Abstract
Background Tetrabromobisphenol A (TBBPA) can be characterized as an endocrine-disrupting chemical (EDCs). It
has been widely used as a brominated flame retardant in industrial products. EDCs have effects on female reproduc-
tion leading to issues, such as infertility, hormone imbalance, and endometriosis. In Korea, the problems of infertility
and decreasing birth rate are of significant concern. Exposure to EDCs might have a harmful effect on female fertility
by mediating a decrease endometrial receptivity. This study aimed to investigate the effects of TBBPA on infertil-
ity, particularly on early implantation events in the uterine endometrium. Human endometrial adenocarcinoma
and trophoblastic cell lines were used in this study. The cytotoxicity of TBBPA on Ishikawa cells and Jeg-3 cells
was measured using the Cell Counting Kit-8 assay. The mRNA expression was analyzed by reverse transcription-
quantitative polymerase chain reaction, and protein levels were measured by western blotting. The attachment rate
was analyzed using an attachment assay, and the outgrowth area was measured using an outgrowth assay.
Results
The mRNA expression of interleukin (IL)-6, IL-1β, tumor necrosis factor-α, and leukemia inhibitory factor
was significantly increased upon treatment of Ishikawa cells by TBBPA. Moreover, the outgrowth area in the TBBPA
group was significantly decreased compared to that in the control. In contrast, TBBPA had a minor effect on protein
levels and attachment rates.
Conclusions
In this study, TBBPA induced an inflammatory milieu in mRNA expression. An increase in inflammation-
related cytokines in the endometrium can disrupt embryo implantation. TBBPA disrupted the outgrowth of spheroids
in the endometrium; however, the protein levels and attachment rate were comparable to those in the control group.
The effect of TBBPA on implantation events should be elucidated further.
Keywords
Implantation, Endocrine disrupting chemicals (EDCs), Tetrabromobisphenol A, Ishikawa cells, Jeg-3 cells,
Infertility
Background
Female infertility refers to the inability of a woman to
conceive or carry a pregnancy to full term. Many causes
of female infertility are known, including problems with
ovulation, fallopian tube or uterus, and hormone imbal -
ance [1, 2]. According to a report published by the Korea
Society of Obstetrics and Gynecology, the infertility rate
in Korea was estimated to be approximately 10% in 2019,
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Environmental Sciences Europe
†Myoungjoo Koo and Inyoung Kang contributed equally to this work.
*Correspondence:
Jaewang Lee
[email protected]
1 Department of Biomedical Laboratory Sciences, Eulji University, 553,
Sanseong-Daero, Sujeong-Gu, Seongnam-Si, Gyeonggi-Do, Republic
of Korea
Page 2 of 11Koo et al. Environmental Sciences Europe (2023) 35:69
which is higher than the global average of 8% [3]. Addi -
tionally, over the decades, the number of patients receiv -
ing assisted reproductive technology (ART) for infertility
has increased in South Korea [4, 5]. Several causes of
implantation failure are known, including uterine fac -
tors, embryo factors, endometrial receptivity, hormonal
factors, and immunological factors. However, the effects
of endocrine-disrupting chemicals (EDCs) including
tetrabromobisphenol-A (TBBPA) on the uterine endo -
metrium have not been fully investigated [6, 7].
EDCs interfere with the function of the endocrine sys -
tem in humans and animals [8]. The endocrine system
regulates body function, especially reproduction and the
hormone cycle [9, 10]. EDCs can block the effects of nat -
ural hormones though structures similar to hormones,
leading to alterations in hormone levels and disruption of
physiological homeostasis [11, 12]. They can bind to sex
hormone receptors and inhibit or activate the production
of hormones, such as estrogen and progesterone [13].
As a result, the hormone pathway is interfered by EDCs,
which might have an impact on cell signaling [14].
Bisphenol A (BPA) is an industrial chemical used in
the production of plastics and epoxy resins [15]. It is
commonly found in polycarbonate plastics, which are
used in water bottles, food containers, and canned foods
[16]. BPA is an EDC that binds to estrogen receptors
in the human endocrine system [17]. Exposure to BPA
leads to reproductive and developmental disorders and
impaired immune function [18, 19]. TBBPA is a member
of the bisphenol family; it is structurally similar to BPA.
