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Vol. 30, Issue 3, 262-269, March 2002
Laboratory of Human Toxicology and Molecular Epidemiology, Wadsworth Center, New York State Department of Health, Albany, New York
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Abstract |
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Polycyclic aromatic hydrocarbons (PAHs) and metals are often environmental cocontaminants, yet there have been relatively few studies of combined effects of PAHs and metals on cytochrome P450 (P450)-catalyzed metabolism. We examined the effects of NaAsO2 in combination with benzo[a]pyrene (BAP) on CYP1A1 and CYP1B1 in T-47D human breast cancer cells by using estrogen metabolism as a probe of their activities. Exposure to BAP caused elevated rates of the 2- and 4-hydroxylation pathways of estrogen metabolism, indicating induction of both CYP1A1, an estradiol 2-hydroxylase, and CYP1B1, an estradiol 4-hydroxylase. BAP-induced metabolism peaked 9 to 16 h after exposure and returned to near-basal levels by 48 h. Concentration-response studies showed maximal induction of the 2- and 4-hydroxylation pathways at 3 µM BAP; higher levels caused reduced rates of metabolism due to inhibition of CYP1A1 and CYP1B1. NaAsO2 caused pronounced decreases in the induction of CYP1A1 and CYP1B1 by 3 µM BAP because cotreatment with 10 µM NaAsO2 inhibited the rates of the 2- and 4-hydroxylation pathways by 86 and 92%, respectively. Western immunoblots showed diminished levels of BAP-induced CYP1A1 by coexposure to NaAsO2. The levels of the CYP1A1 and CYP1B1 mRNAs induced by BAP were not significantly affected by coexposure to NaAsO2; however, heme oxygenase 1 mRNA levels were markedly induced by coexposure to BAP and NaAsO2. These results indicate a post-transcriptional inhibitory effect of arsenite on the expression of CYP1A1 and CYP1B1 in T-47D cells, possibly resulting from reduced heme availability.
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Introduction |
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Among
the environmental contaminants of most concern due to their toxicity,
including carcinogenicity, are heavy metals, such as arsenic, lead, and
mercury, and polycyclic aromatic hydrocarbons (PAHs1) typified by benzo[a]pyrene
(BAP). PAHs and heavy metals are often cocontaminants in the
environment, yet there have been relatively few studies of the combined
toxic and particularly the carcinogenic effects elicited by PAHs and
heavy metals. The carcinogenicity of BAP and other PAHs is a
consequence of their metabolic activation catalyzed by cytochromes P450
(P450) and epoxide hydrolase (Wood et al., 1976
; Kapitulnik et al.,
1978
). Covalent adducts formed by the reaction of PAH diol epoxide
metabolites with guanine in mutational hotspots of critical genes such
as that of the p53 tumor suppressor (Denissenko et al., 1996
), if not
efficiently repaired, may initiate tumorigenesis.
Several members of the P450 superfamily in conjunction with epoxide
hydrolase have been shown to catalyze the metabolism of BAP to
carcinogenic intermediates. In extrahepatic tissues, CYP1A1 and CYP1B1
are thought to be the most important enzymes in catalyzing the
formation of mutagenic intermediates from BAP and a number of other
PAHs, including several that are potent mammary gland carcinogens in
rodents. CYP1B1 appears to be more active than CYP1A1 in the conversion
of a number of PAHs to genotoxic intermediates (Shimada et al., 1996
).
In the presence of epoxide hydrolase, both CYP1A1 and CYP1B1 catalyze
the conversion of BAP to its 7,8-dihydrodiol, and both enzymes can in
turn metabolically activate this BAP metabolite to a mutagenic form
(Shimada et al., 1996
, 1999
; Kim et al., 1998
). 7,12-Dimethylbenz[a]anthracene-induced carcinogenesis, an
extensively studied model of PAH-induced carcinogenesis, recently was
found to be dependent on CYP1B1: the CYP1B1 knockout mouse is
refractory to
7,12-dimethylbenz[a]anthracene-induced
carcinogenesis (Buters et al., 1999
).
