[Role of autophagy in cadmium-induced damage to the blood-testis barrier in mice].

OBJECTIVE: To investigate the role of autophagy in cadmium chloride (CdCl2)-induced damage to the blood-testis barrier (BTB) in mice. METHODS: Twenty four-week-old male C57BL/6 mice were randomly divided into four groups and intraperitoneally injected with CdCl2 at 0 mg/kg/d (the control), 0.5 mg/kg/d (low-dose), 1.0 mg/kg/d (medium-dose) and 2.0 mg/kg/d (high-dose) respectively for 28 consecutive days. Then the morphological changes of the testis tissue was observed by HE staining, the integrity of BTB measured with the biotracer, and the expressions of the BTB components ZO-1 and N-Cadherin proteins detected by Western blot. The TM4 Sertoli cells were treated with CdCl2at 0, 2.5, 5 and 10 µmol/L respectively for 24 hours, followed by determination of the expression levels of ZO-1 and N-Cadherin as well as the autophagy-related proteins LC3II and p62. Then the cells were again treated with CdCl2 in the presence of the autophagy inhibitor chloroquine (CQ) at 5 µmol/L or the autophagy inducer rapamycin (Rap) at 50 nmol/L for 24 hours, followed by measurement of the expressions of LC3II, p62, ZO-1 and N-Cadherin by Western blot. RESULTS: Compared with the control group, the cadmium-exposed mice showed increased interstitial space in the seminiferous tubules, formation of intracellular cavitation in the germ cells with decreased layers and disordered arrangement, and damaged integrity of the BTB. The expressions of the ZO-1 and N-Cadherin proteins were significantly down-regulated in the testis tissue of the mice in the medium- and high-dose CdCl2 groups (P < 0.05), and even more significantly in the CdCl2-exposed cells in comparison with those in the control mice (P < 0.01), while the expressions of the LC3II and p62 proteins were remarkably up-regulated (P < 0.05). The expressions of ZO-1, N-Cadherin, LC3II and p62 were also up-regulated in the cells co-treated with CQ and CdCl2 (P < 0.01), those of ZO-1, N-Cadherin and p62 down-regulated (P< 0.05) and that of LC3II up-regulated (P < 0.05) in the cells co-treated with Rap and CdCl2. CONCLUSION: CdCl2 can damage the integrity of the mouse BTB, which may be attributed to its ability to enhance the autophagy in Sertoli cells and regulate the expressions of BTB proteins.

[Effect of autophagy in cadmium chloride induced apoptosis of mouse spermatogenic cells].

OBJECTIVE: To study the effect of autophagy in cadmium chloride(CdCl_2)-induced apoptosis of mouse spermatocytes(GC-2 spd) cells and explore the underlying molecular mechanisms. METHODS: The cells were treated with different concentrations of CdCl_2(0, 5 and 10 µmol/L) for 24 h. Hoechst33342 staining and monodansylcadaverine(MDC) were performed to explore the formation of autophagosomes and apoptotic bodies. The apoptosis of cadmium-treated cells was examined by TUNEL staining. Autophagy inhibitor 3-methyladenine(3-MA)(60 µmol/L), apoptotic inhibitorCaspase inhibitor Z-VAD-FMK( zVAD-FMK)(50 nmol/L), autophagy inducer rapamycin(RAPA)(50 nmol/L) and lysosomal inhibitor chloroquine(CQ)(10 µmol/L) were added to cell culture in the presence/absence of CdCl_2(10 µmol/L) to treat GC-2 spd cells for 24 h. The expression levels of autophagy-related proteins LC3, P62, and pro-apoptotic proteins cleaved Caspase-3 and cleaved Caspase-9 were examined by Western blot. RESULTS: Autophagosomes aggregated and the number of apoptotic cells increased after exposure to CdCl_2 for 24 h. Western blot result showed that in the 5 and 10 µmol/L CdCl_2 exposure groups, the protein expression levels of LC3II/LC3I increased to 9.23±0.81 and 12.15±0.80 compared with the control group(5.50±0.56)(P<0.05), LC3II protein expression level increased to 3.35±0.14 and 3.47±0.32 compared with the control group(2.35±0.34)(P<0.05), P62 protein expression level increased to 1.48±0.12 and 1.80±0.22 compared with the control group(0.83±0.09)(P<0.05). Compared with the CdCl_2-treated group, the protein expression levels of LC3II/LC3I, LC3II, P62, cleaved Caspase-9 and cleaved Caspase-3 after 3-MA treatment decreased to 0.90±0.07(CdCl_2 group: 1.47±0.06), 1.57±0.14(CdCl_2 group: 2.45±0.29), 0.82±0.05(CdCl_2 group: 1.44±0.18), 0.18±0.01(CdCl_2 group: 0.28±0.01) and 0.61±0.84(CdCl_2 group: 1.15±0.04)(P<0.05). Compared with the CdCl_2-treated group, the protein expression levels of cleaved Caspase-9 and cleaved Caspase-3 after zVAD-FMK treatment decreased to 0.12±0.01(CdCl_2 group: 0.28±0.01) and 0.34±0.01(CdCl_2 group: 1.15±0.04)(P<0.05), while those of LC3II/LC3I, LC3II and P62 had no significant change(P>0.05). Compared with the CdCl_2-treated group, RAPA enhanced cadmium-induced LC3II/LC3I, LC3II and P62 protein expressions to 2.22±0.21(CdCl_2 group: 1.56±0.06), 3.72±0.21(CdCl_2 group: 2.97±0.15) and 2.41±0.19(CdCl_2 group: 1.52±0.35)(P<0.05). Western blot result showed that compared with the CdCl_2 group, the protein expressions of LC3II/LC3I, LC3II, P62 and cleaved Caspase-3 in the CdCl_2 and CQ treatment groups increased to 3.21±0.31(CdCl_2 group: 2.09±0.25), 4.49±0.43(CdCl_2 group: 2.72±0.26), 2.59±0.19(CdCl_2 group: 1.84±0.19) and 2.43±0.23(CdCl_2 group: 1.50±0.27)(P<0.05). CONCLUSION: Cadmium chloride induces apoptosis of mouse spermatocyte cells by inhibiting autophagosome-lysosomal fusion and prompting abnormal aggregation of autophagosomes.

