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Biomedical subjects

P M Foster

Publications and source records attributed to P M Foster.

At least 19 recordsLinked to original sources

Androgen-mediated development in male rat offspring exposed to flutamide in utero: permanence and correlation of early postnatal changes in anogenital distance and nipple retention with malformations in androgen-dependent tissues.

Male offspring exposed in utero to antiandrogens often display alterations in androgen-dependent developmental markers (e.g., anogenital distance [AGD], nipple retention) together with clearly adverse responses such as genital malformations and reproductive tract lesions. The objectives of this study were to determine whether in utero exposure to flutamide results in permanent changes in male AGD and nipple retention, characterize the dose-response relationship between flutamide-mediated alterations in these landmarks and clearly adverse antiandrogenic effects, and establish the predictive value and relationship between AGD and nipple retention, and other adverse manifestations. Male offspring were exposed in utero to 0, 6.25, 12.5, 25, or 50 mg/kg/day (po) of flutamide from gestation days 12 to 21. Offspring were uniquely identified at birth, and various androgen-mediated end points (AGD, areola/nipple retention, cryptorchidism, reproductive tract weights, and malformation incidence) were examined throughout life. In utero flutamide exposure significantly decreased the AGD on postnatal day (PND) 1 and increased areola/nipple retention in male rats on PND 13. Flutamide-induced alterations in AGD and areolae/nipples in early postnatal life correlated with a reduction in AGD and retained nipples observed in the adult. Prenatal flutamide exposure resulted in dose-responsive increases in cryptorchidism. Hypospadias were observed in all flutamide-exposed offspring. In utero flutamide exposure induced partial or complete prostate agenesis and decreased the weights of the seminal vesicles, levator ani bulbocavernosus (LABC) muscle, testes, and epididymides in a dose-dependent manner. Epididymal malformations were observed mainly in the 50 mg/kg/day flutamide dose group. In general, flutamide-induced alterations in dihydrotestosterone (DHT)- and testosterone (T)-dependent development each had similar respective dose-response curves. DHT-mediated development was more sensitive to in utero flutamide exposure than T-dependent processes. However, the dose-response curves for flutamide-induced changes in cryptorchidism and seminal vesicle weight were intermediate between the dose-response curves for DHT- and T-mediated development, indicating that proper development of these tissues may require both androgens. The LABC also displayed a dose-dependent decrease in weight that was similar to dose-response observed with seminal vesicle weight and was the most sensitive T-dependent end point measured. Flutamide-induced decreases in AGD predicted subsequent malformations as evidenced by logistic regression and receiver operator characteristic analysis of malformations versus AGD. However, the AGD that would predict a 10% incidence of seminal vesicle malformations is equivalent to a female AGD. An almost fully feminized phenotype of 10-12 nipples was observed in animals that had malformations in T-dependent tissues, whereas 6 or more nipples were observed in animals with malformation in DHT-dependent tissues. These data suggest that flutamide-mediated changes in AGD and nipple retention are not sensitive predictors of altered T-mediated development.

Anal Canal↗

Altered gene profiles in fetal rat testes after in utero exposure to di(n-butyl) phthalate.

Di(n-butyl) phthalate (DBP) has antiandrogenic-like effects on the developing reproductive tract in the male rat and produces regions of interstitial cell hyperplasia and gonocyte degeneration in the developing fetal testes at maternal doses of 100-500 mg/kg/day. Neither DBP nor its primary metabolites interact with the androgen receptor in vitro. The present study was performed to examine gene expression in the fetal rat testes following in utero DBP exposure. Pregnant Sprague-Dawley rats received corn oil, DBP (500 mg/kg/day), or flutamide (reference antiandrogen, 50 mg/kg/day) by gavage daily from gestation day (GD) 12 to 21. Dose levels were selected to maximize fetal response with minimal maternal toxicity. Testes were isolated on GD 16, 19, and 21. Global changes in gene expression were determined by microarray analysis. Selected genes were further examined by quantitative RT-PCR. DBP, but not flutamide, reduced expression of the steroidogenic enzymes cytochrome P450 side chain cleavage, cytochrome P450c17, and steroidogenic acute regulatory protein. Testicular testosterone and androstenedione were decreased on GD 19 and 21, while progesterone was increased on GD 19 in DBP-exposed testes. Testosterone-repressed prostate message-2 (TRPM-2) was upregulated, while c-kit (stem cell factor receptor) mRNA was downregulated following DBP exposure. TRPM-2 and bcl-2 protein staining was elevated in GD 21 DBP-exposed Leydig and Sertoli cells. Results of this study have led to the identification of several possible mechanisms by which DBP can induce its antiandrogenic effects on the developing male reproductive tract without direct interaction with the androgen receptor. Our results suggest that the antiandrogenic effects of DBP are due to decreased testosterone synthesis. In addition, enhanced expression of cell survival proteins such as TRPM-2 and bcl-2 may be involved in DBP-induced Leydig cell hyperplasia, whereas, downregulation of c-kit may play a role in gonocyte degeneration. Future studies will explore the link between these identified gene expression alterations and ultimate adverse responses.

