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Vol. 26, Issue 9, 868-874, September 1998
Department of Pharmacology and Molecular Toxicology, University of Massachusetts Medical Center
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Abstract |
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1,1,1-Trichloro-2,2-bis(4-methoxyphenyl)ethane (methoxychlor) is a widely used pesticide that is pro-estrogenic. We have elucidated the human cytochrome P450 enzymes responsible for conversion of methoxychlor into its major metabolite, the mono-O-demethylated derivative (mono-OH-M) that is estrogenic. Incubation of methoxychlor with microsomes from insect cells overexpressing either CYP1A2, CYP2C18, or CYP2C19 yielded mono-OH-M with turnover numbers of 14.9, 15.5, and 39.1 nmol/min/nmol of P450, respectively. CYP2B6 and CYP2C9 were much less active. Incubations with purified CYP2C19 and CYP2C18 resulted in formation of mono-OH-M, and also the bis-demethylated metabolite. Co-incubation of liver microsomes with methoxychlor and various P450 isoform-selective inhibitors suggested involvement of several P450s in mono-O-demethylation, including CYP1A2, CYP2A6, CYP2C9, and CYP2C19. A role for CYP2C19, CYP1A2, and CYP2A6 was also indicated by multivariate regression analysis of the mono-O-demethylase activity in a panel of human liver microsomes characterized for isoform-specific catalytic activities (R2 = 0.96). Based on the totality of the evidence, CYP2C19 appears to be the major catalyst of methoxychlor mono-O-demethylation. However, in individuals lacking functional CYP2C19 (e.g. the "poor metabolizer" phenotype), CYP1A2 may play the predominant role. CYP2A6, CYP2C9, and CYP2B6 probably contribute to a lesser extent. Although CYP2C18 is an efficient methoxychlor demethylase, its expression in liver is reportedly low or absent, suggesting a negligible role for this enzyme in methoxychlor metabolism. Lengthy incubations of liver microsomes with methoxychlor produced other secondary and tertiary metabolites. Efficient conversion of methoxychlor to estrogenic mono-OH-M by liver microsomes suggests that methoxychlor has the potential to be estrogenic in humans, as observed in several animal species.
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Introduction |
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1,1,1-Trichloro-2,2-bis(4-methoxyphenyl)ethane
(methoxychlor1)
(fig. 1) is a
1,1-bis(p-chlorophenyl)-2,2,2-trichloroethane (DDT)
substitute preferred as an insecticide because of its limited persistence in the biosphere (Gardner and Bailey, 1975
). In addition, it exhibits low acute toxicity in mammals (Hodge et al.,
1950
). However, methoxychlor elicits broad endocrine toxicities related to its estrogen-like behavior including adverse developmental, reproductive, and behavioral effects (Chapin et al., 1997
;
reviewed in Cummings, 1997
). Moreover, methoxychlor may induce
endocrine cancers in rodents (Reuber, 1980
).
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The in vivo estrogenic effects of methoxychlor are
attributed to the action of its metabolites, or, additionally, in the
case of technical grade preparation, to its phenolic impurities (Bulger and Kupfer, 1985
). Indeed, both the mono- and bis-demethylated metabolites (mono-OH-M and bis-OH-M, respectively) exhibit estrogenic activity in vitro, whereas the parent compound is
essentially inactive (Bulger et al., 1978
; Ousterhout
et al., 1981
). The cytochrome P450 isoforms that catalyze
demethylation (Kishimoto and Kurihara, 1996
) and
ortho-hydroxylation (Dehal and Kupfer, 1994
; Stresser et al., 1996
) have been identified in rats, but little
information is available regarding its metabolism by human P450s
(Stresser and Kupfer, 1997
, 1998
). In this report, we identify the
major P450s expected to catalyze conversion of methoxychlor to its
single major metabolite, the mono-O-demethylated derivative.
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Materials and Methods |
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Chemicals.