[Effect of reactive oxygen species in cadmium chloride induced apoptosis of mouse Leydig cells].

OBJECTIVE: To study the effect of reactive oxygen species(ROS) in cadmium chloride-induced apoptosis of mouse Leydig cells(TM3 cells) and explore the underlying molecular mechanisms. METHODS: TM3 cells were used as an in vitro model for studying reproductive toxicity induced by cadmium exposure. The cells were treated with different concentrations of CdCl_2(0, 5 and 10 µmol/L) for 24 h. CCK-8 assay was used to detect the effect of CdCl_2 on TM3 cell activity. Hoechst33342 staining was performed to explore the formation of apoptotic bodies. DCFH-DA probe was used to detect the level of ROS in the cells. TM3 cells were pretreated with 1 mmol/L NAC for 1 h and then treated with 10 µmol/L CdCl_2 for 24 h. The protein expression levels of pro-apoptotic proteins Caspase-9 and cleaved Caspase-3 were detected by Western blot; RT-qPCR was used to measure the expression of anti-apoptotic gene Bcl-2 and pro-apoptotic genes Caspase-9 and Caspase-3. RESULTS: After exposure to CdCl_2 for 24 h, viability of TM3 cells decreased and the number of apoptotic bodies increased. Western blot result showed that the protein level of Caspase-9 in the 10 µmol/L CdCl_2 treatment group was increased to 0.86±0.10(P<0.05) compared with the control group(0.56±0.07). Compared with the control group(0.37±0.11), the protein level of cleaved Caspase-3 in the 5 and 10 µmol/L CdCl_2 treatment groups were increased to 0.65±0.03 and 1.05±0.13(P<0.05). Compared with the control group(46.80±1.24), the intracellular ROS content in the 5 and 10 µmol/L treatment groups increased to 60.47±1.39 and 80.63±1.34(P<0.05). Compared with the cadmium-treated group, NAC inhibited Caspase-9(CdCl_2 group: 0.89±0.07; CdCl_2+NAC group: 0.28±0.02)and cleaved Caspase-3(CdCl_2 group: 1.53±0.21; CdCl_2+NAC group: 0.66 ±0.07), the difference was statistically significant(P<0.05). At the same time, NAC decreased the ROS level(62.64±0.93) in the CdCl_2 exposure group(80.13±0.94)(P<0.05). In addition, RT-qPCR result showed that the Caspase-9 mRNA levels in the 5 and 10 µmol/L CdCl_2 treatment groups were 1.40±0.14 and 1.90±0.12(P<0.05), compared with the control group(0.97±0.10). Compared with the control group(0.88±0.08), the cleaved Caspase-3 mRNA levels in the 5 and 10 µmol/L CdCl_2 treatment groups were increased to 1.42±0.11 and 1.59±0.12(P<0.05). While in the 5 and 10 µmol/L CdCl_2-treated group, compared with the control group(0.94±0.02), the Bcl-2 mRNA level were decreased to 0.60±0.02 and 0.50±0.09(P<0.05). Compared with the cadmium treatment group(0.57±0.06), NAC could significantly improve the cadmium-induced Bcl-2 mRNA expression level(0.92±0.03), and Caspase-9(CdCl_2 group: 1.96±0.07; CdCl_2+NAC group: 1.04±0.02) and Caspase-3(CdCl_2 group: 1.65±0.02; CdCl_2+NAC group: 0.66±0.04) were decreased(P<0.05). CONCLUSION: The Caspase cascade in mouse Leydig cells can be activated by excessive ROS induced by CdCl_2, and inhibition of ROS production can significantly reduce the CdCl_2-induced apoptosis of TM3 cells.

