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Vol. 30, Issue 2, 113-118, February 2002
Institute of Pharmaceutical Science, Hiroshima University School of Medicine, Minami-ku, Hiroshima, Japan
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Abstract |
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The in vitro metabolism of p,p'-DDT [1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane], an important environmental pollutant, was examined in rat liver, focusing on reductive dechlorination. When p,p'-DDT was incubated with liver microsomes of rats in the presence of NADPH or NADH, a dechlorinated metabolite, p,p'-DDD [1,1-dichloro-2,2-bis(4-chlorophenyl)ethane], was formed under anaerobic conditions together with a dehydrochlorinated metabolite, p,p'-DDE [1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene]. p,p'-DDE was also formed from p,p'-DDD by liver microsomes. The dechlorinating activity was inhibited by carbon monoxide, metyrapone, and SKF 525-A (proadifen hydrochloride), but the dehydrochlorinating activity was unaffected. The reductase activity toward p,p'-DDT was induced by the pretreatment of rats with phenobarbital and dexamethasone. The dechlorination was catalyzed enzymatically by recombinant cytochrome P450 2B1, 3A1, 2B6, and 3A4. When p,p'-DDT was incubated with liver microsomes of rats in the presence of both a reduced pyridine nucleotide and FMN, p,p'-DDD was also formed under anaerobic conditions. In this case, the dechlorinating activity was not abolished when the microsomes were boiled. The reductase activities were inhibited by carbon monoxide. Hematin exhibited reductase activity toward p,p'-DDT in the presence of NADH and FMN. The activity of hematin was also supported by FMNH2. The reductive dechlorination also seems to proceed nonenzymatically with the reduced flavin, catalyzed by the heme group of cytochrome P450. Similar enzymatic and nonenzymatic reducing activities were observed toward o,p'-DDT [1,1,1-trichloro-2,2-bis(2-chlorophenyl-4-chlorophenyl)ethane].
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Introduction |
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p,p'-DDT
[1,1,1-trichloro-2,2-bis(2-chlorophenyl-4-chlorophenyl)ethane] is
a broad-spectrum insecticide, which was used from the 1940s in large
quantities, but was banned in many countries in the 1970s because of
its persistence in the environment. It was replaced in part by less
persistent alternatives. This pesticide, however, is still used mainly
in developing countries. p,p'-DDT and related
compounds, many of which are carcinogenic and mutagenic, are also known
to be environmental estrogens. p,p'-DDT is a
phenobarbital-type inducer, which induces the cytochrome P450
(CYP1) 2B and 3A subfamily (Lewis and Lake, 1997
;
Nims et al., 1998
). p,p'-DDT and its metabolites
accumulate in animal tissues and induce various enzymes (Esaac and
Matsumura, 1980
). The higher levels of p,p'-DDE
[1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene] than
p,p'-DDT in tissues reflect its stability (Morgan
and Roan, 1971
). These compounds mimic hormones and bind to the
estrogen receptor and androgen receptor (Robinson et al., 1985
;
Kelce et al., 1995
; Chen et al., 1997
). p,p'-DDT
and related compounds, p,p'-DDD
[1,1-dichloro-2,2-bis(4-chlorophenyl)ethane],
o,p'-DDT [1,1,1-trichloro-2,2-bis(2-chlorophenyl-4-chlorophenyl)ethane], and
dicofol [1,1-bis(4-chlorophenyl)-2,2,2-trichloroethanol], are known
to be xenobiotic estrogens, but p,p'-DDE is an
antiandrogen (You, 2000
). To assess the possible risks associated with
human exposure to the pesticide, it is essential to thoroughly
elucidate its metabolism in mammalian species, birds, and marine and
freshwater species.
p,p'-DDT is converted by reductive dechlorination
to p,p'-DDD in insects, birds, and animals
(Hassall, 1972
; Esaac and Matsumura, 1980
). Several reports have
indicated that p,p'-DDT is mainly metabolized to
p,p'-DDE by dehydrochlorination in mammalian
species, insects, and microorganisms, and
p,p'-DDD is an intermediate of the reaction,
which may proceed via
-hydroxyl-DDD (Benitez et al., 1995
; Fox et
al., 1998
). p,p'-DDT and
p,p'-DDE are further oxidized to
2,2-bis(4-chlorophenyl)acetic acid
(p,p'-DDA), the major excreted metabolite
in animals (Wallcave et al., 1974
; Gold and Brunk, 1982
). The
dechlorination is of considerable significance because this reaction is
the first and also is the rate-limiting step in the metabolism of
p,p'-DDT in mammals and microorganisms. A role of
CYP in the microsomal reduction of p,p'-DDT was
suggested (Esaac and Matsumura, 1980
; Baker and Van Dyke, 1984
; Kelner
et al., 1986
). However, the mechanism of microsomal reductive
dechlorination of p,p'-DDT is not known in
detail. Furthermore, the metabolism of o,p'-DDT,
which contaminates technical-grade DDT about 20%, has not been
established. In the present study, the in vitro metabolism of
p,p'-DDT and o,p'-DDT by
rat liver microsomes was examined, focusing on reductive dechlorination
to DDD isomers.
