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Endocrine-disrupting chemicals (EDC) are molecules that interfere with endocrine signaling pathways and produce adverse consequences on animal and human physiology, such as infertility or behavioral alterations. Some EDC act through binding to androgen or/and estrogen receptors primarily operating through a genomic mechanism regulating gene expression. This mechanism of action may induce profound developmental adverse effects, and the major targets of the EDC action are the gene products, i.e., mRNAs inducing the synthesis of various peptidic molecules, which include neuropeptides and enzymes related to neurotransmitters syntheses. Available immunohistochemical data on some of the systems that are affected by EDC in lower and higher vertebrates are detailed in this review. [ABSTRACT FROM AUTHOR]

Some environmental contaminants interact with hormones and may exert adverse consequences as a result of their actions as endocrine disrupting chemicals (EDCs). Exposure in people is typically a result of contamination of the food chain, inhalation of contaminated house dust or occupational exposure. EDCs include pesticides and herbicides (such as dichlorodiphenyl trichloroethane or its metabolites), methoxychlor, biocides, heat stabilisers and chemical catalysts (such as tributyltin), plastic contaminants (e.g. bisphenol A), pharmaceuticals (i.e. diethylstilbestrol; 17α-ethinylestradiol) or dietary components (such as phytoestrogens). The goal of this review is to address the sources, effects and actions of EDCs, with an emphasis on topics discussed at the International Congress on Steroids and the Nervous System. EDCs may alter reproductively-relevant or nonreproductive, sexually-dimorphic behaviours. In addition, EDCs may have significant effects on neurodevelopmental processes, influencing the morphology of sexually-dimorphic cerebral circuits. Exposure to EDCs is more dangerous if it occurs during specific 'critical periods' of life, such as intrauterine, perinatal, juvenile or puberty periods, when organisms are more sensitive to hormonal disruption, compared to other periods. However, exposure to EDCs in adulthood can also alter physiology. Several EDCs are xenoestrogens, which can alter serum lipid concentrations or metabolism enzymes that are necessary for converting cholesterol to steroid hormones. This can ultimately alter the production of oestradiol and/or other steroids. Finally, many EDCs may have actions via (or independent of) classic actions at cognate steroid receptors. EDCs may have effects through numerous other substrates, such as the aryl hydrocarbon receptor, the peroxisome proliferator-activated receptor and the retinoid X receptor, signal transduction pathways, calcium influx and/or neurotransmitter receptors. Thus, EDCs, from varied sources, may have organisational effects during development and/or activational effects in adulthood that influence sexually-dimorphic, reproductively-relevant processes or other functions, by mimicking, antagonising or altering steroidal actions. [ABSTRACT FROM AUTHOR]

Several environmental chemicals have the capability of impacting endocrine function (endocrine disrupting chemicals [EDCs]), and therefore they may have long-term consequences, especially if exposure occurs during embryonic development. In this study we present data relative to two widely used animal models: the Japanese quail and the mouse. These two species have been used to understand neural, neuroendocrine, and behavioral components of reproduction and are optimal models to understand how these components are altered by precocious exposure to EDCs. In particular, we discuss the effects of embryonic exposure to diethylstilbestrol, genistein, or ethylene,1,1-dichloro-2,2-bis(p-chlorophenyl) on the sexually dimorphic parvocellular vasotocin system and male copulatory behavior in quail and the effects of bisphenol A on the nitrinergic and kisspeptin systems and their behavioral impact in the mouse. In both models the exposure to EDCs during the critical period (early embryonic period in birds, perinatal period in rodents) alters the differentiation of relevant sexually dimorphic pathways, often inducing the appearance of a sex-reversed neurochemical phenotype that is the most probable cause of the final alteration of sexually differentiated behaviors in the adult animal. In conclusion, the data presented here should stimulate a critical reanalysis of the way to determine the “safe” exposure levels to EDCs for wild species and humans, considering behavior and related neural circuits among the factors to be analyzed. [ABSTRACT FROM AUTHOR]

The widespread use of 17α-ethinylestradiol (EE2), and other estrogenic endocrine disruptors, results in a continuous release of estrogenic compounds into aquatic environments. Xenoestrogens may interfere with the neuroendocrine system of aquatic organisms and may produce various adverse effects. The aim of the present study was to expose European sea bass larvae (Dicentrarchus labrax) to EE2 (0.5 and 50 nM) for 8 d and determine the expression levels of brain aromatase (cyp19a1b), gonadotropin-releasing hormones (gnrh1, gnrh2, gnrh3), kisspeptins (kiss1, kiss2) and estrogen receptors (esr1, esr2a, esr2b, gpera, gperb). Growth and behavior of larvae as evidenced by locomotor activity and anxiety-like behaviors were measured 8 d after EE2 treatment and a depuration period of 20 d. Exposure to 0.5 nM EE2 induced a significant increase in cyp19a1b expression levels, while upregulation of gnrh2, kiss1, and cyp19a1b expression was noted after 8 d at 50 nM EE2. Standard length at the end of the exposure phase was significantly lower in larvae exposed to 50 nM EE2 than in control; however, this effect was no longer observed after the depuration phase. The upregulation of gnrh2, kiss1, and cyp19a1b expression levels was found in conjunction with elevation in locomotor activity and anxiety-like behaviors in larvae. Behavioral alterations were still detected at the end of the depuration phase. Evidence indicates that the long-lasting effects of EE2 on behavior might impact normal development and subsequent fitness of exposed fish. [ABSTRACT FROM AUTHOR]