Despite being considered a general and perpetual con -
taminant of the environment, TBBPA is a widely used
industrial product [20]. Exposure to TBBPA is common
in everyday life as it is included in plastic materials, and
it accounts for approximately 60% of the production in
the entire brominated flame retardants (BFRs) market,
thereby accounting for the highest percentage of BFRs
[21, 22]. In addition, highest consumption of TBBPA has
been recorded in Asia when compared to global con -
sumption [23] and TBBPA has been detected in serum
of Korean population, ranging from 0.05 to 75 ng/g lipid
weight [24]. Unfortunately, the function of TBBPA as an
EDC has not been fully elucidated. Various studies have
its effects on endocrine and reproductive systems [25].
TBBPA promotes the growth of uterine fibroids, which
are known to cause recurrent implantation failure (RIF)
[26–28]. Nevertheless, TBBPA is not regulated, and the
effect of TBBPA on early human implantation has not
been studied.
Embryo implantation is also an important part of
reproduction, specifically in the process of pregnancy,
and a major cause of pregnancy loss [29]. It refers to
the attachment and invasion of a fertilized embryo into
the uterine endometrium. The synchronized receptive
state of the uterus and development of the embryo are
crucial for the implantation process [30, 31]. Endo -
metrial receptivity is maintained for only a few days,
which is defined as the implantation window. Endo -
metrial receptivity is regulated by ovarian hormones,
such as estrogen and progesterone. These hormones
influence the expression of attachment and inflamma -
tion molecules such as leukemia inhibitory factor (LIF),
interleukin (IL)-6, and tumor necrosis factor (TNF)-α.
Currently, whether TBBPA leads to implantation fail -
ure and decreased endometrial receptivity has not been
examined [32, 33]. Therefore, the aim of this study was
to investigate the harmful effects of TBBPA on the early
implantation and outgrowth processes using a three-
dimensional spheroid cell culture model with Jeg-3 and
Ishikawa cells.
Materials and methods
Cell culture
The endometrial epithelial-like Ishikawa cell line and
human trophoblastic Jeg-3 cell line were cultured in Dul -
becco’s modified Eagle medium (DMEM, Welgene, Gyeo-
ngsan, Korea) supplemented with 10% fetal bovine serum
(FBS, Gibco, Waltham, MA, USA) and 1% penicillin and
streptomycin (P/S, Lonza, Morristown, NJ, USA). Cells
were cultured under standard conditions (37 °C, 5% CO2)
[34]. Ishikawa cells were used to represent the human
endometrium, which is the implantation site. Jeg-3 cells
were used to represent the human embryo because of the
inner cell mass surrounded by trophoblastic cells. TBBPA
(Sigma-Aldrich, St. Louis, MO, USA) was dissolved in
dimethyl sulfoxide (DMSO, Sigma-Aldrich) and used to
treat Ishikawa cells to determine its effect of on endome -
trial cells.
Cell viability assay
A cell viability assay was performed to determine the
cytotoxic dose of TBBPA. Ishikawa cells and Jeg-3 cells
were detached using 0.25% Trypsin/EDTA (Gibco) and
suspended to seed in 96-well plates at a density of 1 × 103/
well. The cells were exposed to 0.01–100 μM TBBPA
for 24 or 48 h. The viability of the cells was evaluated
using Cell Counting Kit-8 (CCK-8, Dojindo, Kumamoto,
Japan). After incubating with different concentrations of
TBBPA, 10 µL of CCK-8 reagent was added to each well,
followed by incubation for 1 h at 37 °C. Cell viability was
detected at 450 nm using MultiskanGO (ThermoFisher,
Waltham, MA, USA) [35, 36]. The cells were divided into
control and TBBPA groups. The control group was cul -
tured with 1% FBS containing 0.1% DMSO in DMEM.
Page 3 of 11
Koo et al. Environmental Sciences Europe (2023) 35:69
Reverse transcription‑quantitative polymerase chain
reaction (RT‑qPCR)
Ishikawa and Jeg-3 cells were detached using 0.25%
Trypsin/EDTA and seeded in a 6-well plate (SPL,
Pocheon, Korea) at a density of 1 × 105 /well. Ishikawa
cells were treated with TBBPA at concentrations of 0.1, 1,
and 10 μM for 48 h. For the comparison of 2D versus 3D
spheroids of Jeg-3 cells, 1 × 105 cells per well were seeded
for the 2D group, and 100 Jeg-3 spheroids were used
for 3D groups. The mRNA expression of IL-1α, IL-1β,
integrin alpha V (ITGαV), and LIF was detected in 2D
and 3D spheroids and compared. Total RNA from cells
and spheroids was extracted using TRIzol (Invitrogen,
Waltham, MA, USA). For RT-qPCR analysis, 500 ng of
mRNA was converted to complementary DNA (cDNA)
using the PrimeScript ™ 1st strand cDNA Synthesis Kit
(Takara, Kusatsu, Japan). RT-qPCR was performed using
SYBR green reagent (Meridian Bioscience, Cincinnati,
OH, USA) and primers (BIONEER, Daejeon, Korea).
