In vitro differentiation of rat spermatogonia into round spermatids in tissue culture.

STUDY QUESTION: Do the organ culture conditions, previously defined for in vitro murine male germ cell differentiation, also result in differentiation of rat spermatogonia into post-meiotic germ cells exhibiting specific markers for haploid germ cells? SUMMARY ANSWER: We demonstrated the differentiation of rat spermatogonia into post-meiotic cells in vitro, with emphasis on exhibiting, protein markers described for round spermatids. WHAT IS KNOWN ALREADY: Full spermatogenesis in vitro from immature germ cells using an organ culture technique in mice was first reported 5 years ago. However, no studies reporting the differentiation of rat spermatogonia into post-meiotic germ cells exhibiting the characteristic protein expression profile or into functional sperm have been reported. STUDY DESIGN, SAMPLES/MATERIALS, METHODS: Organ culture of testicular fragments of 5 days postpartum (dpp) neonatal rats was performed for up to 52 days. Evaluation of microscopic morphology, testosterone levels, mRNA and protein expression as measured by RT-qPCR and immunostaining were conducted to monitor germ cell differentiation in vitro. Potential effects of melatonin, Glutamax® medium, retinoic acid and the presence of epidydimal fat tissue on the spermatogenic process were evaluated. A minimum of three biological replicates were performed for all experiments presented in this study. One-way ANOVA, ANOVA on ranks and student's t-test were applied to perform the statistical analysis. MAIN RESULTS AND THE ROLE OF CHANCE: Male germ cells, present in testicular tissue pieces grown from 5 dpp rats, exhibited positive protein expression for Acrosin and Crem (cAMP (cyclic adenosine mono phosphate) response element modulator) after 52 days of culture in vitro. Intra-testicular testosterone production could be observed after 3 days of culture, while when epididymal fat tissue was added, spontaneous contractility of cultured seminiferous tubules could be observed after 21 days. However, no supportive effect of the supplementation with any factor or the co-culturing with epididymal fat tissue on germ cell differentiation in vitro or testosterone production was observed. LIMITATIONS, REASONS FOR CAUTION: The human testis is very different in physiology from the rat testis, further investigations are still needed to optimize the organ culture system for future use in humans. WIDER IMPLICATIONS OF THE FINDINGS: The successful differentiation of undifferentiated spermatogonia using the testis explant culture system might be employed in future to produce sperm from human spermatogonia as a clinical tool for fertility preservation in boys and men suffering infertility. LARGE SCALE DATA: None. STUDY FUNDING AND COMPETING INTERESTS: This work was supported financially by the Frimurare Barnhuset in Stockholm, the Paediatric Research Foundation, Jeanssons Foundation, Sällskåpet Barnåvard in Stockholm, Swedish Research Council/Academy of Finland, Emil and Wera Cornells Foundation, Samariten Foundation, the Swedish Childhood Cancer Foundation as well as through the regional agreement on medical training and clinical research (ALF) between Stockholm County Council and Karolinska Institutet. All authors declare no conflicts of interests.

Inter-laboratory control data for reproductive endpoints required in the OPPTS 870.3800/OECD 416 reproduction and fertility test.

BACKGROUND: The U.S. EPA revised the Reproduction and Fertility Effects Test Guideline (OPPTS 870.3800/OECD 416) in 1998, adding numerous endpoints in an effort to incorporate new methodologies, improve the sensitivity for detecting reproductive toxicants, and more efficiently utilize study animals. Many of these new endpoints have not been used in regulatory reproductive toxicology studies prior to their inclusion in the test guidelines; thus, the Health and Environmental Sciences Institute (HESI) of the International Life Sciences Institute (ILSI) initiated the Reproductive Endpoints Project to examine the utility of these new endpoints. METHODS: This report provides a retrospective analysis of 43 multi-generation studies (16 in Wistar rats, 27 in Sprague-Dawley rats) conducted according to the latest version of the test guidelines. It focuses on vehicle (negative) control values (means and ranges) for the various endpoints to examine inter-laboratory variability. RESULTS: Based on the compiled data, the most variable endpoints across laboratories and their associated coefficients of variation (CV) for each generation were: percent abnormal sperm (166-205%), testicular spermatid concentration (126-147%), postimplantation loss (97-104%), primordial follicle counts (69%, only measured in P2 females), and epididymal sperm concentration (52-57%). Absolute and relative prostate and thymus weights, weanling uterine weights, and anogenital distance had CVs of 25-50%. Sources of variability included procedural differences between laboratories, inherent biological variability, and/or small sample sizes for some endpoints. CONCLUSIONS: These inter-laboratory control data provide a means for laboratories to review their performance on reproductive toxicity measures, and provide perspective for interpreting their own control data and data from treated animals.

