Effect of triiodothyronine administration on estrogen receptor contents in peripuberal Sertoli cells

Hormonal control of Sertoli cell metabolism regulates spermatogenesis

Hormonal regulation is essential to spermatogenesis. Sertoli cells (SCs) have functions that reach far beyond the physical support of germ cells, as they are responsible for creating the adequate ionic and metabolic environment for germ cell development. Thus, much attention has been given to the metabolic functioning of SCs. During spermatogenesis, germ cells are provided with suitable metabolic substrates, in a set of events mediated by SCs. Multiple signaling cascades regulate SC function and several of these signaling pathways are hormone-dependent and cell-specific. Within the seminiferous tubules, only SCs possess receptors for some hormones rendering them major targets for the hormonal signaling that regulates spermatogenesis. Although the mechanisms by which SCs fulfill their own and germ cells metabolic needs are mostly studied in vitro, SC metabolism is unquestionably a regulation point for germ cell development and the hormonal control of these processes is required for a normal spermatogenesis.

Ontogeny of androgen and estrogen receptor expression in porcine testis: Effect of reducing testicular estrogen synthesis

Reducing endogenous estrogen leads to increased proliferation of porcine Sertoli cells during the first 2 months of life. The resulting increase in porcine Sertoli cell numbers is maintained through puberty. The reduced estrogen appears to be the direct hormonal mediator because essentially no changes are observed in other hormones. However, the mechanism for this effect on Sertoli cell proliferation is unknown. The objective of these studies was to evaluate estrogen receptors alpha and beta (ESR1 and ESR2) in conjunction with androgen receptor (AR) on Sertoli cells and other testicular cell types, as an initial step toward understanding how reduced estrogen leads to increased Sertoli cell numbers. Testis sections from treated animals (aromatase inhibition to decrease endogenous estrogen beginning at 1 week of age) and from littermate controls treated with vehicle were subjected to immunocytochemical labeling for ESR1, ESR2, and AR. Three observers scored Sertoli cells, interstitial cells, peritubular myoid cells, and germ cells for intensity of labeling (0: absent; 1+: weak; 2+: moderate; or 3+: strong labeling). AR in Sertoli cells was readily detected at 1 week of age, was very faint in 2-month vehicle controls, and labeling appeared to increase in 3-month vehicle controls. AR in Sertoli cells, interstitial cells, and apparently germ cells was increased in treated animals at 2 months of age compared with the vehicle controls. This increase was confirmed in western blots. ESR1 and ESR 2 were clearly present in Sertoli cells from 1-week-old animals; ESR in Sertoli cells generally decreased with age with the decrease more apparent for ESR2. ESR1 in Sertoli cells and peritubular myoid cells exhibited some treatment-related effects but reduction of endogenous estrogen did not appear to affect ESR2 in the boar testis. The observed alterations in AR and ESR1 may mediate the increases in Sertoli cell proliferation following inhibition of endogenous estrogen production or may reflect the altered function of the Sertoli cells and peritubular myoid cells.

The menace of endocrine disruptors on thyroid hormone physiology and their impact on intrauterine development

The delivery of the appropriate thyroid hormones quantity to target tissues in euthyroidism is the result of unopposed synthesis, transport, metabolism, and excretion of these hormones. Thyroid hormones homeostasis depends on the maintenance of the circulating 'free' thyroid hormone reserves and on the development of a dynamic balance between the 'free' hormones reserves and those of the 'bound' hormones with the transport proteins. Disturbance of this hormone system, which is in constant interaction with other hormone systems, leads to an adaptational counter-response targeting to re-establish a new homeostatic equilibrium. An excessive disturbance is likely to result, however, in hypo- or hyper- thyroid clinical states. Endocrine disruptors are chemical substances forming part of 'natural' contaminating agents found in most ecosystems. There is abundant evidence that several key components of the thyroid hormones homeostasis are susceptible to the action of endocrine disruptors. These chemicals include some chlorinated organic compounds, polycyclic aromatic hydrocarbons, herbicides, and pharmaceutical agents. Intrauterine exposure to endocrine disruptors that either mimic or antagonize thyroid hormones can produce permanent developmental disorders in the structure and functioning of the brain, leading to behavioral changes. Steroid receptors are important determinants of the consequences of endocrine disruptors. Their interaction with thyroid hormones complicates the effect of endocrine disruptors. The aim of this review is to present the effect of endocrine disruptors on thyroid hormones physiology and their potential impact on intrauterine development.

