Peripubertal exposure to low doses of tributyltin chloride affects the homeostasis of serum T,E2, LH,and body weight of male mice

Previous studies have shown that tributyltin could act as an endocrine disruptor in mammals. However, the data on the low‐dose effect of tributyltin in animals are still lacking. The objective of this study was to demonstrate the endocrine disruption induced by low levels of tributyltin chloride (TBTCl) in male KM mice. The animals were treated with 0.05 or 0.5 mg TBTCl/kg body weight/3 days from postnatal days (PNDs) 24 to 45, and killed on PNDs 49 and 84, respectively. Mice treated with 0.5 mg TBTCl/kg exhibited decreased serum and intratesticular testosterone (T) levels on PND 49 and then followed by an obvious recovery on PND 84. Furthermore, mice treated with 0.05 mg TBTCl/kg showed reduced serum 17β‐estradiol (E2) levels on PND 49. However, treatments with TBTCl resulted in a dose‐dependent increase in serum E2 concentration of the mice on PND 84. Administration of TBTCl also decreased levels of serum luteinizing hormone and intratesticular E2 on PND 84. In addition, mice exposed to 0.05 mg/kg TBTCl exhibited an increase in body weight in the late stage of the experiment. These results indicate that treatment with low doses of TBTCl could disturb hormone homeostasis and body weight gain in rodents, and exposure to different levels of TBTCl might have different effects on changing some physiologic parameters. © 2010 Wiley Periodicals, Inc. Environ Toxicol, 2011.     

Long-lasting effects of lindane on mouse spermatogenesis induced by in utero exposure

Long-lasting effects on mouse spermatogenesis induced by prenatal exposure to the insecticide lindane have been investigated by conventional reproductive endpoints complemented by the flow cytometric (FCM) DNA content analysis of testis cells and by the Sperm Chromatin Structure Assay (SCSA). Two lindane dose levels, 15 and 25 mg/kg bw, and diethylstilboestrol (DES, 10 microg/kg bw) as positive control, were administered daily by gavage to pregnant CD1 mice on gestation days (GD) 9-16. Reproductive endpoints were evaluated on F1 male mice on postnatal day (PND) 60; additionally, animals treated with lindane 25 mg/kg per day and DES were examined on PND 100 to evaluate the possible reversibility of the effects. On PND 60, lindane and DES caused a reduction in the sperm head count and concentration, with recovery in older lindane 25 mg/kg per day animals (PND 100). By contrast, the DES group exhibited a greater reduction in the sperm head count on PND 100 than on PND 60. Changes in biochemical parameters in the testes, lactate dehydrogenase-C(4) (LDH-C(4)), and sorbitol dehydrogenase (SDH) activities, were also observed in adult treated F1 mice. Furthermore on PND 60, the FCM analysis revealed changes in the pattern of testicular germ cell distribution, especially in the haploid subcompartment, in the lindane 25 mg/kg per day group. A dose-dependent increase in chromatin abnormalities of the epididymal sperm was also shown by SCSA. These changes recovered on PND 100. Preliminary qualitative examination did not reveal any significant difference in the structure of testicular tissue; however, there were suggestions of a moderate increase in number and size of Leydig cells in both DES- and lindane-treated animals. The partial reversibility of these effects and the lack of structural modification of the testicular tissue as evidenced by histopathologic assessment suggest a functional impairment of sperm production and maturation, possibly associated with changes induced by lindane on factors affecting intratesticular steroidogenesis.     

Effects of n-butylparaben on steroidogenesis and spermatogenesis through changed E2 levels in male rat offspring