Effects of feed restriction on fertility in female rats.

BACKGROUND: Feed restriction with its resultant body weight loss impacts the rodent estrous cycle; however, the manifestation of these changes in a regulatory study design has not been documented. This study reports the effects of feed restriction in the context of an FDA regulatory submission. METHODS: Adult female rats (n = 20/group; weighing approximately 200 g each) were provided rodent chow ad lib (control) or at 20, 15, 10, or 7.5 g/rat/day (g/day) during a 2-week pre-mating phase, throughout the mating phase, and up to gestation day (GD) 7. On GD 8, all animals were provided ad lib feed until necropsy on GD 14. Estrous cyclicity, mating, and fertility parameters were evaluated. RESULTS: Ad lib rats consumed approximately 20 and 28 g/day during the pre-mating and gestation phases, respectively. All measured fertility parameters in the 20 g/day group were similar to control values. In the 15 g/day group, body weight was reduced by 16% at 2 weeks, prolonged diestrus occurred, and fertility was compromised due to reductions in corpora lutea. Within 2 weeks, mean body weight in groups receiving < or = 10 g/day was reduced by > or = 29% compared to ad lib values, and overt changes in estrous cyclicity, mating, and fertility occurred. The 7.5 g/day group was not sustainable beyond the pre-mating phase. CONCLUSIONS: For this study type, feed intake at < or = 50% ad lib values (< or = 10 g/day) was inadequate due to the magnitude and rapidity of body weight effects. Estrous parameters appeared slightly more sensitive than functional measures, as body weight changes of approximately 16% appeared near the threshold of changing routinely calculated estrous cycle parameters and were later associated with reduced fertility. In general, body weight differences of 10-15% by themselves were not adverse to normal reproduction (20 g/day).

Effects of feed restriction during organogenesis on embryo-fetal development in rabbit.

BACKGROUND: Appropriate maternal nutrition and body weight gain during pregnancy is well established as a major factor in healthy prenatal development in humans. Given the role of nutrition and body weight gain in normal development, pharmaceuticals intended to reduce appetite and promote weight loss will generate developmental toxicity data that may be challenging to interpret. To aid with this, the effects of feed restriction, and subsequent reduction in maternal body weight gain, on embryo-fetal development was investigated in the rabbit. METHODS: Groups of 15 pregnant New Zealand White rabbits were offered 150 (control), 110, 75, 55, 35, and 15 g feed/day from gestation day (GD) 7-19. Cesarean sections were carried out on GD 29 and fetuses were examined for external, visceral, and skeletal development. RESULTS: Maternal body weights at the end of the feed restriction period (GD 20) were 0.97, 0.98, 0.93, 0.94, and 0.86 x control for the 110, 75, 55, 35, and 15 g feed/day groups, respectively. Only at 15 g feed/day was there a net maternal body weight loss (the GD 20 body weight was 0.93 x the GD 6 body weight) at the end of the feed restriction period. Six does aborted in the 15 g feed/day group; there were no other abortions associated with feed restriction. Fetal body weight was significantly reduced at 75, 55, 35, and 15 g feed/day (0.95, 0.90, 0.86, and 0.84 x control, respectively). There were no external or visceral malformations or variations, and no skeletal malformations associated with feed restriction. The incidence of fetuses with sternebrae 5 or 6 unossified was increased at feed levels < or = 75 g/day. At a feed level of 35 g/day there was an increase in unossified metatarsals and metacarpals, and an increase in the number of fetuses with a reduced number of caudal vertebrae ossified. Although these findings were not increased at a feed level of 15 g/day, the lack of dose response was likely due to increased abortion and subsequent decrease in fetuses available for evaluation at 15 g feed/day. CONCLUSION: These data demonstrate that feed restriction to feed levels that produce substantial reductions in maternal body weight gain can result in developmental toxicity expressed by abortion, reduced fetal weight, and alterations in ossification. Abortion only occurred when feed was restricted to an amount that produced maternal body weight loss (15 g feed/day) whereas reduced fetal weight and increased incidence of fetuses with unossified sternebrae, metatarsals, metacarpals, or caudal vertebrae were noted at feed levels of < or = 75 g/day. There were no fetal malformations associated with feed restriction.

The effects of feed restriction during organogenesis on embryo-fetal development in the rat.

