B L Xu1, Q Z Zhao2, X Y Gao1, G J Hou1. 1. Children's Hospital of Zhengzhou, Zhengzhou, China. 2. Basic Medical College, Zhengzhou University, Zhengzhou, China.
Abstract
Sex hormones from environmental and physiological sources might play a major role in the pathogenesis of hepatoblastoma in children. This study investigated the effects of estradiol and bisphenol A on the proliferation and telomerase activity of human hepatoblastoma HepG2 cells. The cells were divided into 6 treatment groups: control, bisphenol A, estradiol, anti-estrogen ICI 182,780 (hereinafter ICI), bisphenol A+ICI, and estradiol+ICI. Cell proliferation was measured based on average absorbance using the Cell Counting-8 assay. The cell cycle distribution and apoptotic index were determined by flow cytometry. Telomerase activity was detected by polymerase chain reaction and a telomeric repeat amplification protocol assay. A higher cell density was observed in bisphenol A (P<0.01) and estradiol (P<0.05) groups compared with the control group. Cell numbers in S and G2/M phases after treatment for 48 h were higher (P<0.05), while the apoptotic index was lower (P<0.05) and telomerase activities at 48 and 72 h (P<0.05) were higher in these groups than in the control group. The cell density was also higher in bisphenol A+ICI (P<0.01) and estradiol+ICI (P<0.05) groups compared with the ICI group. Furthermore, cell numbers were increased in S and G2/M phases (P<0.05), while the apoptotic index was lower (P<0.05) and telomerase activities at 48 and 72 h were higher (P<0.05) in these groups than in the ICI group. Therefore, bisphenol A and estradiol promote HepG2 cell proliferation in vitro by inhibition of apoptosis and stimulation of telomerase activity via an estrogen receptor-dependent pathway.
Sex hormones from environmental and physiological sources might play a major role in the pathogenesis of hepatoblastoma in children. This study investigated the effects of estradiol and bisphenol A on the proliferation and telomerase activity of humanhepatoblastomaHepG2 cells. The cells were divided into 6 treatment groups: control, bisphenol A, estradiol, anti-estrogen ICI 182,780 (hereinafter ICI), bisphenol A+ICI, and estradiol+ICI. Cell proliferation was measured based on average absorbance using the Cell Counting-8 assay. The cell cycle distribution and apoptotic index were determined by flow cytometry. Telomerase activity was detected by polymerase chain reaction and a telomeric repeat amplification protocol assay. A higher cell density was observed in bisphenol A (P<0.01) and estradiol (P<0.05) groups compared with the control group. Cell numbers in S and G2/M phases after treatment for 48 h were higher (P<0.05), while the apoptotic index was lower (P<0.05) and telomerase activities at 48 and 72 h (P<0.05) were higher in these groups than in the control group. The cell density was also higher in bisphenol A+ICI (P<0.01) and estradiol+ICI (P<0.05) groups compared with the ICI group. Furthermore, cell numbers were increased in S and G2/M phases (P<0.05), while the apoptotic index was lower (P<0.05) and telomerase activities at 48 and 72 h were higher (P<0.05) in these groups than in the ICI group. Therefore, bisphenol A and estradiol promote HepG2 cell proliferation in vitro by inhibition of apoptosis and stimulation of telomerase activity via an estrogen receptor-dependent pathway.
Hepatoblastoma (HB) is the most common malignant, solid liver tumor in children, arising
from multipotent stem cells that differentiate into liver and bile duct epithelial cells
in undifferentiated embryonic tissue (1). It
accounts for about 25% of pediatric liver tumors and 50-69% of malignant hepatic tumors
among primary embryonal tumors (2). HB is
presumed to be caused by abnormal hyperplasia and differentiation of healthy liver
cells, although the details of its pathogenesis remain unknown (3).It has been suggested that environmental factors and sex hormones play major roles in
the etiology of HB (4). Estrogen maintains the
function of sex organs and regulates metabolism in humans (5). Environmental sources of estrogen include pesticides, plastics,
detergents, combustion products, as well as industrial and agricultural waste products
(6). Once estrogen enters the body, it can
affect the endocrine system and promote the growth of hormone-sensitive tumors.