Glucose-6-phosphate, glucose-6-phosphate dehydrogenase, NADPH,
coumarin, troleandomycin, tranylcypromine, sulfaphenazole, diethyldithiocarbamate, EDTA disodium salt, and activated charcoal (untreated powder) were purchased from Sigma Chemical
Co. (St. Louis, MO). Furafylline was obtained from Salford Ultrafine
Chemicals and Research (Manchester, United Kingdom). Tolbutamide and
ketoconazole were purchased from Research Biochemials International
(Natick, MA). S-Mephenytoin was obtained from Gentest Corp.
(Woburn, MA). Quinidine and
-naphthoflavone were obtained from
Aldrich Chemical Co. (Milwaukee, WI). Bis-OH-M was kindly provided by
Dr. T. Fujita (Kyoto University, Kyoto, Japan) and Dr. J. Sanborn
(Illinois Natural History Survey, Urbana, IL). Methoxychlor was
purchased from Chem Service (West Chester, PA).
[ring-UL-14C]Methoxychlor was
obtained from Sigma (5.85 mCi/mmol) or California Bionuclear (La Brea,
CA; 1.8 mCi/mmol).
[ring-UL-14C]Mono-OH methoxychlor
was prepared biosynthetically by incubation of
[ring-UL-14C]methoxychlor with human
liver microsomes as described below.
Microsome Preparation.
Portions of human livers were obtained from National Disease Research
Interchange (Philadelphia, PA) or Prof. Urs Meyer (Basel, Switzerland)
and kept frozen at
70oC until use. Livers were
thawed and homogenized in 0.25 M sucrose (5 ml sucrose/g liver), using
a Potter-Elvehjem homogenizer and a Teflon pestle (Eberbach Corp., Ann
Arbor, MI), and microsomes were prepared by differential centrifugation
(Burstein and Kupfer, 1971
). The resulting microsomal pellets were
resuspended in 1.15% KCl solution, followed by centrifugation at
105,000g for 1hr. The microsomal pellet, after discarding
the supernatant, was covered with 1.15% KCl (nominally 2 ml) and
stored at
70oC until use. Protein concentration
was determined by the method of Lowry et al. (1951)
, using
bovine serum albumin as a standard. Minor modifications were
incorporated into the assay that improve the range of linearity with
protein concentration (Stauffer, 1975
). Additional human liver
microsomes, characterized for P450 isoform catalytic activities, were
purchased from International Institute for the Advancement of Medicine
(Exton, PA). Microsomes from insect cells engineered to express single
human P450 isoforms were purchased from Gentest, Inc. (Woburn, MA).
Incubation of Microsomes with [14C]Methoxychlor or [14C]Mono-OH-M. Incubations with human and rat liver microsomes were conducted in a 100- or 250-µl volume in a shaking water bath at 37°C. The assay mixture contained the following components at the concentrations indicated: sodium phosphate (70 mM, pH 7.4), MgCl2 (10 mM), EDTA (1 mM), microsomal protein (0.05-1.0 mg/ml), KCl (30 mM), and substrate (usually 1 or 25 µM) delivered in ethanol (1% v/v). After a 2-min preincubation period at 37°C, the reaction was initiated with an NADPH-regenerating system [glucose 6-phosphate (10 mM), glucose-6-phosphate dehydrogenase (2.0 units/ml), and NADPH (0.5 mM)]. Control incubations were conducted in the absence of the cofactor NADPH. The reaction was terminated at various times by the addition of 10 volumes of ice-cold ethanol. After centrifugation, the supernatant was transferred to borosilicate tubes and evaporated under nitrogen gas. The residue was dissolved in 50 µl of ethanol, and a portion was applied to a TLC plate (normal phase, 9:1 chloroform:acetone or reversed phase TLC (C18 TLC) in a solvent system of methanol:water:acetic acid (75:24:1, v/v) (10). To obtain sufficient [14C]mono-OH-M for use as a substrate, 10 incubations that contained human liver microsomes (1 mg/ml), [14C]methoxychlor (53 µM) and an NADPH-regenerating system in a final volume of 5 ml were conducted for 2 hr at 37°C. Additional components were similar to that described above. After addition of ethanol to terminate the reaction and centrifugation, the supernatants were combined, evaporated to dryness, and resuspended in a small volume of ethanol. After TLC analysis, the zone containing the [14C]mono-OH-M (verified by co-migration of authentic [3H]mono-OH-M) was recovered by scraping the plate followed by ethanol elution. Incubations with insect cell microsomes containing cDNA-expressed P450s were conducted in a similar manner, except that samples were not agitated during the incubation period.