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Experimental Procedures |
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Materials.
p,p'-DDT, p,p'-DDE, and
p,p'-DDD were purchased from Tokyo Chemical
Industry Co., Ltd (Tokyo, Japan). o,p'-DDT,
o,p'-DDD, p,p'-DDMU
[1-chloro-2,2-bis(4-chlorophenyl)ethylene],
p,p'-DDA, dicofol, and
o,p'-DDE were obtained from Labor Dr.
Ehrenstorfer-Schäfers (Augsburg, Germany). FMN and hematin
(Fe3+) were from Sigma Chemical Co. (St. Louis,
MO). Reduced FMN was prepared photochemically from FMN by the
previously described method (Kitamura et al., 1999a
).
p,p'-DDT and o,p'-DDT were
used after recrystallization from n-hexane. Microsomal
preparations from recombinant rat CYP 2B1 and 3A1 expressed in insect
cells and from nine recombinant human CYP isoforms (i.e., CYP 1A1, 1A2, 2A6, 2B6, 2C9, 2D6, 2E1, 3A4, and 4A11) expressed in a human B lymphoblastoid cell line were purchased from GENTEST (Woburn, MA).
Animals. Male rats (Slc:SD; 180-210 g; Slc:Japan; Shizuoka, Japan) were used. In some experiments, phenobarbital was administered to rats intraperitoneally at a dose of 80 mg/kg for 3 days, 3-methylcholanthrene at 25 mg/kg for 3 days, dexamethasone at 100 mg/kg for 4 days, clofibrate at 250 mg/kg for 3 days, and acetone at 3 g/kg orally for 1 day.
Preparation of Liver Microsomes.
Rat livers were homogenized in 4 volumes of 1.15% KCl. The homogenate
was centrifuged at 9000g for 20 min, and the supernatant fraction was separated into microsomes and cytosol by centrifugation at
105,000g for 60 min. The microsomes were washed by
resuspension in 2 volumes of the KCl solution and by resedimentation at
105,000g for 60 min. The pellets of microsomes were
resuspended in the solution to make 1 ml equivalent to 1 g of
liver. Protein contents in the liver microsomal preparation of
untreated, phenobarbital-treated, dexamethasone-treated,
clofibrate-treated, acetone-treated, and 3-methylcholanthrene-treated
rats were 12.6 to 14.8, 18.5 to 20.9, 14.5 to 16.7, 13.4 to 15.8, 12.5 to 14.4, and 13.4 to 17.2 mg of protein/ml, respectively, as determined
by the method of Lowry et al. (1951)
.
Identification of Reductive Metabolites of p,p'-DDT Formed by Rat Liver Microsomes. Two reductive metabolites of p,p'-DDT or p,p'-DDD were determined from a large-scale incubation mixture. The large-scale incubation mixture consisted of 1 µmol of the substrate, 5 µmol of NADPH, and 1 ml of liver microsomes of untreated rats in a total volume of 5 ml of 0.1 M Tris-HCl buffer, pH 7.4. After incubation for 20 min, the mixture was extracted with 20 ml of n-hexane. The supernatant was evaporated to dryness, and 0.1 ml of methanol was added. The solution was injected into a high-performance liquid chromatograph and a gas chromatograph-mass spectrometer. Gas chromatograph-mass spectrometer was performed using a Shimadzu GC-17A/QP-5000 (Kyoto, Japan) in the electron impact mode. A DB-5 fused-silica capillary column (30-m × 0.25-mm i.d.; J & W Scientific, Inc., Folsom, CA) was used. The column temperature was held at 100°C for 3 min, then increased at a rate of 15°C/min to 240°C. One microliter of sample was injected into the injection port, which was held at 250°C. Splitless injection was used. The retention times of p,p'-DDD, p,p'-DDE, and p,p'-DDMU were 13.4, 13.0, and 12.4 min, respectively. The mass spectra of p,p'-DDD, p,p'-DDE, and p,p'-DDMU showed m/z 320 (M+), 235, and 165, m/z 318 (M+), 246, and 176, and m/z 284 (M+), 212, and 176, respectively.