Androgen Antagonists↗

Effects of in utero exposure to linuron on androgen-dependent reproductive development in the male Crl:CD(SD)BR rat.

Linuron (3-(3,4-dichlorophenyl)-1-methoxy-1-methylurea) is a herbicide that blocks androgen action in the male rat. Studies were undertaken to characterize the ability of linuron to activate transcription through the human androgen receptor (AR) in vitro and to determine whether in utero linuron exposure induces dose-responsive alterations in androgen-dependent reproductive development in the male rat. In vitro, linuron competitively antagonized transcriptional activity of the AR induced by dihydrotestosterone (DHT) in a dose-responsive manner with an equilibrium dissociation constant (K(B)) of 75.8 x 10(-8) M. Pregnant rats were administered linuron by gavage at 0, 12.5, 25, or 50 mg/kg/day (n = 11/group) from gestation day 12 to 21. Anogenital distance of resulting offspring was unaffected, whereas male areola/nipple retention was increased in a dose-responsive manner. Hypoplastic testes in adult offspring were seen in 2/56 rats (2/10 litters), 8/69 rats (4/11 litters), and 5/44 rats (3/8 litters), while hypoplastic epididymides occurred in 1/56 rats (1/10 litters), 8/69 rats (4/11 litters), and 2/44 rats (1/8 litters) in the 12.5, 25, and 50 mg/kg/day dose groups, respectively. Partial agenesis of the epididymides was observed in 3/44 rats (2/8 litters) only in the 50 mg/kg/day group. These data indicate that in utero exposure to linuron preferentially impairs testosterone-mediated, rather than DHT-mediated, reproductive development. This effect is distinctly different from the effects induced by flutamide, an AR antagonist that shares structural similarities with linuron. Furthermore, these data suggest that dose-response studies utilizing late gestational exposure to endocrine-active compounds may be more robust than the traditional or EPA-modified multigeneration protocols in identifying adverse effects.

Androgens↗

Effects of di-n-butyl phthalate (DBP) on male reproductive development in the rat: implications for human risk assessment.

The National Toxicology Program (NTP) conducted a continuous breeding study in SD rats with di-n-butyl phthalate (DBP) given via the diet at dose levels of up to 650 mg/kg/day. In the parental generation effects on reproduction were modest (small decreases in litter size and pup weight following treatment). However, the F(1) male offspring had marked decreases in fertility (at 650 mg/kg/day), with reduced sperm counts and reproductive tract malformations on reaching adulthood. A no-observed-adverse-effect level (NOAEL) was not established for the study [lowest-observed-adverse-effect level (LOAEL) 66 mg/kg/day]. In a study conducted at CIIT, the majority of these adverse changes could be reproduced over a similar dose range, but with a much shorter dosing regimen covering a critical window of development (gestation days 12-20). A default risk assessment for DBP indicates a reference dose (RfD) of 66 microg/kg/day, based on a LOAEL of 66 mg/kg/day and default factors of 10 for inter-species and inter-individual differences and the lack of a NOAEL. Human exposure data would indicate worst-case scenarios to infants (via formula) in the dose range of the RfD. A default risk assessment appears to be inappropriate since rodents, unlike primates, metabolize phthalate diesters (including DBP) to monoesters extensively in the gut following oral administration. It is believed that the monoester is the active principle for induction of reproductive and developmental toxicity of specific phthalate esters. Thus, if humans produce very low levels of the monoester from an environmental exposure to the diester, the likelihood of any reproductive or developmental toxicity via the oral route appears extremely remote.