Cadmium-induced apoptosis of Leydig cells is mediated by excessive mitochondrial fission and inhibition of mitophagy.

Cadmium is one of the environmental and occupational pollutants and its potential adverse effects on human health have given rise to substantial concern. Cadmium causes damage to the male reproductive system via induction of germ-cell apoptosis; however, the underlying mechanism of cadmium-induced reproductive toxicity in Leydig cells remains unclear. In this study, twenty mice were divided randomly into four groups and exposed to CdCl2 at concentrations of 0, 0.5, 1.0 and 2.0 mg/kg/day for four consecutive weeks. Testicular injury, abnormal spermatogenesis and apoptosis of Leydig cells were observed in mice. In order to investigate the mechanism of cadmium-induced apoptosis of Leydig cells, a model of mouse Leydig cell line (i.e. TM3 cells) was subjected to treatment with various concentrations of CdCl2. It was found that mitochondrial function was disrupted by cadmium, which also caused a significant elevation in levels of mitochondrial superoxide and cellular ROS. Furthermore, while cadmium increased the expression of mitochondrial fission proteins (DRP1 and FIS1), it reduced the expression of mitochondrial fusion proteins (OPA1 and MFN1). This led to excessive mitochondrial fission, the release of cytochrome c and apoptosis. Conversely, cadmium-induced accumulation of mitochondrial superoxide was decreased by the inhibition of mitochondrial fission through the use of Mdivi-1 (an inhibitor of DRP1). Mdivi-1 also partially prevented the release of cytochrome c from mitochondria to cytosol and attenuated cell apoptosis. Finally, given the accumulation of LC3II and SQSTM1/p62 and the obstruction of Parkin recruitment into damaged mitochondria in TM3 cells, the autophagosome-lysosome fusion was probably inhibited by cadmium. Overall, these findings suggest that cadmium induces apoptosis of mouse Leydig cells via the induction of excessive mitochondrial fission and inhibition of mitophagy.

[Impact of Cadmium on the expressions of piRNAs in the rat testis].

OBJECTIVE: To study the impact of cadmium (Cd) on the expressions of PIWI-interacting RNAs (piRNA) in the rat testis and its possible action mechanism. METHODS: Twelve 6-week-old SD rats were randomly divided into a Cd-exposure and a control group, the former gavaged with CdCl2 at 3 mg/kg/d and the latter with normal saline, all for 28 successive days. Then the testicular tissues were collected from the rats, sperm concentration and motility were obtained by computer-assisted sperm analysis (CASA), and piRNA sequencing was performed using the gene chip, followed by bioinformatics analysis of differentially expressed piRNAs. RESULTS: Compared with the controls, the rats in the Cd-exposure group showed significantly decreased sperm concentration and motility (P < 0.05). The expressions of 272 piRNAs were up-regulated and 402 down-regulated after 28 days of Cd exposure, and 4 of the up-regulated piRNAs were consistent with the results of gene chip verification. Bioinformatics analysis showed that the 4 up-regulated piRNA target genes were involved in 50 biological processes, such as negative regulation of apoptosis, positive regulation of gene expression and positive regulation of GTPase activity, and mainly concentrated in 13 signaling pathways including transcription dysregulation, calcium and mitogen-activated protein kinase signaling pathways in cancer. Among them, PIRNA-DQ765261 had a binding site with Bcl-2. CONCLUSION: Cadmium can induce changes in the expressions piRNAs in the rat testicular tissue, and some piRNAs may be involved in the autophagy and apoptosis of sperm. Bcl-2 may be the target of PIRNA-DQ765261.

Reproductive toxicity of cadmium in pubertal male rats induced by cell apoptosis.

