Microcystin-LR causes cytotoxicity effects in rat testicular Sertoli cells

Microcystins (MCs) are produced by cyanobacteria. The most toxic and widely distributed MC is microcystin-LR (MC-LR). The aim of this study was to investigate whether exposure to MC-LR could induce oxidative stress, leading the further toxicity effects on Sertoli cells in vitro. Sertoli cells obtained from rats were cultured with a medium containing 0, 0.5, 5, 50 or 500 nM/l MC-LR. We examined the decrease of mitochondrial membrane potential (MMP), the increase of reactive oxygen species (ROS) production, the increase of lipid peroxidation and decrease of superoxide dismutase (SOD) activity in Sertoli cells after treatment with MC-LR in vitro, and higher expression of caspase-9 and caspase-3, the increase of apoptosis rate. Therefore, we deduced that direct exposure to microcystin-LR could induce oxidative stress generation in Sertoli cells, and subsequently depressed cellular viability and caused cells to undergo apoptosis, resulting in the reproductive toxicity in male rats.     

The toxic effects of microcystin-LR on rat spermatogonia in vitro

Microcystin-leucine arginine (MC-LR), a cyclic heptapeptide produced by several bloom-forming cyanobacteria, has strong reproductive toxicity. We examined whether MC-LR could enter spermatogonia and investigated the toxic effects of MC-LR on spermatogonia in vitro. Multispecific organic anion-transporting polypeptides (Oatps), which transported MCs, were screened as well. Spermatogonia were exposed to 0, 0.5, 5, 50, and 500 nmol/L (nM) MC-LR for 6 h. Cell viability and total antioxidant capacity significantly decreased, meanwhile, the ratio of apoptotic cells, reactive oxidative species (ROS) production, mitochondrial membrane potential (MMP), and intracellular free Ca²⁺ increased after exposure to 5 nM and higher concentrations of MC-LR. MC-LR can immigrate into spermatogonia. At least 5 Oatps (Oatp1a5, -3a1, -6b1, -6c1, and -6d1) were detected at the mRNA level in spermatogonia, and the expression of these Oatps was affected by MC-LR, especially Oatp3a1. This study demonstrated that MC-LR can be transported into spermatogonia and leads to cytotoxicity.     

Decline of sperm quality and testicular function in male mice during chronic low-dose exposure to microcystin-LR

The effects of chronic low-dose exposure to microcystins were preliminarily studied on sperm quality and testicular function in male mice. Microcystin-LR (MC-LR) was orally administered to male mice at 0, 1, 3.2, and 10 μg/L for 3 and 6 months. Our preliminary study found in three-month group, sperm quality declined at 3.2 and 10 μg/L doses, testosterone dropped at 10 μg/L, levels of LH and FSH increased, and Leydig cells exhibited apoptosis. Similar, but more pronounced, effects were observed in groups treated with MC-LR for 6 months. Compared to control (0 μg/L), the rate of sperm abnormality was higher and testosterone levels were lower following administration of 3.2 and 10 μg/L MC-LR and structural damage to the testis was observed with 10 μg/L dose. Thus, chronic low-dose treatment with MC-LR results in substantial toxicity to male reproduction, causing declines in sperm quality, decreased levels of serum testosterone, and injury to the testis.     

Microcystin (-LR) affects hormones level of male mice by damaging hypothalamic-pituitary system

Microcystin (-LR) (MC-LR) is a broad distributed hepatotoxic microcystin produced by common freshwater phytoplankton species. Recently, its toxic effects on male reproductive system drew great attention. To investigate its reproductive toxicity and the underlying mechanism, BALB/c mice were exposed to MC-LR by intraperitoneal injection with different injection duration (1, 4, 7 and 14 days) and injection concentration (3.75, 7.5, 15 and 30 μg kg b.w.⁻¹ day⁻¹) as an in vivo test. For in vitro test, isolated mice Leydig cells were exposed to MC-LR at doses of 1, 10, 100, 250, 500 750 and 1000 nmol/L for 24 h. MC-LR did not induce significant changes in Kiss-1, GPR54, Gnrhr, Fshr or Lhr expression. It decreased the Gnrh expression in a dose- and duration-dependent manner. It increased and subsequently decreased the expressions of FSH, LH and testosterone. In in vivo test, MC-LR was not able to enter Leydig cells and had no cytotoxicity on Leydig cells. The results showed that MC-LR affected male mice serum hormones and mRNA expressions by damaging the hypothalamic-pituitary systems.     