Incubations With Heterologously Expressed Purified P450s.
Purified CYP2C9, 2C18, 2C19, 2D6, NADPH cytochrome P450 reductase, and
cytochrome b5, expressed in
Escherichia coli, were obtained from Drs. Toby Richardson
and Eric Johnson (The Scripps Research Institute, La Jolla, CA).
Components, added in order, were 10 pmol P450, 0.2 units NADPH-P450
reductase, 40 pmol cytochrome b5 (when
present), and 1.5 µg L-
-dilauroyl-phosphatidylcholine, sonicated
in H2O. When cytochrome
b5 was omitted from the reaction, buffer
only was used in its place. These components were allowed to incubate
on ice for 25 min before the addition of sodium phosphate buffer,
MgCl2, KCl, and substrate. The samples were then
incubated at 37°C for 2 min, before initiating the reaction by the
addition of an NADPH regenerating system consisting of glucose
6-phosphate (2.5 µmol), NADPH (0.125 µmol), and glucose-6-phosphate
dehydrogenase (0.5 IU) in 25 µl H2O. The final
volume of the mixture was 250 µl.
Chemical Inhibition Experiments.
Incubations with human P450 isoform-selective inhibitors were conducted
in a manner similar to that described above. The concentrations of
inhibitors and conditions used to maximize selectivity were based on
the data of Newton et al. (1995)
or Chauret et
al. (1997)
. Inhibitors and the concentrations used were
furafylline (20 µM), sulfaphenazole (100 µM), quinidine (10 µM),
TAO (50 µM), tranylcypromine (50 µM),
-naphthoflavone (2.5 µM), DDTC (30 µM), S-(+)-mephenytoin (500 µM),
tolbutamide (500 µM), coumarin (200 µM), and ketoconazole (1 µM).
All inhibitors were dissolved in ethanol, and the final concentration
of ethanol in all incubations was 1%. Two inhibition protocols were
followed. With TAO, DDTC, and furafylline, all components except
methoxychlor were incubated for 15 min at 37°C. After the
preincubation period, methoxychlor was added and the incubation was
continued for 10 min before being terminated by the addition of
ethanol. With all other inhibitors, the preincubation period was
omitted.
Regression Analysis.
Univariate or stepwise multiple linear regression analysis was
performed to compare methoxychlor mono-O-demethylase
activity (dependent variable) with one or more P450 isoform specific
marker activities [independent variable(s)] in panels of human liver microsomes using Instat Version 3 (GraphPad Software, Inc. San Diego,
CA). Analysis of variance was used to determine whether the model was
statistically significant (e.g. p values of
0.05). Michaelis-Menten parameters were determined from nonlinear,
least squares regression analysis using the equation for a
single-enzyme model with CYP1A2 or CYP2C19 catalysis, v = (Vmax[S])/(Km + [S]), or with human liver microsomes, using the equation for a
two-enzyme model, v = [(Vmax1[S])/(Km1 + [S])]/[(Vmax2[S])/(Km2 + [S])] (Origin Version 5.0, Microcal Software, Inc., Northampton, MA).
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Results |
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Demethylation of Methoxychlor.
Liver microsomes pooled from 3 individuals were incubated with
saturating levels of methoxychlor (25 µM). A single major metabolite, the mono-O-demethylated derivative is observed (fig.
2). Formation of mono-OH-M was
proportional to protein concentration up to 2 mg/ml (fig.
3) and with time up to 20 min (fig.