Each experiment was performed at least in triplicate
and was repeated more than three times. For inflamma -
tion targets, IL-6 (Bio-Rad, Hercules, CA, USA), IL-1β,
and TNF- α were examined. Furthermore, ITGαV and
LIF were examined as attachment targets. All data were
normalized to that of glyceraldehyde-3-phosphate dehy -
drogenase (GAPDH). The primer sequences used in this
study are summarized in Table 1. The PCR method was
performed as follows: hold stage at 95 °C for 15 min and
PCR cycle of denaturation at 95 °C for 30 s, annealing at
61 °C for 30 s, and extension at 72 °C for 30 s [37].
Western blot analysis
To quantify the level of protein, western blot analysis was
performed using cell lysates. Ishikawa cells were seeded
in 6-well plates at a density of 1 × 105 cells/well. Total
protein was extracted using radioimmunoprecipitation
assay lysis buffer (Thermo Fisher) with proteinase inhibi -
tor (Thermo Fisher). Total protein concentration was
determined by bicinchoninic Acid assay (Thermo Fisher).
A total of 15 µg of protein was used for the experiments.
Each sample was separated using 10% sodium dodecyl
sulfate (SDS)-polyacrylamide gel electrophoresis (PAGE)
and transferred to polyvinylidene fluoride (PVDF) mem -
branes. The membranes were blocked with 5% skim milk
for 2 h at room temperature and then incubated with pri-
mary antibody against IL-6 (1:800) (Abcam, Cambridge,
UK), TNF-α (1:500) (Abcam), LIF (1:200) (Santa Cruz
Biotechnology, Dallas, TX, USA), and GAPDH (1:5000)
(Santa Cruz Biotechnology) overnight at 4 °C on an
orbital shaker. The membranes were washed thrice using
Tris-buffered saline with 1% Tween 20. For IL-6, TNF-
α, and LIF, incubation was performed with anti-rabbit
horseradish peroxidase-conjugated immunoglobulin
(IgG) secondary antibody for 2 h at room temperature.
For GAPDH, incubation was performed with anti-mouse
horseradish peroxidase-conjugated IgG secondary anti -
body for 2 h at room temperature. The proteins on the
membranes were analyzed using the iBright CL750 imag-
ing system (Applied Biosystems, Waltham, MA, USA).
The data were evaluated using ImageJ software (NIH,
Bethesda, MD, USA).
Attachment assay
Ishikawa cells were cultured for 48 h in a T25 flask with or
without TBBPA treatment. Then, the cells were detached
using 0.25% Trypsin/EDTA and seeded in a 12-well plate
at a density of 1 × 105 and cultured with DMEM contain -
ing 10% FBS. After 8 h, the medium was changed for
each experimental group. DMEM with 1% FBS was used
for the control and TBBPA groups. Formation of Jeg-3
Table 1 Primer sequence
Genes Primer sequence Product size (bp) GenBank Accession
number
Annealing
Temperature (℃)
IL-1α F: CTG AAG GAG ATG CCT GAG ATA C 383 NM_000575.5 61
R: GAA CTG TCA ACA CTG CAC AAG
IL-1β F: TAA AGA GAG CTG TAC CCA GAG A 217 NM_000576.3
R: AAG TGA GTA GGA GAG GTG AGA G
TNF-α F: CTC CTC ACC CAC ACC ATC AG 134 NM000594.4
R: ATA GAT GGG CTC ATA CCA GGG
ITGαV F: AAT CTT CCA ATT GAG GAT ATC AC 140 NM_002210.5
R: AAA ACA GCC AGT AGC AAC AAT
LIF F: CCA ACG TGA CGG ACT TCC C 82 NM000981.4
R: TAC ACG ACT ATG CGG TAC AG
GAPDH F: GGA GCG AGA TCC CTC CAA AA 197 NM_002046.7
R: GGC TGT TGT CAT ACT TCT CA
Page 4 of 11Koo et al. Environmental Sciences Europe (2023) 35:69
spheroid was performed using hanging drop method at
a density of 500 cells per spheroid for 48 h in DMEM
supplemented with 10% FBS and rotation at 45 RPM in
a shaking incubator, as shown in Fig. 5A. Spheroids with
sizes ranging from 150 to 300 were used for this experi -
ment. After harvesting the spheroids, they were seeded
on Ishikawa cells treated with TBBPA. The attachment
rates were observed at 5, 10, 20, and 30 min and 1, 2, 4,
and 24 h [38]. The attachment assay performed in this
study is illustrated in Fig. 1A.