PAHs are not only substrates of human CYP1A1 and CYP1B1 but also are
inducers of these enzymes through binding to and activation of the
aromatic hydrocarbon receptor (AhR). The regulation of expression of
both CYP1A1 and CYP1B1 is complex because gene transcription not only
involves the AhR but also a number of transcription factors, and is
potentially influenced by the actions of transcriptional coactivators
and corepressors. For reasons that are not currently known, in some
human Ah-responsive cells, CYP1A1 is inducible but not CYP1B1, in other
cells CYP1B1 is inducible but not CYP1A1, and in yet others both
enzymes are inducible (Christou et al., 1994
; Spink et al., 1994
,
1998b
; Döhr et al., 1995
; Kress and Greenlee, 1997
). There are
several potential points, including transcription, translation, and
incorporation of the heme prosthetic group, at which other chemicals,
including environmental cocontaminants, could potentially modulate
expression and catalytic activity of CYP1A1, CYP1B1, and other P450s.
In several recent studies, an effect of arsenite on expression of
cytochromes P450 in hepatocyte cultures was reported (Jacobs et al.,
1999
; Vakharia et al., 2001
), although the mechanism responsible
for this effect has not been determined.
Human CYP1A1 and CYP1B1 are also 17
-estradiol
(E2) hydroxylases. CYP1A1 is primarily an
E2 2-hydroxylase (Spink et al., 1992
), whereas
CYP1B1 is primarily an E2 4-hydroxylase with a
lesser activity at C-2 (Spink et al., 1994
; Hayes et al., 1996
). The resultant catechol estrogens, 2- and 4-hydroxyestradiol (2- and 4-OHE2), are converted to 2- and
4-methoxyestradiol (2- and 4-MeOE2) by the action
of constitutively expressed catechol O-methyltransferase. This metabolism of E2 can be used as a probe of
the AhR-regulated expression of CYP1A1 and CYP1B1 in human breast
epithelial and breast tumor cells (Spink et al., 1998b
). In this study,
we used the T-47D line of estrogen receptor-
-positive breast tumor
cells, which rapidly metabolize BAP (Merrick et al., 1985
) and express both CYP1A1 (Vickers et al., 1989
) and CYP1B1 (Spink et al., 1998b
) in
response to exposure to Ah-receptor activation, to investigate the
effects of BAP alone or in combination with
NaAsO2 on the expression of CYP1A1 and CYP1B1.
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Materials and Methods |
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Cell Culture and Treatments.
T-47D cells were obtained from the American Type Culture Collection
(Rockville, MD) and were maintained in a 37°C incubator with a
humidified atmosphere containing 5% CO2. For
experimental protocols, the medium was DC5
(Gierthy et al., 1996
) consisting of Dulbecco's modified Eagle's
medium, without phenol red, and with 5% bovine calf serum (Cosmic calf
serum; Hyclone Laboratories, Logan, UT), 10 mM nonessential amino
acids, 2 mM L-glutamine, and 10 µg/l insulin. BAP was
added to the cultures alone or in combination with varying
concentrations of NaAsO2. The vehicle for BAP was
dimethyl sulfoxide (DMSO), which was used at a highest concentration of
0.1% (v/v).
RNA Isolation and RT-PCR.
Total RNA was isolated by phenol-guanidinium thiocyanate extraction
(Chomczynski and Sacchi, 1987
), and portions (2.5-5 µg) were primed
with oligo-dT, reverse-transcribed using Superscript II reverse
transcriptase (Invitrogen, Carlsbad, CA) and treated with RNase
H (Invitrogen) according to the manufacturer's protocol. Primers for
the amplification of glyceraldehyde-3-phosphate dehydrogenase (GAPDH)
and CYP1A1 cDNAs were as previously reported (Fasco et al., 1995
). The
primers for the amplification of CYP1B1 cDNA were those used previously
(Spink et al., 1998a
). Competitor DNAs were synthesized by the method
of Förster (1994)
. Each amplified sequence spanned an exon-exon
junction. PCR of the CYP1A1, CYP1B1, and GAPDH cDNAs was carried out as
described (Spink et al., 1998a
) with core reagents from PerkinElmer
(Foster City, CA), but with the addition of TaqStart antibody
(CLONTECH, Palo Alto, CA) and Taq extender (Stratagene, La
Jolla, CA), and were amplified with the same PCR-plus-competitor mix
used for the calibration curve at dilutions that fell within the linear
range of the competitor curve. PCR products were resolved on a 2% 3:1
NuSieve (FMC Bioproducts, Rockland, ME) agarose gel, followed by
staining with 0.75 µg/ml ethidium bromide for photography and
quantitation by densitometric scanning of the photographic negative.