Animals↗

Dose-dependent alterations in androgen-regulated male reproductive development in rats exposed to Di(n-butyl) phthalate during late gestation.

Di(n-butyl) phthalate (DBP) is a commercially important plasticizer and ubiquitous environmental contaminant. Since previous, limited dose-response studies with DBP that reported alterations in male reproductive development and function failed to establish a NOAEL (no-observed-adverse-effect level), an extensive dose-response study was conducted. Pregnant CD rats were given DBP by gavage at 0, 0.5, 5, 50, or 100 mg/kg/day (n = 19-20) or 500 mg/kg/day (n = 11) from gestation day 12 to 21. In male offspring, anogenital distance was decreased at 500 mg DBP/kg/day. Retained areolas or nipples were present in 31 and 90% of male pups at 100 and 500 mg/kg/day, respectively. Preputial separation was not delayed by DBP treatment in males with normal external genitalia, but cleft penis (hypospadias) was observed in 5/58 rats (4/11 litters) at 500 mg/kg/day. Absent or partially developed epididymis (23/58 rats in 9/11 litters), vas deferens (16/58 animals in 9/11 litters), seminal vesicles (4/58 rats in 4/11 litters), and ventral prostate (1/58 animals) occurred at 500 mg/kg/day. In 110-day-old F(1) males, the weights of the testis, epididymis, dorsolateral and ventral prostates, seminal vesicles, and levator ani-bulbocavernosus muscle were decreased at 500 mg/kg/day. At 500 mg/kg/day, widespread seminiferous tubule degeneration was seen in 25/58 rats (in 9/11 litters), focal interstitial cell hyperplasia in 14/58 rats (in 5/11 litters), and interstitial cell adenoma in 1/58 rats (in 1/11 litters). For this 10-day prenatal (embryonic and fetal) exposure to DBP, the NOAEL and LOAEL (lowest-observed-adverse-effect level) were 50 and 100 mg/kg/day, respectively. This is currently the lowest NOAEL described for the toxicity of DBP.

Androgens↗

Disruption of androgen-regulated male reproductive development by di(n-butyl) phthalate during late gestation in rats is different from flutamide.

Gestational and lactational exposure to di(n-butyl) phthalate (DBP) at >/=250 mg/kg/day disrupts male rat reproductive development and function. Although this indicates an antiandrogenic mechanism, DBP and its biologically active metabolite do not interact with the androgen receptor (AR) in vitro. In the present study, we compared the effects of DBP and the antiandrogen flutamide using a shorter exposure during the prenatal period of male sexual differentiation in rats. Pregnant CD rats received DBP at 0, 100, 250, or 500 mg/kg/day po (n = 10) or flutamide at 100 mg/kg/day po (n = 5) from Gestation Days 12 to 21. In F1 males, DBP (500 mg/kg/day) and flutamide caused hypospadias; cryptorchidism; agenesis of the prostate, epididymis, and vas deferens; degeneration of the seminiferous epithelium; and interstitial cell hyperplasia of the testis. Flutamide and DBP (250 and 500 mg/kg/day) also produced retained thoracic nipples and decreased anogenital distance. Interstitial cell adenoma occurred at 500 mg DBP/kg/day in two males. The only effect seen at 100 mg DBP/kg/day was delayed preputial separation. In contrast to flutamide, DBP caused a low incidence of prostate agenesis and hypospadias with no vaginal pouch. The low incidence of DBP-induced intraabdominal testes contrasted with the high incidence of inguinal testes seen with flutamide. Thus prenatal male sexual differentiation is a sensitive period for the reproductive toxicity of DBP. A no observed adverse effect level was not established and the lowest observed (adverse) effect level was 100 mg/kg/day. Flutamide and DBP disrupted the androgen signaling necessary for male sexual differentiation but with a different pattern of antiandrogenic effects. DBP is an example of an environmental antiandrogen that disrupts androgen-regulated male sexual differentiation without interacting directly with the AR, as does flutamide.

