Gary R. Klinefelter

Modulation of Rat Leydig Cell Steroidogenic Function by Di(2-Ethylhexyl)Phthalate

Abstract Exposure of rodents to phthalates is associated with developmental and reproductive anomalies, and there is concern that these compounds may be causing adverse effects on human reproductive health. Testosterone (T), secreted almost exclusively by Leydig cells in the testis, is the primary steroid hormone that maintains male fertility. Leydig cell T biosynthesis is regulated by the pituitary gonadotropin LH. Herein, experiments were conducted to investigate the ability of di(2-ethylhexyl)phthalate (DEHP) to affect Leydig cell androgen biosynthesis. Pregnant dams were gavaged with 100 mg−1 kg−1 day−1 DEHP from Gestation Days 12 to 21. Serum T and LH levels were significantly reduced in male offspring, compared to control, at 21 and 35 days of age. However, these inhibitory effects were no longer apparent at 90 days. In a second set of experiments, prepubertal rats, from 21 or 35 days of age, were gavaged with 0, 1, 10, 100, or 200 mg−1 kg−1 day−1 DEHP for 14 days. This exposure paradigm affected Leydig cell steroidogenesis. For example, exposure of rats to 200 mg−1 kg−1 day−1 DEHP caused a 77% decrease in the activity of the steroidogenic enzyme 17β-hydroxysteroid dehydrogenase, and reduced Leydig cell T production to 50% of control. Paradoxically, extending the period of DEHP exposure to 28 days (Postnatal Days 21–48) resulted in significant increases in Leydig cell T production capacity and in serum LH levels. The no-observed-effect-level and lowest-observed-effect-level were determined to be 1 mg−1 kg−1 day−1 and 10 mg−1 kg−1 day−1, respectively. In contrast to observations in prepubertal rats, exposure of young adult rats by gavage to 0, 1, 10, 100, or 200 mg−1 kg−1 day−1 DEHP for 28 days (Postnatal Days 62–89) induced no detectable changes in androgen biosynthesis. In conclusion, data from this study show that DEHP effects on Leydig cell steroidogenesis are influenced by the stage of development at exposure and may occur through modulation of T-biosynthetic enzyme activity and serum LH levels.

Methods for assessing sperm motility, morphology, and counts in the rat, rabbit, and dog: A consensus report☆

Reproductive toxicity studies are increasingly including assessments of sperm parameters including motility, morphology, and counts. While these assessments can provide valuable information for the determination of potential reproductive toxicity, the methods for conducting the assessments have not been well developed in all laboratories and are continually evolving. The use of different methods in different laboratories makes comparison of data among laboratories difficult. To address the differences in methods, a working group was convened to discuss methods currently in use, share data, and try to reach consensus about optimal methods for assessing sperm parameters in rats, rabbits, and dogs. This article presents the consensus report, as well as future research needs, with the hope that optimized common methods will aid in the detection of reproductive effects and enhance interlaboratory comparisons.

Rodent Leydig cell tumorigenesis: a review of the physiology, pathology, mechanisms, and relevance to humans.

Leydig cells (LCs) are the cells of the testis that have as their primary function the production of testosterone. LCs are a common target of compounds tested in rodent carcinogenicity bioassays. The number of reviews on Leydig cell tumors (LCTs) has increased in recent years because of its common occurrence in rodent bioassays and the importance in assessing the relevance of this tumor type to humans. To date, there have been no comprehensive reviews to identify all the compounds that have been shown to induce LCTs in rodents or has any review systematically evaluated the epidemiology data to determine whether humans were at increased risk for developing LCTs from exposure to these agents. This review attempts to fill these deficiencies in the literature by comparing the cytology and ontogeny of the LC, as well as the endocrine and paracrine regulation of both normal and tumorigenic LCs. In addition, the pathology of LCTs in rodents and humans is compared, compounds that induce LC hyperplasia or tumors are enumerated, and the human relevance of chemical-induced LCTs is discussed. There are plausible mechanisms for the chemical induction of LCTs, as typified by agonists of estrogen, gonadotropin releasing hormone (GnRH), and dopamine receptors, androgen receptor antagonists, and inhibitors of 5alpha-reductase, testosterone biosynthesis, and aromatase. Most of these ultimately involve elevation in serum luteinizing hormone (LH) and/or LC responsiveness to LH as proximate mediators. It is expected that further work will uncover additional mechanisms by which LCTs may arise, especially the role of growth factors in modulating LC tumorigenesis. Regarding human relevance, the pathways for regulation of the hypothalamo-pituitary-testis (HPT) axis of rats and humans are similar, such that compounds that either decrease testosterone or estradiol levels or their recognition will increase LH levels. Hence, compounds that induce LCTs in rats by disruption of the HPT axis pose a risk to human health, except for possibly two classes of compounds (GnRH and dopamine agonists). Because GnRH and prolactin receptors are either not expressed or are expressed at very low levels in the testes in humans, the induction of LCTs in rats by GnRH and dopamine agonists would appear not to be relevant to humans; however, the potential relevance to humans of the remaining five pathways of LCT induction cannot be ruled out. Therefore, the central issue becomes what is the relative sensitivity between rat and human LCs in their response to increased LH levels; specifically, is the proliferative stimulus initiated by increased levels of LH attenuated, similar, or enhanced in human vs. rat LCs? There are several lines of evidence that suggest that human LCs are quantitatively less sensitive than rats in their proliferative response to LH, and hence in their sensitivity to chemically induced LCTs. This evidence includes the following: (1) the human incidence of LCTs is much lower than in rodents even when corrected for detection bias; (2) several comparative differences exist between rat and human LCs that may contribute, at least in part, to the greater susceptibility of the rat to both spontaneous and xenobiotic-induced LCTs; (3) endocrine disease states in man (such as androgen-insensitivity syndrome and familial male precocious puberty) underscore the marked comparative differences that exist between rats and man in the responsiveness of their LCs to proliferative stimuli; and (4) several human epidemiology studies are available on a number of compounds that induce LCTs in rats (1,3-butadiene, cadmium, ethanol, lactose, lead, nicotine) that demonstrate no association between human exposure to these compounds and induction of LC hyperplasia or adenomas. (ABSTRACT TRUNCATED)

