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Vol. 26, Issue 8, 822-824, August 1998
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Abstract |
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The effects of pyrazole, which is known to induce hepatic cytochrome P4502A5 (CYP2A5) through posttranscriptional mechanisms, on the level of CYP2A5 in liver and extrahepatic tissues were examined in this study. Intraperitoneal administration of pyrazole at 200 mg/kg for 3 days induced CYP2A4/5 mRNAs and proteins and microsomal coumarin 7-hydroxylation activity in liver and kidney of C57BL/6 mice. A marginal increase (30%) in CYP2A4/5 mRNAs was also observed in the olfactory mucosa but not in the lung, and no increase in CYP2A4/5 proteins or microsomal coumarin 7-hydroxylation activity was observed in either the olfactory mucosa or lung. CYP2A4/5 proteins were not detected on immunoblots in other tissues examined, including breast, bone marrow, testis, prostate, ovary, and uterus from control or pyrazole-treated mice. On the other hand, pyrazole treatment induced CYP2E1 in the olfactory mucosa as well as in liver and kidney, indicating that the olfactory mucosa was exposed to pyrazole. The lack of CYP2A inducibility in the olfactory mucosa was also observed for several other known inducers of hepatic CYP2A5, including cobaltous chloride, stannous chloride, griseofulvin, thioacetamide, and aminotriazole. These results suggest that the mechanisms involved in the induction of hepatic and renal CYP2A5 by pyrazole and other xenobiotic compounds may be tissue-specific.
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Introduction |
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CYP2A512
is a major P450 isoform in mouse olfactory mucosa (OM)
and is also expressed in liver, kidney, and lung (Su et al., 1996
). Previous studies have shown that hepatic CYP2A5 is inducible by
a number of xenobiotic compounds, including phenobarbital (Honkakoski and Lang, 1989
), pyrazole (Kojo et al., 1991
), heavy metals,
such as stannous chloride (Emde et al., 1996
) and cobaltous
chloride (Kocer et al., 1991
), and porphyrinogenic agents,
such as griseofulvin, thioacetamide, and aminotriazole (Salonpaa
et al., 1995
). The inducibility of CYP2A5 in extrahepatic
tissues has not been studied extensively. CYP2A5 is inducible in the
kidney by cerium chloride in DBA/2 but not C57BL/6 mice (Salonpaa
et al., 1992
) and by pyrazole and others in NMRI mice (Emde
et al., 1996
); however, it is not known whether CYP2A5 is
also inducible in lung and OM and whether it is expressed in any other
tissues. Induction of CYP2A5 in extrahepatic tissues may increase the
rates of target tissue metabolic activation of toxic chemicals and
potentially lead to increased sensitivity to xenobiotic toxicity.
In the present study, we examined the inducibility of CYP2A5 by
pyrazole in liver and extrahepatic tissues of C57BL/6 mice. The cDNA
probes and antibodies used for detecting CYP2A5 could not distinguish
CYP2A4 from CYP2A5. Thus the combined levels of CYP2A4 and CYP2A5 (or
CYP2A4/5) were determined on immunoblots and RNA blots. Microsomal
activity toward coumarin, a preferred substrate for CYP2A5 but not a
substrate for CYP2A4 (Negishi et al., 1989
), was also
determined to monitor specific induction of CYP2A5. In addition, the
effects of several other known inducers of hepatic CYP2A5, including
cobaltous chloride, stannous chloride, griseofulvin, thioacetamide, and
aminotriazole, were also compared in liver and OM. Our results indicate
that the mechanisms involved in the induction of hepatic and renal
CYP2A5 by pyrazole and other xenobiotic compounds may be
tissue-specific.
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Materials and Methods |
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Animal Treatments.
Two-month-old male C57BL/6 mice (about 20 g in body weight) were
used in this study. Animals were treated essentially according to
published protocols for induction of hepatic CYP2A5 with pyrazole (Kojo
et al., 1991
), stannous chloride (Emde et al.,
1996
), cobaltous chloride (Kocer et al., 1991
),
griseofulvin, thioacetamide, and aminotriazole (Salonpaa et
al., 1995
). Pyrazole was dissolved in PBS and was injected once
daily (200 mg/kg body weight; ip) for 3 consecutive days. Tissues were
collected on the fourth day. Stannous chloride was injected once daily
(50 mg/kg; ip) for 2 days in 1.75% sodium citrate (pH 7.4), and
tissues were collected 24 hr after the last injection. Cobaltous
chloride was injected once daily (30 mg/kg; sc) for 2 days in saline,
and tissues were collected 24 hr after the last injection. Griseofulvin
(1000 mg/kg; suspended in corn oil) and thioacetamide (10 mg/kg;
dissolved in saline) were injected only once (ip), and tissues were
collected 48 hr after injection. Aminotriazole was also injected once
(1000 mg/kg; ip; in saline), and tissues were collected 24 hr after injection. The control groups for each treatment received the corresponding vehicle only. All tissues were quick-frozen on dry ice
and stored at
85oC until use. Tissues from each
treatment or control group of six mice were combined and used for the
preparation of microsomes or RNAs.
RNA Blot and Immunoblot Analysis.
