Social partner cooperativeness influences brain oxytocin transcription in Trinidadian guppies (Poecilia reticulata).

For non-kin cooperation to be maintained, individuals need to respond adaptively to the cooperative behaviour of their social partners. Currently, however, little is known about the biological responses of individuals to experiencing cooperation. Here, we quantify the neuroregulatory response of Trinidadian guppies (Poecilia reticulata) experiencing cooperation or defection by examining the transcriptional response of the oxytocin gene (oxt; also known as isotocin), which has been implicated in cooperative decision-making. We exposed wild-caught females to social environments where partners either cooperated or defected during predator inspection, or to a control (non-predator inspection) context, and quantified the relative transcription of the oxt gene. We tested an experimental group, originating from a site where individuals are under high predation threat and have previous experience of large aquatic predators (HP), and a control group, where individuals are under low predation threat and naïve to large aquatic predators (LP). LP, but not HP, fish showed different behavioural responses to the behaviour of their social environment, cooperating with cooperative partners and defecting when paired with defecting ones. In HP, but not LP, fish brain mid-section oxt relative transcription varied depending on social partner behaviour. HP fish experiencing cooperation during predator inspection had lower oxt transcription than those experiencing defection. This effect was not present in the control population or in the control context, where the behaviour of social partners did not affect oxt transcription. Our findings provide insight into the neuromodulation underpinning behavioural responses to social experiences, and ultimately to the proximate mechanisms underlying social decision-making.

High liver content of polybrominated diphenyl ether (PBDE) in otters (Lutra lutra) from England and Wales.

Polybrominated diphenyl ethers (PBDEs), used as flame retardants since the 1970s, are being phased out of use, but are persistent and widespread in the environment. Historical declines in Eurasian otter (Lutra lutra) populations have been associated with exposure to dieldrin and polychlorinated biphenyls (PCBs), but links with other persistent organic pollutants have not been explored. In this study, liver samples from 129 otters, collected across England and Wales from 1995-2006, were analysed for PBDEs, together with PCBs, DDT breakdown products, and hexachlorobenzene. Associations with geographical location and life history parameters were explored. Concentrations of PBDEs in otters (∑BDE 12-70000ngg(-1) lipid) paralleled those measured in marine mammals, with PBDE-47 the dominant congener and high levels of PBDE-99 and -100. Otter livers contained high concentrations of PBDE-153 and -209, typical of terrestrial top predators. Inter-individual variation in PBDE concentrations was high and correlated with geographical location. ∑PBDE was 25% of ∑PCB, and comparable with ∑DDT, identifying PBDEs as a major contaminant in otter populations in England and Wales.

The vas::egfp transgenic zebrafish: a practical model for studies on the molecular mechanisms by which environmental estrogens affect gonadal sex differentiation.

The vas::egfp transgenic zebrafish (Danio rerio) could significantly enhance studies on the mechanisms by which environmental estrogens disrupt sexual differentiation, because the developing gonad can be visualized during early life via fluorescence detection. There are methodological challenges regarding dissecting out the gonads in early-life-stage fish, however, and transgene responses to estrogen exposure have not been tested. The authors exposed vas::egfp transgenic zebrafish and their wild-type siblings to the model estrogen 17α-ethinylestradiol (EE2; 0.62 ng/L and 3.33 ng/L measured concentrations) during sexual development (20-60 d posthatch) and used enhanced green fluorescent protein (egfp) fluorescence to identify and dissect single gonads (at 40 d posthatch) to provide sufficient RNA for individual gene expression analyses, retaining the remaining gonad in the body cavity for histological analyses of sex and stage of development. Genotyping confirmed that all transgenic control fish were phenotypically egfp positive (showed green fluorescence). Interestingly, however, in a few transgenic fish exposed to EE2, no phenotypic egfp signal was seen, most notably for the 3.33 ng/L EE2 exposure. It was subsequently found that gonadal vasa expression was reduced by this concentration of EE2. Hepatic vitellogenin expression demonstrated that the vas::egfp and wild-type lines responded to estrogen with an equivalent sensitivity. The authors conclude that the vas::egfp zebrafish provides an enhanced and practical system for mechanistic studies on the effects of environmentally relevant concentrations of estrogens on gonad development.

Environmental estrogen-induced alterations of male aggression and dominance hierarchies in fish: a mechanistic analysis.

Environmental estrogens have been shown to affect aspects of fish behavior that could potentially impact on wild populations, but the physiological mechanisms underpinning these effects are unknown. Using small colonies of zebrafish (Danio rerio), we evaluated the impacts of estrogen exposure on the aggression of dominant males, the associated implications for their social status and reproductive success, and their signaling mechanisms. The aggression of dominant males exposed to 17α-ethinylestradiol (EE(2); 10 ng/L nominal) was reduced significantly, and half of these fish subsequently lost their dominance, behavioral changes that were reflected in their reproductive success. Plasma androgen and the expression of genes involved in sex steroid production/signaling (cyp19a1b, cyp17, hsd11b2, hsd17b3, ar) and aggression (avplrv1b, tph1b, htr1a, sst1, sstr1, th, slc6a3, ar) were higher in control dominant versus subordinate males, but suppressed by EE(2) exposure, such that the differences between the social ranks were not retained. The expression levels of avpl (brain), which promotes aggression and dominance, and ar and cyp17 (gonad) were elevated in nonexposed males paired with EE(2)-exposed males. Our findings illustrate that disruptions of behaviors affecting social hierarchy, and in turn breeding outcome, as a consequence of exposure to an environmental estrogen are signaled through complex interconnecting gonadal and neurological control mechanisms that generally conform with those established in mammalian models. The extensive molecular, genetic, physiological, and behavioral toolbox now available for the zebrafish makes this species an attractive model for integrated analyses of chemical effects spanning behavior to molecular effect mechanisms.