Outgrowth assay
To determine the effect of TBBPA on spheroid out -
growth, Ishikawa cells were treated with TBBPA for 48 h
in a T25 flask. The cells were then detached using 0.25%
Trypsin/EDTA and seeded on a 12-well plate at a density
of 5 × 104 in DMEM with 10% FBS. After 8 h, the medium
was replaced with DMEM supplemented with 1% FBS
for the control and TBBPA groups. The cells in the nega -
tive control groups were replaced with DMEM without
FBS. Spheroids were seeded on Ishikawa cells after the
medium was changed, followed by incubation for 72 h
under standard conditions (37 °C, 5% CO2) [39, 40]. The
EVOS M500 imaging system (ThermoFisher) was used
for capturing photos of outgrowth areas with a magnifi -
cation of 40X. The outgrowth area was measured using
the ImageJ software (NIH). The outgrowth assay in this
study is illustrated in Fig. 1A.
Statistical analysis
All experiments were performed at least in triplicates. All
values are represented as ± standard error of the mean
(SEM). Attachment rate data were analyzed using the
chi-square test. The outgrowth area data were analyzed
using the t-test, and a difference between groups with a
P-value of less than 0.001 was considered statistically sig -
nificant. Other results were analyzed using one-way anal-
ysis of variance (one-way ANOVA) with Tukey’s post-hoc
multiple comparison tests. Statistical significance was set
at P value of less than 0.05. The Jeg-3 2D vs. 3D mRNA
expression was analyzed by t-test and a difference with
a P value of less than 0.05 was considered statistically
significant.
Results
The expression of Jeg‑3 cells 2D vs Jeg‑3 spheroids
To investigate the difference between 2 and 3D cultures,
the expression of mRNA markers related to attachment
Fig. 1 Experimental design and difference of mRNA expression between 2D culture and 3D culture of Jeg-3. The mRNA expression of Jeg-3 2D
culture and 3D culture using qRT-PCR (ITGaV, LIF , IL-1α and IL-1β) (n > 3) One-way analysis of variance; Tukey’s multiple comparison test (p < 0.05). A
Experimental design for this study. B Jeg-3 2D cultured and 3D culture mRNA expression. ***P < 0.0001
Page 5 of 11
Koo et al. Environmental Sciences Europe (2023) 35:69
(ITGαV and LIF) and inflammation (IL-1α and IL-1β)
was evaluated using qRT-PCR. The mRNA expression of
IL-1α was increased in the 3D culture group than in the
2D culture group. (IL-1α, 2D 1.04 ± 0.16 vs 3D 3.68 ± 0.21)
(Fig. 1B). The mRNA expression levels of ITGαV, LIF, and
IL-1β in the 2D culture group were comparable to those
in the 3D culture group. Based on these results, we con -
firmed the difference in mRNA expression between 2D
models and 3D models, and 3D models were more suit -
able for recapitulating the physiological state. Therefore,
in this study, we applied 3D spheroid model to the fol -
lowing experiments performed under in vivo conditions.
The effects of TBBPA on the viability of Ishikawa and Jeg‑3
cells
To examine the concentration of TBBPA that demon -
strated cytotoxic effects on cells for 24 h and 48 h, the
cells were treated with TBBPA at concentrations of 0.1,
1, 10, and 100 μM. The highest dose of TBBPA decreased
viability of both Ishikawa and Jeg-3 cells at 24 h and 48 h
(P < 0.0001). The concentrations of 0.1, 1, and 10 μM of
TBBPA did not affect viability of either Ishikawa cells
or Jeg-3 cells for 24 h (Fig. 2A, C) or 48 h (Fig. 2B, D).
(Ishikawa 24 h, control, 1.00 vs TBBPA 0.1 µM, 1.23 vs
TBBPA 1 µM, 1.12 vs TBBPA 10 µM, 1.04 vs TBBPA
100 µM, 0.19), (Ishikawa 48 h, control, 1.00 vs TBBPA
0.1 µM, 0.96 vs TBBPA 1 µM, 0.99 vs TBBPA 10 µM,
0.97 vs TBBPA 100 µM, 0.14), (Jeg-3 24 h control, 1.00
vs TBBPA 0.1 µM, 1.04 vs TBBPA 1 µM, 1.04 vs TBBPA
10 µM, 1.04 vs TBBPA 100 µM, 0.21), (Jeg-3 48 h, con -
trol, 1.00 vs TBBPA 0.1 µM, 1.04 vs TBBPA 1 µM, 1.01
vs TBBPA 10 µM, 1.00 vs TBBPA 100 µM, 0.16). Since
no statistical differences were observed among TBBPA
groups except among cells treated with a concentration
of 100 μM, the cells were treated with 0.1, 1, and 10 μM
during the next steps. A cytotoxicity test was performed
to confirm the absence of cytotoxic effects.
