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Vol. 58, Issue 4, 852-858, October 2000
and
, and Androgen Receptor: Structure-Activity Studies
Chemical Industry Institute of Toxicology, Research Triangle Park, North Carolina (K.W.G., S.C.M.); Department of Pharmacology and Cancer Biology, Duke University Medical Center, Durham, North Carolina (D.P.M.); Department of Pharmacology and Molecular Toxicology, University of Massachusetts Medical Center, Worcester, Massachusetts (S.S.D., D.K.); and Department of Veterinary Physiology and Pharmacology, Texas A&M University, College Station, Texas (S.S.)
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Abstract |
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We previously demonstrated differential interactions of the
methoxychlor metabolite
2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE)
with estrogen receptor
(ER
), ER
, and the androgen receptor (AR). In this study, we characterize the ER
, ER
, and AR activity of structurally related methoxychlor metabolites. Human hepatoma cells
(HepG2) were transiently transfected with human ER
, ER
, and AR
plus an appropriate steroid-responsive luciferase reporter vector.
After transfection, cells were treated with various concentrations of
HPTE or structurally related compounds in the presence (for detecting
antagonism) and absence (for detecting agonism) of 17
-estradiol and
dihydrotestosterone. The monohydroxy analog of methoxychlor, as well as
monohydroxy and dihydroxy analogs of
2,2-bis(p-hydroxyphenyl)-1,1-dichloroethylene, had ER
agonist activity and ER
and AR antagonist activity similar to HPTE.
The trihydroxy metabolite of methoxychlor displayed only weak ER
agonist activity and did not alter ER
or AR activities. Replacement
of the trichloroethane or dichloroethylene group with a methyl group
resulted in a compound with ER
and ER
agonist activity that
retained antiandrogenic activities. This study identifies some of the
structural requirements for ER
and ER
activity and demonstrates
the complexity involved in determining the mechanism of action of
endocrine-active chemicals that simultaneously act as agonists or
antagonists through one or more hormone receptors.
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Introduction |
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Methoxychlor
[1,1,1-trichloro-2,2-bis(4-methoxyphenyl)ethane] is a chlorinated
hydrocarbon pesticide structurally similar to
dichlorodiphenyltrichloroethane [DDT;
1,1,1-trichloro-2,2-bis(chlorophenyl)ethane]. Like
o,p'-DDT, methoxychlor is estrogenic in vivo (Bulger et al., 1978
; Gray et al., 1989
; Alm et al., 1996
; Chapin et al., 1997
; Cummings, 1997
; Hall et al., 1997
). However, methoxychlor has low
affinity for the estrogen receptor (ER) and the in vivo estrogenic activity is caused by metabolism to phenolic estrogenic metabolites. The primary estrogenic metabolite of methoxychlor is
2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE). HPTE
competes with estradiol for binding to ER, induces ornithine
decarboxylase and uterotrophic activity in ovariectomized rats, and is
approximately 100-fold more active than methoxychlor (Bulger et al.,
1978
; Ousterhout et al., 1981
; Shelby et al., 1996
).
Estrogenic responses are mediated through two separate estrogen
receptors, ER
and ER
. These two receptors have homologous DNA and
ligand binding regions (Kuiper and Gustafsson, 1997
; Tremblay et al.,
1997
; Ogawa et al., 1998
), and most compounds have similar binding
affinities and transcriptional activities with ER
and ER
(Kuiper
et al., 1996
, 1998
; Mosselman et al., 1996
; Tremblay et al., 1997
).
We previously demonstrated that HPTE is an ER
agonist and an ER
antagonist in HepG2 human hepatoma cells transfected with estrogen-responsive reporter constructs (Gaido et al., 1999
). This
unique activity of HPTE makes it an ideal compound with which to
evaluate the in vitro and in vivo differences in ER-subtype dependent
responses. We have also shown that HPTE is an androgen receptor (AR)
antagonist in vitro (Maness et al., 1998
). The differential activity of
HPTE with ER
, ER
, and AR may explain why some of the responses
induced by methoxychlor in vivo differ from those induced by estradiol.
For example, the ability of methoxychlor to act as an ER antagonist in
the ovary (Hall et al., 1997
) may be caused by the high level of ER
expression relative to ER
in this tissue (Saunders et al., 1997
).