三硝基甲苯对雄性生殖毒性的研究

急性、亚急性和亚慢性TNT染毒大鼠睾丸铜锌含量和多种酶活性皆有所变化;睾丸和血清睾酮含量下降。大鼠辜丸游离间质细胞与TNT共同孵育时,睾酮形成量明显下降;间质细胞与TNT孵育后,活性氧与脂质过氧化阳性物质含量明显增加。补锌在一定程度上能拮抗TNT对大鼠的生殖毒性。横断面调查表明,TNT接触男工自觉性功能降低者增加,血清睾酮含量下降,精液常规检查有阳性所见。     

An oral two-generation reproductive toxicity study of S-111-S-WB in rats

S-111-S-WB (CAS No. 72968-38-8), a mixture of perfluoro fatty acid ammonium salts, was administered daily via oral gavage to 30 Crl:CD(SD) rats/sex/group at 0.025, 0.125 and 0.6mg/(kgday) over two generations to assess potential reproductive toxicity. Reproductive performance, mean litter size, pup survival and pup weights were unaffected. Lower mean body weights were observed in 0.6mg/(kgday) group F(0) and F(1) males. Higher liver weights, correlating to hepatocellular hypertrophy in the 0.6mg/kg group, were noted for parental males in the 0.125 and 0.6mg/(kgday) groups, parental females in the 0.6mg/(kgday) group and F(1) pups in the 0.125 and 0.6mg/(kgday) groups. Higher kidney weights, correlating to renal tubule hypertrophy in the 0.6mg/kg group, were observed for parental males and females in the 0.125 and 0.6mg/(kgday) groups. Systemic exposure (measured only in females) to total S-111-S-WB was proportional to dose following 9 weeks of daily administration on the gestation day 19. Total S-111-S-WB concentration in the serum of male and female pups was 1.2-1.4-fold higher than in the dams 2h following administration to the dams on lactation day 13. A dosage level of 0.6mg/(kgday) was considered to be the no-observed-adverse-effect level (NOAEL) for reproductive function. A dosage level of less than 0.025mg/(kgday) was considered to be the NOAEL for F(0) and F(1) parental systemic toxicity based on microscopic hepatic findings in the males of all test article groups, and a dosage level of 0.025mg/(kgday) was considered to be the NOAEL for neonatal toxicity based on higher liver weights in the F(1) and F(2) pups at 0.125mg/(kgday) and higher.     

Fetal testosterone insufficiency and abnormal proliferation of Leydig cells and gonocytes in rats exposed to di(n-butyl) phthalate

Adult male rats previously exposed on gestation days (GD) 12-21 to di(n-butyl) phthalate (DBP) have reproductive tract malformations, particularly agenesis of the epididymis, decreased sperm production, and Leydig cell hyperplasia and adenomas. Although similar effects are produced by the potent androgen receptor (AR) antagonist flutamide and are indicative of disruption of male sexual differentiation via an antiandrogenic mechanism, DBP is not an AR antagonist. The purpose of the study was to determine whether DBP causes pathologic changes and alterations in androgen status in the testis during the prenatal period of male reproductive tract differentiation. Pregnant CD rats were given corn oil, DBP (500 mg/kg/day), or flutamide (100 mg/kg/day) p.o. on GD 12-21. At GD 16-21, DBP caused hyperplasia of Leydig cells, many of which were 3beta-hydroxysteroid dehydrogenase- and/or AR-positive. Focal areas of hyperplasia had increased numbers of Leydig cells positive for proliferating cell nuclear antigen (PCNA). At GD 21, testis atrophy was apparent, seminiferous cords in DBP-exposed fetuses were enlarged and contained multinucleated gonocytes that, unlike controls, were PCNA-positive. DBP, but not flutamide, markedly decreased testicular testosterone levels at GD 18 and 21. Fewer epididymal ducts and reduced AR staining in some ducts were evident with DBP treatment, whereas decreased overall AR staining was seen with flutamide in the presence of mild Leydig cell hyperplasia. Leydig cell proliferation is likely a compensatory mechanism to increase testicular steroidogenesis triggered by testosterone insufficiency. The overall decrease in androgen concentration is not corrected and results in reproductive tract malformations. The multinuclearity and proliferation of gonocytes suggests an underlying Sertoli cell dysfunction.     