Abnormalities, Drug-Induced↗

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 LC's 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)

Animals↗

Male reproductive tract malformations in rats following gestational and lactational exposure to Di(n-butyl) phthalate: an antiandrogenic mechanism?

Di(n-butyl) phthalate (DBP), a widely used plasticizer suspected of having estrogenic properties, was investigated for its effects on the prenatal and early neonatal development of the reproductive tract. Pregnant CD rats (n = 10) were given DBP at 0, 250, 500, or 750 mg/kg/day (p.o.) throughout pregnancy and lactation until their offspring were at postnatal day 20. Maternal body weights throughout the dosing period were comparable in all groups. At 750 mg/kg/day, the number of live pups per litter at birth was decreased and maternal effects on pregnancy and postimplantation loss are likely to have occurred. Anogenital distance was decreased at birth in the male offspring at 500 and 750 mg/kg/day. The epididymis was absent or underdeveloped in 9, 50, and 71% of adult offspring (100 days old) at 250, 500, and 750 mg/kg/day, respectively, and was associated with testicular atrophy and widespread germ cell loss. Hypospadias occurred in 3, 21, and 43% of males and ectopic or absent testes in 3, 6, and 29% of males at 250, 500, and 750 mg/kg/day, respectively. Absence of prostate gland and seminal vesicles as well as small testes and seminal vesicles were noted at 500 and 750 mg/kg/day. Vaginal opening and estrous cyclicity, both estrogen-dependent events, were not affected in the female offspring, although low incidences of reproductive tract malformations were observed at 500 and 750 mg/kg/day. In the male offspring, DBP produced the same spectrum of effects elicited by the antiandrogen flutamide. Thus, DBP specifically impaired the androgen-dependent development of the male reproductive tract, suggesting that DBP is not estrogenic but antiandrogenic in the rat at these high dose levels. For human risk assessment, determining if this toxicity is metabolite-mediated will be critical, since marked species differences in metabolism exist.

Androgen Antagonists↗

Expression cloning of a rat testicular transcript abundant in germ cells, which contains two leucine zipper motifs.

The aim of the present study was to identify specific, novel germ cell markers that could be used to monitor normal and abnormal spermatogenesis. Of several cloned cDNAs isolated from an adult rat testis cDNA library using an expression screening strategy, clone 813B4 (700 base pairs) hybridized exclusively to three mRNA transcripts in samples isolated from rat testes on and after Day 21 of life and to epididymides from some, but not all, adult rats. After further screening, two identical clones encoding a 2.2-kilobase cDNA (KTT4) were isolated and found to contain an open reading frame of 578 amino acids including two leucine zipper motifs. On Northern blots, KTT4 mRNA was abundant in samples from round spermatids, and homologous mRNAs were present in testes from mice and marmosets. A zoo blot revealed that the KTT4 gene is conserved in humans, monkeys, mice, dogs, and cattle. On sections of rat testes, KTT4 mRNA was first detectable in pachytene spermatocytes at stage VII and thereafter was abundant in round and elongating spermatids until step 15. Expression of KTT4 was not altered by ethane dimethane sulphonate-induced androgen withdrawal, but in rats treated 14 days previously with methoxyacetic acid, a marked reduction in KTT4 was noted associated with the depletion of round spermatids. In conclusion, the present study identified a conserved gene expressed in meiotic and post-meiotic germ cells; database searches have shown it to be homologous to recently published sequences for an outer dense fiber protein of the sperm tail (Odf2/Odf84).

Amino Acid Sequence↗

The effect of implantation of osmotic pumps on rat thyroid hormone and testosterone levels in the plasma, an implication for tissue 'S' phase studies.