For the determination of heme oxygenase 1 (HO-1) mRNA levels, a
real-time PCR technique was used (for review, see Bustin, 2000
). A
271-base pair fragment of the HO-1 cDNA was amplified by using the
LightCycler System (Roche Molecular Biochemicals, Indianapolis, IN)
with the primers of Premkumar et al. (1995)
. Quantitation was achieved
by monitoring the fluorescence of intercalated SYBR Green I at each
cycle. All mRNA levels were analyzed in triplicate, each representing
three separate reverse transcriptions of RNA isolated from individual wells of control or treated T-47D cells.
Assay of Cellular Estrogen Metabolism.
For the analysis of E2 metabolism, confluent
cultures of T-47D cells in six-well plates were exposed to the
indicated concentrations of BAP, NaAsO2,
2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), or the solvent
vehicle 0.1% v/v DMSO in 2 ml of medium per well. After the specified
time period for enzyme induction, media were replaced with media
containing 1 or 5 µM E2. At the indicated times, these media were recovered and treated with
b-glucuronidase/sulfatase for hydrolysis of the metabolite conjugates
as previously described (Spink et al., 1994
). These enzyme-treated
samples were subjected to solid-phase extraction and preparation of the
metabolite-trimethylsilyl derivatives. The metabolite derivatives were
analyzed by gas chromatography/mass spectrometry with stable-isotope
dilution and selected-ion monitoring as described (Spink et al., 1994
,
1998b
). Rates of metabolite formation were normalized to cellular
protein content as determined by the bicinchoninic acid assay method
(Smith et al., 1985
) by using a commercial reagent (Pierce Chemical,
Rockford, IL).
Determination of Microsomal E2 Hydroxylase Activity.
To evaluate the inhibitory effects of BAP and
NaAsO2 on human CYP1A1 and CYP1B1, the
E2 hydroxylase activities of the two enzymes were
determined essentially as described (Spink et al., 1992
). Human
recombinant CYP1A1 and CYP1B1, both coexpressed with human
NADPH/cytochrome P450 oxidoreductase in Sf9 cells
(Supersomes), were obtained from GENTEST (Woburn, MA). Microsomal
incubations (250 µl) contained 5 mM MgCl2, 10 µM of E2 as substrate, 10 pmol of
cDNA-expressed CYP1A1 or CYP1B1, and 2 mM ascorbic acid, and were
buffered at pH 7.4 with 100 mM sodium phosphate. The reaction mixtures
were preincubated at 37°C for 5 min in the presence of added BAP or
NaAsO2, and enzymatic reactions were initiated
with NADPH at a final concentration of 1.4 mM. After 10 min, the
reactions were terminated by the addition of two volumes of ice-cold 30 mM ascorbic acid, addition of internal standards, and immediate extraction with ethyl acetate. The extracts were dried over anhydrous sodium sulfate, evaporated to dryness under N2,
and trimethylsilyl derivatives were prepared. The derivatized samples
were analyzed by gas chromatography/mass spectrometry with selected-ion monitoring.
Western Immunoblot Analysis of NADPH-P450 Reductase (CPR) and CYP1A1. Cultures in six-well plates were exposed to BAP and NaAsO2 as indicated, after which the cell monolayers were washed with phosphate-buffered saline and solubilized by addition of gel sample buffer (250 µl/well), which did not contain reducing agent or dye. Equal amounts of protein from each well (2 µg for CPR, 4 µg for CYP1A1) were run on 10% Bis-Tris polyacrylamide gels (NuPAGE; Invitrogen) together with a series of standards consisting of either purified, recombinant human CPR (Panvera, Madison, WI) or human CYP1A1 (Supersomes from GENTEST). The proteins were transferred to Immobilon membranes (Millipore, Bedford, MA) that were then blocked with 5% nonfat dry milk in Tris-buffered saline containing 0.05% Tween 20 (Bio-Rad, Hercules, CA). The primary antibodies were goat anti-rat CPR (GENTEST) and goat anti-rat CYP1A1 (Daiichi, Tokyo, Japan), which were used at dilutions of 1:1000 and 1:2000, respectively, in Tris-buffered saline containing 0.05% Tween 20 and 0.5% nonfat dry milk. The secondary antibody was horseradish peroxidase conjugated-donkey anti-goat IgG (Cruz Marker compatible; Santa Cruz Biotechnology, Santa Cruz, CA) used at 1:7500 dilution for analysis of CPR or 1:20,000 for CYP1A1. Immunoreactive proteins were detected by using the SuperSignal West Pico Chemiluminescent Substrate (Pierce Chemical), and exposed films were subjected to scanning densitometry on a Pharmacia LKB ImageMASTER densitometer (Amersham Biosciences, Inc., Piscataway, NJ). The resulting band intensities for the detected proteins fell within linear standard curves prepared over the 1.3- to 20-fmol range for CPR and over the 0.1- to 2.0-fmol range for CYP1A1, and were thus converted to molar amounts of CPR and CYP1A1.