Insights into testicular damage induced by ethinylestradiol in rats

The present study was conducted to clarify the mechanisms of testicular toxicity induced by ethinylestradiol using a rat model maintaining testicular testosterone levels. Twelve-week-old male SD rats were implanted subcutaneously with testosterone (800 mg)-filled tubes on the back 2 days before ethinylestradiol treatment, and subsequently administered orally 10 mg/kg/day ethinylestradiol for 4 consecutive weeks. At termination, measurements of hormone levels in serum and the testis, sperm head counts in the testis, weights of genital organs and histopathological examination were performed. Results show that the supply of testosterone alone induced markedly increased serum testosterone levels, slightly decreased testicular testosterone levels, and atrophic Leydig cells. Treatment of rats with ethinylestradiol alone significantly decreased testosterone levels in serum and the testis, sperm head counts, and weights in the testis, epididymis and prostate. Histological features included atrophy of Leydig cells, decreased number of elongated spermatids, degeneration of germ cells, and tubular atrophy. Co-administration of testosterone almost completely prevented the aforementioned changes brought about by ethinylestradiol, except for Leydig cell atrophy. From these results, we attribute testicular toxicity during ethinylestradiol exposure to the suppression of testicular testosterone levels.     

Reduction of spermatogenesis and steroidogenesis in mice after fentin and fenbutatin administration

The present study was designed to assess potential reproductive toxicity caused by fentin and fenbutatin in the mice. Adult male mice received i.p. injections of fentin hydroxide and fenbutatin oxide at a dose of 0, 10 or 25 microg/kg body weight on 1st, 3rd and 5th day of experimentation. Mice were sacrificed on day 25 and analyzed for spermatogenesis and steroidogenesis. A significant decrease in epididymal sperm count, sperm motility, sperm viability and sperm function (HOS coiling) were observed in experimental mice when compared with controls. The decrease in sperm quantity and quality was significant in the 25 microg/kg group than that in the control group. The activity levels of testicular steroidogenic enzymes, 3beta-hydroxysteroid dehydrogenase (3beta-HSD) and 17beta-hydroxysteroid dehydrogenase (17beta-HSD) were significantly decreased in treated mice indicating decreased steroidogenesis after organotin compounds administration. The levels of serum testosterone decreased with an increase in follicle stimulating hormone and luteinizing hormone in experimental mice when compared to control mice. The results suggest that fentin and fenbutatin cause impairment of spermatogenesis through the inhibition of testosterone production.     

Distribution of microcystin-LR to testis of male Sprague–Dawley rats

Microcystins (MCs) are a group of cyclic heptapeptide toxins produced by naturally freshwater cyanobacteria. Among more than 90 identified analogues of microcystins, microcystin-LR (MC-LR) is the most abundant and toxic. Our previous investigations indicated that MC-LR displays male reproductive toxicity, but the target of MC-LR in testes remains unclear. To this end, the present study is designed to elucidate whether microcystin-LR could be distributed to testes and explore the target cells in testes. In the in vivo study, male Sprague–Dawley rats were injected intraperitoneally with MC-LR at a dose of 300 μg/kg per day for 6 days. MC-LR was detected in testes, mainly within seminiferous tubules, which was further validated by Western blot. The concentrations of MC-LR were determined by LC–MS analysis, with a result of 0.0252 ± 0.0037 and 0.0056 ± 0.0012 μg/g dry weight in liver and testis respectively. In the in vitro study, Primary cultured spermatogonia, Sertoli cells and Leydig cells were exposed to MC-LR respectively, and MC-LR was observed to enter spermatogonia and Sertoli cells, but not Leydig cells. These results suggested that the reproductive toxicity of MC-LR were induced by its distribution in testis. Spermatogonia and Sertoli cells are important target cells.     