The research indicates that pollution control in developing countries has a limited success. The steroids role in carcinogenesis has become the main anxiety in environmental protection, biomonitoring and the clinical research, environmental health research has been highly focused on the estrogen receptor level and aromatase polymorphisms disturbances. Xenoestrogens and estrogen in the context of environmental exposure play very important role in carcinogenesis by binding to estrogen receptors, whose distribution is described through age and gender. This review provides detailed information about the types of cancer which is etiologically attributed to environmental exposure to xenoestrogens. The types of cancer that have been examined in the literature reviewed on this research is found to be linked with the environmental exposure causing health issues in reproductive system, lung, breast, kidney, pancreas and brain. The result of the data mining on this research problem described strong correlation between the environmental exposures to xenoestrogens with increased intensity of gender related cancer risks. The current study indicates that there was a need to further evaluate agents to this point that were defined as endocrine disruptors and considered as major molecules in carcinogenesis. The revision may be used to further elaborate and discuss the research of cancer aetiology by making further improvements to their related legislation. The research investigates the causes of cancers associated with environmental exposure to xenoestrogens. [ABSTRACT FROM AUTHOR]

In vertebrates, sexual differentiation of the reproductive system and brain is tightly orchestrated by organizational and activational effects of endogenous hormones. In mammals and birds, the organizational period is typified by a surge of sex hormones during differentiation of specific neural circuits; whereas activational effects are dependent upon later increases in these same hormones at sexual maturation. Depending on the reproductive organ or brain region, initial programming events may be modulated by androgens or require conversion of androgens to estrogens. The prevailing notion based upon findings in mammalian models is that male brain is sculpted to undergo masculinization and defeminization. In absence of these responses, the female brain develops. While timing of organizational and activational events vary across taxa, there are shared features. Further, exposure of different animal models to environmental chemicals such as xenoestrogens such as bisphenol A-BPA and ethinylestradiol-EE2, gestagens, and thyroid hormone disruptors, broadly classified as neuroendocrine disrupting chemicals (NED), during these critical periods may result in similar alterations in brain structure, function, and consequently, behaviors. Organizational effects of neuroendocrine systems in mammals and birds appear to be permanent, whereas teleost fish neuroendocrine systems exhibit plasticity. While there are fewer NED studies in amphibians and reptiles, data suggest that NED disrupt normal organizational-activational effects of endogenous hormones, although it remains to be determined if these disturbances are reversible. The aim of this review is to examine how various environmental chemicals may interrupt normal organizational and activational events in poikilothermic vertebrates. By altering such processes, these chemicals may affect reproductive health of an animal and result in compromised populations and ecosystem-level effects. [ABSTRACT FROM PUBLISHER]

Endocrine disrupting chemicals ( EDCs) are ubiquitous in aquatic ecosystems where they have adverse effects on exposed organisms. In addition to causing physiological changes, EDCs often target fitness-related behaviors such as locomotion and courtship. Ethinylestradiol ( EE2) is an estrogen mimic that has been found to reduce courtship and aggression in males. However, the consequences of these reductions are not always explicitly addressed. One way in which EE2 may lead to decreased fitness occurs when males respond differently to exposed vs. unexposed conspecifics. To examine this, video playback was used to determine whether male Siamese fighting fish, Betta splendens, respond differently to exposed and unexposed males. Males were presented with four different combinations of videos of males played simultaneously: exposed swimming and unexposed swimming, exposed courting and unexposed courting, unexposed courting and unexposed courting, and exposed courting and exposed courting. Males directed more behaviors to the unexposed than the exposed courting male when presented simultaneously, likely because these unexposed males were perceived as a greater threat to mating success. Additionally, males spent more time tracking and gill flaring, two behaviors that are indicative of fight intent, when presented with two courting unexposed males. This combination could be considered the most threatening because there are two rival vigorously courting males present. These results suggest that EE2 exposure could result in exposed males receiving decreased attention from other males. However, since EE2 exposure also decreases competitive and courtship abilities, this would be far outweighed by the costs. [ABSTRACT FROM AUTHOR]