The physiological consequences of a chemical that is an ER
agonist,
an ER
antagonist, and an AR antagonist are unknown, and HPTE can
serve as a model for investigating the effects of an agent that
modulates multiple endocrine pathways. Additional studies with HPTE and
structural analogs may lead to further insights on ligand specificity
for ER
, ER
, and AR. Therefore we compared the ER
, ER
, and
AR activity of HPTE and structural analogs and show that some chemicals
similar in structure to HPTE also demonstrate unique ER
, ER
, and
AR activity.
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Materials and Methods |
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Chemicals. HPTE was synthesized by dissolving 1 g of methoxychlor (Aldrich Chemical Co., Milwaukee, WI) in 100 ml of methylene chloride and then treating with excess boron tribromide in methylene chloride (Aldrich) for 24 h. Water (5 ml) was carefully added, and crude HPTE was isolated in methylene chloride. The residue (0.8 g) was purified by preparative thin-layer chromatography (TLC). The resulting HPTE was >97% pure as determined by gas-liquid chromatography.
Monohydroxymethoxychlor was synthesized by dissolving 1.0 g of methoxychlor in methylene chloride. Approximately 1.5 mol equivalents of boron dibromide in methylene chloride was slowly added over a period of 1 to 2 h. The progress of demethylation was monitored by TLC. The monohydroxymethoxychlor metabolite was isolated by preparative TLC using hexane/acetone (92:8) as solvent. Yields of 250 to 300 mg were obtained and the products were greater than 98% pure as determined by gas chromatography-mass spectrometry (GC-MS). Trihydroxymethoxychlor and the corresponding trimethoxymethoxychlor were synthesized by ChemSyn Labs (Lenexa, KS). Dimethoxy-DDE was synthesized by dissolving 1.0 g of methoxychlor in dimethyl sulfoxide. Anhydrous sodium bicarbonate (3.0 g) was added and the mixture was heated at 140°C for 1 h. The mixture was diluted with water and the dimethoxy-DDE product was isolated by extraction with chloroform. The crystalline residue from the chloroform extract (0.75 g) was greater than 98% pure as determined by GC-MS. Dihydroxy-DDE was prepared from 2,2-bis(p-hydroxyphenyl)-1,1-dichloroethylene (p,p'-DDE) following the same procedure as described above for HPTE. Dihydroxy-DDE was greater than 98% pure as determined by GC-MS. Monohydroxy-DDE was prepared from p,p'-DDE following the same procedure as described above for monohydroxymethoxychlor. Monohydroxy-DDE was greater than 98% pure as determined by GC-MS. All other chemicals were obtained from Sigma Chemical Co. (St. Louis, MO) and were
97% pure.
Plating and Transfection.
Transfection experiments were
performed as described previously (Maness et al., 1998
; Gaido et al.,
1999
). HepG2 human hepatoma cells (ATCC, Rockville, MD) were plated in
triplicate in 24-well plates (Falcon Plastics, Oxnard, CA) at a density
of 105 cells/well in complete medium consisting
of phenol red-free Eagle's minimal essential medium (GIBCO/BRL, Grand
Island, NY) supplemented with 10% resin-stripped fetal bovine serum
(Hyclone, Logan, UT), 2% L-glutamine, and 0.1% sodium
pyruvate. Cells were incubated overnight at 37°C in a humidified
atmosphere of 5% CO2/air and then transfected
after the Superfect procedure (Qiagen, Valencia, CA) with three
plasmids. For detection of ER
activity, cells were transfected with
human ER
expression plasmid, plus an estrogen-responsive complement
3-luciferase (C3-Luc) reporter plasmid, and a constitutively active
cytomegalovirus (CMV)-
-galactosidase reporter plasmid (transfection
and toxicity control) (Tzukerman et al., 1994
; Gaido et al., 1999
). For
detection of ER
activity, cells were transfected with a human ER
expression plasmid, a C3-Luc reporter plasmid, and
CMV-
-galactosidase reporter plasmid (Gaido et al., 1999
; Hall and
McDonnell, 1999
). For detection of AR activity, cells were transfected
with a human AR expression plasmid, plus an androgen-responsive MMTV-Luc reporter plasmid, and CMV-
-galactosidase reporter plasmid (Maness et al., 1998
). Transfected cells were rinsed with PBS and dosed
with various concentrations of test chemical and dimethyl sulfoxide
(vehicle control; Sigma) in complete medium. After a 24 h incubation,
cells were rinsed with PBS and lysed with 65 µl of lysing buffer (25 mM Tris-phosphate, pH 7.8, 2 mM
1,2-diaminocyclohexane-N,N,N',N'-tetraacetic acid, 10% glycerol, 0.5% Triton X-100, 2 mM dithiothreitol). Lysate was divided into two 96-well plates for luciferase and
-galactosidase determination.