Subchronic supplementation of lithium carbonate induces reproductive system toxicity in male rat

Lithium is frequently used as an effective drug for the treatment of several psychiatric disorders in human. This alkali element and its salt, at its higher doses, may lead to various side effects or has several toxic effects after prolonged therapeutic use. To test this hypothesis, the present study was designed to investigate the adverse effect of subchronic exposure of lithium carbonate on reproductive organs of male rat. Rats were exposed to lithium carbonate at doses of 500, 800, 1100 mg/kg of diet for 90 days. The weight of reproductive organs, histology of testis, epididymis, seminal vesicle, prostate, testicular interstitial fluid volume (IFV), testosterone level, sperm morphology and fertility index were analyzed. Treatment with higher doses of lithium carbonate (i.e. 800, 1100 mg/kg diet) significantly reduced testes, epididymis and accessory sex organs weights, whereas, lower dose (500 mg/kg diet) did not show any untoward effect. Similarly, the sperm number from cauda epididymis and daily sperm production was significantly decreased with higher doses of lithium carbonate. The serum testosterone levels and IFVs were also reduced significantly. Seminal vesicle and prostate secretions were completely blocked and spermatozoa were not seen in the lumen of epididymis and vas deference. Histological studies have revealed that lithium carbonate (1100 mg/kg) caused degeneration of spermatogenic cells and vacuolization of sertoli cells cytoplasm in the testis. The sperm transit rate and production of abnormal spermatozoa were significantly (P<0.01) increased. When the lithium carbonate-treated males were mated with normal cyclic females, the fertility index declined to 50% even after 30 days of withdrawal of lithium carbonate treatment. These results clearly suggest that subchronic exposure of lithium carbonate promote reproductive system toxicity and reduces fertility of male rats.     

Comparative Cytotoxic Effects and Possible Mechanisms of Deoxynivalenol,Zearalenone and T-2 Toxin Exposure to Porcine Leydig Cells In Vitro

Mycotoxins such as zearalenone (ZEN), deoxynivalenol (DON) and T-2 toxin (T-2) are the most poisonous biological toxins in food pollution. Mycotoxin contaminations are a global health issue. The aim of the current study was to use porcine Leydig cells as a model to explore the toxic effects and underlying mechanisms of ZEN, DON and T-2. The 50% inhibitory concentration (IC₅₀) of ZEN was 49.71 μM, and the IC₅₀ values of DON and T-2 were 2.49 μM and 97.18 nM, respectively. Based on the values of IC₅₀, ZEN, DON and T-2 exposure resulted in increased cell apoptosis, as well as disrupted mitochondria membrane potential and cell cycle distribution. The results also showed that ZEN and DON significantly reduced testosterone and progesterone secretion in Leydig cells, but T-2 only reduced testosterone secretion. Furthermore, the expression of steroidogenic acute regulatory (StAR) protein and 3β-hydroxysteroid dehydrogenase (3β-HSD) were significantly decreased by ZEN, DON and T-2; whereas the protein expression of cholesterol side-chain cleavage enzyme (CYP11A1) was only significantly decreased by ZEN. Altogether, these data suggest that the ZEN, DON and T-2 toxins resulted in reproductive toxicity involving the inhibition of steroidogenesis and cell proliferation, which contributes to the cellular apoptosis induced by mitochondrial injury in porcine Leydig cells.     

Effects of bismuth citrate on the viability and function of Leydig cells and testicular macrophages

Bismuth is present in several popular over-the-counter drugs for nausea and diarrhea and is occasionally abused by patients with chronic gastrointestinal disorders. The most common consequence of bismuth overdose is neurological dysfunction. In experimental animals, bismuth overdose results in lowered serum testosterone levels, suggesting that reproductive dysfunction may be an additional component of bismuth toxicity. Although the precise mechanisms responsible for the lowered testosterone levels are unknown, it has been shown that bismuth accumulates within testicular macrophages. This may be important because these cells, which are commonly found in direct contact with Leydig cells, are known to exert paracrine influences on the Leydig cells for local control of testosterone production. However, bismuth may also exert direct effects on Leydig cells because it passes by these cells on its way to the phagocytic macrophages. The purpose of the present studies was to isolate both testicular macrophages and Leydig cells from rat testis and study the direct effects of bismuth on these cells with regard to their viability and function. We found that when Leydig cells were treated for 24 h with bismuth (1-100 microM) no change in viability or secretion of testosterone was observed. However, when testicular macrophages were similarly treated with bismuth a significant effect on viability was observed with as little as 6.25 microM bismuth, with near-complete cell death at 50 microM after 24 h. However, bismuth had no effect on the viability on testicular macrophages at 50 microM up to 8 h, therefore, we studied the secretion of tumor necrosis factor alpha (TNF-alpha) after 4 h of exposure to 50 microM bismuth and found no influence on the production of TNF-alpha. Taken together, it seems likely that bismuth has no direct effects on Leydig cells but, rather, lowers testosterone levels by killing testicular macrophages, thereby interrupting their local paracrine influence on Leydig cells through factors other than TNF-alpha.     