Assay of Reductase Activity. The incubation mixture consisted of 0.1 µmol of p,p'-DDT or o,p'-DDT (50 µl of methanol solution), 1 µmol of NADPH or NADH, and 0.2 ml of liver microsomes in a final volume of 1 ml of 0.1 M K,Na-phosphate buffer, pH 7.4. Incubation was performed using a Thunberg tube under anaerobic conditions. The side arm contained NADPH or NADH, and the body contained all the other components. The tube was gassed for 3 min with nitrogen, evacuated with an aspirator for 5 min, and again gassed with nitrogen. The reaction was started by mixing the components of the side arm and the body together and was continued for 30 min at 37°C. The mixture, after addition of 1 µg of phenothiazine as an internal standard, was extracted once with 5 ml of n-hexane, and the extract was evaporated to dryness in vacuo. The residue was dissolved in 0.1 ml of methanol and then subjected to high-performance liquid chromatography (HPLC).
HPLC. HPLC was performed in a Hitachi L-6000 high-performance liquid chromatograph (Tokyo, Japan) equipped with an ultraviolet absorption detector. The instrument was fitted with a 4 × 125-mm LiChrospher RP-Select B (5 µm) (Merck, Darmstadt, Germany). The mobile phase was acetonitrile/H2O (6:4). The chromatograph was operated at a flow rate of 1.0 ml/min at ambient temperature and at a wavelength of 254 nm. Elution times of p,p'-DDA, dicofol, p,p'-DDD, o,p'-DDD, p,p'-DDT, p,p'-DDMU, o,p'-DDT, p,p'-DDE, and o,p'-DDE were 4.5, 15.4, 16.5, 17.8, 27.7, 29.0, 35.3, and 36.7 min, respectively. The amounts of metabolites formed were determined from the peak areas.
Thin-Layer Chromatography (TLC). Silica gel plates (Kieselgel 60 GF254, 0.2 mm thick; Merck, Darmstadt, Germany) were developed in n-hexane/acetone (9:1, v/v). Spots were visualized under UV light (254 nm). The Rf values of authentic p,p'-DDA, dicofol, p,p'-DDD, p,p'-DDT, p,p'-DDMU, and p,p'-DDE were 0.12, 0.33, 0.36, 0.48, 0.52, and 0.63, respectively.
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Results |
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Metabolism of p,p'-DDT by Rat Liver Microsomes. p,p'-DDT was incubated with liver microsomes of untreated rats in the presence of NADPH for the detection of metabolites, as described under Experimental Procedures. Two peaks were detected in an HPLC chromatogram of the extract of the incubation mixture (Fig. 1A). These peaks were not detected in the control, which was incubated without the substrate. The metabolites detected at 16.5 and 35.3 min correspond to p,p'-DDD and p,p'-DDE, respectively. In the case of boiled microsomes, these metabolites were not detected. The metabolites corresponding to p,p'-DDT and p,p'-DDE were isolated as described under Experimental Procedures. They were identified unequivocally as p,p'-DDT and p,p'-DDE by mass spectrometry, TLC, and HPLC comparison with authentic samples. The further metabolized products p,p'-DDMU and p,p'-DDA were not detected by HPLC or TLC as metabolites of p,p'-DDT with liver microsomes (data not shown). When p,p'-DDT was incubated with liver cytosol in the presence of NADPH, p,p'-DDD and p,p'-DDE were not detected in the chromatogram of the extract (Fig. 1B). In contrast, dicofol, an oxidized product of p,p'-DDT, and phenolic metabolites were also not detected in the HPLC chromatogram, even when p,p'-DDT was incubated with liver microsomes in the presence of NADPH under aerobic conditions (data not shown).