Determination of BAP Uptake.
The extent of uptake of BAP into T-47D cells was evaluated by
determining the level of BAP remaining in the medium and the amount
that could be recovered from the cells at various times after exposure.
BAP was extracted from the media samples by use of Sep-Pak
C18 cartridges (Waters, Milford, MA), and BAP was
recovered from the trypsinized cells by sonication of the cell pellets
in the presence of acetonitrile. The BAP levels in these extracts were
determined by reversed phase, high-performance liquid chromatography (Vakharia et al., 2001
).
Determination of Cell Viability.
The effects on cell viability of exposure to 3 µM BAP alone or in
combination with varying concentrations of NaAsO2
for 12 h were assessed in 96-well plates, as described by
Borenfreund et al. (1988)
, by using
3-[4,5-dimethylthiazol-2-yl]-2,5-diphenyltetrazolium bromide (MTT).
Statistical Analyses.
Statistical differences among treatment groups were evaluated by
analysis of variance and use of the Student-Newman-Keuls test for
multiple comparisons. These evaluations were performed using the
SigmaStat software package, version 2.0 (Jandel Scientific, San Rafael,
CA). For determination of EC50 values for mRNA
induction, concentration-response data were fit to the four-parameter
sigmoidal function,
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Results |
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The time course of BAP uptake, CYP1A1 and CYP1B1 mRNA levels, and the rates of the 2- and 4-hydroxylation pathways of E2 metabolism in T-47D cells were determined after a single exposure to medium containing 3 µM BAP. There was a rapid disappearance of BAP from the medium of T-47D cultures because only 30% of the initial BAP could be recovered from the medium at 3 h (Fig. 1A). BAP was rapidly taken up in these cells and was apparently rapidly metabolized because at 3 h 20% of the initial BAP was present in the cells, but the level declined rapidly thereafter (Fig. 1B). With extended incubation the cultures became depleted of BAP because by 12 h only 5% of the original BAP could be recovered from the medium, and BAP could no longer be detected in extracts of the cells.
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The time courses of the effects of BAP exposure on the levels of CYP1A1 and CYP1B1 mRNAs in T-47D cells were determined by using competitive RT-PCR. After exposure to 3 µM BAP, the levels of both the CYP1A1 (Fig. 1C) and CYP1B1 (Fig. 1D) mRNAs increased for the first 9 h, but declined steadily thereafter, returning to near-basal levels by 48 h. The rates of 2-MeOE2 (Fig. 1E) and 4-MeOE2 (Fig. 1F) synthetic activities, reflecting the activities of CYP1A1 and CYP1B1, respectively, also showed transient elevations after exposure to 3 µM BAP. Although the data for 2- and 4-MeOE2 formation are very precise, they should be seen as representing mean velocities, averaged over 6-h periods. Uncertainty of the exact nature of the time course of the induction of the activities of CYP1A1 and CYP1B1 arises from probable changes in metabolic velocities during these 6-h assay periods. Therefore, theoretical limits for the rates of change of the metabolic velocities at the beginning and the end of each assay period were used to approximate ranges of possible curves that describe the time course of induction and decline of E2 metabolism. These ranges are depicted by the shaded areas within the curves (Fig. 1, E and F). From these curves it is estimated that the rates of 2- and 4-MeOE2 formation reached maxima by 9 to 16 h, and by 48 h, the rates of 2- and 4-MeOE2 synthetic activities had returned to near-basal levels.