Parabens are widely used as antibacterial agents, which are concerned recently in the relationship between the use of parabens and reproductive toxicity. So that reassessment of the risk of parabens is needed. In this study, one of parabens, n-butylparaben (n-BP) was orally administered to pregnant Wistar rats (0, 64, 160, 400 and 1000 mg/kg/day) from gestation day (GD) 7 through postnatal day (PND) 21. Reduced anogenital distance (AGD) and delayed preputial separation (PPS) were observed in the male offspring. The weights of the testes were significantly reduced at PND 21–90. The weights of the epididymides were significantly reduced at all monitoring points, except PND 35. Seminal vesicle weights were significantly reduced on PND 21. Serum testosterone (T) was significantly decreased, especially on PND 49. The levels of 17β-estradiol (E₂) showed an increase at each of the tested points except on PND 180. Serum luteinising hormone (LH) and follicle-stimulating hormone (FSH) levels in the n-BP treated groups were lower on PND 21, 35 and 49 but elevated on PND 90 compared to control levels. n-BP reduced epididymal cauda sperm counts and daily sperm production in a dose-dependent manner; this difference was statistically significant at exposure groups of 400 and 1000 mg/kg/day. The present study strongly suggests that exposure to n-BP in utero and during lactation has adverse effects on the reproductive system in male offspring, with a no observed adverse effect level (NOAEL) of 160 mg/kg/day. To our knowledge, this is the first study that reports increased E₂ levels of male rats following n-BP exposure; we suggest that E₂ levels may be considered as biomarkers for some endocrine disrupting chemicals (EDCs).     

Lonidamine affects testicular steroid hormones in immature mice

The effects on the hypothalamus-pituitary-testicular axis of the well-known antispermatogenic drug lonidamine (LND) has not been elucidated so far. In the present study, the possible changes of the testicular steroid hormones were evaluated in immature mice for a better characterization of the LND adverse effects both in its use as antitumoral agent and male contraceptive. Male CD1 mice were orally treated on postnatal day 28 (PND28) with LND single doses (0 or 100 mg/kg b.w.) and euthanized every 24 h from PND29 to PND32, on PND35 and on PND42 (1 and 2 weeks after the administration, respectively). Severe testicular effects were evidenced in the LND treated groups, including: a) significant testis weight increase, 24 h and 48 h after dosing; b) sperm head counts decrease (more than 50% of the control) on PND29-32; c) damage of the tubule morphology primarily on the Sertoli cell structure and germ cell exfoliation. All these reproductive endpoints were recovered on PND42. At the same time, a significant impairment of the testicular steroid balance was observed in the treated mice, as evidenced by the decrease of testosterone (T) and androstenedione (ADIONE) and the increase of 17OH-progesterone (17OH-P4) on the first days after dosing, while the testicular content of 17beta-estradiol (E2) was unchanged. The hormonal balance was not completely restored afterwards, as levels of T, ADIONE and 17OH-P4 tended to be higher in the treated mice than in the controls, on PND35 and PND42. These data showed for the first time that LND affects intratesticular steroids in experimental animals. However further data are needed both to elucidate the mechanism responsible for the impairment of these metabolic pathways and to understand if the androgens decrease observed after LND administration could be partially involved in the testicular damage.     

Neonatal Exposure to Endocrine Disrupting Chemicals Impairs Learning Behaviour by Disrupting Hippocampal Organization in Male Swiss Albino Mice

Hippocampus is highly susceptible to endocrine disrupting chemicals exposure particularly during the critical phase of brain development. In this study, mice offspring were exposed to endocrine disruptors mancozeb (MCZ) and imidacloprid (IMI) individually (40 mg MCZ and 0.65 mg IMI/kg/day) as well as to their equimixture (40 mg MCZ + 0.65 mg IMI/kg/day) through the diet of lactating mothers from post‐natal day (PND) 1 to PND 28. Half of the randomly selected male offspring were killed at PND 29, and the rest half were left unexposed and killed at PND 63. Brain weight, histology, plasma hormone profile and working memory performance were the various end‐points studied. Brain weight was significantly decreased in the mixture‐exposed group at PND 29, which persisted to PND 63. Total thickness of pyramidal cell layers decreased significantly along with misalignment, shrinkage and degeneration of pyramidal neurons in CA1 and CA3 regions of the IMI and mixture‐exposed groups. The length and branch points of dendrites of pyramidal neurons were decreased significantly in mixture‐exposed group at both PND 29 and PND 63. Dendritic spine density was also reduced in mixture‐exposed group offspring. Testosterone level was significantly decreased only at PND 29, but corticosterone level was increased at both PND 29 and PND 63 in mixture‐exposed offspring. T‐maze task performance revealed significantly increased time duration and reduced path efficiency in mixture‐exposed group offspring. The results thus indicate that pesticide mixture exposure could lead to changes in learning behaviour even at doses that individually did not induce any adverse effect on hippocampal organization.     

