Introduction
Bisphenol A (BPA) is well-documented as an endocrine disruptor with detrimental effects on reproduction [
1]; as a result of increasing scrutiny of BPA, there is a broad interest in substitution of alternative bisphenols for human consumption. The most common alternative bisphenol, Bisphenol S (BPS), includes a sulfone group (SO
2) in place of the dimethylmethylene group [C (CH3)
2] in BPA [
2]. BPS has shown a range of deleterious effects following oral ingestion, inhalation or dermal absorption [
3], with the most common route of intake for humans being exposure through contaminated water and food at relatively low doses [
4]. To date, however, there have been only limited experimental studies of the possible harmfulness of low BPS doses.
Previous studies of BPS in male rats have reported a range of deleterious effects on hormonal balance, reduced germinal epithelium of seminiferous tubules and increased generation of reactive oxygen species [
5,
6]. Recent studies have reported BPS induces epigenetic changes, including alterations in the histone code in oocytes, increased DNA methylation in mouse spermatocytes and changes to transcriptome and proteome of cells in testicular tissue and many other cells types [
7‐
10]. Collectively, these findings suggest BPS may disrupt male reproductive functions through post-translational modifications (PTMs) of nucleic acids and proteins [
1,
11,
12] and regulation of transcriptionally silenced spermatozoa [
13]. In particular, lysine acetylation and tyrosine phosphorylation of sperm proteins regulate spermatogenesis and sperm capacitation [
14‐
16]. Based on these studies, it is possible that low doses of BPS could modulate male reproduction through PTMs of protein and nucleic acid structure. BPS is classified as an endocrine disruptor and its dose-response is more likely to be nonmonotonic, hence, very-low doses may be more effective than high doses. Therefore, we have chosen wide range of much lower BPS doses than was published before [
5,
6]. Using a wide range of low- and very-low doses BPS administered in drinking water for 8 weeks to young adult male mice, we want to determine the effect of BPS doses form the environment. Our findings provide one of the first indications that low doses of BPS regulate PTMs of spermatozoa and lead to possible negative effects on male reproduction.
Material and methods
All chemicals, including BPS (CAS: 80–09-1, cat. No. 103039) were purchased from Sigma-Aldrich (USA), unless stated otherwise.
Animals
All animal procedures were done in accordance with the Protection of Animals against Cruelty (Act No. 246/1992) under the supervision of the Animal Welfare Advisory Committee at the Ministry of Education, Youth, and Sports of the Czech Republic. Adult 7-week-old ICR male mice were purchased from Velaz Ltd. (Prague, Czech Republic), housed in standard cages in groups of 3 and maintained in a 12/12-h light/dark cycle at 21 ± 1 °C with a relative humidity of 60%. Bisphenol contamination was reduced using intact polysulfonate cages and glass drinking bottles. Mice were maintained on a phytoestrogen-free diet (1814P Altromin, Altromin Specialfutter GmbH & Co., Germany) with ultrapure water available ad libitum.
BPS dosage and sample collection
Mice were randomized into four experimental groups and allowed to adapt for 1 week. Vehicle control (0.1% ethanol; VC) and BPS for three treatment groups were administered through drinking water at final concentrations of 0, 0.0038, 3.8, and 380 μg/L, respectively, for 8 weeks (8–16 weeks of age). The following dosages were presumed [0, 0.001, 1, and 100 μg/kg body weight (bw)/day] with actual exposure estimated based on the knowledge of recorded body weight and water intake as previously reported [
17]. A wide range of doses and the route of exposure have been chosen appropriate to the real human exposure; doses of experimental animals through the drinking water have been used with respect to the welfare of animals. Hereafter, experimental groups will be stated as BPS1, BPS2 and BPS3.
Nine mice per group were included in three individual independent experiments (n = 36). Animal weights were recorded at the end of the experiments mice euthanised by cervical dislocation. Blood samples were collected by cardiac puncture, and serum was stored at − 80 °C until hormonal assay performance. Left and right testes were collected, weighed, and processed for histology and proteomics, respectively.
Sperm isolation and assessment
From the mice described above, the cauda epididymidis was dissected in 0.5 mL Whitten’s medium (Suppl. Table
S1), and sperm were allowed to swim out for 30 min. Thereafter, sperm concentration and motility were evaluated using Makler chamber and light microscope (Olympus CKX 41; Germany) equipped with a 10× objective (CAchN NA 0.25). 10 μl of sperm suspension was pipette to the Makler chamber, thereafter spermatozoa were counted in 3 lines, each of 10 squares and divide by 3 to obtain average sperm concentration in million per milliliter. Simultaneously, each spermatozoon across the counted area was identified either as motile or immotile. Accordingly, the sperm motility was expressed as the ratio of motile to immotile spermatozoa. The analysis was performed blindly to avoid bias.