In order to monitor the effect of the procedures required to s.c. implant osmotic pumps into rats on plasma thyroid and testosterone hormone levels, male Fischer 344 rats (8-10 weeks old) were divided into six groups of 10 rats and the groups treated in the following manner: (1) controls housed 5 per cage; (2) controls housed individually; (3) animals anaesthetised for surgery and individually housed; (4) anaesthetised, sham operated and individually housed; (5) anaesthetised, s.c. implanted with osmotic pumps containing saline and individually housed; (6) anaesthetised, s.c. implanted with osmotic pumps containing 5-bromo 2-deoxyuridine (BRDU) and individually housed. Four days after performing the surgery the study was terminated and the level of hormones in the plasma determined by radio immunoassay (RIA). Tri-iodothyronine (T3) and thyroxine (T4) plasma levels (free and total) were significantly decreased with each additional step in the procedure used for the s.c. implantation of an osmotic pump containing BRDU, when compared with the individually housed controls. Similarly, testosterone plasma levels were significantly decreased by the s.c. implantation of osmotic pumps, implying a 'stress' response might occur following implantation. These observations might need to be considered by investigators when performing toxicological research which, as part of the study, uses osmotic pumps for the delivery of the nucleotide precursor required for monitoring cells in 'S' phase.

Animals↗

Application of benchmark dose risk assessment methodology to developmental toxicity: an industrial view.

The U.S. EPA first signalled its intention to use benchmark dose risk techniques in 1991. Subsequently, publication of draft Guidelines for the Risk Assessment of Reproductive Toxicity data indicated the Agency's intention for wide use of the technique. In developmental toxicity experiments, a number of factors need to be considered before attempting benchmark dose calculations, as compared to the conventional NOAEL approach. For example, care in the assessment of potential litter effects (the litter is the unit of such a study) on the data and whether the data are continuous (e.g. foetal body weight) or discontinuous (e.g. specific or grouped developmental defects where the abnormality is present or absent). Two examples of the use of the benchmark dose approach will be made. First, in the analysis of foetal body weight, where a benchmark dose estimate for an agent producing a 5% decrease in mean foetal weight may be calculated from a shift in the distribution of foetal weights between groups, or by conversion of data to reflect changes in the incidence of 'small' pups (i.e. those towards the extreme of the normal range). The second example involves studies conducted on the developmental toxicity of a triazole antifungal. In the first study, the agent was clearly teratogenic, but a NOAEL was not established and thus necessitated a second study. Analysis of benchmark does estimates (e.g. for % foetuses malformed) from the first study indicated that these were not significantly changed when the data from the second study were combined (i.e. the second study did not aid the risk assessment). The benchmark dose approach has significant scientific and practical advantages over the conventional NOAEL methodology in risk assessments derived from developmental toxicity studies.

Animals↗

Identification of stage-specific changes in protein secretion by isolated seminiferous tubules from rats following exposure to short-term local testicular heating.

The objective of this study was to identify the early (after 4 and 24 h) effects of short-term local testicular heating (43 degrees C for 30 min) on the secretion of proteins by seminiferous tubules isolated from adult rats at stages II-V, VI-VIII or IX-XII of the spermatogenic cycle, and cultured in vitro for 24 h with [35S]methionine. Incorporation of [35S]methionine into secreted and intracellular proteins was assessed and the pattern of protein secretion was evaluated using two-dimensional SDS-PAGE. Seminiferous tubules isolated from control rats exhibited the characteristic, androgen-dependent increase in protein secretion at stages VI-VIII. At 4 h after exposure to local testicular heating, seminiferous tubules at these stages showed a significant increase (P < 0.001) in the overall incorporation of [35S]methionine into secreted proteins, whereas seminiferous tubules at stages II-V and IX-XII showed no significant change. In marked contrast, seminiferous tubules isolated from rats 24 h after local testicular heating showed a significant decrease in the incorporation of [35S]methionine into secreted proteins at stages VI-VIII (P < 0.001) and to a lesser extent at IX-XII (P < 0.05), whereas seminiferous tubules at stages II-V showed no change in incorporation. Prior treatment to maintain normal intratesticular concentrations of testosterone in heat-exposed rats failed to prevent these changes. Similar results were obtained when incorporation of [35S]methionine into intracellular proteins was evaluated 4 and 24 h after exposure to local testicular heating.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

Identification of stage-specific changes in protein secretion by isolated seminiferous tubules from the rat following exposure to either m-dinitrobenzene or nitrobenzene.