A Metabolite of Methoxychlor, 2,2-Bis(p-Hydroxyphenyl)-1,1,1-Trichloroethane, Reduces Testosterone Biosynthesis in Rat Leydig Cells Through Suppression of Steady-State Messenger Ribonucleic Acid Levels of the Cholesterol Side-Chain Cleavage Enzyme

Abstract Postnatal development of Leydig cells involves transformation through three stages: progenitor, immature, and adult Leydig cells. The process of differentiation is accompanied by a progressive increase in the capacity of Leydig cells to produce testosterone (T). T promotes the male phenotype in the prepubertal period and maintains sexual function in adulthood; therefore, disruption of T biosynthesis in Leydig cells can adversely affect male fertility. The present study was designed to evaluate the ability of a xenoestrogen, methoxychlor (the methoxylated isomer of DDT [1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane]), to alter Leydig cell steroidogenic function. Purified progenitor, immature, and adult Leydig cells were obtained from, respectively, 21-, 35-, and 90-day-old Sprague-Dawley rats treated with graded concentrations of the biologically active metabolite of methoxychlor, 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), and assessed for T production. HPTE caused a dose-dependent inhibition of basal and LH-stimulated T production by Leydig cells. Compared to the control value, reduced T production by progenitor and immature Leydig cells was apparent after 10 h of HPTE treatment in culture; the equivalent time for adult Leydig cells was 18 h. The reversibility of HPTE-induced inhibition was evaluated by incubating Leydig cells for 3, 6, 10, 14, or 18 h and measuring T production after allowing time for recovery. After treatment with HPTE for 3 h, T production by immature and adult Leydig cells for the 18-h posttreatment period was similar to the control value, but that of progenitor Leydig cells was significantly lower. The onset of HPTE action and the reversibility of its effect showed that Leydig cells are more sensitive to this compound during pubertal differentiation than in adulthood. T production was comparable when control and HPTE-treated immature Leydig cells were incubated with pregnenolone, progesterone, and androstenedione, but HPTE-treated Leydig cells produced significantly reduced amounts of T when incubations were conducted with 22R-hydroxycholesterol (P < 0.01). This finding suggested that HPTE-induced inhibition of T production is related to a decrease in the activity of cytochrome P450 cholesterol side-chain cleavage enzyme (P450scc) and cholesterol utilization. The reduced steady-state mRNA level for P450scc in HPTE-treated Leydig cells was demonstrated by reverse transcription-polymerase chain reaction and densitometry. In conclusion, this study showed that HPTE causes a direct inhibition of T biosynthesis by Leydig cells at all stages of development. This effect suggests that reduced T production could be a contributory factor in male infertility associated with methoxychlor and, possibly, other DDT-related compounds.