BACKGROUND: Given the role of nutrition and body weight gain in normal development, pharmaceuticals intended to reduce appetite and promote weight loss will generate safety data that may be challenging to interpret. To aid with this, the effects of feed restriction and subsequent body weight reductions on embryo-fetal development were investigated in the rat. METHODS: Groups of 20 timed pregnant female Sprague-Dawley rats were offered Certified Rodent Diet 5002 either ad libitum or in restricted amounts of 20, 15, 10, and 7.5 g/day from Gestation Day (GD) 6-17. Clinical signs, body weights, and food consumption were recorded. Cesarean sections were performed on GD 21 and fetuses were sexed, weighed, and examined for external, visceral, and skeletal development. RESULTS: Mean maternal body weights at the end of the feed restriction period, GD 18, were reduced 0.87 x, 0.80 x, 0.69 x, and 0.63 x control mean in the 20, 15, 10, and 7.5 g/day groups, respectively. Mean body weight gains for the restriction period inclusive, GD 6-18, were 0.49 x and 0.24 x control at 10 and 7.5 g/day, respectively, and a mean body weight loss occurred at 10 and 7.5 g/day (0.95 x and 0.85 x mean GD 6 body weight, respectively). Fetal body weights were reduced 0.95 x, 0.93 x, 0.90 x, and 0.76 x control at 20, 15, 10, and 7.5 g/day, respectively. This resulted in a reduction in gravid uterine weight at 10 and 7.5 g/day. There were no external, visceral, or skeletal malformations attributed to feed restriction. There was an increase in the skeletal variation of wavy ribs and a decrease in ossification at 7.5 g/day. CONCLUSIONS: These data demonstrate that feed restriction-induced reductions in maternal gestational body weight gain of approximately 50% compared to ab lib fed rats only caused a reduction in fetal body weight. Even up to a 15% maternal gestational body weight loss had no effect on embryo viability in rats, but retarded fetal growth significantly enough to induce minor changes in skeletal development. There were no external, visceral, or skeletal malformations associated with any of the levels of maternal body weight reduction or loss.

The use of the rat in developmental immunotoxicology studies.

The benefits and costs are discussed for the possibility of using pups generated in breeding studies for additional assessments, such as evaluating immunotoxicity. Such an approach is logistically challenging, but not overwhelming.

Comparison of the developmental and reproductive toxicity of diethylstilbestrol administered to rats in utero, lactationally, preweaning, or postweaning.

The objective of the study was to determine which period of exposure produces the most marked effects on the reproductive capacity and sexual development of the rat, with particular emphasis on the relative sensitivity of in utero and postnatal exposures. The endocrine active chemical, diethylstilbestrol (DES) was used as an agent known to affect many of the endpoints examined. Hitherto, such comparisons have been made between studies, rather than within a study. Our data will be helpful in the interpretation of future multigenerational assay data. In preliminary studies, DES was shown to be active in the immature rat uterotrophic assay with a lowest detected dose of 0.05 mg DES/kg body weight by sc injection and 10 mg DES/l (1.6 mg DES/kg body weight) by administration in drinking water. A dose of 60 microg DES/l drinking water ( approximately 6.5mg DES/kg body weight/day) was selected for the main study since this represented the midpoint of the drinking water uterotrophic dose response and produced no overt maternal toxicity. The study used 10 groups of concomitantly pregnant animals, including 2 control groups. The first comparison was between the effects of exposure to DES in utero, and exposure from conception to weaning. Another group of animals was exposed to DES in utero and cross-fostered to untreated pregnant females to prevent lactational transfer of DES to pups. Two groups were exposed to DES neonatally, either from birth to postnatal day (PND) 10 (pups thus having only lactational exposure), or from birth until weaning (PND 21; pups thus having both lactational exposure and self-exposure via drinking water). In addition, a dose response study to DES was conducted on animals exposed from weaning to PND 100, when the first phase of the study was terminated. Pups exposed to DES in utero and pups exposed from weaning to PND 100 were bred to assess fertility of the F1 animals and the sexual development of F2 offspring. This last comparison was to determine the extent to which weanling rats could be used in endocrine toxicity studies to assess their potential to show activity in utero. The most sensitive period of exposure for inducing developmental effects in F1 animals was from weaning onwards. The neonatal to weaning period (PND 1-21) was the next most sensitive. Essentially no effects were induced in F1 animals exposed in utero. No effects of any kind were observed in animals only exposed over the early neonatal period of PND 1-10. The mean day of vaginal opening, testes descent, and prepuce separation was only altered in groups where postnatal exposure to DES continued beyond PND 10, or was started at weaning. No changes were observed in anogenital distance or caudal sperm counts. Some changes in organ weights were observed, but the interpretation of these was often confused by concomitant changes in body weight. In general, histopathological examination of tissues yielded no additional information. In breeding studies with animals exposed to DES in utero, or from weaning, reduced litter sizes and marginal advances in the day of vaginal opening were observed in the offspring, together with changes in organ weights. However, no unique sensitivity was noted for exposure in utero. Evaluation of the several exposure periods and the many markers monitored in this study may have individual strengths in individual cases, but when rigorously compared using the reference estrogen DES, many preconceptions regarding their absolute or relative value were not upheld. Further, each of these markers is subject to natural variability, as demonstrated by comparisons made among the 5 separate control groups available in parts of the present study. This variability increases the chance that small changes observed in endocrine toxicity studies employing small group sizes and a single control group, or no concomitant control group, may be artifactual. The most marked effects observed in this study were on the developmental landmarks in the F1 animals induced by exposures after PND 10. Some effects on developmental landmarks and organ weights were observed in F2 animals following exposure either in utero or postweaning. This study therefore does not establish a unique role for exposures in utero or during the early neonatal period.