Pubertal and early adult exposure to fenvalerate disrupts steroidogenesis and spermatogenesis in mice at adulthood

Fenvalerate, a pyrethroid insecticide used worldwide, has been shown to have a potentially adverse effect on male reproduction. Our earlier study showed that maternal fenvalerate exposure during lactation impaired testicular development in male offspring. In this study, we investigated the effects of pubertal and early adult exposure to fenvalerate on steroidogenesis and spermatogenesis in mice. Male mice were administered fenvalerate (60 mg/kg) by gavage daily from postnatal day 35 (PND35) to PND63. Results showed that sperm count was significantly decreased in fenvalerate‐treated mice. In addition, fenvalerate markedly decreased the layers of spermatogenic cells, disturbed the array of spermatogenic cells and increased the number of apoptotic cells in testes. The adverse effects of fenvalerate on male reproduction seemed to be associated with a decrease in serum and testicular testosterone (T). Although pubertal and early adult exposure to fenvalerate had little effect on the number of Leydig cells in testes, mRNA and protein levels of testicular T biosynthetic enzymes including P450_17α and P450scc were significantly downregulated in fenvalerate‐treated mice. In conclusion, pubertal and early adult fenvalerate exposure induces a deleterious effect on steroidogenesis and spermatogenesis in adulthood. The decreased testicular T synthesis partially contributes to fenvalerate‐induced impairment on spermatogenesis. Copyright © 2010 John Wiley & Sons, Ltd.     

Perinatal exposure to low doses of tributyltin chloride advances puberty and affects patterns of estrous cyclicity in female mice

Tributyltin (TBT), a proven endocrine‐disrupting chemical, is well known to induce imposex in female gastropods. Herein we demonstrate the effects of low doses of tributyltin chloride (TBTCl) on the female offspring of KM mice. Pregnant mice were administered by gavage with 0, 1, 10, or 100 μg TBTCl/kg body weight/day from day 6 of pregnancy through the period of lactation. TBTCl dramatically advanced the age of onset of vaginal opening (VO) and first vaginal estrus, and reduced body weights at VO and first estrus. Furthermore, perinatal treatment with TBTCl significantly reduced the number of days between VO and first estrus. In addition, female offspring from dams exposed to 10 and 100 μg kg^?1 TBTCl exhibited altered patterns of estrous cyclicity in adulthood. In conclusion, perinatal exposure to low doses TBTCl result in early puberty and impaired estrous cyclicity in female mice, which suggest that TBTCl might act as an estrogen agonist or/and a disruptor on hypothalamic–pituitary function in the present study. © 2012 Wiley Periodicals, Inc. Environ Toxicol, 2012.     

Effects of in utero linuron exposure on rat Wolffian duct development

Linuron is an herbicide that displays weak androgen receptor antagonist activity. Male offspring exposed in utero to 50 mg/kg/day linuron often exhibit malformations in Wolffian duct derivatives (i.e. the epididymis and vas deferens). The objectives of this study were to determine the point during the perinatal period that linuron-induced epididymal lesions can be identified, to characterize linuron-mediated perinatal testicular and epididymal pathology, and to determine whether male rat fetuses exposed prenatally to linuron exhibit decreased intratesticular and serum testosterone (T) levels. Pregnant rats were administered corn oil vehicle or linuron by gavage at 0 or 50 mg/kg/day (n = 3 controls, 5-11 linuron-treated dams per time point) from gestation days (GD) 12 to 21 or to termination. Male fetuses or offspring were necropsied on GD 17, 19, and 21, and postnatal days (PND) 7 and 14. Epididymal malformations were not observed in fetuses from linuron-treated dams but were seen in linuron-exposed male offspring on PND 7 and 14. No testicular lesions were observed at any time point. The growth and development of linuron-exposed fetuses were altered, as evidenced by slight decreases in fetal weight and increased levels of immunoreactive proliferating cell nuclear antigen (PCNA) on GD 21. Intratesticular and serum T levels were not decreased in linuron-exposed male fetuses. These findings indicate that the adversely altered adult phenotype following in utero exposure to linuron is very similar to that produced by the antiandrogens di-n-butyl phthalate (DBP) and di(2-ethylhexyl) phthalate (DEHP). However, the absence of testicular lesions or alterations in fetal testosterone levels would suggest that the effect of linuron on the developing Wolffian ducts is distinctly different from DBP or DEHP.     