Cadmium (Cd) is a heavy metal that is widely present in modern industrial production. It is a known, highly toxic environmental endocrine disruptor. Long-term exposure to Cd can cause varying degrees of damage to the liver, kidney, and reproductive system of organisms, especially the male reproductive system. This study aimed to explore the mechanism of Cd toxicity in the male reproductive system during puberty. Eighteen healthy 6-week-old male Sprague-Dawley rats were randomly divided into three groups (control group, low-dose group, and high-dose group) according to their body weight, with six in each group. Cd (0, 1, and 3 mg/kg/day) was given by gavage for 28 consecutive days. The results showed that Cd exposure to each dose group caused a decrease in the testicular organ coefficient and sperm count, compared with the control group. Cd exposure resulted in significant changes in testicular morphology in the 3 mg/kg/day Cd group. In the 1 and 3 mg/kg/day Cd groups, serum testosterone decreased and apoptosis of testicular cells increased significantly (p < 0.05). In addition, compared with the control group, the activity of glutathione peroxidase and superoxide dismutase in each Cd exposure dose group decreased, but the content of malondialdehyde in the high-dose, 3 mg/kg/day Cd treatment group significantly increased (p < 0.05). Although Cd exposure caused an increase in the messenger RNA (mRNA) levels of Bcl-2, Caspase-3 and Caspase-9 in the testicular tissues (p < 0.05), Bcl-2 expression was unchanged (p > 0.05). The expression level of Akt mRNA in testicular tissue of rats in the high-dose 3 mg/kg/day Cd group was increased (p < 0.05). Our data suggest that Cd affected testosterone levels, and apoptosis was observed in spermatids.

The role of STAT3/p53 and PI3K-Akt-mTOR signaling pathway on DEHP-induced reproductive toxicity in pubertal male rat.

Di (2-ethylhexyl) phthalate (DEHP) is a known environmental endocrine disruptor that impairs development of testis and spermatogenesis. This study aims to explore the effects of STAT3/p53 and PI3K-Akt-mTOR signaling pathway on DEHP-induced reproductive toxicity in pubertal male rat. 24 6-week-old male Sprague-Dawley rats were randomly divided into 4 groups (Control, low-dose, middle-dose and high-dose group) and were treated with increasing concentration of DEHP (0, 250, 500, 1000 mg/kg/day) respectively for 28 consecutive days by intragastric administration. Our results showed that DEHP exposure induced obvious morphological changes of testis, decreased organ coefficient of testis and sperm count, and increased testicular cell apoptosis in the 500 and 1000 mg/kg/day DEHP groups (p < .05). The serum testosterone decreased in a dose-dependent manner after treatment with DEHP. Furthermore, the exposure of DEHP elevated the levels of oxidative stress accompanied by upregulated expression of p53 and reduced expression of STAT3. In addition, compared with the control group, the expression of PI3K, p-Akt and p-mTOR proteins significantly decreased, whereas the downstream autophagy-related proteins phosphorylated ULK1, Beclin-1, Atg7, LC3-II obviously increased in the 250 mg/kg/day DEHP group (p < .05). The expression of p62 was reduced in DEHP-treated groups. Our data indicated that autophagy could be activated to protect testes from DEHP-induced reproductive damage by inhibiting PI3K-Akt-mTOR signaling pathway in the 250 mg/kg/day DEHP group. STAT3/p53-mediated mitochondrial apoptosis pathway might play a major role to cause testis injury and reproductive dysfunction in the 500 and 1000 mg/kg/day DEHP groups.

Di(2-ethylhexyl)phthalate induces reproductive toxicity via JAZF1/TR4 pathway and oxidative stress in pubertal male rats.

Di(2-ethylhexyl)phthalate (DEHP) is a typical endocrine-disrupting chemical and reproductive toxicant. Although previous studies have attempted to describe the mechanism by which DEHP exposure results in reproductive dysfunction, few studies focused on puberty, a critical period of reproductive development, and the increased susceptibility to injury in adolescents. To elucidate the mechanism underpinning the testicular effects of DEHP in puberty, we sought to investigate the JAZF1/TR4 pathway in the testes of pubertal rats. Specifically, we focused on the role of the JAZF1/TR4 pathway in male reproduction, including the genes JAZF1, TR4, Sperm 1, and Cyclin A1. In the present study, rats were exposed to increasing concentrations of DEHP (0, 250, 500, and 1000 mg/kg/day) by oral gavages for 30 days. Then we assayed testicular zinc and oxidative stress levels. Our results indicated that DEHP exposure could lead to oxidative stress and decrease the contents of testicular zinc. Additionally, significant morphological changes and cell apoptosis were observed in testes exposed to DEHP, as identified by hematoxylin and eosin staining and the terminal deoxynucleotidyl transferase-mediated nick and labeling assay. By measuring the expression levels of the above relevant genes by qPCR, we found the DEHP-induced increased expression of JAZF1 and decreased expression of TR4, Sperm 1, and Cyclin A1. Therefore, we have demonstrated that in vivo exposure to DEHP might induce reproductive toxicity in pubertal male rats through the JAZF1/TR4 pathway and oxidative stress.