-Galactosidase activity was determined by adding 20 µl of
-galactosidase assay reagent to 30 µl of lysate in the second 96-well plate.
-Galactosidase assay reagent consisted of a 4 mg/ml
solution of chlorophenol red-
-D-galactopyranoside (CPRG; Sigma) in 150 µl of CPRG buffer (60 mM
Na2HPO4, 40 mM
NaH2PO4, 10 mM KCl, 1 mM
MgSO4, 50 mM
-mercaptoethanol, pH 7.8)
Absorbance at 570 nm was determined over a 30 min period using a
Vmax kinetic microplate reader (Molecular
Devices, Menlo Park, CA).
HepG2 cells lack detectable levels of endogenous ER
, ER
, and AR
and in the absence of transfected receptor, Luc activity remains below
the level of detection (data not shown). Background activity after
receptor transfection averaged 150 ± 56 normalized Luc units with
ER
, 31 ± 6 normalized Luc units with ER
, and 5 ± 1 normalized Luc units with AR. We have previously confirmed by Western
analysis that ER
and ER
are expressed at equal concentrations under the conditions of our assay (Hall and McDonnell, 1999Statistical Analysis. Unless otherwise noted, values presented in this study represent the means ± S.E. resulting from at least three separate experiments with triplicate wells for each treatment dose. Dose-response data were analyzed using the sigmoidal dose-response function of the graphical and statistical program Prism (GraphPad, San Diego, CA).
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Results |
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We compared the activity of HPTE and structural analogs in HepG2
cells transfected with expression vectors for human ER
, ER
, and
AR along with the appropriate reporter plasmid (Fig. 1). HepG2 cells were dosed with set
concentrations of chemical alone and in combination with an inducing
dose of either 17
-estradiol (E2) or dihydrotestosterone (DHT) for
determining antagonistic activity with ER
/
and AR, respectively.
HPTE (Fig. 1C) exhibited ER
agonist, and ER
and AR antagonist
activity as described previously (Maness et al., 1998
; Gaido et al.,
1999
). HPTE does display some partial ER
agonist activity of
approximately 13% of that obtained with a maximally inducing dose of
estradiol (Maness et al., 1998
). The monohydroxy metabolite of
methoxychlor, as well as the mono- and dihydroxy analogs of
p,p'-DDE (Fig. 1, B, H, and I), also had ER
agonist and
ER
and AR antagonist activity. Bisphenol A exhibited ER
and ER
agonist activity but did not have antiandrogenic activity (Fig. 1K).
Replacement of the trichloromethyl of HPTE or dichloromethylene group
of dihydroxy-DDE results in a conversion from ER
antagonist activity
to full ER
agonist activity but retains ER
agonist and AR
antagonist activity (Fig. 1, C and I versus L). Trimethoxy and
trihydroxy ring substituted compounds (Fig. 1, D and E) exhibited
minimal ER
agonist activity and did not affect ER
or AR-dependent
responses.
|
Concentration-response curves for selected ER
and ER
agonists are
presented in Fig. 2, A and B. EC50 values for ER
and ER
agonist activity
are presented in Table 1. HPTE and
dihydroxy-DDE were most potent as ER
agonists and were approximately
17- and 25-fold less potent, respectively, than estradiol. HPTE and
dihydroxy-DDE were followed in ER
agonist potency by monohydroxy
methoxychlor, bisphenol A, monohydroxy-DDE, bishydroxyphenylmethane,
and bishydroxyphenylethane. Bishydroxyphenylmethane and
bishydroxyphenylethane were equally potent as ER
agonists and were
approximately 285-fold less potent than estradiol.
|
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We characterized the ER
antagonist activity of selected compounds in
HepG2 cells by determining the effect of various concentrations across
a complete estradiol dose-response range (Fig. 3,
A-C). Each of the tested
compounds caused parallel shifts in the estradiol dose-response curve,
indicating competitive antagonism. Schild regression analyses were
performed and equilibrium dissociation (KB)
values determined (Table 1). HPTE, monohydroxy methoxychlor, monohydroxy-DDE, and dihydroxy-DDE demonstrated relatively similar antagonist potencies.
|
Similar experiments were performed to characterize AR antagonist
activity (Fig. 4, Table 1). HPTE,
dihydroxy-DDE, and p,p'-DDE demonstrated similar AR
antagonist potencies. Monohydroxy-DDE, bishydroxyphenylmethane, and
bishydroxyphenylethane were approximately 3- to 5-fold less potent than
HPTE, dihydroxy-DDE, and p,p'-DDE.