Spermatotoxicity of dichloroacetic acid

The testicular toxicity of dichloroacetic acid (DCA), a disinfection byproduct of drinking water, was evaluated in adult male rats given both single and multiple (up to 14 d) oral doses. Delayed spermiation and altered resorption of residual bodies were observed in rats given single doses of 1500 and 3000 mg/kg; these effects persisted to varying degrees on post-treatment days 2, 14, and 28. Delayed spermiation and formation of atypical residual bodies also were observed on days 2, 5, 9, and 14 in rats dosed daily with 1440, 480, 160, and 54 mg/kg. Distorted sperm heads and acrosomes were observed in step 15 spermatids after 14 doses of 480 and 1440 mg/kg. Decreases in the percentage of motile sperm occurred after 9 doses of 480 and 1440 mg/kg and 14 doses of 160 mg/kg. Increased numbers of fused epididymal sperm were observed on days 5, 9, and 14 in rats dosed with 1440, 480, and 160 mg/kg, respectively; other morphologic abnormalities occurred at 160 mg/kg and higher. On day 14, a significant decrease in epididymis weight was observed at 480 and 1440 mg/kg, and epididymal sperm count was decreased at 160 mg/kg and higher. These studies demonstrate that the testicular toxicity induced by DCA are similar to those produced by the analogue, dibromoacetic acid. However, the testicular toxicity of DCA is less severe at equal molar concentrations. Moreover, the DCA-induced testicular lesions occur with greater potency as the duration of dosing increases, indicating the importance of using low-dose subchronic exposures to assess the health risk of prevalent disinfection byproducts.

Spermatotoxicity of dibromoacetic acid in rats after 14 daily exposures

Halogenated acetic acids are major disinfection by-products of water chlorination and ozonation. Limited data in experimental animals indicate that repeated doses of dichloroacetic acid (DCA) or single doses of dibromoacetic acid (DBAA) cause testicular damage. In the present study, spermatotoxic effects were investigated in rats given oral doses of 0, 10, 30, 90, or 270 mg DBAA/kg/day for 14 days. In rats dosed with 270 mg/kg/day, there were marked effects on epididymal sperm motility and morphology including the flagellar fusion of 2 or more sperm. Testis weight, epididymis weight, and testicular sperm head counts were mildly reduced relative to control, whereas epididymal sperm counts were substantially decreased. Histologic changes in the testis included retention of Step 19 spermatids in Stages IX to XII, abnormal development of late spermatids, and the formation of atypical structures resembling residual bodies that were observed predominantly in Stages X to XIV and I of the cycle of the seminiferous epithelium. At the dosage of 90 mg/kg/day, effects on spermiation, spermatid development, epididymal sperm counts, sperm motility, and sperm morphology were less severe than at the higher dosage. Reduced caput sperm counts and mild effects on spermiation also occurred at 30 and 10 mg/kg/day. These studies indicate that subchronic exposure to DBAA has the potential to affect reproductive outcome in the rat. Compared to previous studies of DCA (12), DBAA, on a molar basis, appears to be a stronger testicular toxicant than the dichloro analogue.

The method of sperm collection significantly influences sperm motion parameters following ethane dimethanesulphonate administration in the rat.

Sperm motion analysis following exposure to a reproductive toxicant is one means of evaluating the functional integrity of the testis and epididymis. In this study we sought to determine whether the method used to collect sperm from the proximal cauda epididymidis, where sperm are not completely mature, has a significant influence on sperm motion parameters. Two methods of collecting rat sperm for motion analysis were used: one based on an aspiration technique selected from the literature; the other, a new approach based on diffusion of sperm from the epididymal tubule. The two methods were tested for sensitivity to effects on sperm motility parameters 4 days after a single exposure to ethane dimethanesulphonate (EDS). Since EDS is known to decrease serum testosterone (T), an additional group of rats received T-filled implants just prior to dosing to determine if the decrease in serum T alone had an effect on sperm motility. The results of the study yielded strikingly different interpretations of the effect of a 65 mg/kg BW dose of EDS on the motility of sperm taken from the proximal cauda epididymidis. Sperm collected by aspiration showed no significant decrease in the percentage of motile or progressively motile sperm compared to vehicle-treated animals. On the contrary, sperm collected by diffusion showed large, significant decreases in the percentages of both motile and progressively motile sperm. This difference was due largely to lower percentages of motile and progressively motile sperm in control sperm samples collected by aspiration. Similarly, the motion parameters of sperm collected by the aspiration method were unaffected by EDS/T treatment.(ABSTRACT TRUNCATED AT 250 WORDS)

Preliminary screening for the potential of drinking water disinfection byproducts to alter male reproduction

