Abstract:
Background: Bisphenols are widely used in manufacturing polycarbonate plastic, plastic toys
and food containers. One of these bisphenols, bisphenol A (BPA) is the major component of
baby bottles, dental sealants, epoxy resins and food packaging has been well documented for
its hazardous and estrogenic mode of action. In many countries, BPA has been banned in some
applications and has been replaced by bisphenol S (BPS). However, nearly similar estrogenic
potential of BPS to BPA has been reported in different studies. It has been detected in food,
receipt papers and in water. Humans are prone to its exposure through dermal exposure and
dietary food intake. An increase in the concentrations of BPS has been detected from 2010 to
2014 in human body fluids, suggesting the possibility of increased exposure to BPS in daily
life. BPS has shown estrogenic mode of action, oxidative stress inducing potential, obesogenic
effect as well as anti-androgenic effects in vitro. In the in vivo studies, BPS exhibited antiandrogenic
effect in male zebra fish, decreased gonadosomatic index in female fish and
affected endocrine functions. Similarly, BPS concentrations have been linked to the oxidative
stress in the humans, however, in mammalian reproductive system; data regarding BPS toxicity
is limited. In present studies, we first assessed in vitro effect of BPS on testicular tissues and
sperm. Secondly, we aimed to evaluate whether sub-chronic and chronic exposure of BPS can
modulate reproductive functions of male rats in vivo. Lastly, the potential effect of BPS on
gonadal development of male rats exposed during pre-natal and neonatal periods were
evaluated.
Materials and methods: Stock solution of BPS was prepared by dissolving 0.5 g in 5 mL of
ethanol and was further diluted with media/water to the final concentration of less than 0.5%
ethanol in the media/water. In order to attain the first goal, testicular tissues and sperm from
adult rats were incubated with media alone or in combination with different concentrations
(0.5, 1, 10 and 100 μg/L) of BPS for two hours in 5% CO2 and 95% air at 37 0C. Testicular
testosterone concentration was determined through Enzyme Linked Immuno Sorbant assay
(ELISA), while testicular tissue and sperm oxidative stress was determined through estimation
of antioxidant enzymes activity, lipid peroxidation (LPO) and generation of reactive oxygen
species. To achieve the second goal, adult male rats were treated with different concentrations
(1 - 50 μg/kg/day) of BPS through oral gavage for 28 days. Secondly, male rats (22 days old)
were provided with water containing different concentrations of BPS (0.5, 5 and 50 μg/L) for
a period of 48 weeks in water. Animals were killed by cervical dislocation; blood was collected
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and was used for determination of different hormones in the plasma while testicular and
epididymis tissues were used for histology, oxidative stress determination and evaluation of
different parameters of sperm. In the next set of experiments, effect of BPS on the development
of male gonads was assessed by exposing the animals to different concentrations of BPS during
pre-natal and neonatal period of development. In the pre-natal exposure study, pregnant female
rats were provided with water containing 0 and 0.5 - 50 μg/L of BPS. The pups born were
assessed for alteration in the early sexual development and reproductive functions during adult
hood. In the neonatal exposure study, male pups were subcutaneously injected with different
concentrations of BPS (0.5 - 50 mg/kg.day in 50 μL castor oil) from post-natal day 1 to 10 and
were followed in the adulthood for alterations in the reproductive functions. Plasma hormones
levels, histological changes and alteration in the sperm parameters were determined and
compared with the control.
Results: In the in vitro exposure study, oxidative stress in the testis and sperm was enhanced
along with the increase in antioxidant enzymes activity. At the highest concentration, BPS
induced formation of reactive oxygen species, caused lipid peroxidation, affected superoxide
dismutase levels, and increased DNA fragmentation in the rat spermatozoa. Similarly, BPS
induced reduction in the testosterone secretion by the testis at highest concentrations tested. On
the other hand, in the in vivo sub-chronic and chronic exposure study, testicular reactive oxygen
species (ROS) and lipid peroxidation (LPO) were significant increase in the higher doses tested
while antioxidant enzymes activity were significantly reduced. Sub-chronic exposure for 28
days reduced plasma and intra-testicular testosterone, plasma luteinizing hormone (LH) and
follicle stimulating hormone (FSH) concentrations were suppressed in the groups treated with
higher doses of BPS. Testicular morphology revealed thin seminiferous epithelium in the
treated groups than control. In the epididymis, area of the tubular epithelium showed significant
reduction and empty lumen were observed in the groups treated with higher concentrations of
BPS. Chronic exposure of male rats to different concentrations of BPS showed a significant
alteration in the gonadosomatic index (GSI) and relative reproductive organs weights.
Oxidative stress in the testis was significantly elevated while sperm motility, daily sperm
production (DSP) and number of sperm in epididymis were reduced. Plasma testosterone, LH
and FSH concentrations were reduced and estradiol levels were high in 50 μg/L exposed
groups. Histological observations included significant reduction in the epithelial height of the
testis along with disrupted spermatogenesis. Other prominent observations were empty lumen
of the seminiferous tubules and caput region of the epididymis.
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Pre-natal exposure to different concentrations of BPS induced no significant alteration in early
sexual development as well as in adulthood of male rats. Body weight gain, Ano-genital
distance (AGD), nipple retention (NR) and organs weight exhibited no change. However,
exposure to different concentrations of BPS in the neonatal stage resulted significant decrease
in GSI and relative organs weights in BPS 5 and BPS 50 mg/kg.day treated groups as compared
to the control. Slight delay in puberty onset in the highest dose treated group was noted but this
delay was not different than control. Hormonal analysis showed a significant reduction in
testosterone and significant elevated levels of estradiol was observed in the treated groups
compared to the control. Histological alterations included reduction in epithelial height and
diameter of the seminiferous tubules and spermatids arrest. Reduction in the DSP and sperm
number in the caput was observed in the highest dose treated group than control.
Conclusion: In conclusion, BPS can not only induce oxidative stress in the sperm and testis in
vitro but can also exert its toxicological and endocrine disrupting potential in vivo. Beside its
effect in adult animals, exposure to higher concentrations to BPS during neonatal stage of
development imparts adverse alterations in the reproductive tissues of male rats. BPS exposure
exert its effects by inhibiting cell defense system, inducing ROS and LPO which results in
adverse structural and functional changes in the reproductive system. These changes are more
prominent and long lasting when the animals are exposed in early stages of life especially
during the neonatal stage of development. These affects seems to be accompanied by
gonadotropin suppression, estrogenic and antiandrogenic effects of BPS, which ends up with
the deleterious alterations in the testis of rats that can lead into infertility.