Hormonal profiling
Blood serum samples in three independent experiments (n = 5 mice per group) were assayed with Immunobeads Milliplex MAP kit (HPTP1MAG-66 K, MSHMAG-21 K; Merck Millipore, USA) for the following hormone levels: adrenocorticotropic hormone, follicle-stimulating hormone, growth hormone, luteinising hormone, thyroid-stimulating hormone, cortisol, progesterone, testosterone, triiodothyronine, and thyroxine.
Quantitative and qualitative analyses of testes
One testis from each animal (
n = 9 per group) was fixed in Bouin solution, embedded in paraffin wax with random orientation, and sectioned completely into 10-μm-thick slides. The total testis volume, total germ epithelium volume, and interstitium volume were estimated according to the Cavalieri principle [
18]. The fractions of spermatogenesis (pre-spermiation stages I–VI; middle spermiation stages VII–VIII; post-spermiation stages IX–XII) were found using the point grid approach [
19,
20]. To determine the precision and accuracy of the stereological analysis, the coefficient of error was estimated (Suppl. Tab.
S2) [
18]. Qualitative analysis of seminiferous tubes was performed according to the methods described by the Society of Toxicologic Pathology [
21,
22] to assess the following abnormalities: missing germ cell layers and germ cell depletion, retained spermatids (spermiation failure), multinucleate and apoptotic germ cells, and exfoliation of spermatogenic cells into the lumen. At least 100 seminiferous tubules were evaluated blind to treatment group for each testicular cross section. The quantitative assessment was performed on a Nikon Eclipse Ti-U microscope (Nikon, Japan) equipped with a motorised stage (Prior, UK) using a 10× objective (Plan Fluor, NA 0.3) and Stereologer 11 software (SRC, Biosciences Tampa, FL, USA) for histopathological evaluation was performed using a 40× objective (UPlanFl, NA 0.75).
Western blot
Testicular tissue and sperm were dissolved in lysis buffer (40 mM Tris base, 7 M urea, 2 M thiourea, 4% CHAPS, 120 mM dithiothreitol), enriched with Complete Mini Protease Inhibitor Cocktail (Roche, Switzerland), for 30 min on ice. Sperm samples of three individuals belonging to the same experimental group were pooled. Thereafter, samples were subjected to sodium dodecyl sulfate polyacrylamide gel electrophoresis on 4–15% separating Mini-PROTEAN precast gels and blotted using a Trans-Blot Turbo Transfer System onto polyvinylidene difluoride membranes (Bio-Rad Laboratories, France). The membranes were blocked in 1% bovine serum albumin in TBS with 0.5% Tween-20 for 60 min at room temperature and incubated overnight at 4 °C with primary antibodies diluted in blocking buffer. The following primary antibodies were used: anti-acetyl lysine antibodies (cat. no. ab80178; Abcam, UK), anti-phospho-tyrosine antibodies (cat. no. ab10321; Abcam), anti-acetylated α-tubulin antibodies, and anti-γH2AX antibodies. Mouse monoclonal anti-α-tubulin antibodies (cat. no. T6199; Sigma, St. Louis, MO, USA) and rabbit monoclonal anti-histone H3 antibodies (cat. no. D1H2; Cell Signaling Technology, Danvers, MA, USA) were used as the loading control for γH2AX and acetylated α-tubulin, respectively. Horseradish peroxidase-conjugated secondary antibodies (goat anti-mouse or anti-rabbit IgG; dilution: 1:15,000; Invitrogen, Carlsbad, CA, USA) were applied for 60 min at 22 °C. Target proteins were visualised using ECL Select Western Blotting Detection Reagent (GE Healthcare Life Sciences, UK) and a ChemiDoc MP System (Bio-Rad). Alternatively, proteins were visualised using a colorimetric Opti-4CN substrate kit (Bio-Rad), followed by matrix-assisted laser desorption ionisation time-of-flight (MALDI-TOF) mass spectrometry (MS) for peptide detection in the dissected bands.
Proteome profiling
Testis lysates from animals in the experimental groups were collected for complete proteomic analysis. Nano-liquid chromatography-MS (nano-LC-MS) was used for protein identification and quantification, as described previously [
7]. The acetylome and phosphorylome were analysed separately.