Occurrences and exposure risk of 21 target endocrine-disrupting pesticides (EDPs) were investigated in the eight typical drinking water sources (including six rivers and two reservoirs) with different hydraulic characteristics and intensive agricultural activities in agricultural watershed over a year. A multi-residue analytical methodology was developed for screening 21 target compounds in water sources based on gas chromatography-mass spectrometry (GC-MS), and the results showed that within the 21 EDPs, only trifluralin was occasionally detected (27.1 %), indicative of widespread occurrences of EDP residues in these areas. Dominant detected EDPs of dicofol and cypermethrin accounted for more than 20 % of the total EDPs (37.9 to 2948.9 ng l) in the eight sites, which were both currently used in abundance. Clustering analysis indicated that the obvious spatial difference appeared among river basins with different agricultural aeras, and the levels of detected EDPs in the two reservoirs were also much lower than other sites due to the less intensive of agricultural activities. Besides, results of temporal distribution analysis showed that occurrences of EDPs decreased in winter and spring mainly because of the decline in the usage of cypermethrin and dicofol, and the temporal variation of organics was similar with that of EDPs. It might be concluded that the agricultural intensive was the main factor affecting the occurrence of EDPs. The EDPs risk assessment revealed that the high ecological risk are existing at polluted drinking water sources in Eastern China after a long-term influence, and it is very necessary to remedy polluted natural waters. [ABSTRACT FROM AUTHOR]

Only a small proportion of the published research on endocrine-disrupting chemicals (EDC) directly examined effects on neuroendocrine processes. There is an expanding body of evidence that anthropogenic chemicals exert effects on neuroendocrine systems and that these changes might impact peripheral organ systems and physiological processes. Neuroendocrine disruption extends the concept of endocrine disruption to include the full breadth of integrative physiology (i.e., more than hormones are upset). Pollutants may also disrupt numerous other neurochemical pathways to affect an animal's capacity to reproduce, develop and grow, or deal with stress and other challenges. Several examples are presented in this review, from both vertebrates and invertebrates, illustrating that diverse environmental pollutants including pharmaceuticals, organochlorine pesticides, and industrial contaminants have the potential to disrupt neuroendocrine control mechanisms. While most investigations on EDC are carried out with vertebrate models, an attempt is also made to highlight the importance of research on invertebrate neuroendocrine disruption. The neurophysiology of many invertebrates is well described and many of their neurotransmitters are similar or identical to those in vertebrates; therefore, lessons learned from one group of organisms may help us understand potential adverse effects in others. This review argues for the adoption of systems biology and integrative physiology to address the effects of EDC. Effects of pulp and paper mill effluents on fish reproduction are a good example of where relatively narrow hypothesis testing strategies (e.g., whether or not pollutants are sex steroid mimics) have only partially solved a major problem in environmental biology. It is clear that a global, integrative physiological approach, including improved understanding of neuroendocrine control mechanisms, is warranted to fully understand the impacts of pulp and paper mill effluents. Neuroendocrine disruptors are defined as pollutants in the environment that are capable of acting as agonists/antagonists or modulators of the synthesis and/or metabolism of neuropeptides, neurotransmitters, or neurohormones, which subsequently alter diverse physiological, behavioral, or hormonal processes to affect an animal's capacity to reproduce, develop and grow, or deal with stress and other challenges. By adopting a definition of neuroendocrine disruption that encompasses both direct physiological targets and their indirect downstream effects, from the level of the individual to the ecosystem, a more comprehensive picture of the consequences of environmentally relevant EDC exposure may emerge. [ABSTRACT FROM AUTHOR]

Kisspeptins, the products of Kiss1 gene acting via G protein-coupled receptor 54 (also termed Kiss1R), have recently emerged as essential gatekeepers of puberty onset and fertility. Compelling evidence has now documented that expression and function of hypothalamic Kiss1 system is sensitive not only to the activational effects but also to the organizing actions of sex steroids during critical stages of development. Thus, studies in rodents have demonstrated that early exposures to androgens and oestrogens are crucial for proper sexual differentiation of the patterns of Kiss1 mRNA expression, whereas the actions of oestrogen along puberty are essential for the rise of hypothalamic kisspeptins during this period. This physiological substrate provides the basis for potential endocrine disruption of reproductive maturation and function by xeno-steroids acting on the kisspeptin system. Indeed, inappropriate exposures to synthetic oestrogenic compounds during early critical periods in rodents persistently decreased hypothalamic Kiss1 mRNA levels and kisspeptin fibre density in discrete hypothalamic nuclei, along with altered gonadotropin secretion and/or gonadotropin-releasing hormone neuronal activation. The functional relevance of this phenomenon is stressed by the fact that exogenous kisspeptin was able to rescue defective gonadotropin secretion in oestrogenized animals. Furthermore, early exposures to the environmentally-relevant oestrogen, bisphenol-A, altered the hypothalamic expression of Kiss1/kisspeptin in rats and mice. Likewise, maternal exposure to a complex cocktail of endocrine disruptors has been recently shown to disturb foetal hypothalamic Kiss1 mRNA expression in sheep. As a whole, these data document the sensitivity of Kiss1 system to changes in sex steroid milieu during critical periods of sexual maturation, and strongly suggest that alterations of endogenous kisspeptin tone induced by inappropriate (early) exposures to environmental compounds with sex steroid activity might be mechanistically relevant for disruption of puberty onset and gonadotropin secretion later in life. The potential interaction of xeno-hormones with other environmental modulators (e.g., nutritional state) of the Kiss1 system warrants further investigation. [ABSTRACT FROM AUTHOR]