The concentration-response effects of a 12-h exposure to BAP on the 2- and 4-hydroxylation pathways of E2 metabolism in T-47D cells were evaluated (Fig. 2). The induction curve is bell shaped, with the highest metabolic rates observed from exposure to 3 µM BAP, and lower metabolic rates were observed with BAP concentrations lower and higher than 3 µM. Because this type of concentration-response curve often reflects enzyme inhibition by the higher levels of the inducing agent, the effects of BAP on E2 metabolism induced by TCDD were investigated. Addition of BAP to TCDD-treated T-47D cultures during the E2 metabolism assay period markedly inhibited metabolite formation when the BAP was present at 3 and 10 µM (Fig. 3). At 10 µM BAP, the rates of TCDD-induced 2- and 4-MeOE2 formation were both inhibited by more than 90%. In contrast to the concentration-response curves for formation of 2- and 4-MeOE2, concentration-response curves for CYP1A1 and CYP1B1 mRNA levels are sigmoidal, with no apparent inhibitory effects at the higher BAP levels (Fig. 4). From these data, EC50 values of 1.75 ± 0.07 and 1.88 ± 0.16 µM BAP were determined for the induction of the CYP1A1 and CYP1B1 mRNAs, respectively.
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To examine the effects of NaAsO2 on the induction of E2 metabolism in T-47D cells, the compound was added to cultures at various concentrations in combination with 3 µM BAP. NaAsO2 at 1, 3, or 10 µM added in the presence of 3 µM BAP did not affect cell viability as determined by the MTT assay (Fig. 5A). These levels of NaAsO2 in combination with BAP did not significantly affect the levels of induced CYP1A1 (Fig. 5B) or CYP1B1 (Fig. 5C) mRNAs. Exposure of T-47D cells to NaAsO2 in combination with 3 µM BAP had marked effects on the formation of 2- and 4-MeOE2, reflecting decreases in the activities of CYP1A1 and CYP1B1, respectively. Exposure to 10 µM NaAsO2 in combination with 3 µM BAP had very similar effects on the CYP1A1- and CYP1B1-catalyzed activities because the rates of 2-MeOE2 (Fig. 5D) and 4-MeOE2 (Fig. 5E) production were both significantly reduced at 1 µM NaAsO2 and here reduced by 87 and 91%, respectively, at 10 µM NaAsO2 compared with that elicited by 3 µM BAP alone.
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Direct effects of BAP and NaAsO2 on CYP1A1 and CYP1B1 activities were investigated in microsomal reactions with cDNA-expressed enzymes. Consistent with the effects of added BAP on the activities of CYP1A1 and CYP1B1 induced by TCDD in T-47D cells (Fig. 3), BAP potently inhibited both CYP1A1 and CYP1B1. Addition of 10 µM BAP to microsomal incubations caused 96% inhibition of CYP1A1-catalyzed E2 2-hydroxylase activity (Fig. 6A) and 99% inhibition of CYP1B1-catalyzed E2 4-hydroxylase activity (Fig. 6B). NaAsO2 also inhibited the activities of cDNA-expressed CYP1A1 and CYP1B1. Addition of 10 µM NaAsO2 caused 21 and 43% inhibition of the CYP1A1 and CYP1B1 E2 hydroxylase activities, respectively.
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Because NaAsO2 appears to both inhibit CYP1A1 and
CYP1B1 activities and to diminish the induction of the two enzymes, an
experiment was designed to evaluate the relative importance of these
two effects of NaAsO2 in T-47D cells. TCDD was
used as the inducer of CYP1A1 and CYP1B1 to avoid the confounding
effects of enzyme inhibition by BAP. As previously reported (Spink et
al., 1998b
), TCDD caused a marked elevation in the rates of formation
of 2-MeOE2, 4-MeOE2,
6
-OHE2, and 15
-OHE2
as a consequence of the induction of CYP1A1 and CYP1B1 (Fig.
7). Addition of 10 µM
NaAsO2 together with 10 nM TCDD during the 12-h
period for enzyme induction resulted in significant reductions in the
rates of E2 metabolism determined during the
assay phase. Not only were rates of 2-MeOE2 and
4-MeOE2 reduced, but also rates of formation of
6
-OHE2, and 15
-OHE2, two additional products of CYP1A1-catalyzed E2
metabolism (Spink et al., 1992
), were reduced relative to rates of
cultures that received TCDD only. However, if 10 µM
NaAsO2 was added in the E2
metabolism phase of the experiment rather than the induction phase, no
significant changes in the rates of E2 metabolism
were observed, suggesting that the effects of arsenite on
E2 metabolism in T-47D cultures were primarily on
the levels of TCDD-induced CYP1A1 and CYP1B1 and not as a result of
inhibiting their activities.