Statistics
The data were processed with GraphPad Prism 8 (GraphPad Software Inc., San Diego, CA, USA). Based on Shapiro-Wilk normality distribution tests, analysis of variance (ANOVA) and Kruskal-Wallis tests were used for normally and non-normally distributed data. In cases of significant overall findings, differences between individual group pairs were assessed by Tukey’s and Dunn’s post-hoc tests, respectively. Results with P less than 0.05 were considered statistically significant. Normally and non-normally distributed data were expressed as means and medians, respectively.
Discussion
Male reproduction involves sensitive machinery, which is required for spermatozoon development and can be affected by exposure to various environmental stimuli. Because mature spermatozoa have been transcriptionally silenced, changes in PTMs can regulate protein activity and modify other crucial biomolecules. Indeed, lysine acetylation and phosphorylation have been shown to be indispensable for the proper function of sperm [
14,
15]. Our findings suggested that PTMs may be affected by pollutants from the environment. In our study, we simulated the exposure of adult males to BPS, a common endocrine disruptor, at very low doses (~ 0.001 and 1 μg/kg bw/day). Moreover, we chose ~ 100 μg/kg bw, which has been suggested to induce reproductive toxicity [
3,
5]. The 8-week exposure covered the whole duration of spermatogenesis; therefore, we assumed that the sperm quality and testicular tissues would be affected at the tissue/cell and proteome levels. We also evaluated the effects of endocrine disruption on post-translational modifications of testicular/sperm proteins in accordance with our hypothesis of the “post-translational effect” of very low doses of these agents.
Recent studies have demonstrated that bisphenols alter steroid signalling pathways, having negative effects on male and female reproduction. Our observations did not reveal hormonal changes, even after higher BPS exposure, whereas comparable doses were found to be effective in rats [
6]. However, earlier results showing that endocrine disruptors lead to hormonal imbalances should be revised because alternative mechanisms of hormone-derived actions have been noted. For example, oestrogen-like action results in carcinogenesis [
23], and changes in the distributions of oestrogen receptors and androgen-converting enzyme aromatase have been reported [
24]. Endocrine disruptors have also been shown to modulate downstream signalling of activated G protein-coupled oestrogen receptors [
25]. It is difficult to identify bisphenol-affected mechanisms after systemic exposure; therefore, cellular and molecular markers are appropriate for assessment of the risk of bisphenol exposure. Based on our findings, we speculate that different doses of BPS may have different effects. For example, whereas extremely low doses (BPS1: ~ 0.001 μg BPS/kg bw) affected sperm motility, higher BPS doses (BPS3: ~ 100 μg/kg bw) showed significant effects on testicular tissues. Surprisingly, moderate doses of BPS (BPS2: equal to daily intake of approx. 0.1 μg/kg bw) did not show any effects on spermiogram recording and histological assessment. This finding was consistent with the phenomenon of nonlinear effects [
26], with the lowest dose of BPS (BPS1) inducing motility failure rather compared with the other BPS doses. Therefore, proteome profiling was used to test a wide range of BPS doses and characterise the dose-dependent mode of action.
Because of the lack of effect of BPS on the whole proteome of testicular tissues, protein acetylation and phosphorylation were chosen for further analysis. Although no significant effects were observed in terms of acetylation and phosphorylation of the detected peptides, γH2AX, a mark of DNA damage, was increased in BPS3 testicular tissues, demonstrating the increased occurrence of abnormalities. In sperm lysates, protein acetylation and phosphorylation were detected using specific antibodies against acetylated lysine and phosphorylated tyrosine. The choice of PTMs was consistent with the earlier described biological role of both PTMs in sperm capacitation and fertilisation ability [
14,
27]. Indeed, altered levels of acetylated and phosphorylated proteins were observed after exposure to very-low-dose BPS (BPS1). This finding was presumably associated with decreased motility, resulting in detection of candidate proteins. We can assume that differentially acetylated and/or phosphorylated may be responsible for motility failure, in accordance with the significance of PTMs in major proteins, including phospho-hexokinase-1 [
28] and phospho-outer dense fibre protein-2 [
29]. Decreased phospho-tyrosine signals at 100 kDa suggest a lack of hexokinase-1 activity, which is associated with male infertility [
30]. Our findings supported the mechanism of action of BPA described previously through fertility-related proteins, including protein phosphorylation [
31]. Our study suggested that in addition to phosphorylation, bisphenols altered other PTMs, particularly protein acetylation. However, western blot analysis using anti-acetylated tubulin did not show any decrease, as expected, and other protein targets for acetylation were considered, including ATP synthase and actin, both of which are involved in sperm motility [
32,
33].
Open AccessThis article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit
http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (
http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.
Publisher’s Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.