Structure and control of a cell-cell adhesion complex associated with spermiation in rat seminiferous epithelium.

Spermiation, the release of late spermatids from the Sertoli cell, is disrupted by a number of toxicants. Control of the spermiation process, and the proteins that interact to adhere mature spermatids to Sertoli cells, is poorly understood. In these studies we used immunohistochemistry, coimmunoprecipitation/Western blotting, and mass spectrometry to refine an earlier model of sperm adhesion proposed by our laboratory. We have identified specific proteins linked together as part of a multiprotein complex, as well as several additional proteins (cortactin, ERK1/2, and 14-3-3 zeta) that may be functioning in both structural and signal transduction roles. The current and prior data suggest that protein phosphorylation is central to the control of spermiation. We also present and characterize an in vitro tubule culture system that allowed functional testing of the spermiation model by pharmacologic manipulation, and yielded data consistent with the importance of protein phosphorylation in spermiation.

The effects of perinatal tebuconazole exposure on adult neurological, immunological, and reproductive function in rats.

Studies are under way to address concerns of potential persistent immunotoxic, reproductive, and neurotoxic effects of perinatal exposure to several pesticides. Tebuconazole, a triazole fungicide, was evaluated as part of this project. Sprague-Dawley dams were administered tebuconazole (0, 6, 20, or 60 mg/kg) by oral gavage daily from gestational day 14 to postnatal day (PND)7; the pups were then dosed daily at the same levels from PND7-42. Separate groups of rats were used for testing of immunological parameters, neurobehavioral testing using a screening battery of functional tests, and cognitive evaluations. Other groups of rats were evaluated for reproductive development and function, while yet others were sacrificed at the end of the dosing period for histological analyses of major organs systems, including neuropathological assessments. Pup viability and body weight were decreased in the highest dose group. There were no differences in the fertility indices in the exposed rats mated as adults. In the sheep RBC-immunized high-dose rats, spleen weights and cellularity were increased, and the ratio of cell types was altered compared to controls. There were, however, no biologically significant changes in the immune function of these rats. At necropsy on PND46 or 152, kidney, liver, and spleen weights were altered by tebuconazole treatment, but a dose-response relationship was not clear for most organs; only decreased kidney and increased liver weights were consistent in both sexes. Histological analyses were generally unremarkable outside of the brain. One month after the end of dosing, acquisition of learning the platform location in a water tank (i.e., Morris water maze) was impaired in the high-dose group; there were no differences in neuromuscular ability, motor activity, or swim speed to account for this finding. Furthermore, there was no effect on recall of the position during a free-swim trial. Neuropathological evaluations revealed pyknotic cells across hippocampal cell fields in animals of all tebuconazole treatment groups, with the highest incidence in the 20 and 60 mg/kg/day dose groups, coincident with cell loss within pyramidal cell layer of CA3-4 cell fields of the hippocampus and layer V of the neocortex. Thus, perinatal exposure to tebuconazole produced neurobehavioral deficits and neuropathology in rats, but did not alter immunological or reproductive function.

The effects of perinatal/juvenile heptachlor exposure on adult immune and reproductive system function in rats.