Differential oxidative stress responses to microcystins LR and RR in intraperitoneally exposed tilapia fish (Oreochromis sp.)

Increasing evidence suggests that oxidative stress may play a significant role in causing microcystin (MCs) toxicity not only in mammals, but also in fish. MCs are a family of cyclic peptide toxins produced by some species of freshwater cyanobacteria (blue-green algae). Among the microcystins, MC-LR is the most extensively studied. In the present study the differential response of the antioxidant enzymes superoxide dismutase (SOD), catalase (CAT), glutathione peroxidase (GPx) and glutathione reductase (GR) as well as lipid peroxidation (LPO) as a biomarker of oxygen-mediated toxicity were assessed in liver, kidney and gill tissues of tilapia (Oreochromis sp.) exposed to MCs. Fish were injected intraperitoneally (i.p.) with a single dose of 500 microg/kg MC-LR or 500 microg/kg MC-RR and sacrificed after 7 days. The results show that MCs exposure induces adaptive responses such as increase in the antioxidant enzymatic activities, mainly those of SOD and CAT, as well as in LPO values. With regard to LPO values, the liver was the most affected organ by MC-LR. MC-RR, however, did not affect this parameter in the liver of the exposed fish. Oxidative stress biomarkers, therefore, are valuable tools in the assessment of early responses of fish to the increasing occurrence of cyanobacterial blooms worldwide.     

Protective effects of testosterone propionate on reproductive toxicity caused by Endosulfan in male mice

To investigate the protective effect of testosterone propionate (TP) on reproductive toxicity caused by endosulfan in male mice, three group experiments were designed: the control group received 0 and 0, the endosulfan group received 0.8 and 0, and the endosulfan + TP group received 0.8 mg/kg/d endosulfan and 10 mg/kg/d TP, respectively. The results showed that TP significantly prevented the declines of concentration and motility rates in sperm, reduced the rate of sperm abnormalities in epididymis; and antagonized the decreases in spermatogenous cell and sperm numbers in testes induced by endosulfan. TP also decreased the numbers of cavities formed, prevented the decreases of plasma testosterone and androgen receptor (AR) mRNA in testicular tissue, alleviated the increase of LH induced by endosulfan. It is likely that TP relieve the reproductive toxicity by reversing the endosulfan‐induced decreases in testosterone secretion and AR expression that resulted from the alteration of Leydig cell function. © 2014 Wiley Periodicals, Inc. Environ Toxicol 31: 142–153, 2016.     

The mechanism for lindane-induced inhibition of steroidogenesis in cultured rat Leydig cells

The in vitro effect of the gamma-isomer of hexachlorocyclohexane, lindane, on rat Leydig cell steroidogenesis was studied. Leydig cells from mature male rats were incubated with human chorionic gonadotropin (hCG, 1 IU) for 3 h at 34 degrees C in the presence of different doses of lindane (2-200 microg/ml; 2-200 ppm). Results demonstrate that lindane produces a dose-dependent inhibition of testosterone production in hCG-stimulated Leydig cells. The decreased testosterone synthesis was accompanied with a half-reduced LH/hCG receptor number without any modification in the K(d) value. In addition, lindane also decreased cAMP production. These effects were not due to a detrimental action of lindane on cell viability. Results of this study demonstrate a direct inhibitory action of lindane on testicular steroidogenesis, at least in part, through a reduction in the classical second messenger production involved in this pathway.     

Differential effects of octylphenol, 17beta-estradiol, endosulfan, or bisphenol A on the steroidogenic competence of cultured adult rat Leydig cells.