Gene expression in Ishikawa cells treated with TBBPA
To investigate the effect of TBBPA on Ishikawa cells,
mRNA expression was detected using qPT-PCR.
The mRNA expression of inflammatory markers was
increased in Ishikawa cells treated with TBBPA. Among
inflammation-related genes, the mRNA expression of
Fig. 2 The cell viability of Ishikawa and Jeg-3 by Cell Counting Kit (CCK8) assay. Cell count kit 8 (CCK-8) assay was conducted to determine cell
cytotoxicity of TBBPA. Ishikawa cells and Jeg-3 cells were treated with TBBPA for 24/48 h (n > 3). One-way analysis of variance; Tukey’s multiple
comparison tests, a vs b vs c vs d vs e (p < 0.05). A Ishikawa cell line TBBPA 0.1–100 μM treated for 24 h. B Ishikawa cell line TBBPA 0.1–100 μM treated
for 48 h. C Jeg3 cell line TBBPA 0.1 μM ~ 100 μM treated 24 h. D Jeg3 cell line TBBPA 0.1 μM ~ 100 μM treated 48 h. *P < 0.05, **P < 0.001, ***P < 0.0001
Page 6 of 11Koo et al. Environmental Sciences Europe (2023) 35:69
IL-6, IL-1β, and TNF-α was significantly increased in
the TBBPA-treated groups compared to that in the con -
trol groups (IL-6, control, 1.001 ± 0.028 vs TBBPA 10 µM,
1.38 ± 0.05), (IL-1β, control, 1.00 ± 0.03 vs TBBPA 0.1 µM,
1.73 ± 0.07 vs TBBPA 1 µM, 1.30 ± 0.03) (TNF-α, con -
trol 1.00 ± 0.03 vs TBBPA 0.1 µM, 4.09 ± 0.36 vs TBBPA
1 µM, 4.56 ± 0.25 vs TBBPA 10 µM, 4.72 ± 0.56) (Fig. 3A).
For attachment-related genes, the expression of LIF in
the TBBPA groups was significantly increased com -
pared to that in the control groups (Fig. 3B; LIF, control,
1.00 ± 0.03 vs TBBPA 1 µM, 3.29 ± 0.13 vs TBBPA 10 µM,
4.31 ± 0.15). These findings indicate that TBBPA affects
inflammation and attachment of endometrium cells,
which was determined based on the effects observed at
the mRNA level.
Protein expression of Ishikawa cells treated with TBBPA
To identify the protein levels of TBBPA in Ishikawa cells,
the expression of inflammation- and attachment-related
proteins, namely, LIF, TNF-α, and IL-6 were detected.
In the previous experiment, the mRNA expression of
LIF, TNF-α, and IL-6 was elevated in the TBBPA-treated
groups. To identify whether mRNA elevation led to an
increase in protein levels, western blot assay was used.
The levels of the proteins were slightly increased in all
TBBPA groups; however, the difference was not statisti -
cally significant (Fig. 4A, B).
Attachment rate of Jeg‑3 spheroid on Ishikawa cells
treated with TBBPA.
As observed in the previous experiment, the expression
of attachment-related marker LIF was increased at the
mRNA and protein levels, indicating that TBBPA might
enhance the attachment rate of spheroids. To determine
the attachment rate of spheroids to Ishikawa cells treated
with TBBPA, attachment assays were performed (Con -
trol vs TBBPA 10 µM, 5 min 0/89 vs 0/93, 10 min 1/89
vs 2/93, 20 min 17/89 vs19/93, 30 min 27/89 vs 32/93,
60 min 80/89 vs 85/93, 90 min 85/89 vs 87/93, 2 h 89/89
vs 92/93, 4 h 89/89 vs 92/93, 24 89/89 vs 93/93; Fig. 5A).
Early attachment rates (0 ~ 30 min) were slightly higher
in the TBBPA groups (10 μM) than in the control groups.
After 90 min, the attachment rate was not significantly
different among the experimental groups (Fig. 5B).