4). With longer incubation times, lesser
products of secondary and tertiary metabolism are detected, including
bis-OH-M and tris-OH-M (fig. 4). Low level catalysis to additional
ring-hydroxylated metabolites (Stresser and Kupfer, 1998
) and a
metabolite(s) that binds covalently to liver microsomal protein have
also been demonstrated previously (Bulger and Kupfer, 1989
). Similarly,
incubation of 25 µM methoxychlor for 10 min with microsomes from four
different human livers yielded mono-OH-M, whereas bis-OH-M, tris-OH-M,
or other metabolites were not detected or was produced only in small
amounts (table 1). In contrast, rat liver
microsomes are efficient in catalyzing methoxychlor conversion to both
mono-OH-M and bis-OH-M (table 1). Accordingly, for three of the four
human liver samples shown in table 1, longer incubation times of 60 min
were necessary to generate quantifiable bis-OH-M when mono-OH-M was
used as the substrate. With rat liver microsomes, nearly complete
conversion of mono-OH-M to bis-OH-M was observed. The mono-demethylase
activity was assessed in a panel of 26 samples of human liver
microsomes overall and was found to vary 23-fold (data not shown),
ranging from 91 to 2056 pmol/min/mg protein (mean ± SD, 354 ± 392; median, 304). To assess metabolism at concentration that might
be more relevant to environmental exposures, incubations were also
conducted at 1 µM methoxychlor using livers from 14 individuals.
Rates of mono-O-demethylation varied 80-fold (data not
shown), ranging from 14 to 1130 pmol/min/mg protein (mean ± SD,
169 ± 283; median, 101).
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Effect of Chemical Inhibitors.
The effect of chemical inhibitors on human liver
mono-O-demethylation of methoxychlor at two different
substrate concentrations is shown in fig.
5A (gray bars, 1 µM methoxychlor; black bars, 25 µM
methoxychlor). Only moderate inhibition was observed, by several
inhibitors using 25 µM methoxychlor. Tranylcypromine, an inhibitor of
CYP2C19-catalyzed S-(+)-mephenytoin 4'-hydroxylase (Inaba
et al., 1985
) and CYP2A6-catalyzed 7-hydroxylation of
coumarin (Draper et al., 1997
), inhibited demethylation to
the greatest extent, followed by furafylline and sulfaphenazole. At 1 µM substrate, strong inhibition was observed by CYP2C19 inhibitors
tranylcypromine and S-mephenytoin; tolbutamide, furafylline,
TAO, sulfaphenazole, and coumarin exhibited moderate inhibition. At
both substrate concentrations, quinidine, ketoconazole, and DDTC were
found, overall, to be weak inhibitors. These data suggested that
multiple isoforms could catalyze mono-O-demethylation of
methoxychlor. To explore this possibility in greater detail, we
examined the effect of selected inhibitors on individual preparations
of human liver microsomes that exhibited varied isoform-specific
catalytic activity (fig. 5B). As expected, inhibitor effects
varied substantially, depending on the liver, confirming multiple
isoform involvement in methoxychlor demethylation.
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Correlation Studies with P450 Isoform-Specific Catalytic
Activities.
Methoxychlor mono-demethylase activity was measured in a panel of 13 (using 1 µM methoxychlor) or 16 (using 25 µM methoxychlor) human
liver microsomal preparations that had been characterized previously by
the vendor for several P450-isoform selective activities (table
2). With 1 µM methoxychlor,
mono-demethylation correlated significantly with phenacetin
O-deethylase (R2 = 0.54), a
marker of CYP1A2 activity (Distlerath et al., 1985
) and
S-(+)-mephenytoin 4'-hydroxylase activity
(R2 = 0.79), a marker of CYP2C19 content
(Wrighton et al., 1993
; Goldstein et al., 1994
).
Similar, but slightly less significant, correlations were observed
using 25 µM substrate concentration. Additionally, at this
concentration of methoxychlor, mono-demethylation correlated
significantly with total P450 content of the microsomes. Stepwise
multiple regression analysis indicated that, in addition to CYP1A2 and
2C19 marker activities, CYP2A6-catalyzed 7-hydroxylation of coumarin
(Yamano et al., 1990
; Miles et al., 1990
) could
account for the variability in the data at 1 µM substrate
concentration.