The objective of this study was to identify effects of two known Sertoli cell toxicants on the secretion of proteins by seminiferous tubules (ST) isolated from adult rats at different stages of the spermatogenic cycle and cultured in vitro for 24 hr with [35S]methionine. Adult rats received a single oral dose of 50 mg/kg metadinitrobenzene (m-DNB) or 300 mg/kg nitrobenzene (NB). Long lengths of ST at stages II-V, VI-VIII or IX-XII were then isolated from control and treated rats at 1 or 3 days post-treatment; selection of stages was based on the stage specificity of the early (24-72 hr) adverse effects of m-DNB and NB on spermatogenesis in vivo. In addition, ST at the same stages were isolated from untreated rats and cultured in the presence or absence of m-DNB or NB (10(-4)M). Incorporation of [35S]methionine into secreted proteins was assessed and the pattern of protein secretion evaluated using two-dimensional sodium dodecyl sulfate-polyacrylamide gel electrophoresis (2-D SDS-PAGE). ST isolated from rats pretreated 24 hr earlier with NB in vivo showed a significant decrease in the overall incorporation of [35S]methionine into secreted proteins at stages VI-VIII and IX-XII, whereas ST at stages II-V showed no such change; comparable protein changes were observed when 10(-4) M NB was added in vitro for 24 hr to ST isolated at the same stages from untreated rats.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

Effect of age on seminiferous tubule protein secretion and the adverse effects of testicular toxicants in the rat.

This study has assessed the effect of age on protein secretion by seminiferous tubules (ST) isolated from rats and their response to Sertoli cell toxicants. ST were isolated from immature (aged 28 days), late pubertal (aged 45 days) and young adult (aged 70 days) rats and cultured in vitro for 24 h with 35S-methionine in the presence or absence of FSH (1 mg/ml), m-dinitrobenzene (m-DNB) or nitrobenzene (NB) (both at 10(-4)M). Incorporation of 35S-methionine into newly synthesized proteins in the culture medium (secreted proteins) was assessed and the pattern of protein secretion evaluated using two-dimensional sodium dodecylsulphate polyacrylamide gel electrophoresis (2-D SDS-PAGE). These data were compared with those obtained using cultures of immature rat Sertoli cells+germ cells (SC+GC). Addition of FSH, m-DNB or NB in vitro either had no effect (NB) or had a small stimulatory effect (FSH and m-DNB) on the incorporation of 35S-methionine into overall secreted proteins by ST isolated from immature rats. At the same doses, addition of either FSH, m-DNB or NB to SC+GC co-cultures resulted in increased incorporation of radiolabel into secreted proteins in all instances. In contrast, the same additions to ST isolated from adult rats resulted in a 20-34% decrease in the overall incorporation of 35S-methionine into secreted proteins. ST isolated from late pubertal rats showed a similar response to adult rats except that the decreases in incorporation induced by FSH, m-DNB and NB were smaller. Analysis by 2-D SDS-PAGE revealed considerable age-dependent differences in the proteins secreted by ST from immature and adult rats, of which 13 were identified as being of potential importance. Most of these proteins were prominent secretory products of ST from adult rats, but were minor or non-detectable products of cultures of ST or SC+GC from immature rats. Most of these proteins disappeared or decreased in abundance after culture of ST with m-DNB or NB. Two proteins showed the reverse pattern, being more prominent secretory products in immature than mature rats, and their secretion was unaffected or was increased by toxicant exposure. These results demonstrate that there are major age-dependent differences in the secretion of total and specific proteins by isolated ST and that these are probably related to changes in the germ cell complement with age.(ABSTRACT TRUNCATED AT 400 WORDS)

Aging↗

Reactions of nitrosonitrobenzenes with biological thiols: identification and reactivity of glutathion-S-yl conjugates.