Chronic exposure to perfluorononanoic acid impairs spermatogenesis,steroidogenesis and fertility in male mice

Perfluoroalkyl acids (PFAAs) are widely used in commercial applications and that they are ubiquitous and persistent in the environment. Perfluorononanoic acid (PFNA), a member of PFAAs, has been detected in human and wildlife. Previous acute exposure studies have shown the adverse effect of PFNA on the testis. The present study was aimed to examine the effect of chronic PFNA exposure, from prepuberty to adulthood, on testicular functions and fertility in Parkes (P) male mice and to investigate the possible mechanism(s) of its action. PFNA (0.2 and 0.5 mg/kg) was orally administered to P male mice for 90 days from prepuberty (postnatal day [PND] 25) to adulthood (PND 114). Histologically, testes in PFNA‐treated mice showed non‐uniform degenerative changes in the seminiferous tubules. The treatment also had adverse effects on testicular expression of steroidogenic markers, serum levels of cholesterol and testosterone, sperm parameters and on litter size. A marked increase in the level of lipid peroxidation and decrease in the activities of antioxidant enzymes were observed in the testis of PFNA‐treated mice compared to controls. Further, a significant decrease in expression of proliferating cell nuclear antigen (PCNA) and in the number of PCNA‐positive cells, and an increase in expression of caspase‐3 were also noted in PFNA‐treated mice testis. In conclusion, the results suggest that chronic exposure to PFNA in male mice interferes with testosterone biosynthesis and causes oxidative stress in the testis, leading to alterations in spermatogenesis, sperm quality and fertility potential.     

Effects of bisphenol A given neonatally on reproductive functions of male rats

Male Sprague-Dawley rats (Crj:CD (IGS) were treated neonatally with bisphenol A (BPA) to evaluate effects on reproductive parameters. Animals were given BPA subcutaneously in corn oil to dosages of 0.002-97 mg/kg body weight, or 0.9 mg/kg 17beta-estradiol (E2) once a day from postnatal day (PND) 0 to PND 9. Preputial separation, copulatory rate, fertility rate, sperm analysis, serum testosterone levels, and gene expression in the testis were assessed. Males in the E2 group showed a decrease in testis weight and alterations of estrogen-mediated gene expression in the testis on PND 10, and by PND 150 incomplete preputial separation, decreases in the copulatory rate, testicular and accessory organ weights and number of sperm. In contrast, males in all BPA groups showed normal reproductive parameters. These results indicate that in male rats, BPA given during the neonatal period neither affected reproductive function nor evoked estrogen-mediated gene responses in the testis.     

Effect of human dietary exposure levels of genistein during gestation and lactation on long-term reproductive development and sperm quality in mice.

The objective of the present study was to determine the long-term reproductive effects of gestational and lactational exposure (0, 0.1, 0.5, 2.5 and 10 mg/kg/day) to genistein on male mice at levels comparable to or greater than human dietary exposures. Testicular growth, sperm count and motility, and sperm fertilizing ability in vitro was assessed in male offspring on postnatal days (PND) 105 and 315. Selected genes were also examined by real-time PCR to determine whether genistein caused changes in gene expression similar to those previously observed with diethylstilbestrol (DES). No significant treatment-related effects on male offspring body weight, anogenital distance, seminal vesicle weight or testis weight were observed. There were also no significant effects on sperm count, the percent of motile sperm or the number of motile sperm at any age. The in vitro fertilizing ability of epididymal sperm was increased significantly in the high-dose group approximately 17% (P < 0.001) on PND 105 and 315. The results indicate that developmental exposure of mice to genistein at human exposure levels does not induce adverse effects on sperm quality or changes in testicular gene expression similar to DES.     