This study was performed to determine if developmental exposure of rats to heptachlor (H) during the last half of gestation through puberty adversely affects adult functioning of the immune and reproductive systems. Time-bred pregnant female Sprague-Dawley rats were dosed by gavage with H (0, 30, 300, or 3000 microg/kg/day) from gestation day (GD) 12 to postnatal day (PND) 7, followed by direct dosing of the pups with H through PND 42. Separate groups of rats were evaluated with a battery of immune function tests, while other groups of rats were evaluated for reproductive development and function. Additional groups of rats were euthanized at the end of the dosing period for histological analyses of major organ systems. Some dams and PND 7 pups were euthanized; milk, plasma, fat and/or tissues were assayed for H and heptachlor epoxide B (HEB), a major metabolite of H. The amount of H and HEB found in milk, blood, fat, and tissues was proportional to the dose of H administered. There were no effects on the number or survival of pups born to H-exposed dams nor to pups exposed postnatally. There were no effects on the number of treated dams delivering litters or on litter size, nor were there any effects on any of the reproductive end points examined in the F(0) or F(1) rats. There were no effects of H exposure on lymphoid organ weights, splenic natural killer (NK) cell activity, and splenic lymphoproliferative (LP) responses to mitogens and allogeneic cells in a mixed lymphocyte response (MLR) assay at 8 weeks of age. H exposure did not alter delayed or contact hypersensitivity at 10 or 17 weeks of age, respectively. However, the primary IgM antibody response to sheep red blood cells (SRBCs) was suppressed in a dose-dependent manner in males, but not females, at 8 weeks of age. The percentage of B lymphocytes (OX12(+)OX19(-)) in spleen was also reduced in the high-dose males. The anti-SRBC IgM response was reduced only in males exposed to 30 microg H/kg/day in a separate group of rats 21 weeks of age. In these same rats, at 26 weeks of age, the secondary IgG antibody response to SRBCs was suppressed in all of the H-exposed males, but not females. These data indicate that perinatal exposure of male rats to H results in suppression of the primary IgM and secondary IgG anti-SRBC responses. Suppression of these antibody responses persisted for up to 20 weeks after the last exposure to H, at a total exposure of approximately 1500 microg H/kg/rat.

Neurotoxicological outcomes of perinatal heptachlor exposure in the rat.

The developing nervous system has been identified as a potential target of pesticide exposure. Heptachlor is a cyclodiene pesticide that was widely used for many years, and for which inadvertent exposure to children and fetuses took place in the early 1980s; yet little is known regarding the developmental neurotoxicity of it and other cyclodienes. The aim of this study was to determine whether perinatal heptachlor exposure results in persistent alterations in nervous system function. Pregnant Sprague-Dawley dams were dosed from gestational day (GD) 12 to postnatal day (PND) 7, whereupon the rat pups were dosed directly until PND 21 (group A) or PND 42 (group B). Dose levels were 0, 0.03, 0.3, or 3 mg/kg/day, po. There were no dose-related effects on maternal weight, litter size, or pup growth. GABA(A) receptor binding (using [(35)S] tert-butylbicyclophosphorothionate; TBPS) and GABA-stimulated Cl- flux were evaluated in control and high-dose brain tissues taken on PND 7, 21, and 43. The B(max) values for [(35)S]-TBPS binding in brainstem, but not cortex, were decreased in female rats across all ages tested. There were no such changes in male rats, nor were K(D) values altered in either tissue or gender. GABA-stimulated Cl- flux was decreased in female cortex synaptoneurosomes only on PND 21. The ontogeny of the righting response (PND 2-5) was delayed in the high-dose females. All subsequent testing took place a week to months after dosing ceased. The functional observational battery (FOB) showed treatment-related, but not necessarily dose-related, changes in different aspects of the rat's reactivity and activity levels. Group-A rats also showed altered within-session habituation of motor activity. There were no heptachlor-related differences in motor activity following challenge with a range of chlordiazepoxide doses. Cognitive assessments were conducted in both groups of rats. There were no statistically significant differences among treatment groups in a one-trial passive avoidance test, although there was a trend toward less learning. In group B, rats (both sexes), heptachlor altered spatial learning in the Morris water maze during two weeks of daily training (2 trials/day). On probe trials, heptachlor-treated rats did not show significant preference for the correct quadrant (all dose groups in males, high dose in females). These rats did not show alterations on subsequent working-memory training (where the platform position was relearned each day). Thus, perinatal exposure to heptachlor produced neurochemical and persistent neurobehavioral changes, including alterations in spatial learning and memory.

Protein kinase activity is central to rat germ cell apoptosis induced by methoxyacetic acid.