|
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Discussion |
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ER
and ER
bind structurally diverse classes of chemicals,
and it is difficult to compare structure-dependent receptor binding or
transactivation between chemical classes. In contrast,
structure-activity correlations within a single structural class such
as the triphenylethanes can be used to design ER agonists and
antagonists (e.g., tamoxifen) for clinical applications as selective
estrogen receptor modulators. For a series of mono-, di-, and
trihydroxyphenyl ethane/ethylene analogs structurally related to
methoxychlor, the order of potency as ER
agonists was
dihydroxyphenyl > monohydroxyphenyl > trihydroxyphenyl, suggesting that the optimal structure for ER
agonist activity contained two p-hydroxyphenyl groups substituted at a single
ethane or ethylene carbon atom (i.e., bis-substitution). In contrast, the fully methylated metabolites (e.g., Fig. 1, A versus C; Fig. 1, G
versus D) were significantly less active as ER
agonists; this is
consistent with previous studies with methoxychlor and HPTE (Bulger et
al., 1978
; Ousterhout et al., 1981
; Shelby et al., 1996
). A similar
pattern was observed for the substituted diphenylmethane analogs even
though only a limited number of these compounds were tested (Fig. 1, J
and N versus M).
With few exceptions (Fig. 1, K and L), the bishydroxy/methoxyphenyl
ethane or ethylene analogs were not significant ER
agonists, and
only two bishydroxyphenylmethanes (Fig. 1, J and N) induced measurable
ER
-dependent reporter gene activity. Thus, our results demonstrate
that this series of bishydroxyphenyl-substituted ethanes, ethylenes,
and methanes are preferential ER
agonists and exhibit weak to
nondetectable ER
agonist activity. These results are unique because
previous studies for ER subtype-dependent ligand binding and
transactivation report similar ER
and ER
activity for various
structural classes of estrogenic compounds (Kuiper et al., 1996
, 1998
;
Mosselman et al., 1996
; Tremblay et al., 1997
).
The results of our studies also demonstrate that methoxychlor and
structurally related analogs exhibit minimal ER
antagonist activity
but that three compounds (Fig. 1, B, H, and I) in addition to HPTE
(Fig. 1C) are highly effective ER
antagonists. Structural features
required for this response include bis(4-hydroxyphenyl) or
bis(4-hydroxyphenyl),(4-methoxyphenyl) groups attached to
chlorine-substituted ethane/ethylene moieties. Additional compounds are
required to more accurately define structural requirements for ER
antagonist activities; however, our results clearly demonstrate
remarkable structure-dependent differences among these compounds for
activity as ER
antagonists.
Several compounds investigated in this study exhibited antiandrogenic
activity. Four analogs that were ER
antagonists (Fig. 1, B, C, H,
and I) were among the most active antiandrogens and exhibited activity
similar to that observed for p,p'-DDE. Interestingly, both
p,p'-DDE (Fig. 1F) and dihydroxy-DDE (Fig. 1I) exhibited similar antiandrogenic activities, and the interchange of two p-chloro and two p-hydroxyl substituents had
minimal effects on this AR response. In contrast, the two
p-hydroxyl groups (but not p-chloro substituents)
conferred both ER
agonist and ER
antagonist activity on
dihydroxy-DDE, demonstrating that subtle substituent changes can affect
some but not all ligand-activated hormone receptor action.
Methoxy-DDE and monohydroxy-DDE are impurities in technical grade
methoxychlor (Bulger et al., 1985
), and dihydroxy-DDE is formed during
the metabolism of methoxychlor in mice (Kapoor et al., 1970
). HPTE,
monohydroxy-methoxychlor, monohydroxy-DDE, and dihydroxy-DDE have
previously been shown to compete with estradiol for ER binding in vitro
and demonstrate uterotropic activity in vivo (Bulger et al., 1978
,
1985
; Ousterhout et al., 1981
). Thus, exposure to methoxychlor results
in a complex interaction of multiple metabolites with different
activities at ER
, ER
, and AR.