Correlations between estrogen and tumorigenesis have been investigated in various
studies (7-10). It has been demonstrated that estrogen regulates the expression of
specific biomarkers in breast cancer (11).
Another study has suggested that estrogen promotes angiogenesis and, consequently, the
proliferation of hemangiomas in children (12).
However, there is little known about the role of estrogen in hepatoblastoma.Telomerase is a type of reverse transcriptase consisting of a ribonucleoprotein complex
with a RNA template and various catalytic and regulatory subunits. It is expressed in
98% of immortalized cell lines and >90% of malignant tumors (13). Telomerase activity is principally responsible for the infinite
proliferative capacity of tumors (14).This study investigated the effects of physiological and environmental estrogen on HB by
treating humanhepatoblastomaHepG2 cells with 17β-estradiol(E2) and bisphenol A (BPA),
and then evaluating cell proliferation, apoptosis, and telomerase activity. The
mechanism of action of these hormones was examined using anti-estrogen ICI 182,780
(hereinafter ICI).
Material and Methods
Cells and reagents
The HepG2 cell line was provided by the Medical School of Zhengzhou University.
Phenol red-free Roswell Park Memorial Institute (RPMI) 1640 medium and fetal bovine
serum (FBS) were obtained from Gibco (USA). ICI was purchased from Santa Cruz
Biotechnology Co., Ltd. (China). E2 was from IBL International (Germany). The cell
counting kit (CCK)-8 was from Dojindo (Japan). Dimethyl sulfoxide (DMSO) was obtained
from Zhengzhou Chengxiang Chemical Technology Ltd. (China). The reverse transcription
kit was purchased from Invitrogen (USA). SYBR Green supermix was from Toyobo (Japan),
and the Telo TAGGG Telomerase PCR enzyme-linked immunosorbent assay (ELISA) kit was
from Nanjing KeyGEN Biotech Co., Ltd. (China). Penicillin and streptomycin were
purchased from Beijing BioDee Biotechnology Co. Ltd (China).
Primer and probe design
Primers and probes were synthesized by Invitrogen. The sequence of forward primer TS
was 5′-AATCCGTCGAGCAGAGTT-3′,
which was labeled with biotin at the 5′-end. The sequence of reverse primer CX was
5′-CCCTTACCCTTACCCTTACCCTTA-3′.
The probe sequence was 5′-CCCTAACCCTAACCCTAA-3′ labeled with digoxin at the 5′-end.
Cell culture
HepG2 cells were cultured in RPMI 1640 medium containing 10% FBS, 100 U/mL
penicillin, and 100 U/mL streptomycin at 37°C with 5% CO2and saturated
humidity. After the cells had attached to the culture dish, the medium was replaced
with phenol red-free RPMI 1640 medium, and the cells were cultured for 24 h. The
cells were examined daily by phase contrast microscopy.
Reagent preparation and determination of effective doses
BPA, E2, and ICI were dissolved in DMSO and stored at −20°C. Working solutions were
prepared by diluting the stock solutions in phenol red-free RPMI 1640 medium. HepG2
cells were resuspended at 1×106 cells/mL and seeded in a 96-well plate
with 200 μL each well. After adherence, the culture medium was removed, and cells
were washed twice with phosphate-buffered saline (PBS) before BPA or E2 was added at
various concentrations (0, 2×10−5, 2×10−4, 2×10−3,
2×10−2, 2×10−1, 2×100, 2×101, and
2×102 μg/mL BPA; 0, 1×10−5, 1×10−4,
1×10−3, 1×10−2, 1×10−1, 1×100,
1×101, and 1×102ng/mL E2). Normal liver cells were similarly
treated with the various concentrations of BPA or E2. ICI was used at
1×10−6 M according to a previous report (15).
