Juan D. Suarez

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.

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.

Optimization of the Hamilton-Thorn Computerized Sperm Motility Analysis System for Use with Rat Spermatozoa in Toxicological Studies

To optimize the Hamilton-Thorn Motility Analyzer (HTM; Hamilton-Thorn Research, Beverly, MA) for use in reproductive toxicology studies with rat spermatozoa, the accuracy and precision of the instrument were assessed under a variety of instrument settings. Videotapes of both fast- and slow-swimming sperm were analyzed repeatedly to obtain data across a range of sperm velocities as might be encountered as a consequence of exposure to reproductive toxicants. Acquisition rates were varied across the HTM menu choices (30, 19, 10, or 7 frames/sec) as were the number of frames analyzed (5 to 20) at each framing rate. For fast-swimming samples (mean straight-line velocity (VSL) approximately 130 microns/sec) generally good agreement between computer-assisted sperm analysis (CASA) and manually obtained data was found for percentage of motile sperm and straight-line velocity; i.e., CASA values were within 10% of manual values for most frame/rate combinations. The accuracy of these measures held true over a wide range of sperm concentrations and percentage motilities. However, CASA measures were less accurate for sperm samples of lower velocities (mean VSL approximately 50 microns/sec and mean VSL approximately 30 microns/sec) in that the velocity of very slow sperm was overestimated (particularly at 30 frames/sec). A soft-ware change (6.5R) and performing analyses at 19 instead of 30 frames/sec improved straight-line accuracy for the slow sperm and enhanced the discrimination between fast (presumably control) and slow (presumably treated) sperm samples. These data show that this motility analyzer could be successfully configured to evaluate rodent sperm samples. The use of such CASA systems in toxicology studies will provide valuable information that may improve human reproductive risk assessment.

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.

Multiple effects of ethane dimethanesulfonate on the epididymis of adult rats

Ethane dimethanesulfonate (EDS), a Leydig cell toxicant which results in transient infertility, was used in a 4 day postexposure experimental protocol designed to identify any effects this compound might exert on the epididymis. The techniques of efferent duct ligation and testosterone (T) implantation were used to negate the role of testicular effects on the epididymal parameters. Numerous evaluations were performed including light and electron microscopy, computer assisted sperm motion analyses, and electrophoresis of sperm membrane proteins. EDS was shown to affect the epididymis in a dose-dependent fashion. The action of EDS on the epididymis is in part due to Leydig cell cytotoxicity and the resulting decrease in circulating androgen since T implantation prevented some of the changes in sperm proteins and motility. However, neither efferent duct ligation nor T implantation prevented the formation of sperm granulomas in the caput epididymidis, the distinct morphological alterations of the corpus epididymidis, the modification of certain sperm membrane proteins, or the decrease in the progressive motility and velocity of sperm following EDS treatment. Although we cannot prove these effects of EDS are due to a direct action on the epididymis, it is now clear that EDS has a distinct action on the epididymis which is unrelated to circulating T or testicular fluid.

The use of purified rat Leydig cells complements the H295R screen to detect chemical-induced alterations in testosterone production

Abstract Exposure to endocrine disrupting chemicals has been associated with compromised testosterone production leading to abnormal male reproductive development and altered spermatogenesis. In vitro high-throughput screening (HTS) assays are needed to evaluate risk to testosterone production, yet the main steroidogenesis assay currently utilized is a human adrenocortical carcinoma cell line, H295R, which does not synthesize gonadal steroids at the same level as the gonads, thus limiting assay sensitivity. Here, we propose a complementary assay using a highly purified rat Leydig cell assay to evaluate the potential for chemical-induced alterations in testosterone production by the testis.We evaluated a subset of chemicals that failed to decrease testosterone production in the HTS H295R assay. The chemicals examined fit into one of two categories based on changes in substrates upstream of testosterone in the adrenal steroidogenic pathway (17α-hydroxyprogesterone and 11-deoxycorticosterone) that we predicted should have elicited a decrease in testosterone production. We found that 85% of 20 test chemicals examined inhibited Leydig cell testosterone production in our assay. Importantly, we adopted a 96-well format to increase throughput and efficiency of the Leydig cell assay. We identified a selection criterion based on the AC50 values for 17α-hydroxyprogesterone and 11-deoxycorticosterone generated from the HTS H295R assay that will help prioritize chemicals for further testing in the Leydig cell screen. We hypothesize that the greater dynamic range of testosterone production and sensitivity of the Leydig cell assay permits the detection of small, yet significant, chemical-induced changes not detected by the HTS H295R assay. Summary Sentence The greater dynamic range of testosterone production in a primary rat Leydig cell assay permitted detection of chemical-induced testosterone inhibition that was not detected by the high-throughput screening format of the H295R steroidogenesis assay.