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Studies With Recombinant P450 Isoforms.
Insect cell microsomes containing various, singly expressed P450
isoforms were found to catalyze methoxychlor
mono-O-demethylation (fig. 6).
The most active isoform at 25 µM was CYP2C19, supporting our previous
results with recombinant P450s expressed in lymphoblastoid cells
(Stresser and Kupfer, 1998
). Slightly less active were CYP1A2 and 2C18.
Mono-OH-M was formed also by CYP2B6 and CYP2C9, but was not detected
when CYP3A4, CYP3A5, or control cell microsomes lacking expressed P450
were used. Similar results were observed using 1 µM methoxychlor as
substrate, although CYP2C18 was the most active at this concentration.
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Kinetic Studies With Recombinant CYP2C19 and 1A2 and Human Liver
Microsomes.
Kinetic analysis of mono-demethylation was performed with microsomes
from insect cells overexpressing CYP1A2 or CYP2C19 (fig. 7) and human liver microsomes (fig.
8). Nonlinear regression analysis revealed the data for CYP1A2 and CYP2C19 followed standard
Michaelis-Menten kinetics for a one-enzyme model, whereas that for
human liver microsomes fit a two-enzyme model. Kinetic parameters are
shown in table 4. Both P450 isoforms
exhibited similar apparent Michaelis-Menten constants of approximately
0.5-0.6 µM. CYP2C19 exhibited a 2-fold higher
Vmax and therefore displayed a greater
value for
Vmax/KM, a
measure of in vitro intrinsic clearance (Rane et
al., 1977
). Human liver microsomes, pooled from the livers of
three individuals, exhibited a low KM
component of 0.35 µM and a high KM
component of 12 µM. Despite relatively large errors associated with
these parameters, the Eadie-Hofstee plot clearly shows involvement of more than one enzyme.
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Discussion |
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The biotransformation of methoxychlor by animals has been
investigated extensively (Chapin et al., 1997
; Kishimoto and
Nurihara, 1996
; Dehal and Kupfer, 1994
; Kishimoto et al.,
1995
; Bulger et al., 1985
; Schlenk et al., 1997
;
Kapoor et al., 1970
; Davison et al., 1982
), but
relatively few studies have been conducted with human tissues (Stresser
and Kupfer, 1998
; Bulger and Kupfer, 1989
; Kupfer et al.,
1990
). Human liver microsomes catalyze primarily mono-O-demethylation of this insecticide. Secondary and
tertiary metabolism occur during longer incubation periods, resulting
in a second demethylation and ortho-hydroxylation. There is
low level metabolism to other ortho-hydroxylated metabolites
and this may occur without prior O-demethylation. In
addition, methoxychlor undergoes activation to a reactive metabolite of
unknown structure that binds covalently to microsomal protein (Bulger
and Kupfer, 1989
). The estrogenicity of methoxychlor mono- and
bis-phenolic metabolites has been established (Bulger et
al., 1978
, 1985
; Ousterhout et al., 1981
), but whether
catechol or other metabolites exhibit estrogenic or anti-estrogenic
effects has not yet been determined. The estrogenic action of
methoxychlor in animals has prompted concern that human exposure to
methoxychlor may elicit endocrine disrupting effects (Chapin et
al., 1997
; Cummings, 1997
).