Treatment groups
Cells were divided into 6 treatment groups as follows: control (DMSO only), BPA, E2,
ICI, BPA+ICI, and E2+ICI. The volume of DMSO in each group was <0.1% of the total
volume.
Analysis of cell proliferation
Cells were seeded at 1×105 cells/well in a 96-well plate. After adherence,
the culture medium was removed, and cells were washed twice with PBS. CCK-8 solution
(10 μL) was added to each well at 0, 24, 48, 72, 96, and 120 h, and the cells were
cultured for an additional 3 h before the absorbance at 450 nm (A450nm)
was determined using a microplate reader (Bio-Rad). A growth curve was generated from
the measured values.
Examination of the cell cycle distribution and apoptosis
Cells were collected at the logarithmic growth phase and seeded at 3×105
cells/25 mL culture flask. After 24 h, the cells were washed twice with PBS and
subjected to the various treatments. After 48 h, 1-5×106 cells were
collected by trypsinization and centrifuged at 12,000 g for 5 min at
4°C. The cells were then repeatedly washed with PBS and fixed in pre-cooled 70%
alcohol at −20°C overnight. After washing with PBS, the cells were treated with RNase
A (10 μL of a 20 μg/mL stock solution in 500 μL PBS) for 30 min at 37°C, followed by
centrifugation at 8,000 g for 5min at 4°C. The cells were then
incubated with 10 μL of a propidium iodide solution (50 μg/mL in 500 μL PBS) for 30
min at room temperature in the dark. Cell cycle and apoptosis analyses were carried
out by flow cytometry (BD Biosciences, USA) using CellQuest software (BD Biosciences,
USA). A total of 10,000 cells was used to analyze and the cell cycle distribution
with FlowJo software (USA).
Analysis of telomerase activity
A PCR-telomeric repeat amplification protocol (TRAP)-ELISA kit (16,17) was used to
determine the telomerase activity of HepG2 cells according to the manufacturer’s
instructions. Briefly, the cells were collected at each time point and washed twice
with normal saline. A lysis solution (200 μL) was then added to dissolve the cells.
After 30 min of incubation, the cells were centrifuged at 12,000 g
for 20 min at 4°C, and the supernatant was stored at −80°C until use. Two microliters
of telomerase extraction solution incubated at 65°C for 10 min was used for the
negative control. The TRAP reaction was carried out in a 50 μL volume including 2×
substrate buffer (25 μL), TS and CX primers (2 μL or 100 ng each) 2 U Taq enzyme (1
μL), TRAP template (1 μL), and sterile diethylpyrocarbonatewater. Sterile paraffin
oil (40 μL) was used to overlay the reaction solution. Telomeric repeat sequences
were synthesized by telomerase at 25°C for 30 min, and then the enzyme was
inactivated at 94°C for 5 min. The PCR conditions were as follows: 30 cycles of 94°C
for 30 s, 50°C for 30 s, and 72°C for 90 s, followed by final extension at 72°C for
10 min. To detect telomerase activity, a polyvinyl chloride panel was coated with
1:50 biotin-streptavidin (50 μL per well) overnight at 4°C. The following day, the
panel was washed four times with cleaning solution (10 mM Hepes-KOH, 1.5 mM
MgCl2, 10 mM KCl, and 1 mM DTT). PCR product (5 μL) was mixed with 20
μL denaturation solution (0.5% NaOH), followed by incubation for 10 min at room
temperature and then addition of 225 μL hybridization solution. A total of 100 μL of
the mixture was transferred to the panel, and hybridization was carried out at 37°C
for 3 h. After three washes with washing buffer, 100 μL peroxidase-conjugated
anti-digoxin antibody was added to the panel, followed by incubation for 30 min at
37°C. After five washes with washing buffer, 100 μL substrate buffer (containing
3,3′,5,5′-tetramethylbenzidine) was added to the panel. Color development was allowed
to proceed for 10-15 min. The reaction was terminated by addition of 2M sulfuric
acid. Telomerase activity was determined by measuring the A450nm
(reference wavelength: 630 nm) on a microplate reader. Negative and positive control
measurements corresponded to A450nm <0.2 and A450nm >1.0,
respectively.