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Dechlorinating Activity of Rat Liver Microsomes Toward p,p'-DDT. The time course of the dechlorination of p,p'-DDT to p,p'-DDD by liver microsomes from rats in the presence of NADPH was essentially linear for 45 min. The formation of p,p'-DDE from p,p'-DDT was also observed, but the amounts were about one-hundredth of those of p,p'-DDD (Fig. 2A). When the reductase activity was assayed with various amounts of microsomes under anaerobic conditions, the reductase activity increased linearly with increasing amount of liver microsomes up to 4.0 mg of protein. In contrast, very low activities were observed under aerobic conditions (Fig. 2B). In the other experiments of this study, incubations were carried out for 30 min using 0.2 ml of liver microsomes (about 3 mg of protein, equivalent to 200 mg of wet liver weight) under anaerobic conditions.
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Identification of CYP Isoforms Involved in the Dechlorination. Identification of CYP isoforms involved in the dechlorination of p,p'-DDT in liver microsomes was attempted by using recombinant rat and human CYPs. Recombinant rat CYP 2B1 and 3A1 catalyzed this dechlorination in the presence of NADPH at rates of 1.16 and 1.03 nmol/min/nmol CYP, respectively. Recombinant human CYP 3A4 and 2B6 exhibited substantial activities for dechlorination of p,p'-DDT in the presence of NADPH. Human CYPs 1A1, 1A2, 2A6, 2C9, 2D6, 2E1, and 4A11 also showed some dechlorinase activity (Fig. 5). Control microsomes of human B lymphoblastoid cells exhibited no appreciable dechlorinase activity. These facts suggest that the dechlorination of p,p'-DDT is catalyzed predominantly by phenobarbital- and dexamethasone-inducible CYPs, but other CYPs also contribute to the dechlorination.
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Heme-Based Dechlorination in Liver Microsomes. The NADH- and NADPH-dependent dechlorinating activities in liver microsomes of untreated rats were enhanced by the addition of FMN. Even when the microsomal fraction was boiled, the activities with both NAD(P)H and FMN were not abolished but were enhanced to some extent (Table 1). The activity was sensitive to inhibition by carbon monoxide. When FMN was replaced with flavin adenine dinucleotide or riboflavin, a similar result was obtained in the dechlorination of p,p'-DDT (data not shown). These facts suggest that CYP is also involved in the nonenzymatic dechlorination of p,p'-DDT in the liver microsomes of rats.
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Reductive Metabolism of o,p'-DDT by Liver Microsomes. o,p'-DDT, the isomer of p,p'-DDT, is known to contaminate technical-grade DDT and to have a higher estrogenic activity than p,p'-DDT. In this study, the dechlorinating activity toward o,p'-DDT by rat liver microsomes was compared with that toward p,p'-DDT. The liver microsomes exhibited reductase activity toward o,p'-DDT in the presence of NADPH, NADH, or both NADPH and NADH. The reductase activity in the presence of these cofactors toward o,p'-DDT was similar to that in the case of p,p'-DDT. Similar reducing activity of boiled liver microsomes was observed in the presence of NADPH and FMN (Fig. 6).
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Metabolism of p,p'-DDD by Liver Microsomes. Metabolism of p,p'-DDD by rat liver microsomes was also examined. When p,p'-DDD was incubated with liver microsomes in the presence of NADPH under anaerobic conditions, two peaks corresponding to authentic p,p'-DDE and p,p'-DDMU were detected in the HPLC chromatogram of the extract of the incubation mixture (Fig. 7). The metabolites isolated by HPLC were identified unequivocally as p,p'-DDE and p,p'-DDMU by comparison with authentic samples (data not shown). When p,p'-DDE was incubated similarly with liver microsomes in the presence of NADPH, p,p'-DDMU was not detected (data not shown).
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Discussion |
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It is known that halogenated hydrocarbons, including
p,p'-DDT, are metabolized to dehalogenated
metabolites by reductive dehalogenation. Previous studies showed that
the dehalogenation of carbon tetrachloride, hexachloroethane,
halothane, or (
-bromoisovaleryl)urea occurred in the liver
microsomal fraction of mammalian species and that cytochrome P450 was
involved in the microsomal dehalogenation (Fujii et al., 1981
; Kubic
and Anders, 1981
; Ahr et al., 1982
; Nastainczyk et al., 1982
; Oka et
al., 1996
). Recent experiments have demonstrated that rat liver
microsomes can directly transform halothane to dehalogenated
metabolites in a reductive reaction involving the formation of a
halothane-free radical intermediate (Baker and Van Dyke, 1984
). In
contrast, it has been shown that p,p'-DDT is
mainly metabolized to p,p'-DDD and
p,p'-DDE by reductive dechlorination and
dehydrochlorination, respectively. In the reduction of
p,p'-DDT to p,p'-DDD,
Kelner et al. (1986)
demonstrated that thiols stimulated the reductive
dechlorination in liver microsomes. It was also reported that the
pesticide covalently bound to microsomal protein and lipids owing to
the formation of a DDT free-radical intermediate that led to the
formation of p,p'-DDD (Baker and Van Dyke, 1984
).