Fig. 3 The mRNA expression related to inflammation
and attachment in Ishikawa cells. The mRNA markers related
to inflammation were assessed by qRT-PCR. The mRNA expression
of Ishikawa cells treated with TBBPA (0.1 μM ~ 10 μM) for 48 h. The
mRNA expressions were normalized with GAPDH. (n > 3) One-way
analysis of variance; Tukey’s multiple comparison tests (p < 0.05)
A IL-6, IL-1β, and TNF-α mRNA expression of Ishikawa cells treated
with TBBPA for 48 h. B ITGαV and LIF mRNA expression of Ishikawa
cells treated TBBPA for 48 h. *P < 0.05, **P < 0.001, ***P < 0.0001
Fig. 4 The protein level of Ishikawa cells treated with TBBPA. The
protein level that has increased in the qRT-PCR. All targets normalized
with GAPDH. Ishikawa cells were treated with TBBPA for 48 h
and 20 µg/mL were used for Western blot assay. A The protein level
of Ishikawa cell treated with TBBPA (LIF, TNF-a, IL-6) (n > 3) One-way
analysis of variance; Tukey’s multiple comparison tests (p < 0.05) B The
Western blot band of GAPDH, TNF-a, LIF, and IL-6
Page 7 of 11
Koo et al. Environmental Sciences Europe (2023) 35:69
Outgrowth assay of Jeg‑3 spheroids on Ishikawa cells
treated with TBBPA.
To determine the effect of TBBPA on outgrowth, an out -
growth assay was conducted by examining Jeg-3 sphe -
roids seeded on Ishikawa cells, as shown in Fig. 6A.
Ishikawa cells were treated with TBBPA at a concentra -
tion of 10 μM. In the TBBPA groups, the outgrowth area
significantly decreased (P < 0.0001; control 11.6 ± 0.55 vs
TBBPA 10 µM 7.38 ± 0.35 vs negative control 6.77 ± 0.36;
Fig. 6B). This result indicates that TBBPA negatively
influenced the outgrowth area even though the attach -
ment-related protein levels were comparable.
Discussion
In the present study, we investigated whether TBBPA has
deleterious effects on the implantation and invasion pro -
cesses using the three-dimensional spheroid cell culture
method. For examining the potential risks and evidence
of the effects of TBBPA on female infertility, it is essen -
tial to investigate the toxicity of TBBPA in the endome -
trium and trophoblastic spheroids, which represented
the embryo in this study. TBBPA induced inflammation
milieu, increased the expression of the IL-6, IL-1β and
TNF-a mRNA levels, and reduced the outgrown area,
even though the protein levels and attachment rate were
comparable to the control groups in this study. However,
the potential mechanism of TBBPA has not yet been
elucidated.
For in vitro spheroid models, 2D cultured systems are
generally used, but they do not fully represent physi -
ological human cells. However, 3D spheroids can mimic
human in vivo cell conditions much better than 2D cul -
ture systems [41]. Differences in data among 2D and 3D
models have been observed [42, 43]. The main concern
associated with the use 3D culture models in this study
was that they were prepared with a cancer cell line.
Cancer cells do not represent primary non-cancer cells,
which may lead to contrasting results [44]. In this study,
the 2D and 3D culture systems showed different mRNA
expression patterns of inflammation-related genes, such
as IL-1β. Only IL-1β showed a significant difference.
These results indicate that our 3D and 2D models are dif-
ferent from those used in other studies. In addition, the
differences in mRNA expression showed that the use of
the 3D culture system in the study possibly recapitulated
the actual physiology of the human body as previously
described.
Fig. 5 The attachment assay of Jeg3 spheroid on Tetrabrombisphenol A treated Ishikawa cells. A The morphology of Ishikawa cells, Jeg-3 spheroid,
and Jeg-3 Spheroid on Ishikawa cells treated with TBBPA. B Attachment rate (%) (n > 65) T-test; (p < 0.05). The morphology of Ishikawa cells and Jeg-3
spheroids were taken by the EVOS imaging system. The attachment assay was performed to detect the Jeg-3 spheroids attachment rate
Page 8 of 11Koo et al. Environmental Sciences Europe (2023) 35:69
In this study, TBBPA did not affect viability of the
human endometrial cell line at concentrations of 0.1,
1, and 10 μM for 24 or 48 h. However, a concentration
of 100 μM showed significantly decreased cell viability
(P < 0.0001). To confirm the effect of TBBPA at the cel -
lular level, the concentration that did not exert cytotoxic-
ity was determined using the CCK-8 assay. With regard
to the elements concerning authentic human endocrine
systems and the environment, exposure to EDCs occurs
over extended periods and at low concentrations. It is
preferable to conduct the experiment in an environment
identical to the actual setting. However, it is quite diffi -
cult to maintain a cell line for a long time, and it cannot
be reconstructed using cell line experiments. As a refer -
ence, TBBPA treatment was performed at a high dose
without short-term cytotoxicity [45, 46].