Neonatal lead exposure changes quality of sperm and number of macrophages in testes of BALB/c mice

BALB/c mice were exposed to 0.1 ppm lead acetate in the drinking water from postnatal day (PND) 1 for 6 weeks. Until PND21, lead exposure was from mother's milk; thereafter, it was directly from the drinking water. The blood lead levels were the highest in pups before weaning (59.5 ± 0.9 μg/dL) and significantly lower between PND21 and PND42 (20.3 ± 4.7 μg/dL). At PND42, lead-exposed male mice were tested for fertility, sperm DNA, and macrophage number. Mating of lead-treated males with non-treated females confirmed the reduction of fertility in the exposed males. Flow cytometric studies of testicular preparations indicated that the sperm count was not different between lead-exposed and control males; however, the lead-treated mice had a significant increase in the number of testicular cells having a <1n amount of DNA, which coincided with a decrease in the number of testicular cells with a 2n and 4n amount of DNA. The number of testicular macrophages also was decreased in lead-exposed males, which could reflect altered levels of CSF-1 or response to CSF-1, as previously reported [Kowolenko, M., Tracy, L., Lawrence, D.A., 1989. Lead-induced alterations of in vitro bone marrow cell responses to colony stimulating factor-1. J. Leukoc. Biol. 45, 198–206]. Our study showed that exposure to 0.1 ppm of lead during the neonatal and adolescent period is sufficient to reduce fertility in adult male mice; however, it did not affect sperm count on PND42. The presence of an increased number of apoptotic (<1n amount of DNA) testicular cells may be diagnostic of defective sperm function. Thus, an administered dose of 0.1 ppm via drinking water ingestion by neonatal male BALB/c mice sufficient to produce PbB of 20–60 mg/dL compromised reproductive function in these mice as adults.     

The adverse effects of low‐dose exposure to Di(2‐ethylhexyl) phthalate during adolescence on sperm function in adult rats

Di(2‐ethylhexyl) phthalate (DEHP) is the most crucial phthalate derivative added to polyvinyl chloride as a plasticizer. This study examined the effects of low‐dose exposure to DEHP during adolescence on sperm function in adult rats. The male rats were daily gavaged with 30, 100, 300, and 1000 µg kg^?1 of DEHP or corn oil from postnatal day (PND) 42 until PND 105. The selection of DEHP doses ranged from the mean daily intake by the normal‐population exposure levels to no‐observed‐adverse‐effect level of DEHP for the endpoints evaluated until adulthood. Significant increases in the percentage of sperm with tail abnormality, tendency for sperm DNA fragmentation index (DFI) and percentage of sperm with DFI were found in those exposed to 100, 300, and 1000 µg kg^?1 (P < 0.05). We observed a significant increase of hydrogen peroxide (H₂O₂) generation in the sperm of the 1000 µg kg^?1 group compared with the control group (P < 0.05). The excessive production of sperm H₂O₂ coincided with an increase in sperm DFI. In this study, the lowest‐observed‐adverse‐effect level for sperm toxicity was considered to be 100 µg DEHP/kg/day in sperm morphology and chromatin DNA damage. Further research is necessary to clarify the mechanisms of DEHP‐related sperm ROS generation on sperm DNA damage. © 2014 Wiley Periodicals, Inc. Environ Toxicol 31: 706–712, 2016.     

Gestational and lactational exposure to ethinyl estradiol, but not bisphenol A, decreases androgen-dependent reproductive organ weights and epididymal sperm abundance in the male long evans hooded rat.

Many chemicals released into the environment are capable of disrupting normal sex steroid balance, including the oral contraceptive ethinyl estradiol (EE) and the plastic monomer bisphenol A (BPA). EE and BPA are reported to impair reproductive organ development in laboratory animals; however, effects of lower doses of these chemicals have been debated. The goal of the current study was to determine whether relatively low oral doses of EE or BPA would alter male reproductive morphology and associated hormone levels of Long Evans hooded rat. Dams were gavaged with corn oil vehicle, EE (0.05-50 mug/kg/day) or BPA (2, 20, and 200 mug/kg/day) during pregnancy through lactation from gestational day 7 to postnatal day (PND) 18. Anogenital distance was measured at PND2 and nipple retention was measured at PND14 in male pups. Male offspring were euthanized beginning at PND150, and sera and organs were collected for analyses. Adult body weight was significantly decreased in males exposed to 50 mug EE/kg/day. Developmental EE exposure reduced androgen-dependent tissue weights in a dose-dependent fashion; for example, seminal vesicle and paired testes weights were reduced with >/= 5 mug EE/kg/day. Epididymal sperm counts were also significantly decreased with 50 mug EE/kg/day. In contrast, treatment with 2, 20, or 200 mug BPA/kg/day or EE at 0.05-1.5 mug/kg/day did not significantly affect any male endpoint in the current study. These results demonstrate that developmental exposure to oral micromolar doses of EE can permanently disrupt the reproductive tract of the male rat.     