Statistical analysis
Data are reported as means±SD. Comparisons between groups were performed by one-way
analysis of variance. MATLAB software (MathWorks, USA) was used for all statistical
analyses. P<0.05 was considered to be statistically significant.
Results
E2 and BPA stimulate HepG2 cell proliferation
After 120 h of treatment, the effective concentrations of E2 and BPA to stimulate
HepG2 cell proliferation were 2 μg/mL and 10 ng/mL, respectively (Figure 1). For normal liver cells, both BPA and E2
had inhibitory effects on their growth (Figure
2). At various time points, BPA, E2, BPA+ICI, and E2+ICI groups had the
highest proliferation rates, whereas ICI alone had little effect on cell growth
(Figure 3 and Table 1). Cell numbers in the BPA group at 48, 72, and 96 h were
significantly higher (P<0.01 or P<0.05) and those in the E2 group were higher
at 24, 48, and 72 h (P<0.01) compared with control cells. Compared with the ICI
group, cell numbers were higher in the BPA+ICI group at 48, 96, and 120 h (P<0.01
or P<0.05) and in the E2+ICI group at 48, 72, 96, and 120 h (P<0.01). These
results indicate that E2 and BPA induce the proliferation of HepG2 cells.
Figure 1
Screening for optimal concentrations of bisphenol A (BPA) and estradiol
(E2) to stimulate HepG2 cell proliferation. Data are reported as means±SD.
*P<0.05, **P<0.01 compared to no treatment (one-way ANOVA).
Figure 2
Inhibitory effect of bisphenol A (BPA) and estradiol (E2) on normal liver
cell survival. The inhibitory action was stronger with increased dosage of BPA
and E2.
Figure 3
Growth curve of HepG2 cells treated with bisphenol A (BPA) or estradiol
(E2) alone or in combination with the anti-estrogen ICI 182,780 (ICI).
Cell cycle regulation is affected by E2 and BPA
The proportions of cells in the various cell cycle phases were obviously different in
E2- and BPA-treated cells and control cells (P<0.05; Figure 4). Similarly, there were significant differences in the
cell cycle distributions of BPA+ICI and E2+ICI groups compared with the ICI group
(P<0.05). No statistical difference was found between BPA and BPA+ICI groups or
between E2 and E2+ICI groups (P>0.05). These results indicate that E2 and BPA
stimulate HepG2 cell proliferation by altering the cell cycle.
Figure 4
Effect of bisphenol A (BPA) and estradiol (E2) on the HepG2 cell cycle
distribution. Data are reported as means±SD. ICI: ICI 182,780. *P<0.05
compared to control group; #P<0.05 compared to ICI group (one-way
ANOVA).
E2 and BPA inhibit apoptosis of HepG2 cells
Flow cytometry showed that the apoptotic index was markedly reduced in cells treated
with E2 and BPA compared with the control group (P<0.05; Figure 5). Similarly, compared with cells treated with ICI alone,
apoptosis rates were reduced in BPA+ICI and E2+ICI groups (P<0.05). Differences
between control and ICI groups, BPA and BPA+ICI groups, and E2 and E2+ICI groups were
not statistically significant (P>0.05). These data demonstrate that E2 and BPA
inhibit apoptosis of HepG2 cells.
Figure 5
Apoptotic index of HepG2 cells treated with bisphenol A (BPA) or estradiol
(E2) alone or in combination with the anti-estrogen ICI 182,780 (ICI) for 48 h.