Thyroid hormone, glucocorticoids, and prolactin at the nexus of physiology, reproduction, and toxicology

A symposium at the 2003 Annual Meeting of the Society of Toxicology brought together an expert group of endocrinologists to review how non-reproductive hormones can affect the endocrine system. This publication captures the essence of those presentations. Paul Cooke and Denise Holsberger recapitulate the evidence of how thyroid hormones affect male and female reproduction, and reproductive development. Ray Witorsch summarizes the many effects of glucocorticoids on the reproductive system. Finally, Paul Sylvester reviews the mechanism of action of prolactin, and reminds us that this ancient hormone has many functions beyond lactation.

Polybrominated diphenyl ethers (PBDEs): new pollutants-old diseases

Polybrominated diphenyl ethers (PBDEs) are a class of recalcitrant and bioaccumulative halogenated compounds that have emerged as a major environmental pollutant. PBDEs are used as a flame-retardant and are found in consumer goods such as electrical equipment, construction materials, coatings, textiles and polyurethane foam (furniture padding). Similar in structure to polychlorinated biphenyls (PCBs), PBDEs resist degradation in the environment. Less brominated PBDEs like tetra-, penta- and hexa- demonstrate high affinity for lipids and can accumulate in the bodies of animals and humans. Breast milk from North American women contained much higher amounts of PBDEs than levels in breast milk from Swedish women, indicating that North American exposures to PBDEs may be particularly high. Evidence to date suggests that tetra- and penta-BDEs are likely to be the more toxic and bioaccumulative of the PBDE compounds, compared to octa- and deca-congeners. PBDEs are sold as mixtures, under names such as "pentabromodiphenyl ether" and "octabromodiphenyl ether." The pentabromo product is a mixture of tetra-BDEs and penta-BDEs in approximately equal amounts. Pentabromo consists of PBDEs that are believed to be the most toxic. This mixture has been banned by the European Union, but is still used in North America. The United States is the leading producer and user of pentabromo. In August 2003, the State of California passed a bill to phase out the use of penta- and octa-PBDE by 2008. The toxicology of PBDEs is not well understood, but PBDEs have been associated with tumors, neurodevelopmental toxicity and thyroid hormone imbalance. The neurotoxic effects of PBDEs are similar to those observed for PCBs. Children exposed to PBDEs are prone to subtle but measurable developmental problems. It is presumed that PBDEs are endocrine disruptors, but research in this area is scant. Further studies are imperative in a multitude of health and environmental disciplines to determine the adverse effects and mode of action of this widespread emerging pollutant on human health.

Triiodothyronine decreases the activity of the proximal promoter (PII) of the aromatase gene in the mouse Sertoli cell line, TM4

Estrogens and thyroid hormones play a significant role in regulating functions and development of the testis. The synthesis of estrogens from androgens is catalyzed by the enzyme complex termed aromatase, which in the testis displays an age-related cellular compartmentalization, primarily in Sertoli cells in immature animals, whereas in adults it is expressed in Leydig and germ cells. T3 induces a precocious terminal differentiation of prepubertal Sertoli cells together with a dramatic decrease of their aromatase activity. In the present work, we have examined the mechanism by which T3 exerts this inhibitory action on aromatase expression. As an experimental model, we used the mouse Sertoli cell line TM4, which conserves a large spectrum of functional features present in immature Sertoli cells. For instance, after revealing the presence of aromatase by immunocytochemistry and measuring its enzymatic activity, we confirmed in this cell line the functional events previously characterized in primary cultures of immature rat Sertoli cells: 1) a strong stimulation of aromatase activity by dibutyryl-cAMP [(Bu)2cAMP] (simulating FSH action); and 2) the inhibition of aromatase activity by incubation with T3 under basal condition and after (Bu)2cAMP stimulation. After identifying promoter II as the regulatory region located immediately upstream of the transcriptional initiation site in the TM4 cell line by rapid amplification of cDNA ends analysis, we conducted experiments to examine the molecular mechanism by which thyroid hormones modulate aromatase gene expression in this cell line. TM4 cells were transfected with plasmids containing different segments of the rat promoter II sequence ligated to a luciferase reporter gene. Analysis of the activities of these promoter fusions demonstrated that T3 inhibits basal and (Bu)2cAMP-stimulated activity of the aromatase promoter. This effect was not revealed in T3-treated cells transfected with construct in which the steroidogenic factor-1 (SF-1) response element was mutated. These results indicate that the inhibitory effect of T3 requires the integrity of the SF-1 response element and are further supported in the EMSA. The EMSA experiments demonstrated that thyroid hormone/thyroid receptor alpha1 complex (TH/TRalpha1) is able to compete with SF-1 in binding to oligonucleotides containing an SF-1 motif, an element essential for the activity of the PII aromatase promoter. The findings suggest that the binding of the thyroid hormone/thyroid receptor alpha1 complex to the SF-1 motif is the molecular mechanism by which T3 exerts an inhibitory effect on aromatase gene expression in the TM4 cell line.