Continuous exposure to dibromoacetic acid delays pubertal development and compromises sperm quality in the rat.

Previously our work on the haloacid by-products of drinking water disinfection focused on adult exposures. Herein we evaluate the consequence of continuous exposure to dibromoacetic acid (DBA) via drinking water through reproductive development into adulthood. An initial study in which offspring were exposed from gestation day (GD) 15 through adulthood revealed significant delays in preputial separation and vaginal opening, dose-related decreases in the fertility of cauda epididymal sperm, and dose-related diminutions in the sperm membrane protein SP22. Subsequent studies consisted of groups in which exposure ceased on postnatal day 21 (PND 21) versus adulthood. For each exposure, animals were evaluated after puberty (PND 56) as well as at adulthood (PND 120). Exposure to 4, 40, or 400 ppm DBA from GD 15 through PND 21 failed to result in any significant reproductive alterations. By contrast, continuous exposure until adulthood resulted in dose-related alterations consistent with those observed in the dose-finding study. Preputial separation and vaginal opening were delayed 4 and 3 days in males and females exposed to 400 ppm (76.3 mg/kg) DBA. This was associated with increased responsiveness of both the testis and ovary to hCG ex vivo; hCG-stimulated testosterone production by testicular parenchyma on PND 56 was increased at 4 ppm (0.6 mg/kg) DBA and higher. Finally, the quality of proximal cauda epididymal sperm was compromised by continuous exposure to DBA. The sperm membrane proteome was altered in a dose-related manner with SP22, and one of its charged variants, diminished at 40 ppm (3.6 mg/kg) DBA and higher. As more sensitive endpoints are evaluated, lower effect levels can be attributed to haloacid exposure. We are now extending our evaluations to epidemiology studies designed to evaluate sperm quality in men exposed to varying levels of disinfection by-products.     

Effects of perinatal exposure to low doses of tributyltin chloride on pregnancy outcome and postnatal development in mouse offspring

Tributyltin (TBT), an endocrine‐disrupting chemical, is well known to induce imposex in female gastropods. In this study, we assessed the effects of low doses of tributyltin chloride (TBTCl) on dams and their offspring. Pregnant mice were administered by gavage with 0, 1, 10, or 100 μg TBTCl/kg body weight/day from day 6 of pregnancy through the period of lactation. There were no TBT treatment‐related deaths or clinical signs of toxicity for dams, and no treatment‐related effects on body weight, litter sizes, gestational length of dams, and sex ratio, lactational body weight, postnatal survival, age at eruption of incisors, and eye opening of pups. However, at 100 μg/kg, TBTCl retarded the testes descent of male offspring. Behavioral tests showed a significant delay in cliff‐drop aversion response in offspring of 10 and 100 μg/kg groups, but no significant difference in the righting reflex between control and TBT‐exposed offspring was detectable. These results indicate that neurobehavioral toxicity seems to be one sensitive indicator to assess the risk of low doses of TBT. © 2011 Wiley Periodicals, Inc. Environ Toxicol, 2012.     

Differential mRNA expression of neuroimmune markers in the hippocampus of infant mice following toluene exposure during brain developmental period