Data are reported as means±SD. *P<0.05 compared to control group; #P<0.05
compared to ICI group (one-way ANOVA).
Telomerase activity is induced by E2 and BPA
Telomerase activity in HepG2 cells was evaluated by a PCR-TRAP-ELISA. Compared with
the control group, telomerase activity was enhanced in BPA- and E2-treated cells at
48 and 72 h (P<0.05; Figure 6). Similarly,
compared with the ICI group, telomerase activity was higher in BPA+ICI and E2+ICI
groups at 48 and 72 h (P<0.05). There were no differences between ICI and control
groups at any time point (P>0.05).
Figure 6
Effect of bisphenol A (BPA) and estradiol (E2) on telomerase activity in
HepG2 cells. Cells were treated with BPA or E2 alone or in combination with the
anti-estrogen ICI 182,780 (ICI). Telomerase activity was assessed by the
PCR-telomeric repeat amplification protocol (TRAP). Data are reported as
means±SD. **P<0.01 compared to control group; ##P<0.01
compared to ICI group (one-way ANOVA test).
Discussion
HB is the most common type of pediatric liver tumor. It is highly malignant, associated
with poor outcomes, even after treatment, and characterized by occult occurrence,
vascular enrichment, rapid growth, and early metastasis (18,19). The pathogenesis of HB remains
unclear, but it is thought to arise from mutations and changes in hormone levels caused
by environmental factors (4,20). For example, some childhood cases of HB have been linked to the
use of oral contraceptives by the mother (4),
suggesting the influence of estrogen. The estrogen antagonist tamoxifen has been shown
to stimulate HepG2 cell activity and inhibit apoptosis (21). Furthermore, estrogen antagonists inhibit expression of the estrogen
receptor and HepG2 cell proliferation in vitro in time- and
concentration-dependent manners (22). Consistent
with these previous findings, the present results showed that E2 and the environmental
estrogen BPA promote HepG2 cell proliferation, which may be due to inhibition of
apoptosis because treatment with these agents had no effect on the cell cycle
distribution. Co-treatment with ICI did not alter the effects of E2 or BPA, indicating
that these agents act via a non-estrogen receptor-dependent pathway in accordance with
the known mechanism of estrogen receptor signaling (21).The role of telomerase in tumor malignancy has been highlighted by many studies.
According to a previous report, the hyperproliferation of tumor cells in 90% of humanmalignancies is linked to inappropriate telomerase activity (23). A study of 100 immortalized cell lines derived from 18 types of
tumor tissues demonstrated that 98 cell lines had abnormally high telomerase activity by
TRAP in contrast to cells from non-cancerous tissue that were negative for telomerase
activity (24). Here, we showed that E2 and BPA
stimulate telomerase activity in HepG2 cells. Therefore, inhibition of apoptosis by
these two agents may be achieved by stimulation of telomerase activity, which suppresses
telomere shortening, chromosomal damage, and ultimately apoptosis (24). This finding is substantiated by the observation that tamoxifen
induces apoptosis of HepG2 cells by suppression of telomerase function (21). Taken together, these results indicate that
therapeutic agents targeting telomerase may be effective for the treatment of HB.
Moreover, our findings provide an insight into the mechanisms underlying the tumorigenic
effects of physiological and environmental estrogens.
Authors: John M S Bartlett; Cassandra L Brookes; Tammy Robson; Cornelis J H van de Velde; Lucinda J Billingham; Fiona M Campbell; Margaret Grant; Annette Hasenburg; Elysée T M Hille; Charlene Kay; Dirk G Kieback; Hein Putter; Christos Markopoulos; Elma Meershoek-Klein Kranenbarg; Elizabeth A Mallon; Luc Dirix; Caroline Seynaeve; Daniel Rea Journal: J Clin Oncol Date: 2011-03-21 Impact factor: 44.544
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