1,3-Dinitrobenzene (1,3-DNB) but not 1,2-dinitrobenzene (1,2-DNB) or 1,4-dinitrobenzene (1,4-DNB) is a potent testicular toxicant in rats. In vitro metabolism studies have established that 1,3-DNB is reduced to 3-nitroso-nitrobenzene (3-NNB), 3-nitrophenylhydroxylamine (3-NP) and 3-nitroaniline (3-NA) in testicular cytosol and Sertoli cell cultures. To establish a potential role for endogenous glutathione (GSH) in the detoxification of the electrophilic metabolite 3-NNB, we examined the chemical reaction of this compound with biological thiols, including GSH. The effect of pH and thiol concentration upon the reaction were studied. The reaction of GSH with 3-NNB was complex and gave three distinct products. These were identified as 3-NP, 3-NA and a glutathionyl derivative containing a covalently linked S-N bond. The hydroxyl amine and the amine were isolated and fully characterised. The glutathion-S-yl derivative was characterised in solution by proton NMR (400 MHz), infra-red and mass spectroscopy to establish its structure as the semimercaptal, N-(glutathion-S-yl)-N-hydroxy-3-nitroaniline (GSNOH-3NA). Similar reactions were performed with 4-nitrosonitrobenzene (4-NNB) to ascertain the reactivity of this chemical towards thiols. The addition of GSH to 4-NNB resulted in the rapid formation of 4-nitrophenylhydroxylamine (4-NP) and an adduct that was identified as the semimercaptal N-(glutathion-S-yl)-N-hydroxy-4-nitroaniline (GSNOH-4NA).

Acetylcysteine↗

The metabolism of 1,3-dinitrobenzene by rat testicular subcellular fractions.

The metabolism of 1,3-dinitrobenzene by rat testicular subcellular fractions (microsomes, cytosol or 9000 x g supernatant (S-9)) was studied. The effects of NADPH, oxygen, glutathione (GSH) and carbon monoxide upon the rate of metabolism were determined. Three metabolites were identified, and characterised as 3-nitrosonitrobenzene, 3-nitrophenylhydroxylamine and 3-nitroaniline by co-chromatography with authentic standards. These findings indicate the presence of an inherent enzyme system capable of facilitating nitro-reduction in the testes. The implications of these findings to the mechanism of 1,3-DNB-induced testicular toxicity are discussed.

Animals↗

Evaluation of changes in the secretion of immunoactive inhibin by adult rat seminiferous tubules in vitro as an indicator of early toxicant action on spermatogenesis.

A method for culturing isolated seminiferous tubules (ST) from adult rats for 1-3 days has been developed and optimized rigorously on the basis of the secretion of immunoactive inhibin under basal conditions and after maximal stimulation with rat FSH or dibutyryl cyclic AMP. The effect on these cultures of three known testicular toxicants was assessed. Of these, two are thought to act on the Sertoli cell, meta-dinitrobenzene (mDNB) and nitrobenzene (NB), while the third, methoxy acetic acid (MAA), is thought to act on pachytene spermatocytes. In addition, the effect of a possible testicular toxicant, 3-mononitrotoluene (3-MNT), was investigated. These data were compared with those obtained using cultures of immature rat Sertoli cells (SC) or SC + germ cells and with data on the effect of equivalent doses of the compounds on the secretion of immunoactive inhibin in vivo. In studies designed to optimize conditions for the secretion of immunoactive inhibin by ST in culture, significant effects were found of the type of culture medium used, the duration of culture, the total and individual length of tubules used, etc. All subsequent studies with toxicants utilized optimal conditions. Addition of either mDNB or NB to ST cultures at 10(-5) or 10(-3) M, or MAA at 10(-4) M, stimulated basal secretion of immunoactive inhibin by two- to fourfold on Days 1, 2, or 3 of culture while FSH or dibutyryl cyclic AMP-stimulated secretion of immunoactive inhibin was either unaffected or was enhanced to a small extent. At the same doses, mDNB or NB also enhanced secretion of immunoactive inhibin by SC cultures. although these effects were more variable and of smaller magnitude than the effects on ST cultures. In contrast, addition of up to 10(-3) MAA to cocultures of SC + germ cells had no effect on the secretion of immunoactive inhibin. Exposure of rats in vivo to levels of mDNB, NB, or MAA similar to those which stimulated secretion of immunoactive inhibin in vitro resulted in a two- to fourfold increase in the levels of immunoactive inhibin in testicular interstitial fluid (IF) at 1 and 3 days post-treatment, and this was associated with early impairment of spermatogenesis (as judged by testis weight). In contrast to these effects, addition of 3-MNT to ST or SC cultures had no effect except at 10(-3) M, when the secretion of immunoactive inhibin was increased marginally.(ABSTRACT TRUNCATED AT 400 WORDS)

Acetates↗