Methoxyacetic acid (MAA) is a major metabolite of ethylene glycol monomethyl ether (EGME). Previous investigations of the testicular lesion induced by EGME have found that dividing meiotic cells are the most sensitive, although several stages of spermatocytes are also vulnerable. Preliminary data from this lab suggested the involvement of protein kinase activity in the development of this lesion, a hypothesis explored in the present studies. We used cultured seminiferous tubules (STs) from juvenile rats (25-day-old), exposed in vitro to MAA and several inhibitors of protein kinases. Nineteen h following a 5-h exposure to 5 mM MAA (the plasma level in vivo after a toxic dose of EGME), apoptotic spermatocytes were seen in early- and late-stage STs. Cell death was prevented by cotreatment with broad-spectrum inhibitors of protein kinases such as H-7, H-8, K-252a, W-7, and genistein. In corroboration, immunocytochemistry with antibodies to various kinases (PKCmu, zeta, and gamma, AKAP220, CaMKII, MLCK, and Src) showed increased staining around dying spermatocytes following EGME treatment in vivo. 2D-PAGE, autoradiography, and nanospray mass spectrometry was used to separate and identify proteins whose phosphorylation status was most greatly changed following exposure to MAA. One protein was identified by sequence analysis as being glucose-regulated protein 94 (grp94). Westem blotting and immunocytochemistry confirmed this finding. The data we present implicate kinase activities in the pathogenesis of this lesion and suggest the involvement of Sertoli cells.

Effects of arsenic, cadmium, chromium, and lead on gene expression regulated by a battery of 13 different promoters in recombinant HepG2 cells.

Toxic metals occur naturally at low concentrations throughout the environment, but are found in higher concentrations at many of the hazardous waste sites on the EPA Superfund list. As part of the Agency for Toxic Substances and Disease Registry (ATSDR) mandate to evaluate the toxicity of metals and mixtures, we chose four of the high-priority metal pollutants from ATSDR's HAZDAT list, including arsenic, cadmium, chromium, and lead, to test in a commercially developed assay system, CAT-Tox(L) (Xenometrix). This assay employs a battery of recombinant HepG2 cell lines to test the transcriptional activation capacity of xenobiotics in any of 13 different signal transduction pathways. Our specific aims were to identify metal-responsive promoters and determine whether the pattern of gene expression changed with a mixture of metals. Humic acid was used in all assays as a carrier to help solubilize the metals and, in all cases, the cells were exposed to the humic acid-metal mixture for 48 h. Humic acid alone, at 50-100 microM, showed moderate activation of the XRE promoter, but little other notable activity. As(V), at doses of 50-250 microM, produced a complex profile of activity showing significant dose-dependent induction of the hMTIIA, GST Ya, HSP70, FOS, XRE, NFkappaBRE, GADD153, p53RE, and CRE promoters. Pb(II) showed dose-related induction of the GST Ya, XRE, hMTIIA, GRP78, and CYP IA1 promoters at doses in the range of 12-100 microM. Cd(II), at 1.25-15 microM, yielded significant dose-dependent induction of hMTIIA, XRE, CYP IA1, GST Ya, HSP70, NFkappaBRE, and FOS. Whereas Cr(III) yielded small, though significant inductions of the CRE, FOS, GADD153, and XRE promoters only at the highest dose (750 microM), Cr(VI) produced significant dose-related inductions of the p53RE, FOS, NFkappaBRE, XRE, GADD45, HSP70, and CRE promoters at much lower doses, in the range of 5-10 microM. Assays testing serial dilutions of a mixture comprising 7.5 microM Cd(II), 750 microM Cr(III), and 100 microM Pb(II) (the combination of metals most frequently found at National Priority List sites) showed significant dose-dependent induction of the hMTIIA promoter, but failed to show dose-related induction of any other promoter and showed no evidence of synergistic activation of gene expression by the metals in this mixture. Our results thus show metal activation of gene expression through several previously unreported signal transduction pathways, including As(V) induction of GST Ya, FOS, XRE, NFkBRE, GADD153, p53RE, and CRE; Pb(II) induction of GST Ya, XRE, Cyp IA1, and GADD153; Cd(II) induction of NFkBRE, Cyp IA1, XRE, and GST Ya; and Cr(VI) induction of p53RE, XRE, GADD45, HSP70, and CRE promoters, and thus suggest new insights into the biochemical mechanisms of toxicity and carcinogenicity of metals. It is also an important finding that no evidence of synergistic activity was detected with the mixture of Cd(II), Cr(III), and Pb(II) tested in these assays.