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Reductions in the levels of the CYP1A1 and CYP1B1 proteins after cotreatment with arsenite would explain the reduction in the BAP- and TCDD-induced E2 metabolism in T-47D cells. Additionally, reduction in the levels of NADPH-cytochrome P450 reductase could also result in diminished rates of BAP-induced E2 metabolism. To investigate the effects of cotreatments with BAP and arsenite on the levels of CPR and CYP1A1, Western immunoblot analyses of the two proteins in cell lysates were performed. Exposure to 3 µM BAP did not significantly affect the level of CPR in T-47D cells, nor did combined treatments of 1, 3, or 10 µM NaAsO2 together with 3 µM BAP (Fig. 8A), but these treatments had marked effects on the levels of CYP1A1 protein (Fig. 8B). In untreated T-47D cells, CYP1A1 protein was not detectable. After exposure to 3 µM BAP, CYP1A1 was highly induced, and the combined treatments of 3 or 10 µM NaAsO2 together with 3 µM BAP resulted in significantly reduced levels of immunoreactive CYP1A1 compared with exposure to 3 µM BAP alone. Western immunoblot analyses of CYP1B1 expression in T-47D cells were performed in a similar manner to those for CYP1A1 and CPR. Although these analyses were suggestive of a similar effect of arsenite in reducing the BAP-induced level of CYP1B1, the low levels of CYP1B1 expressed in T-47D cells did not allow quantitative measurements of CYP1B1 expression with the available antibody (data not shown). Thus, arsenite was shown to diminish the activities of both CYP1A1 and CYP1B1 in cellular E2 metabolism studies (Figs. 5, D and E, and 7); however, the effect of arsenite on reducing immunoreactive P450 protein was only clearly demonstrated for CYP1A1 (Fig. 8B).
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Because the induction of HO-1 has been observed in response to arsenite
exposure in vivo (Falkner et al., 1993
) and in vitro (Jacobs et al.,
1999
), concomitant with the reduction of P450 activities, we
investigated whether HO-1 mRNA was induced under the conditions of the
experiment in Fig. 5, in which rates of CYP1A1- and CYP1B1-catalyzed
E2 metabolism were diminished by added
NaAsO2. Real-time PCR was used to quantitate the
levels of HO-1 mRNA in T-47D cultures exposed to 3 µM BAP or to 1, 3, or 10 µM NaAsO2 together with 3 µM BAP.
Exposure to 3 µM BAP alone caused a 3.3-fold elevation in HO-1 mRNA
(Fig. 9). Coexposure to 1, 3, or 10 µM
NaAsO2 together with 3 µM BAP caused
8.1-, 66-, and 155-fold elevations in the level of HO-1 mRNA in T-47D
cells.
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Discussion |
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The ability of T-47D cells to rapidly metabolize BAP was initially
reported by Merrick et al. (1985)
, who found that 95% of the BAP
initially present at 4 µM was metabolized within 24 h. Dihydrodiols, tetraols, quinones, and sulfated compounds were detected
as BAP metabolites, as were DNA adducts (Pruess-Schwartz et al., 1986
).
Our results showed a similar rapid uptake and metabolism of BAP in
T-47D cells concomitant with induction of CYP1A1 and CYP1B1, which is
most likely responsible for the BAP metabolism. Comparison of the time
courses of the BAP levels and the levels of CYP1A1- and
CYP1B1-catalyzed activities indicates that the activities of the two
enzymes are dependent on the presence of unmetabolized BAP. Likewise,
the P450 mRNA levels were dependent on the presence of BAP, suggesting
a short (i.e., 1-3 h) half-life for the CYP1A1 and CYP1B1 mRNAs after
metabolic removal of the BAP inducer. The rapid turnover of the mRNAs
and activities in T-47D cells after exposure to BAP suggests that these
cells may provide a system to investigate P450 mRNA and protein
catabolism. In recent studies with HepG2 hepatoma cells, the CYP1A1
mRNA had a similar rapid turnover, with a reported half-life of
2.4 h (Lekas et al., 2000
).
The kinetics and concentration-response relationships of BAP-mediated
induction of CYP1A1 and CYP1B1 are complex because PAHs are inducers
of, substrates for, and inhibitors of CYP1A1 and CYP1B1 (Shimada et
al., 1998
; Willett et al., 1998
; Arcaro et al., 1999
). The
enzyme inhibitory effects result in bell-shaped concentration-response
curves for apparent enzyme induction in vitro (Willett et al., 1998
;
Arcaro et al., 1999
). The shapes of concentration-response
curves vary markedly with time of incubation (Arcaro et al., 1999
).