The molecular mechanism by which a ligand can act as an ER
agonist
and an ER
antagonist is of both toxicological and pharmacological interest. The overall structure of the ER
ligand-binding domain is
very similar to that of ER
(Pike et al., 1999
), and most compounds demonstrate similar binding affinities and transcriptional activities with ER
and ER
(Kuiper et al., 1996
, 1997
; Mosselman et al., 1996
; Tremblay et al., 1997
). The helix 12 region present on both receptors plays an important role in the mechanism of ER action (Darimont et al., 1998
). This region folds over the ligand binding pocket and exposes a region on both receptors involved in coactivator binding. ER
and ER
antagonists such as raloxifene and
hydroxytamoxifen contain bulky constituents that reposition helix 12 and block receptor interaction with coactivators (Brzozowski et al.,
1997
; Pike et al., 1999
). HPTE analogs used in this study do not have substituents of the size and character of raloxifene and consequently less likely to physically reposition helix 12. However, X-ray crystallography and sequence analysis comparison of the ligand-binding domains of ER
and ER
suggest that the agonist orientation of helix 12 in ER
may be unstable and thus easier to antagonize than
ER
(Pike et al., 1999
). The ER
agonist/ER
antagonists identified in this study may be able to stabilize helix 12 in the
agonist orientation for ER
but not for ER
. X-ray crystallographic studies are needed to confirm this hypothesis.
The R,R-enantiomer of tetrahydrochrysene
(R,R-THC) has also recently been shown to have differential
ER
and ER
activity (Meyers et al., 1999
; Sun et al., 1999
). Like
HPTE, R,R-THC behaves as an ER
agonist and an ER
antagonist. In contrast, the S,S-enantiomer (S,S-THC) is an agonist with both ER
and ER
. The
equilibrium dissociation value (KB) for
R,R-THC has not been determined, and whether
R,R-THC is an ER
competitive antagonist remains to be demonstrated. THC compounds differ considerably in structure from the
methoxychlor analogs presented in this study, and this class of
compounds will provide additional information regarding the ligand
specificity of ER
and ER
binding and transactivation.
Less is known about the mechanism of AR antagonism by AR ligands. AR
antagonists are generally thought to prevent or reduce binding of AR to
DNA (Kelce et al., 1995
, 1998
). However, the specific mechanisms
responsible for this inhibition of AR-DNA binding remain unknown.
Much still remains to be determined about the precise roles of ER
,
ER
, and AR in reproductive development and endocrine function,
especially in humans; the physiological consequences of exposure to
chemicals that are ER
agonists, ER
antagonists, and AR
antagonists are unknown. HPTE and its structural analogs give us
further insights into the ligand specificity of ER
, ER
, and AR
and serve as model chemicals for investigating ER
, ER
, and AR
steroid hormone receptor interactions.
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Acknowledgments |
|---|
We thank Dr. Paul Foster, Dr. Chris Corton, and Dr. Katrina Waters for critical review of the manuscript and Dr. Barbara Kuyper for editorial assistance.
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Footnotes |
|---|
Received March 10, 2000; Accepted June 15, 2000
The financial assistance of the National Institutes of Health (ES000834, ES09106, and ES04917) and the Texas Agricultural Experiment Station is gratefully acknowledged.
Send reprint requests to: Dr. Kevin W. Gaido, CIIT, P.O. Box 12137, Research Triangle Park, NC 27709. E-mail: gaido{at}ciit.org
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Abbreviations |
|---|
DDT, dichlorodiphenyltrichloroethane;
ER, estrogen receptor;
AR, androgen receptor;
TLC, thin-layer
chromatography;
E2, 17
-estradiol;
GC-MS, gas chromatography-mass
spectrometry;
p,p'-DDE, 2,2-bis(p-hydroxyphenyl)-1,1-dichloroethylene;
C3, complement 3;
Luc, luciferase;
CMV, cytomegalovirus;
CPRG, chlorophenol
red-
-D-galactopyranoside;
HPTE, 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane;
DHT, dihydrotestosterone;
THC, tetrahydrochrysene.
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References |
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|
|
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transcriptional activity and is a key regulator of the cellular response to estrogens and antiestrogens.
Endocrinology
140:
5566-5578
or estrogen receptor
.
Endocrinology
140:
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J. M. Garcia Pedrero, B. del Rio, C. Martinez-Campa, M. Muramatsu, P. S. Lazo, and S. Ramos Calmodulin Is a Selective Modulator of Estrogen Receptors Mol. Endocrinol., May 1, 2002; 16(5): 947 - 960. [Abstract] [Full Text] [PDF] |
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V. S. Wilson, K. Bobseine, C. R. Lambright, and L. E. Gray Jr. A Novel Cell Line, MDA-kb2, That Stably Expresses an Androgen- and Glucocorticoid-Responsive Reporter for the Detection of Hormone Receptor Agonists and Antagonists Toxicol. Sci., March 1, 2002; 66(1): 69 - 81. [Abstract] [Full Text] [PDF] |
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