In this study, we have characterized the human P450 isoforms that are
the primary catalysts in the major, initial metabolic pathway, namely
that leading to formation of mono-OH-M. An Eadie-Hofstee plot of
methoxychlor mono-O-demethylation by human liver microsomes indicated biphasic enzyme kinetics, suggesting the involvement of
multiple isoforms in this reaction. Indeed, using a panel of recombinant P450 isoforms expressed in E. coli or insect
cells in the present study, and based on previous data with recombinant P450s expressed in lymphoblast cells (Stresser and Kupfer, 1998
), multiple isoforms were shown capable of methoxychlor
mono-O-demethylation. CYP2C18, CYP2C19, and CYP1A2 appear to
be the most active in this catalysis, whereas CYP2C9 displayed variable
activity and 2A6 and 2B6 exhibited overall lesser activity. CYP1A1,
CYP1B1, CYP2D6, CYP2E1, CYP3A4, and CYP3A5 were found incapable of
catalyzing demethylation of methoxychlor. Although CYP2C18 was the most
active at low substrate concentration using the insect cell expressed enzyme, its expression in human liver is believed to be minuscule or
absent (Jung et al., 1997
), and consequently it is unlikely to be a significant methoxychlor demethylase in liver microsomes.
The primary involvement of CYP1A2 and CYP2C19 in demethylation of methoxychlor is supported by correlation analysis. Univariate regression analysis indicated a significant correlation of mono-demethylase activity with CYP2C19 catalyzed S-(+)-mephenytoin 4'-hydroxylase activity, and CYP1A2-catalyzed phenacetin O-deethylase activity, at both subsaturating (1 µM) and saturating (25 µM) methoxychlor concentrations. Stepwise multivariate regression analysis indicated that, in addition to CYP2C19 and CYP1A2 catalyzed marker activities, CYP2A6-catalyzed coumarin 7-hydroxylase activity significantly correlated with mono-demethylation using 1 µM methoxychlor.
Based on the above findings, we pursued further the role of CYP1A2 and
CYP2C19 in mono-O-demethylation of methoxychlor by kinetic
analysis. Both enzymes exhibited single-enzyme Michaelis-Menten kinetics and displayed similar apparent KM
values of 0.5-0.6 µM, consistent with the high affinity component
observed in human liver microsomes. CYP2C19 exhibited a
Vmax of more than 2-fold that calculated
for CYP1A2. This is consistent with our previous findings where
recombinant CYP2C19 expressed in lymphoblast cells was found to be
significantly more active than similarly expressed CYP1A2 (Stresser and
Kupfer, 1998
) under saturating substrate conditions.
We demonstrated that cDNA-expressed CYP2C19, purified from E. coli lysates, catalyzed methoxychlor mono-demethylation at rates more than 4-fold over CYP2C9 and CYP2C18. The effects of cytochrome b5 in an appropriately reconstituted system
on rates of catalysis differed depending on the CYP2C isoform. Whereas
cytochrome b5 inhibited CYP2C9 mono-OH-M
formation and CYP2C19 bis-OH-M formation, it stimulated production of
both metabolites by CYP2C18. The differential effects of cytochrome
b5 on CYP2C isoforms are consistent with previous studies by others (Rodrigues et al., 1996
; Raucy
et al., 1994
).
Inhibition by chemicals reported to exhibit selectivity for certain
P450 isoforms are supportive of a role for CYP2C19 (tranylcypromine, S-mephenytoin,
tolbutamide2), CYP1A2
(
-naphthoflavone, furafylline), CYP2A6 (tranylcypromine, coumarin)
and CYP2C9 (sulfaphenazole, tolbutamide) in the mono-demethylation of
methoxychlor in human liver. Lack of potent inhibition by
any inhibitor in these experiments is consistent with the conclusion that multiple isoforms are involved. As expected, most competitive inhibitors exhibited greater inhibition at subsaturating concentrations of methoxychlor. When individual liver microsomal preparations were
examined for their catalytic activity in the presence of selected
inhibitors, variable inhibition of methoxychlor
mono-O-demethylation was observed, a finding that probably
depended on the content of a particular P450 isoform in a given liver.
The highly variable and idiosyncratic nature of P450 isoform expression
is well documented in human livers (Shimada et al., 1994
).