This has been attributed to the removal of enzyme inducers and enzyme
inhibitors through metabolism. These effects make estimation of toxic
equivalency factors for PAHs by measurement of induced enzyme
activities difficult. Determination of the effects of BAP and other
PAHs on CYP1A1 and CYP1B1 levels by measurement of enzyme activities is
only of value at low concentrations of BAP, where its inhibitory
effects are minimal.
Coexposure of T-47D cells to NaAsO2 and BAP resulted in a marked diminution of the activities of CYP1A1 and CYP1B1 relative to those observed with BAP alone. These effects were observed at arsenite concentrations below those that affected cell viability. Although both CYP1A1- and CYP1B1-catalyzed E2 hydroxylase activities in microsomal incubations were inhibited by arsenite, the magnitude of inhibition was not sufficient to account for the reduction of BAP-induced CYP1A1- and CYP1B1-catalyzed activities in T-47D cells by arsenite. This was most evident for CYP1A1 because addition of 10 µM NaAsO2 inhibited CYP1A1-catalyzed E2 2-hydroxylation in microsomal assays by only 21% (Fig. 6A), whereas addition of 10 µM NaAsO2 to the culture medium caused an 86% reduction in the rate of the BAP-induced E2 2-hydroxylation pathway (Fig. 5D). Further evidence that the effect of arsenite on CYP1A1 and CYP1B1 activities was on the levels of active enzyme rather than a direct inhibitory effect or modulation of the inhibitory effect of BAP was obtained in the experiments with TCDD. In these experiments, arsenite was only effective in the induction phase of the experiment and not during the E2 metabolism assay phase (Fig. 7). The reduction in the levels of immunoreactive CYP1A1 observed on Western blots correlated well with the reduction in 2-MeOE2 formation in response to coexposure to BAP and NaAsO2. Because the levels of CPR were not affected by these coexposures (Fig. 8A), the effects of NaAsO2 on P450s do not appear to be reflective of a general effect on cellular proteins.
Arsenite has been previously shown to reduce the levels of hepatic
P450s of the CYP1A (Falkner et al., 1993
; Jacobs et al., 1999
; Vakharia
et al., 2001
), CYP2B (Jacobs et al., 1999
), and CYP3A families (Jacobs
et al., 1999
). The results reported here indicate that the effect of
arsenite on the expression of cytochromes P450 is retained in a
transformed, immortalized cell line derived from a human breast
carcinoma. The fact that arsenite diminishes expression of P450s of
several gene families suggests a general mechanism. One mechanism that
has been offered to explain the effect is the induction of heme
oxygenase by arsenite (Sardana et al., 1981
; Falkner et al., 1993
),
which would reduce the level of active P450. Several heavy metal
species are known to induce HO-1; arsenite is particularly potent in
this regard. Results reported here show a marked induction of HO-1 mRNA
in T-47D human breast cells coexposed to arsenite and BAP. The
induction of HO-1 by arsenite and the subsequent reduction in the
availability of heme as the prosthetic group for P450s may explain the
reduced P450 activities in T-47D cells, hepatocyte cultures, and in
vivo. However, recent studies by Jacobs et al. (1999)
suggest that
induction of HO-1 may not completely explain the effect of arsenite on
P450 expression. HO-1 is also induced by heme in hepatocyte cultures, but treatment with heme did not result in reduced P450 levels, whereas
cotreatment of hepatocyte cultures with arsenite and heme diminished
levels of CYP2B1/2 (Jacobs et al., 1999
). The authors concluded that a
mechanism in addition to the induction of HO-1 must be involved.
Further studies are underway to resolve the role of HO-1 in the effects
of arsenite reported here.
The observation that the induction of CYP1A1- and CYP1B1-catalyzed
activities by BAP are markedly diminished by cotreatment with arsenite,
but the levels of the mRNAs encoding CYP1A1 and CYP1B1 are not
significantly affected indicates that the primary effects of arsenite
are not at the level of transcription of the two enzymes or mediated by
effects on mRNA stability or catabolism. However, these results do not
rule out possible effects of arsenite on translation. Effects of
arsenite at the level of mRNA translation have been reported, although
they are thought to result in increased rather than decreased rates of
translation. Arsenite and other stress inducers increase the level of
phosphorylation of initiation factor eIF4E, a protein complex that
binds the 7-methylguanosine cap structure of mRNAs. Phosphorylation of
eIF4E increases its affinity for the mRNA cap structure, which
increases the rate of activation of translation (Wang et al., 1998
). We
are not aware of any reports indicating that phosphorylation of eIF4E
decreases the rates of translation of specific mRNAs.