However, the CYP isoform(s) catalyzing the reduction have not been identified.
Some studies on CYP isoforms involved in the reductive dehalogenation
of halogenated hydrocarbons have been conducted. Sprackline et al.
(1996)
demonstrated that the dehalogenation of halothane is mainly
catalyzed by CYP 2A6 and 3A4. Reductive dehalogenation of
hexachloroethane is catalyzed CYP 1A2 (Yanagita et al., 1998
). Oka et
al. (1996)
also demonstrated that debromination of
(
-bromoisovaleryl)urea is catalyzed by CYP 1A1 and 2B1. In the
present study, the dechlorination of p,p'-DDT was
demonstrated to be mainly mediated by CYP 2B1, 3A1, 2B6, and 3A4. It is
known that p,p'-DDT induces CYP 2B1 and 4A1 in
rat livers (Lewis and Lake, 1997
; Nims et al., 1998
). This suggests
that the dechlorinating activity toward p,p'-DDT
would be enhanced by the pretreatment of rats with
p,p'-DDT. Indeed, in a preliminary study in which
rats received intraperitoneal p,p'-DDT at a dose
of 100 mg/kg for 3 days before sacrifice, the liver microsomes
exhibited 5-fold higher activity than those of untreated rats. In
contrast, in the liver microsomal reduction of
p,p'-DDT, NADH was about half as effective as
NADPH. We previously observed that NADH was about half as effective as
NADPH in N-oxide reduction, nitro reduction, and zonisamide
reduction by liver microsomes of animals (Kitamura and Tatsumi, 1984
;
Sugihara et al., 1996
; Tatsumi et al., 1986
). NADH seems to be
generally effective in drug-reductive metabolism with liver microsomes.
In the NADH-dependent reaction, the electron may be transferred through
cytochrome b5.
Clark and Shamaan (1984)
reported that p,p'-DDT
was metabolized to p,p'-DDE by
glutathione-dependent dehydrochlorinase in the housefly. They
demonstrated that the enzyme was identical to glutathione
S-transferase. However, the identity of dehydrochlorinase and glutathione S-transferase has not yet been established.
Dehydrochlorination of lindane was also reported to be catalyzed by
glutathione-dependent dehydrochlorinase in the housefly (Tanaka et al.,
1981
). In our experiment, CYP 1A1, 2B1, 3A1, and 2E1 did not catalyze
the dehydrochlorination (data not shown). We could not confirm a role
of CYP in the dehydrochlorination of p,p'-DDT to
p,p'-DDE. In contrast,
p,p'-DDD was enzymatically metabolized to
p,p'-DDE by rat liver microsomes or cytosol, but only to a small extent. Thus, p,p'-DDE may be
formed via p,p'-DDD by an unknown enzyme system
in rat liver. p,p'-DDMU was also formed from
p,p'-DDD by liver microsomes. This
dehydrochlorination may be catalyzed by liver dehydrochlorinase,
similar to the case of p,p'-DDT. In contrast, it
was reported that p,p'-DDE was dechlorinated to
p,p'-DDMU by marine sediment microcosms (Quensen
et al., 1998
). However, this dechlorinating metabolism of
p,p'-DDE to p,p'-DDMU did
not occur in rat liver (Fig. 8). It is
reported that the major metabolite of p,p'-DDT
remaining in tissues of mammalians is p,p'-DDE (You, 2000
). It remains to be determined whether
p,p'-DDE is formed via
p,p'-DDD, as suggested above or by
dehydrochlorinase, as has been demonstrated in insects. We are
conducting a further study on this point.