There is increasing epidemiologic interest in the role drinking water disinfection byproducts (DBPs) may play in adverse reproductive outcomes such as inability to conceive, spontaneous abortion, and low birth weight. Although dozens of DBPs already have been identified, only a few studies have attempted to determine whether DBPs alter male reproductive parameters such as testicular and epididymal histology, testicular and epididymal sperm numbers, and epididymal sperm morphology and motility in laboratory animals. In these studies, alterations in epididymal sperm motility seemed to be predictive of more generalized toxicity of the male reproductive system. Because there is a need to prioritize DBPs for thorough reproductive and developmental toxicity testing, preliminary screening for the potential of DBPs to alter reproductive function seems warranted. Here, we elected to examine only cauda epididymal sperm motion parameters and testicular and epididymal histopathology. The effects of exposure to two commonly occurring DBPs, bromodichloromethane (BDCM) and chloral hydrate (CH), via drinking water were evaluated in F344 rats at an interim (52 week) necropsy during cancer bioassay studies. Exposure to 22 and 39 mg/kg BDCM and 55 and 188 mg/kg CH did not produce any systemic toxicity. Histopathologic evaluation revealed no gross lesions in the reproductive organs, and no tumors were detected in any tissues. In contrast, exposure to 39 mg/kg BDCM significantly decreased the mean straight-line, average path, and curvilinear velocities of sperm recovered from the cauda epididymidis. This BDCM exposure shifted the average path velocity distribution to a lower modal velocity range. Exposure to 188 mg/kg CH significantly decreased both the percentage of motile and progressively motile sperm. This CH exposure shifted the straight-line velocity distribution to a lower modal velocity range. These are the first reproductive toxicity data from exposure to BDCM and CH. The observed effects on sperm motion occurred in the absence of carcinogenesis. Because the effects of BDCM on sperm motility occurred at a lower exposure than that of other DBPs that compromise sperm motility, a thorough reproductive evaluation now is underway.

Sensitivity of Sertoli and Leydig cells to xenobiotics in in vitro models.

Different chemicals are known to cause testicular damage in the human male and experimental animals. However, the ability to assess the potential and mechanism of action leading to chemically-induced damage in men has been hampered by a lack of good predictive models. Although many of these chemicals were found to impair reproductive capacity in various laboratory animals, only some have caused reproductive damage in men. Mammalian spermatogenesis takes places within the avascular seminiferous tubules of the testis. Specialized tight junctions, which form between adjacent Sertoli cells at the time of puberty, divide the tubular space into the basal and adluminal compartments, and create a blood-testis barrier that restricts passage of substances and ions from the circulation. Thus, the completion of meiosis and post-meiotic germ cell differentiation, which take place in the adluminal compartment, are isolated from circulating substances unable to cross the blood-testis barrier. It seems feasible, therefore, that damage to the germ cells induced by testicular toxicants may be mediated through other cells in the testis such as the Sertoli, peritubular, or Leydig cells. A recently developed two-compartment system for culture of testicular cells can simulate, to some degree, the normal physiologic conditions. In principle, Sertoli cells isolated from mammalian testes are cultured on a permeable support (that is millipore filter) between two fluid compartments. They form a highly polarized epithelial layer with characteristic tight junctions that restrict the passage of substances between the two compartments, in analogy to the blood-testis barrier. We believe this system provides an excellent in vitro model for determining the ability of chemicals to: a) alter the permeability of the blood-testis barrier, b) impair the secretory function of Sertoli cells, or c) affect their viability, all of which could indirectly affect the germ cells. We have utilized this system for examining the effects of cadmium chloride (CdCl2) and other toxic substances known to affect the testis. The Leydig cell toxicity was investigated in testicular perfusion system or cultures of isolated Leydig cells.

Histopathologic changes in the testes of rats exposed to dibromoacetic acid

The present report details histopathologic changes in the testis and epididymis of rats gavaged daily for 2 to 79 d with a by-product of water disinfection, dibromoacetic acid (DBAA). On treatment day 2 abnormal retention of Step 19 spermatids was observed in animals given the highest dosage of 250 mg/kg. Additional changes on day 5 included the fusion of mature spermatids and the presence of atypical residual bodies (ARB) in the epithelium and lumen of Stage X-XII seminiferous tubules. By day 9, ARB were seen in most stages of the seminiferous epithelial cycle and in the caput epididymidis. On day 16 distorted sperm heads were recognized in Step 12, and older spermatids, and luminal cytoplasmic debris was found throughout the epididymis. On day 31, there was vacuolation of the Sertoli cell cytoplasm, extensive retention of Step 19 spermatids near the lumen of Stage IX and X tubules, and vesiculation of the acrosomes of late spermatids. Marked atrophy of the seminiferous tubules was present 6 months after 42 doses of 250 mg/kg. ARB and retention of Step 19 spermatids were observed after 31 and 79 doses of 50 mg/kg and increased retention of Step 19 spermatids was seen in several rats dosed with 10 mg/kg. No abnormalities were detected at the dosage of 2 mg/kg. The changes suggest that the testicular effects of DBAA are sequelae to structural and/or functional changes in the Sertoli cell.