Quantitative RT-PCR was used to examine the effect
of TBBPA on mRNA expression. To determine the
effect of TBBPA on the endometrium, the marker asso -
ciated with inflammation and attachment genes was
examined [47]. When the human embryo is attached
and invaded in the endometrium, cytokines related
to attachment and inflammation are released into the
endometrium and embryo. For inflammation, IL-6,
TNF-α, and IL-1α were used, and for attachment,
LIF and ITGαV, which are released from the embryo,
were used [48]. The inflammation marker IL-6 and
attachment marker LIF interact with each other [49–
51]. The mRNA expression associated with inflamma -
tion and attachment can show the effect of EDCs on
embryo implantation and invasion. The levels of IL-6,
TNF-α, and IL-1β, which are associated with inflam -
mation, were remarkably increased in TBBPA-treated
endometrium cells (P < 0.001). The findings indi -
cate that TBBPA induced an inflammatory milieu in
embryos and the endometrium.
The protein levels were evaluated using western blot
and primary antibodies against IL-6, TNF-α, and LIF.
The results are reflected by an increase at the mRNA
level. Western blotting was performed to confirm the
increase in mRNA expression at the protein level. In this
experiment, TBBPA did not change the protein levels sig-
nificantly. However, the levels of TNF-α in cells treated
with 10 µM of TBBPA were slightly increased (P = 0.058),
indicating that TBBPA has significant effects on mRNA
expression and protein levels, but not on these targets
that used in this experiment. We did not detect changes
in protein levels in response to TBBPA exposure. Their
non-responsiveness to TBBPA may be attributed to the
fact that the treatment time might be too short to detect
responses in the changes in expression. Further studies
should clarify how TBBPA regulates the expression of
inflammation and attachment-related genes to evaluate
its toxicity on female reproduction.
Fig. 6 The outgrowth area of Jeg3 spheroid on TBBPA-treated Ishikawa cells. A The morphology and area of Jeg-3 spheroid outgrowth. B The
outgrowth area. (n = 45 control group, n = 63 TBBPA group, n = 42 negative control group) One-way analysis of variance; Tukey’s multiple comparison
tests (p < 0.0001). The outgrowth area was detected and calculated by the ImageJ system. The relative area was measured compared to the control
group. ***P < 0.0001
Page 9 of 11
Koo et al. Environmental Sciences Europe (2023) 35:69
An attachment assay was used to investigate the effect
of TBBPA on implantation, especially on attachment pro-
cess. We attempted to mimic the EDC-influenced endo -
metrium by treating endometrial cell lines with TBBPA.
In the attachment assay, TBBPA-treated group showed
a slightly higher rate of early implantation than the con -
trol group. However, after 60 min, the TBBPA groups
showed a lower attachment rate than the control groups.
Moreover, no significant differences were noted between
the groups. Because the mRNA expression of LIF was
increased in the TBBPA group, it is considered that the
rate of TBBPA-treated group increased compared to
the control group at the early attachment rate. As men -
tioned above, a limitation of this assay is that spheroids
are made with cancer cells. High proliferation and adhe -
sion are the main characteristics of cancer cell lines and
can sufficiently affect the attachment of spheroids to
the endometrium [52]. For the next study, we are evalu -
ating the impact of TBBPA on mouse primary uterine
cells because cancer cells cannot completely imitate the
pathophysiology of primary cells.
The outgrowth assay was conducted to examine the
invasion of embryo into the endometrium. This implan -
tation process occurs within 72 h in the human body.
Jeg-3 spheroids seeded on TBBPA-treated endometrial
cells represent the human endometrium exposed to
EDCs and embryo implantation. Hence, the outgrowth
assay was conducted for 72 h. This result suggests that
the outgrowth area is decreased because TBBPA affects
molecules when the embryo attaches to the endome -
trium. In this experiment, TBBPA might have a negative
impact on the implantation process in the human body.
The implantation process follows a series of critical
steps, including attachment, invasion, and outgrowth.