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Recent experiments have demonstrated that rat blood can transform
p,p'-DDT to p,p'-DDD in a
reductive reaction involving the heme moiety of hemoglobin (Sugihara et
al., 1998
). The microsomal NAD(P)H-dependent reduction seems to proceed
enzymatically, catalyzed by the CYP system. However, when a flavin was
added to the mixture, the reducing activity was enhanced and was
nonenzymatic in character. The nonenzymatic dechlorination of
p,p'-DDT in liver microsomes presented in this
study seems to proceed in two steps. The first step is the reduction of
a flavin by NADPH-cytochrome P450 reductase with NADPH or
NADH-cytochrome b5 reductase with NADH,
whereas in boiled microsomes, the flavin seems to be reduced
nonenzymatically by NADPH or NADH, as reported by Singer and Kearney
(1950)
. The second step is the nonenzymatic reduction of
p,p'-DDT to p,p'-DDD by the
reduced flavin catalyzed by the heme group of hemoproteins, such as CYP
and cytochrome b5 (Fig. 7). In boiled
microsomes, the activity was increased, possibly because the substrate
and cofactor have easier access to the heme moiety of denatured
hemoproteins. We proposed a similar mechanism for the debromination of
(
-bromoisovaleryl)urea in the blood of rats (Kitamura et al.,
1999a
). We also demonstrated that the major route of dechlorination of
p,p'-DDT in fish was a nonenzymatic reaction by
blood catalyzed by heme (Kitamura et al., 1999b
). Other investigators
demonstrated that reduced iron porphyrins catalyze the reductive
dechlorination of p,p'-DDT (Castro, 1964
; Zoro et
al., 1974
). Here, we suggest that the dechlorination of
p,p'-DDT is also mediated by nonenzymatic
reduction in liver microsomes separately from the enzymatic reduction
by the CYP system.
Bitman et al. (1968)
reported that indicators of estrogenic action
increased after o,p'-DDT administration to rats
and birds, the responses resembling those to 17
-estradiol, whereas
p,p'-DDT exhibited only slight activity. Metcalfe
et al. (2000)
also reported that gonadal development and endocrine
responses were altered in fish exposed to
o,p'-DDT. Furthermore, the relative potencies for
intersex induction are o,p'-DDT > nonylphenol. However, the metabolism of o,p'-DDT
has not been investigated except for a study in pigeon liver
preparations (Hassall and Manning, 1972
). In this study, we
demonstrated that o,p'-DDT is dechlorinated by
rat liver microsomes via enzymatic and nonenzymatic reactions in a
similar ratio to p,p'-DDT. This fact suggests
that o,p'-DDT is metabolized and degraded in the
environment similar to p,p'-DDT.
It is reported that dicofol,
-hydroxyl-p,p'-DDT, has a relatively high
estrogenic activity among DDT analogs. Kapoor et al. (1972)
reported
that dicofol was detected as a minor urinary metabolite of
p,p'-DDT in mice. We also examined the oxidation
of p,p'-DDT to dicofol using rat liver microsomes
as a metabolic activation pathway. However, we could not detect any
oxidized metabolite of p,p'-DDT. The bridge site
of p,p'-DDT may be protected from attack because
of steric hindrance. The possibility remains that aromatic rings of
DDTs may be hydroxylated by liver microsomal enzymes. However,
Sundström et al. (1977)
reported that only small amounts of
3-hydroxy-p,p'-DDE were formed from
p,p'-DDT in pigs. In our experiments, it was
demonstrated that the metabolism of p,p'-DDT or
o,p'-DDT in rats is mainly reductive.
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Footnotes |
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Received July 9, 2001; accepted October 18, 2001.
This work was supported by Grant-in-Aid 13027256 for Scientific Research on Priority Area from the Japanese Ministry of Education, Science, Sports, and Culture and Grant-in-Aid C13672343 for Scientific Research from the Japan Society for the Promotion of Science.
Dr. Shigeyuki Kitamura, Institute of Pharmaceutical Sciences, Hiroshima University, School of Medicine, 1-2-3 Kasumi, Minami-ku, Hiroshima 734-8551, Japan. E-mail: kitamura{at}pharm.hiroshima-u.ac.jp
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Abbreviations |
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Abbreviations used are: CYP, cytochrome P450; p,p'-DDE, 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene; p,p'-DDD, 1,1-dichloro-2,2-bis(4-chlorophenyl)ethane; p,p'-DDA, 2,2-bis(4-chlorophenyl)acetic acid; p,p'-DDMU, 1-chloro-2,2-bis(4-chlorophenyl)ethylene; HPLC, high-performance liquid chromatography; TLC, thin-layer chromatography; SKF 525-A, proadifen hydrochloride.
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References |
|---|
|
|
|---|
-bromoisovaleryl)urea catalyzed by rat blood.
J Pharm Pharmacol
51:
73-78[CrossRef][Medline].
-(bromoisovaleryl)urea.
J Pharm Pharmacol
48:
930-932[Medline].This article has been cited by other articles:
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