Another point at which arsenite might affect the rates of CYP1A1- and
CYP1B1-catalyzed activities is the rate of protein turnover. Our
results show rapid decline in the rates of the BAP-induced E2 2- and 4-hydroxylation pathways after
metabolic removal of the BAP, suggesting rapid degradation of CYP1A1
and CYP1B1. Although there are no data on P450 turnover in T-47D cells,
rates of P450 turnover in rat hepatocytes were found to differ among
the P450s. Proteasome-mediated degradation was demonstrated for CYP1A2,
CYP2E1, CYP3A, and CYP4A (Roberts, 1997
), but appears to require prior labilization of the P450s because it can be stimulated in cell-free experiments by processes such as incubation of the P450 with a suicide
substrate or denaturation by freezing and thawing. Arsenite is known to
react with cysteine residues of some proteins, resulting in loss of
function (Kapahi et al., 2000
). Whether proteasome-mediated degradation
is involved in the turnover of human CYP1A1 and CYP1B1 in extrahepatic
cells and whether arsenite might affect this process by influencing
factors such as protein conformation and heme incorporation are unknown
and will be investigated in future studies.
Although the underlying mechanism is not fully resolved, our results
suggest that coexposure to arsenite in combination with PAHs may lessen
the rate of PAH metabolism by reducing the induced levels and thus
activities of both CYP1A1 and CYP1B1. This reduction in P450 activity
may be a consequence of cross talk among stress-response signaling
pathways that are activated to limit cellular damage caused by exposure
to the toxicants. The diminution of CYP1A1 and CYP1B1 activities by
arsenite in cells of extrahepatic origin may actually lower the rate of
conversion of PAH to DNA-binding and mutagenic species in a coexposure
situation. Due to the rapid metabolism of BAP, it is difficult to
compare levels of BAP that induce CYP1A1 and CYP1B1 in cultured cells
in vitro with those that might occur in humans. The level of arsenite
that elicits significant effects in T-47D cells (1 µM, or 134 µg/l
NaAsO2) appears to be within the range that could
occur in humans. Blood levels of 8 to 15 µg/l (Concha et al.,
1998
) and urinary levels of 133 to1893 µg/l (Hopenhayn-Rich et
al., 1996
) of total arsenic have been reported in exposed
individuals. Cellular levels of arsenic may exceed those in
circulation. This PAH-arsenite interaction is likely to be one of many
such interactions resulting from exposure to complex environmental
mixtures that may affect carcinogenesis.
| |
Acknowledgments |
|---|
We gratefully acknowledge use of the Wadsworth Center's Biochemistry, Molecular Genetics, and Tissue Culture Core Facilities.
| |
Footnotes |
|---|
Received May 15, 2001; accepted November 30, 2001.
This research was supported by the U.S. Environmental Protection Agency's Science to Achieve Results program through Grant R827180010 and by U.S. Public Health Service Grants CA81243 and ES04913. Although the research described in this article has been funded in part by the U.S. Environmental Protection Agency's STAR program, it has not been subjected to the agency's required peer and policy review and therefore does not necessarily reflect the views of the agency, and no official endorsement should be inferred. N.L., who is affiliated with the Division of Environmental Health, Department of Preventive Medicine, Jiangxi Medical College, Nanchang, China, is grateful to the World Health Organization for support.
Dr. David C. Spink, Wadsworth Center, P.O. Box 509, Albany, NY 12201-0509. E-mail: spink{at}wadsworth.org
| |
Abbreviations |
|---|
Abbreviations used are:
PAH, polycyclic aromatic
hydrocarbon;
BAP, benzo[a]pyrene;
P450, cytochrome
P450;
AhR, aromatic hydrocarbon receptor;
E2, 17
-estradiol;
OHE2, hydroxyestradiol;
MeOE2, methoxyestradiol;
DMSO, dimethyl sulfoxide;
RT-PCR, reverse
transcription-polymerase chain reaction;
GAPDH, glyceraldehyde-3-phosphate dehydrogenase;
PCR, polymerase chain
reaction;
HO-1, heme oxygenase 1;
TCDD, 2,3,7,8-tetrachlorodibenzo-p-dioxin;
CPR, NADPH-cytochrome P450 reductase;
MTT, 3-[4,5-dimethylthiazol-2-yl]-2,5-diphenyltetrazolium bromide.
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