A second demethylation of methoxychlor also occurs, forming bis-OH-M, a
more potent estrogen than mono-OH-M (Ousterhout et al.,
1981
; Bulger et al., 1985
). Unlike rats, humans are
inefficient at forming bis-OH-M in vitro, and lengthy
incubation times are usually required to detect this metabolite. The
identity of the human P450s responsible for this reaction has not been
fully characterized, although purified and reconstituted CYP2C18 and
CYP2C19 clearly can catalyze this reaction. CYP2B6 and CYP1A2 catalyze
the ortho-hydroxylation of methoxychlor (Stresser and
Kupfer, 1997
), whereas CYP3A4 is most active in catalyzing
ortho-hydroxylation of mono- or bis-demethylated methoxychlor (Stresser and Kupfer, 1997
, 1998
).
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Conclusions |
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We have found that multiple P450 isoforms contribute to methoxychlor metabolism in human liver microsomes. The sum of the evidence indicates that polymorphically expressed CYP2C19 is the major methoxychlor mono-demethylase, but may be only slightly more involved than CYP1A2. In those individuals lacking or expressing only low levels of CYP2C19, other isoforms, in particular CYP1A2, but also CYP2A6, CYP2C9, and CYP2B6, are likely to be major contributors to this reaction. Because methoxychlor exhibits adverse developmental and reproductive effects in various animal model systems that have been attributed to its estrogenic phenolic metabolites, exposure to this insecticide may pose similar health risks in humans, the magnitude of which may be related to P450 isoform expression.
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Acknowledgments |
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The authors sincerely thank Drs. Eric Johnson and Toby Richardson (The Scripps Research Institute, La Jolla, CA) for providing the purified recombinant P450s.
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Footnotes |
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Received March 16, 1998; accepted May 5, 1998.
This work was supported by Grants ES00834 and ES05737 from the National Institute of Environmental Health Sciences, National Institutes of Health. The contents of this article are solely the responsibility of the authors and do not necessarily represent the official view of the National Institute of Environmental Health Sciences, National Institutes of Health. This manuscript is dedicated to the memory of William H. Bulger, who provided the data for fig. 4.
Portions of this work were presented at the Annual Meeting of the Society of Toxicology, Seattle, WA, on March 1-5, 1998, and appeared in abstract form in Toxicol Sci 42(1-S), Abstract 453, 1998.
2
Although tolbutamide is considered a selective
substrate for CYP2C9 methyl hydroxylation, CYP2C19 was recently
reported to be active in catalyzing this reaction, suggesting that
tolbutamide could be an effective competitive inhibitor of CYP2C19 in
liver microsomes (Shimada et al.,
1997
).
Send reprint requests to: Dr. David Kupfer, Department of Pharmacology and Molecular Toxicology, University of Massachusetts Medical Center, 55 Lake Ave. North, Worcester, MA 01655.
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Abbreviations |
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Abbreviations used are: methoxychlor, [1,1,1-trichloro-2,2-bis(4-methoxyphenyl)ethane]; mono-OH-M, [1,1,1-trichloro-2(4-hydroxyphenyl)-2(4-methoxyphenyl)ethane]; bis-OH-M, [1,1,1-trichloro-2,2-bis(4-hydroxyphenyl)ethane]; tris-OH-M, [1,1,1-trichloro-2(3,4-dihydroxyphenyl)-2(4-hydroxyphenyl)ethane]; CYP, cytochrome P450; TAO, troleandomycin; DDTC, diethyldithiocarbamate.
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-naphthoflavone and methoxychlor pretreatment on the biotransformation and estrogenic activity of methoxychlor in channel catfish (Ictalurus punctatus).
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D. Blizard, T. Sueyoshi, M. Negishi, S. S. Dehal, and D. Kupfer Mechanism of Induction of Cytochrome P450 Enzymes by the Proestrogenic Endocrine Disruptor Pesticide-Methoxychlor: Interactions of Methoxychlor Metabolites with the Constitutive Androstane Receptor System Drug Metab. Dispos., June 1, 2001; 29(6): 781 - 785. [Abstract] [Full Text] |
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D. M. Stresser and D. Kupfer Monospecific Antipeptide Antibody to Cytochrome P-450 2B6 Drug Metab. Dispos., April 1, 1999; 27(4): 517 - 525. [Abstract] [Full Text] |
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