Toluene, a volatile organic compound with a wide range of industrial applications, can exert neurotoxic and immunotoxic effects. However, the effects of toluene exposure on developmental immunotoxicity in the brain have not yet been characterized. To investigate the susceptible window to toluene exposure during development and the effects of fetal and neonatal toluene exposure on the neuroimmune markers, gestational day (GD) 14 pregnant mice, postnatal day (PND) 2 and PND 8 male offspring were exposed to filtered air (control; 0 ppm), or 5 or 50 ppm toluene for 6 h per day for five consecutive days. The neuroimmune markers in the hippocampus of PND 21 were examined using a real‐time RT‐PCR and immunohistochemical analysis. Mice exposed to 50 ppm toluene on PND 2–6 showed significantly increased levels of nerve growth factor (NGF) and tumor necrosis factor (TNF)‐α mRNAs. In contrast, NGF and brain‐derived neurotrophic factor (BDNF) and proinflammatory cytokines TNF‐α, CCL3, NF‐κB, toll‐like receptor (TLR)‐4, astrocyte marker glial fibrillary acidic protein (GFAP), and microglia marker ionized calcium binding adapter molecule (Iba)‐1 mRNAs were increased significantly in mice exposed to 5 ppm toluene on PND 8–12. These results indicate that low‐level toluene exposure during the late postnatal period (PND 8–12) might induce neuroinflammatory mediators via TLR4‐dependent NF‐κB pathway in the hippocampus of PND 21 male mice. Among the three developmental phases, PND 8–12 seems to be most sensitive to toluene exposure. This is the first study to show developmental phase‐ and dose‐specific changes in neuroimmune markers in infant mice following toluene exposure. Copyright © 2011 John Wiley & Sons, Ltd.     

Toxic effects of lactational exposure to 2,3,7,8‐tetrachlorodibenzo‐p‐dioxin (TCDD) on development of male reproductive system: Involvement of antioxidants,oxidants, and p53 protein

2,3,7,8‐Tetrachlorodibenzo‐p‐dioxin (TCDD) is a potent endocrine disruptor compound and induces multiple organ dysfunctions. The effect of TCDD exposure both in adults and in utero has been well established. However, little is known about the effects of TCDD acquired through mother's milk on the development of the male reproductive system. The aim of this study was to investigate the effects and mechanisms of TCDD from lactational exposure. TCDD (1 μg/kg) was administered to C57BL/6 mouse mothers for 4 days from the day of delivery. On postnatal day 30 (PND 30) and postnatal day 60 (PND 60), body weight, body length, and anogenital distance (AGD) of male offspring were measured. The weights of the testes and epididymides were also measured. Epididymides were used for sperm counts, and testes were used to measure the activity of antioxidant enzymes (SOD, CAT, GPX, GR), the parameters of oxidative stress (hydrogen peroxide, MDA), and testosterone. In addition, expression of p53 and the proapoptotic protein, Bax, were analyzed by Western blot. TCDD exposure decreased body weight, body length, and AGD in both PND 30 and PND 60 groups compared with the control group. The activity of all antioxidant enzymes at PND 60 was decreased after TCDD treatment. TCDD treatment decreased testicular testosterone levels in both the PND 30 and PND 60 groups. The expression of p53 and Bax were also upregulated by TCDD and did not return to normal levels by PND 60. These data suggest that TCDD affects development of male offspring when the mother is exposed to TCDD during lactation. In addition, oxidative stress is a major mediator of TCDD‐induced adverse effects, and p53 may play an important role in this mechanism. © 2008 Wiley Periodicals, Inc. Environ Toxicol, 2010.     

Phytoestrogens alter the reproductive organ development in the mink (Mustela vison)

The aim of the present study was to examine the reproductive effects of two perorally applied phytoestrogens, genistein (8 mg/kg/day) and beta-sitosterol (50 mg/kg/day), on the mink (Mustela vison) at human dietary exposure levels. Parental generations were exposed over 9 months to these phytoestrogens and their offspring were exposed via gestation and lactation. Parents and their offspring were sampled 21 days after the birth of the kits. Sex hormone levels, sperm quality, organ weights, and development of the kits were examined. The exposed females were heavier than the control females at the 1st postnatal day (PND). The control kits were heavier than the exposed kits from the 1st to the 21st PND. Phytoestrogens did not affect the organ weights of the adult minks, but the relative testicular weight of the exposed kits was higher than in the control kits. The relative prostate weight was higher and the relative uterine weight lower in the beta-sitosterol-exposed kits than in the control kits. Moreover, the plasma dihydrotestosterone levels were lower in the genistein-exposed male kits compared to the control male kits. This study could not explain the mechanisms behind these alterations. The results indicate that perinatal phytoestrogen exposures cause alterations in the weight of the reproductive organs of the mink kits.