Impact of neonatal onset hypothyroidism on Sertoli cell number, plasma and testicular interstitial fluid androgen binding protein concentration

The impact of neonatal onset hypothyroidism from day 1 postpartum through different postnatal developmental events on rat testis was studied in vivo. Hypothyroidism was induced in neonates by feeding the lactating mother or directly with 0.05% methimazole (MMI) through drinking water from the day of birth and were killed at day 10, 15, 30, 40 and 60 postpartum. Hypothyroidism was confirmed by radioimmunoassay of thyroid hormones and TSH. Sertoli cell number, plasma and testicular interstitial fluid (TIF) androgen binding protein (ABP) concentration was quantified. Sertoli cell number was consistently decreased in all hypothyroid rats. Plasma ABP was also decreased irrespective of the duration of hypothyroidism. Unlike plasma ABP, TIF ABP concentration in hypothyroid rats increased at day 10, and 15 postpartum and decreased in other age groups. Plasma FSH level was increased significantly in all hypothyroid groups. The present investigation points out that suppression of T3 during the critical period of Sertoli cell proliferation affects their number and functional activity.

Toxic effects of octylphenol on cultured rat spermatogenic cells and Sertoli cells

Alkylphenols, including the estrogenic 4-tert-octylphenol (OP), are environmental pollutants. Because administration of OP to adult male rats impairs spermatogenesis and OP has been shown to be toxic to aquatic animals and to mammalian splenocytes in vitro, we studied whether OP exerts direct toxic effects on cultured spermatogenic cells and Sertoli cells isolated from male rats. Cell viability was assessed with a Live/Dead Eukolight viability/cytotoxicity kit. Culture of mixed spermatogenic cells from adult rats with 10(-8) M OP or Sertoli cells from 19- to 21-day-old rats with 10(-12) M OP, but not with 0.08% EtOH (vehicle) or 10(-6) M 17beta-estradiol (E2) or dexamethasone (DEX), significantly decreased the percentage of viable cells after 24 h of treatment. None of the treatments significantly altered total cell number. Flow cytometric analyses of spermatogenic cells revealed that exposure to 10(-4) or 10(-6) M OP yielded abnormal relative ploidy classes. Four hours of treatment with 10(-6) M OP, but not with 10(-6) M E2 or DEX, caused significant chromatin condensation in Sertoli cells as observed with acridine orange staining. The decreased percentage of viable cells after 24 h of exposure to 10(-6) M OP remained when Sertoli cells were cultured in Ca2+-free medium. Sertoli cells contained nuclei of reduced size and labeled 3'-OH DNA ends as detected by microscopic analyses when the cells had been incubated for 24 h with 10(-6) M OP but not with vehicle or 10(-6) M E2 or DEX. The results demonstrate that OP, but not E2 or DEX, is directly toxic to cultured rat spermatogenic cells and Sertoli cells and suggest that this toxic effect in Sertoli cells is exerted through Ca2+-independent apoptosis.

Ontogeny of estrogen receptor-beta expression in rat testis

The recently discovered estrogen receptor-beta (ERbeta) is expressed in rodent and human testes. To obtain insight in the physiological role of ERbeta we have investigated the cell type-specific expression pattern of ERbeta messenger RNA (mRNA) and protein in the testis of rats of various ages by in situ hybridization and immunohistochemistry. In fetal testes of rats 16 days postcoitum and testes of 4-day-old animals, fetal germ cells (gonocytes) reveal the ERbeta mRNA in their cytoplasm and the ERbeta protein in their nucleus. In testes of 11- and 15-day-old rats, ERbeta mRNA and protein were detected in Sertoli cells and type A spermatogonia. No signal was found in other types of germ cells. In the adult testes, expression of ERbeta mRNA as well as ERbeta protein was found in pachytene spermatocytes from epithelial stages VII-XIV and in round spermatids from stages I-VIII. Low ERbeta expression was observed in all type A spermatogonia, including undifferentiated A spermatogonia, whereas no expression was found in In and type B spermatogonia and early spermatocytes. At all ages, Sertoli cells showed a weak hybridization signal as well as weak immunoreactivity for ERbeta. In adult testes, no ERbeta mRNA or protein was detected in the interstitial tissue, indicating that Leydig cells and peritubular myoid cells do not express ERbeta. The expression of ERbeta in fetal and late male germ cells as well as in Sertoli cells suggests that estrogens directly affect germ cells during testicular development and spermatogenesis.