of variation
exhibited in the P-450-dependent metabolism of Tri (Lipscomb et al.,
1997
). Thus, interindividual variability must be taken into account
when considering the role of GSH conjugation in the overall metabolism
and nephrotoxicity of Tri. It should also be noted that among the
separate, duplicate measurements for each individual tissue sample (cf.
Table 4), some amount of variation was observed. Although at least half
of the duplicate samples for either cytosol or microsomes were within
10% of each other, many exhibited significantly more variation. The
reason for this variability is unknown but should not relate to any
defect in the assay method, based on validation of sample recovery,
derivatization efficiency, and corrections that were made for
background or nonenzymatic product formation (present study and Lash
and Jones, 1985
; Lash et al., 1995
, 1998
).
The ability of P-450-dependent metabolism, which becomes active on
addition of an NADPH-regenerating system, to effectively compete with
GSH conjugation and the inability of GSH to diminish rates of chloral
hydrate formation indicate that P-450-dependent oxidation of Tri is the
kinetically favored pathway for Tri metabolism, in agreement with
previous work (reviewed in Davidson and Beliles, 1991
; Goeptar et al.,
1995
). Nonetheless, it is clear that GSH conjugation occurs at
measurable rates in human liver and kidney.
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Acknowledgments |
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We thank Patricia Confer for her expert technical assistance and gratefully acknowledge the generosity of the families of organ donors.
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Footnotes |
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Received June 3, 1998; accepted December 15, 1998.
1 Present address: National Center for Environmental Assessment, U. S. Environmental Protection Agency, 26 W. Martin Luther King Drive, MC-190, Cincinnati, OH 45268.
This study was supported by a cooperative agreement with the U. S. Environmental Protection Agency (CR-824183) by the Strategic Environmental Research and Development Program (SERDP; L.H.L. and J.C.L.). The views expressed in this article are those of the authors and do not necessarily reflect the views or policies of the U. S. Environmental Protection Agency. L.H.L. is a recipient of a Research Career Development Award from the National Institute of Diabetes and Digestive and Kidney Diseases, National Institutes of Health (Grant K04-DK02090).
Send reprint requests to: Lawrence H. Lash, Ph.D., Department of Pharmacology, Wayne State University School of Medicine, 540 East Canfield Ave., Detroit, MI 48201. E-mail: l.h.lash{at}wayne.edu
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Abbreviations |
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Abbreviations used are:
Tri, trichloroethylene;
acivicin, L-(
S,5S)-
-amino-3-chloro-4,5-dihydro-5-isoxazoleacetic
acid;
-lyase, cysteine conjugate
-lyase;
P-450, cytochrome P-450;
DCVG, S-(1,2-dichlorovinyl)glutathione;
GGT,
-glutamyltransferase;
GST, glutathione
S-transferase.
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References |
|---|
|
|
|---|
-lyase activity.
Drug Metab Dispos
18:
50-54[Abstract].
-Glutamyl-p-nitroanilide: A new convenient substrate for determination and study of L- and D-
-glutamyltranspeptidase activities.
Biochim Biophys Acta
73:
679-681.This article has been cited by other articles:
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E. A. Lock and C. J. Reed Trichloroethylene: Mechanisms of Renal Toxicity and Renal Cancer and Relevance to Risk Assessment Toxicol. Sci., June 1, 2006; 91(2): 313 - 331. [Abstract] [Full Text] [PDF] |
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G. Vattemi, P. Tonin, M. Filosto, N. Rizzuto, G. Tomelleri, L. Perbellini, W. Iacovelli, and N. Petrucci Human Skeletal Muscle as a Target Organ of Trichloroethylene Toxicity JAMA, August 3, 2005; 294(5): 554 - 556. [Full Text] [PDF] |
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L. H. Lash, D. A. Putt, S. E. Hueni, R. J. Krause, and A. A. Elfarra Roles of Necrosis, Apoptosis, and Mitochondrial Dysfunction in S-(1,2-Dichlorovinyl)-L-cysteine Sulfoxide-Induced Cytotoxicity in Primary Cultures of Human Renal Proximal Tubular Cells J. Pharmacol. Exp. Ther., June 1, 2003; 305(3): 1163 - 1172. [Abstract] [Full Text] [PDF] |
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T. G. Altuntas and E. D. Kharasch Biotransformation of L-Cysteine S-Conjugates and N-Acetyl-L-Cysteine S-Conjugates of the Sevoflurane Degradation Product Fluoromethyl-2,2-Difluoro-1-(trifluoromethyl)vinyl Ether (Compound A) in Human Kidney in Vitro: Interindividual Variability in N-Acetylation, N-Deacetylation, and beta -Lyase-Catalyzed Metabolism Drug Metab. Dispos., February 1, 2002; 30(2): 148 - 154. [Abstract] [Full Text] [PDF] |
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L. H. Lash and J. C. Parker Hepatic and Renal Toxicities Associated with Perchloroethylene Pharmacol. Rev., May 11, 2001; (2001) 2. [Abstract] [Full Text] |
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B. S. Cummings, J. C. Parker, and L. H. Lash Cytochrome P450-Dependent Metabolism of Trichloroethylene in Rat Kidney Toxicol. Sci., March 1, 2001; 60(1): 11 - 19. [Abstract] [Full Text] [PDF] |
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