Exposure to hazardous substances and male reproductive health: a research framework.

The discovery in the mid-1970s that occupational exposures to pesticides could diminish or destroy the fertility of workers sparked concern about the effects of hazardous substances on male reproductive health. More recently, there is evidence that sperm quantity and quality may have declined worldwide, that the incidence of testicular cancer has progressively increased in many countries, and that other disorders of the male reproductive tract such as hypospadias and cryptorchidism may have also increased. There is growing concern that occupational factors and environmental chemical exposures, including in utero and childhood exposures to compounds with estrogenic activity, may be correlated with these observed changes in male reproductive health and fertility. We review the evidence and methodologies that have contributed to our current understanding of environmental effects on male reproductive health and fertility and discuss the methodologic issues which confront investigators in this area. One of the greatest challenges confronting researchers in this area is assessing and comparing results from existing studies. We elaborate recommendations for future research. Researchers in the field of male reproductive health should continue working to prioritize hazardous substances; elucidate the magnitude of male reproductive health effects, particularly in the areas of testicular cancer, hypospadias, and cryptorchidism; develop biomarkers of exposure to reproductive toxins and of reproductive health effects for research and clinical use; foster collaborative interdisciplinary research; and recognize the importance of standardized laboratory methods and sample archiving.

Prioritization of NTP reproductive toxicants for field studies.

Population studies that evaluate human reproductive impairment are time consuming, expensive, logistically difficult, and with limited resources must be prioritized to effectively prevent the adverse health effects in humans. Interactions among health scientists, unions, and industry can serve to identify populations exposed to potential hazards and develop strategies to evaluate and apply appropriate controls. This report describes a systematic method for prioritizing chemicals that may need human reproductive health field studies. Rodent reproductive toxicants identified from the National Toxicology Program (NTP) Reproductive Assessment by Continuous Breeding (RACB) protocol were prioritized on the basis of potency of toxic effect and population at risk. This model for prioritization links NTP findings with data from the National Occupational Exposure Survey (NOES) and the Hazardous Substance Data Base (HSDB) or the High Production Volume Chemical Database (HPVC) to prioritize chemicals for their potential impact on worker populations. The chemicals with the highest priority for field study were: dibutyl phthalate, boric acid, tricresyl phosphate, and N, N-dimethylformamide.

Differential gene expression detected by suppression subtractive hybridization in the ethylene glycol monomethyl ether-induced testicular lesion.

The solvent ethylene glycol monomethyl ether (EGME) produces the same testicular lesions in rodents and human testis cultures, whose onset is characterized by apoptosis of pachytene spermatocytes. To identify gene changes early in the lesion and determine the possible involvement of cells other than the spermatocytes, we employed a suppression subtractive hybridization technique using whole testes from mice treated 8 h previously with 500 mg/kg EGME to generate two subtracted mouse testis cDNA libraries enriched for gene populations either up-regulated or down-regulated by EGME. A total of 70 clones were screened, and 6 of them were shown by Northern blotting to be differentially expressed in the EGME lesion. The three clones with increased expression after EGME treatment were identical to t-complex testis expressed gene 1 (tctex1), a gene encoding ribosomal protein S25, and a heretofore uncharacterized mouse testis expressed sequence tag. Three other genes suppressed by EGME were tctex2, alpha-2,6-sialyltransferase gene, and another uncharacterized mouse testis expressed sequence tag. Predicted peptide sequences of these clones contain multiple motifs for phosphorylation, glycosylation, and myristoylation. In situ hybridization with the antisense RNA probes further supported the expression changes of these six clones and localized the changes in multiple germ cell stages as well as other cell types (Sertoli, interstitial and peritubular cells). These data at the gene expression level are the first to demonstrate the early involvement in this lesion of cell types other than the dying spermatocytes.

Six high-priority organochlorine pesticides, either singly or in combination, are nonestrogenic in transfected HeLa cells.