In the current studies, we evaluated the effects of 4-tert-octylphenol (OP), endosulfan, bisphenol A (BPA), and 17beta-estradiol on basal or hCG-stimulated testosterone formation by cultured Leydig cells from young adult male rats. Exposure of Leydig cells to increasing concentrations of OP (1 to 2000 nM), 17beta-estradiol (1 to 1000 nM), endosulfan (1 to 1000 nM) or BPA (1 to 1000 nM), alone or with 10 mIU/mL hCG for 4 or 24 h, did not lower ambient testosterone levels, although cells exposed to higher OP concentrations + hCG for 24 h often had modest declines in testosterone (10 to 20%). Of interest, exposure to the highest concentration OP (2000 nM) alone for 4 or 24 h increased testosterone levels (approximately 2-fold in 4-h exposed cells). Whether prior exposure to OP + hCG for 24 h affects the subsequent conversion of steroid substrates to testosterone over 4 h was evaluated. Progressive declines in 1 microM 22(R) hydroxycholesterol, 1 microM pregnenolone, or 1 microM progesterone conversion to testosterone was observed beginning at 100 to 500 nM OP exposure (maximal declines of 40 to 12% of controls were observed); however, the conversion of 1 microM androstenedione to testosterone was not affected by OP. These results suggested that 24-h exposure to OP + hCG has no effect on 17beta-hydroxysteroid dehydrogenase, which converts androstenedione to testosterone, but that it inhibits the 17alpha-hydroxylase/C17-20 lyase step, which converts progesterone to androstenedione. In addition, potentially, OP could inhibit cholesterol side/chain cleavage activity, which converts cholesterol to pregnenolone, and/or 3beta-hydroxysteroid dehydrogenase, which converts pregnenolone to progesterone. Of interest, exposure to increasing concentrations of 17beta-estradiol (1 to 1000 nM), endosulfan (1 to 1000 nM), or BPA (1 to 1000 nM) + hCG for 24 h had no effect on subsequent conversion of 22(R)hydroxycholesterol to testosterone. Furthermore, the inhibiting effects of OP + hCG exposure on subsequent conversion of progesterone to testosterone was unaffected by concomitant exposure to the pure estrogen antagonist, ICI 182,780, or the antioxidants, ascorbate or dimethyl sulfoxide, suggesting that the actions of OP are not mediated through binding to estrogen receptor alpha or beta or by free radical induced damage to steroidogenic enzymes, respectively. These results demonstrate that direct exposure of adult Leydig cells to OP may have subtle effects on their ability to produce testosterone, which may not be detected by measuring ambient androgen levels. In addition, the effects of OP on Leydig cell testosterone formation appear to be different from those of the native estrogen, 17beta-estradiol, and from other reported weak xenoestrogens such as endosulfan and BPA.     

Octylphenol inhibits testosterone biosynthesis by cultured precursor and immature Leydig cells from rat testes

4-tert-octyphenol (OP) is a surfactant additive widely used in the manufacture of a variety of detergents and plastic products. OP has been reported to mimic the actions of estrogen in many cellular systems. The present studies evaluated the direct effects of OP on human chorionic gonadotropin (hCG)-stimulated testosterone biosynthesis by cultured precursor and immature Leydig cells from 23-day old (prepubertal) rats. Exposure to increasing OP concentrations (1 to 2000 nM) progressively decreased hCG-stimulated testosterone formation in both precursor and immature Leydig cells at higher OP concentrations (100 or 500 to 2000 nM). Testosterone levels were reduced approximately 30 to 70% below control at the highest concentration in both cell types. Similar reductions in testosterone associated with OP exposure were observed in cells stimulated with 1 mM 8-Br-cAMP, suggesting that the main actions of OP occur after the generation of cAMP. Increasing concentrations of 17beta-estradiol (1 to 1000 nM) had no effect on hCG-stimulated testosterone formation in both precursor and immature Leydig cells and the inclusion of 100 nM ICI 182,780, a pure estrogen antagonist, in precursor and immature Leydig cells exposed to OP and hCG, did not alter the inhibition by higher OP concentrations of testosterone formation in both cell types. These results suggest that OP is a hormonally active agent, but that some of its actions are distinct from those of 17beta-estradiol and are not mediated through the estrogen receptor alpha or beta pathway. To further localize the potential site(s) of action of OP, cultured precursor and immature Leydig cells were exposed to increasing concentrations of OP and hCG for 24 h. Next, fresh media containing 1 microM 22(R)-hydroxycholesterol, 1 microM pregnenolone, 1 microM progesterone, or 1 microM androstenedione was added, and the conversion of each substrate to testosterone was determined after incubation for 4 h. The conversion of androstenedione to testosterone was unaffected by exposure to OP, suggesting that the 17beta-hydroxysteroid dehydrogenase step is not inhibited. However, the conversion of 22(R)-hydroxycholesterol, pregnenolone and progesterone all were inhibited by prior exposure to OP and hCG. This finding suggests that the 17alpha-hydroxylase/c17-20-lyase step, which converts progesterone to androstenedione, is inhibited by OP, and that the cholesterol side-chain cleavage and 3beta-hydroxysteroid dehydrogenase -isomerase steps, which convert cholesterol to pregnenolone and pregnenolone to progesterone, respectively, are other potential sites of OP action. Because concomitant exposure to the antioxidants alpha-tocopherol or ascorbate did not alter the inhibition of testosterone formation by higher OP concentrations, it does not appear that OP is acting as a pseudosubstrate for the generation of free radicals, which can damage P450 enzymes.     