Total RNA was prepared from frozen tissues with use of TRIZOL Reagent
(Gibco BRL, Grand Island, NY). RNA concentration was determined
spectrally. RNA blot analyses were performed as recently described (Su
et al., 1996
). CYP2A5 mRNA was detected with a 693-bp P-labeled PstI fragment of CYP2A5
cDNA (kindly provided by Dr. Masahiko Negishi, National Institute of
Environmental Health Sciences, National Institutes of Health, Research
Triangle Park, NC). The levels of
-actin mRNA were determined
with a 32P-labeled
-actin cDNA probe
(Clontech, Palo Alto, CA) on the same RNA blots after removal of CYP2A5
cDNA probes. For quantifying the amounts of CYP2A5 mRNA in total RNA
preparations from vehicle- and inducer-treated animals, the density of
the hybridizing bands was determined with a LKB ImageMaster DTS
densitometer (Pharmacia, Piscataway, NJ). The band intensities were
within the linear range of the densitometric response, and the amounts
of total RNA applied were corrected according to the amounts of
-actin detected in RNA samples from pairs of vehicle- and
inducer-treated animals. Immunoblot analyses were performed with an ECL
detection system from Amersham (Arlington Heights, IL). The sources of
the polyclonal antibody to rabbit CYP2A10/11 (Ding and Coon, 1990
) and
the monoclonal antibody (Mab 1-98-1) to rat CYP2E1 (Ding et
al., 1991
) have been described previously. Density of CYP2A5 or
CYP2E1 immunoreactive bands were determined as described above. In all
cases, the relative amounts of P450 proteins in samples from vehicle-
and inducer-treated animals were determined and are shown in arbitrary
units.
Other Methods and Materials.
Microsomes were prepared from combined tissues of six mice in each
group as previously described (Ding and Coon, 1990
). Protein was
determined using BCA reagent (Pierce, Rockford, IL), with bovine serum
albumin as a standard. Microsomal coumarin 7-hydroxylation activity was
measured by the method of Greenlee and Poland (Greenlee and Poland,
1978
). The contents of reaction mixtures and incubation conditions are
described in the legend to table 1.
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Results and Discussion |
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Tissue-Selective Induction of CYP2A5 by Pyrazole. Animals were treated with pyrazole using conditions that are known to induce CYP2A5 in the liver and the levels of CYP2A4/5 mRNAs, microsomal CYP2A4/5 proteins, and microsomal coumarin 7-hydroxylation activities were determined, as shown in table 1. Representative immunoblots and RNA-blots are shown in fig. 1. The levels of the CYP2A mRNAs and proteins were elevated about 5- to 9-fold in livers and kidneys of pyrazole-treated mice, compared with those from vehicle-treated animals. These changes were accompanied by 10- to 16-fold increases in microsomal coumarin 7-hydroxylation activity. A marginal increase (30%) in CYP2A4/5 mRNAs was also observed in the OM but not in lung, and no increase in CYP2A4/5 proteins or microsomal coumarin 7-hydroxylation activity was observed in either OM or lung. In experiments not presented here, CYP2A4/5 proteins were not detected on immunoblots in other tissues examined, including breast, bone marrow, testis, prostate, ovary, and uterus, from control or pyrazole-treated mice.
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Induction of CYP2E1 by Pyrazole. Immunoblot analyses were also conducted to determine the inducibility of CYP2E1 in liver, kidney, and OM by pyrazole treatment. As shown in table 1, the levels of CYP2E1 protein were elevated in the livers (2-fold), kidneys (9-fold), as well as the OM (3-fold) of pyrazole-treated mice, compared with those of vehicle-treated mice. Thus the concentration of pyrazole in the OM was sufficient to induce CYP2E1, indicating that the lack of induction of CYP2A5 in OM was not because pyrazole did not reach this tissue. However, we were unable to determine whether CYP2E1 protein was induced in the lung by pyrazole-treatment, because the antibody detected multiple bands in the P450 region in lung microsomes from both vehicle- and pyrazole-treated mice, which interfered with immunoblot quantitation (data not shown).
Differential Induction of CYP2A5 in Liver and OM by Other Xenobiotic Compounds. Since pyrazole did not induce CYP2A5 in the OM, we examined other known hepatic CYP2A5 inducers, including stannous chloride, cobaltous chloride, griseofulvin, thioacetamide, and aminotriazole, to see if they could induce the enzyme in the OM. As shown in table 2, all of the compounds induced CYP2A4/5 proteins in the liver, with the extent of induction varying between 2- and 14-fold. However, induction of CYP2A4/5 proteins was not observed in the OM with any of the compounds. In contrast, except for the experiments with stannous chloride, there was a general trend of decreased olfactory CYP2A4/5 protein levels after treatment with the hepatic inducers, with a statistically significant decrease in the experiments with griseofulvin (p < 0.05).
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Ting Su
Wenlei He
Jun Gu
Thomas W. Lipinskas
Xinxin Ding
Wadsworth Center,
New York State Department of Health
(T.S., W.H., J.G., T.L., X.D.),
and
Department of Environmental
Health
and Toxicology (T.S., X.D.),
School of Public
Health,
State University of New York at Albany
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Acknowledgements |
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We are grateful to Dr. Masahiko Negishi of the National Institute of Environmental Health Sciences, National Institutes of Health, for providing the CYP2A5 cDNA clone, and to Yali Zhou for technical assistance. The authors gratefully acknowledge the use of the Wadsworth Center's Biochemistry Core facility. We would also like to thank Dr. Laurence Kaminsky of the Wadsworth Center for reading the manuscript.
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Footnotes |
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Received February 27, 1998; accepted April 7, 1998.
This research was supported in part by Grant ES-07462 from the National Institute of Environmental Health Sciences, National Institutes of Health.
2
The nomenclature used in this report is that
of Nelson et al. (1996)
.
Send reprint requests to: Dr. Xinxin Ding, Wadsworth Center, New York State Department of Health, Empire State Plaza, Box 509, Albany, NY 12201-0509.
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Abbreviations |
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Abbreviations used are: P450 or CYP, cytochrome P450; OM, olfactory mucosa; PBS, phosphate-buffered saline, (2.7 mM KCl, 1.5 mM KH2PO4, 134 mM NaCl, and 8.2 mM Na2HPO4·7H2O) .
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References |
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