Each of these steps must occur in a coordinated manner
for successful implantation to take place. Disruptions in
cytokine levels can affect the delicate balance required
during implantation and may lead to implantation fail -
ure or decreased outgrowth of the embryo. In our study,
we examined inflammatory cytokines, including IL-6,
IL-1b, TNF-a, and LIF, which are important cytokines
and factors involved in the complex process of implanta -
tion [53–55]. LIF plays a crucial role in embryo implan -
tation. It is released from the blastocyst and binds to
LIFR on endometrial cells, facilitating the attachment
of the blastocyst to the endometrial lining. Moreover,
the interaction of IL-6 and IL6-R with LIF is involved in
this process of attachment. By studying the mRNA lev -
els of these markers, this study provides valuable insights
into how TBBPA may affect the expression and regula -
tion of these important factors during implantation. The
fact that these markers interact with each other during
the implantation process highlights the importance of
examining them in conjunction to understand their com-
bined effects on implantation success. Research in this
area may provide crucial information about how EDCs
such as TBBPA might impact the process of implanta -
tion and potentially lead to recurrent implantation fail -
ure. In this study, we found that the outgrowth area was
significantly decreased in the TBBPA group, suggesting
that TBBPA exposure may have an adverse impact on the
outgrowth stage of implantation. Understanding these
mechanisms can pave the way for the development of tar-
geted interventions or treatments to counteract negative
effects and improve implantation success rates. Overall,
we suggest that this is a promising and important study
that can contribute significantly to the field of reproduc -
tive biology and fertility research.
This study had several limitations. First, the treatment
time and concentration of TBBPA. In the natural envi -
ronment, human bodies are exposed to EDCs for a long
time at low concentrations. Cell-based experiments have
Limitations
associated with maintenance of the cell line
over the years. Therefore, it is not possible to fully reca -
pitulate the exposure of the human body to EDCs found
in the actual environment. It is expected that experi -
ments on EDC can be carried out through animal experi -
ments. Second, the characteristics of the cell line used
in this study. The cell lines used in this experiment were
human endometrial adenocarcinoma and human chorio -
carcinoma cell lines. When primary cell lines are com -
pared to cancer cell lines, cancer cell lines demonstrate
higher proliferation, adhesion, and differentiation than
the primary cell line. Due to these features, the attach -
ment assay might not recapitulate the actual results. For
further studies, we strongly suggest using a primary cell
line with a real embryo and using an animal model for
the attachment assay. Finally, the effects of EDCs on Jeg-3
spheroids are a limitation of this study. In the physiologi -
cal human body, when implantation occurs, EDCs affect
the embryos and endometrium. In this experiment, we
only treated Ishikawa cells with TBBPA, which is a repre-
sentative model of the human endometrium. Examining
the effect of EDCs both in the endometrium and sphe -
roids used for mimicking embryos may provide a solu -
tion to overcome the limitations of this study.
Conclusion
In this study, the effect of TBBPA on implantation was
studied. The the mRNA levels of IL-6, TNF-α, and IL-1β
increased significantly. In addition, the outgrowth area
decreased significantly in the TBBPA group. Collectively,
we confirmed that TBBPA has an effect on implantation,
especially on the endometrium.
Page 10 of 11Koo et al. Environmental Sciences Europe (2023) 35:69
Abbreviations
ART Assisted reproductive technology
EDCs Endocrine disrupting chemicals
BPA Bisphenol A
TBBPA Tetrabromobisphenol A
BFRs Brominated flame retardants
RIF Recurrent implantation failure
DMEM Dulbecco’s modified Eagle medium
FBS Fetal bovine serum
P/S Penicillin and streptomycin
DMSO Dimethyl sulfoxide
CCK-8 Cell Counting Kit-8
RT-qPCR Reverse Transcription-quantitative polymerase chain reaction
IL-1α Interleukin 1 alpha
IL-1β Interleukin 1 beta
ITGαV Integrin alpha V
LIF Leukemia inhibitory factor
IL-6 Interleukin-6
TNF-α Tumor necrosis factor α
GAPDH Glyceraldehyde 3 phosphate dehydrogenase
BCA Bicinchoninic acid assay
SDS Sodium dodecyl sulfate
PAGE Polyacrylamide gel electrophoresis
PVDF Polyvinylidene fluoride
SEM Standard error of the mean
Acknowledgements
Not applicable.
Author contributions
Conceptualization: MK, KI, LJ; investigation: MK, IK; writing—original draft: MK,
IK; writing—review and editing: JL, JHJ; supervision: JL, JHJ; project administra-
tion: JL, JHJ; funding acquisition: JL.
Funding
This project was financially supported by the Basic Science Research Program
through the National Research Foundation of Korea (NRF), funded by the
Ministry of Education, Republic of Korea (NRF-2018R1D-1A1B07046419 to J.L.).
Availability of data and materials
The data that support the findings of this study are available from the cor-
responding author upon reasonable request.
Declarations
Ethics approval and consent to participate
Not applicable.
Consent for publication
All authors agreed to publish the paper.
Competing interests
The authors declare that they have no competing interests.
Received: 2 June 2023 Accepted: 12 August 2023
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