The reproductive toxicity of organic compounds extracted from drinking water sources on Sprague Dawley rats: An in vitro study

The safety of drinking water always causes worldwide concern. Water pollution increases with urban development and industrialization in developing countries. During recent decades, increasing numbers of environmental organic compounds have been found in aquatic environments. These organic compounds are capable of bioaccumulating to much higher concentrations in food webs and cause health effects on human beings. Reproductive impairment is one of the commonest consequences of environmental pollution. Our goal was to investigate the reproductive toxicity of organic compounds extracted from surface water samples collected in drinking water sources. This study focused on the surface water in lower Yangtze River and Taihu Lake, which act as drinking water sources of Jiangsu province, one of the most rapidly developing regions in China. We used solid‐phase extraction (SPE) to condense organic compounds by 286 times from natural surface water samples and established in vitro system to evaluate their effects on reproductive system. We found that organic compounds destroyed the plasma membrane integrity of Sertoli cells and Spermatogenic cells to a certain degree and significantly depressed viability of Sertoli cells and Spermatogenic cells as well. Accordingly, the proportion of apoptotic Sertoli cells and dead Spermatogenic cells enhanced markedly. Although viability of organic‐compound‐treated Leydig cells did not come down remarkably, testosterone production of Leydig cells decreased evidently. These results suggest that accumulated comprehensive effects of organic compounds in surface water of drinking water sources may induce spermatogenesis malfunction and reduction of testosterone production in the long term. © 2009 Wiley Periodicals, Inc. Environ Toxicol, 2010.     

In vitro/in vivo effects of ethane dimethanesulfonate on Leydig cells of adult rats.

Although ethane dimethanesulfonate (EDS) is well recognized as a Leydig cell toxicant, the dose responsiveness of Leydig cells to EDS, both in vitro and in vivo, is not well established. In addition, the cellular site of action of EDS during Leydig cell toxicity and the status of Leydig cell viability during the affected period remain controversial. We determined the in vitro EC50 (370 microM) and in vivo ED50 (60 mg/kg) for human chorionic gonadotropin (hCG)-stimulated testosterone (T) production using both highly purified (98%) and interstitial (14%) Leydig cell preparations, respectively. Leydig cells were recovered in approximately equal numbers following all in vivo and in vitro EDS exposures. The Leydig cells in these preparations were viable and steroidogenically active (3 beta-HSD positive) subsequent to all exposures, both before and after incubations to stimulate T biosynthesis. When hCG-stimulated T production was decreased 50% following in vivo or in vitro exposures, the morphological integrity of the Leydig cells appeared normal, with no discernible lesion at either the light or the electron microscope level. We used stimulants of various reactions in the pathway of T biosynthesis (20 alpha-hydroxycholesterol and pregnenolone) to determine the site of action impaired when T biosynthesis was decreased. Our results indicate that when Leydig cells are exposed to EDS either in vitro or in vivo, the biosynthesis of T is compromised between the cyclic adenosine monophosphate activation of protein kinase and the cholesterol side chain cleavage enzyme.