There have been increasing concerns that environmental chemicals may adversely affect the health of humans and wildlife by acting as endocrine modulators. These concerns have been augmented by the realization that human exposure occurs not just to single chemical agents, but typically to mixtures of chemicals that could exhibit estrogenic activity qualitatively and/or quantitatively different from that of individual components. To address these concerns, we have evaluated the ability of six organochlorine pesticides (4, 4'-DDT, 4,4'-DDD, 4,4'-DDE, aldrin, dieldrin, or endrin, all classified high priority by ATSDR) to modulate transcriptional activation of an estrogen-responsive reporter gene in transfected HeLa cells. In these assays, HeLa cells cotransfected with an expression vector encoding estrogen receptor and an estrogen-responsive chloramphenicol acetyltransferase (CAT) reporter plasmid were exposed to these pesticides individually and in defined combinations. While estradiol consistently elicited 10- to 23-fold dose-dependent inductions in these assays, the six organochlorine pesticides showed no detectable dose-related response when tested individually. When tested in binary combinations, the pesticide mixtures showed no additional estrogenicity. Thus, the pesticides tested, singly or as mixtures, showed virtually no evidence of estrogenicity.

Rat testicular Src: normal distribution and involvement in ethylene glycol monomethyl ether-induced apoptosis.

Kinase activities were previously proposed to be central to germ cell apoptosis induced by ethylene glycol monomethyl ether (EGME) and its active metabolite methoxyacetic acid (MAA). We evaluated the role of tyrosine kinase pp60(c-src) in control and EGME-treated adult rat testis in vivo, as well as in vitro using cultured adult rat seminiferous tubules treated with MAA. In normal testicular tissue, immunoreactivity of Src was mostly detected in Sertoli cell cytoplasm and reached the maximum level around the lumen at spermiation. Src localization was confirmed by immunostaining of cocultures of Sertoli and germ cells and was further confirmed by electron microscopic observation that immunoreactivity was predominant in Sertoli cell cytoplasm as well as occasionally at the Sertoli/germ cell junctions. A single dose of 200 mg/kg EGME induced an increase of Src immunoexpression in both epithelium and interstitium in rat testis. Eight hours after treatment, an intensive immunostaining of Src began to be observed specifically in the cytoplasm of the dying spermatocytes. The apoptotic changes were replicated by exposure of 5 mM MAA in the adult rat seminiferous tubule culture model. Furthermore, spermatocyte degeneration was significantly prevented by cotreatment with 0.1 microM geldanamycin, 10 microM herbimycin A, or 10 microM PP2, which are inhibitors of Src activity. These data collectively suggest that pp60(c-src) mediates Sertoli-germ cell interaction in physiological events, and may play an important role in EGME/MAA-induced germ cell apoptosis.

The effects of 4-nonylphenol in rats: a multigeneration reproduction study.

The alkylphenol breakdown products of alkylphenol ethoxylates have been shown in in vitro studies to be weakly estrogenic, but few in vivo data address this issue in mammals. Because estrogens have been found to be most potent during developmental/perinatal exposures, this study maximized developmental exposure to nonylphenol (NP) by treating 3.5 generations of Sprague-Dawley rats to NP in diet at 200, 650, and 2000 ppm to determine the range and severity of any toxicity. Dose rate was higher for younger rats; calculated dose ranges were 9-35, 30-100, and 100-350 mg/kg/d for the low (200NP), middle (650NP), and high (2000NP) dose groups, respectively. There were adult (F0, F1, F2) and postnatal day (pnd) 21 (F1, F2, F3) necropsies; the oldest F3 rats were killed on pnd 55-58. Body weight gain was reduced by 8-10% in the 650NP and 2000NP groups. Vaginal opening was accelerated by approximately 2 days (650NP) and approximately 6 days (2000NP) in F1, F2, and F3 generations. Uterine weights at pnd 21 were increased in 650NP (14%) and 2000NP (50%) F1 females, but not in other generations. Testis descent, anogenital distance, and preputial separation were not consistently changed. No consistent changes were seen in pup number, weight or viability, litter indices, or other functional reproductive measures. Relative ovary weight in F2 adults was decreased at 650NP and 2000NP by 12%; relative ovary was unchanged in other generations. Follicle counts were unchanged in F2 adults. Sperm indices, including CASA measures, were unchanged in F0 and F1 males. In F2 rats, epididymal sperm density was reduced by 8% and 13% at 650NP and 2000NP, respectively. Testicular spermatid count was reduced by 13% in 2000NP F2 males; testis and epididymis weights were unchanged. Erosion of gastric and duodenal mucosa was monitored grossly and microscopically, and never found. Kidney weights were increased in 650NP and 2000NP males, and renal medullary tubular dilatation and cyst formation were noted in all generations of males, and often at the lowest dose tested. These data show that NP had limited effects on the reproductive system in the presence of measurable nephrotoxicity. The F2 sperm effects are either statistical/biological "noise," or imply heretofore unknown pharmacokinetics or toxicodynamics. These sperm data should be interpreted cautiously until the findings are repeated.