Physiological and health consequences of social status in zebrafish (Danio rerio).

Social status affects access to food, mates and shelter and has consequences for the physiology of individuals and their health status. In the zebrafish (Danio rerio), an emerging model for studies into animal behavior, the possible consequences of social hierarchy to an individual's physiology and health are unknown. To address this, in this species we assessed the effects of social interaction (for periods of 1-5days) on growth, stress, immune function and reproductive condition. Wide-ranging differences in physiology occurred between the social ranks, some of which were sex-related and time-dependent. In both sexes, dominant fish were larger than subordinates and dominant males had a higher growth rate during the trials. Subordinates had higher plasma cortisol and in males higher telencephalic corticotrophin-releasing hormone, neuropeptide y and glucocorticoid receptor gene expression. Splenic cytokine expression suggested differences in immune status between ranks in both sexes and hematocrit was elevated in subordinate males. In both sexes, dominants and subordinates differed in the expression of genes for various gonadal sex steroid receptors and steroidogenic enzymes and in dominant females the ovary was larger relative to body mass compared with in subordinates. Dominant males had higher plasma 11-ketotestosterone than subordinates and there was an increase in the number of spermatids in their testes over the duration of the study that was not seen in subordinate males. The wide-ranging physiological differences seen between dominant and subordinate zebrafish as a consequence of their social status suggest negative health impacts for subordinates after prolonged durations in those hierarchies.

Unravelling the neurophysiological basis of aggression in a fish model.

BACKGROUND: Aggression is a near-universal behaviour with substantial influence on and implications for human and animal social systems. The neurophysiological basis of aggression is, however, poorly understood in all species and approaches adopted to study this complex behaviour have often been oversimplified. We applied targeted expression profiling on 40 genes, spanning eight neurological pathways and in four distinct regions of the brain, in combination with behavioural observations and pharmacological manipulations, to screen for regulatory pathways of aggression in the zebrafish (Danio rerio), an animal model in which social rank and aggressiveness tightly correlate. RESULTS: Substantial differences occurred in gene expression profiles between dominant and subordinate males associated with phenotypic differences in aggressiveness and, for the chosen gene set, they occurred mainly in the hypothalamus and telencephalon. The patterns of differentially-expressed genes implied multifactorial control of aggression in zebrafish, including the hypothalamo-neurohypophysial-system, serotonin, somatostatin, dopamine, hypothalamo-pituitary-interrenal, hypothalamo-pituitary-gonadal and histamine pathways, and the latter is a novel finding outside mammals. Pharmacological manipulations of various nodes within the hypothalamo-neurohypophysial-system and serotonin pathways supported their functional involvement. We also observed differences in expression profiles in the brains of dominant versus subordinate females that suggested sex-conserved control of aggression. For example, in the HNS pathway, the gene encoding arginine vasotocin (AVT), previously believed specific to male behaviours, was amongst those genes most associated with aggression, and AVT inhibited dominant female aggression, as in males. However, sex-specific differences in the expression profiles also occurred, including differences in aggression-associated tryptophan hydroxylases and estrogen receptors. CONCLUSIONS: Thus, through an integrated approach, combining gene expression profiling, behavioural analyses, and pharmacological manipulations, we identified candidate genes and pathways that appear to play significant roles in regulating aggression in fish. Many of these are novel for non-mammalian systems. We further present a validated system for advancing our understanding of the mechanistic underpinnings of complex behaviours using a fish model.

Impacts of early life exposure to estrogen on subsequent breeding behavior and reproductive success in zebrafish.

Impacts of exposure to environmental estrogens on reproductive development are well documented, but recently wider concern has been raised due to evidence that such exposures can disrupt normal patterns of reproductive behavior, dominance, and parentage, with potential population level implications. It is fundamental therefore to understand any such effects for effective risk assessment. This study investigated the impact of a transient exposure to ethinylestradiol (EE(2)) during early life (from 20-60 days post fertilization), including at a dosing level within the environmental range, on the subsequent reproductive behavior and success in both male and female zebrafish (Danio rerio) in competitive breeding scenarios. There were no obvious effects of the early life EE(2) exposures on the subsequent gonadal phenotypes in either mature males or females. In fact, reproductive success in males exposed to 2.76 ng EE(2)/L was increased in competitive spawning scenarios. In contrast, exposure of females to EE(2) (9.86 ng/L) during early life reduced their subsequent reproductive success in competitive spawning scenarios. Mate choice experiments suggested this was a consequence of the females' diminished courting behavior toward males, rather than any male preference for unexposed females. Reproductive capability of females is generally considered a key determinant in population demographics and dynamics, and therefore the effect of exposure to EE(2) on female reproductive success may have significant implications for exposed fish populations.

Mechanisms of toxicity of di(2-ethylhexyl) phthalate on the reproductive health of male zebrafish.

Phthalates are ubiquitous in the aquatic environment and are known to adversely affect male reproductive health in mammals through interactions with multiple receptor systems. However, little is known about the risks they pose to fish. This project investigated the effects of di(2-ethylhexyl) phthalate (DEHP), the most commonly used phthalate, on the reproductive health of male zebrafish (Danio rerio). Males were treated with 0.5, 50 and 5000 mg DEHP kg(-1) (body weight) for a period of 10 days via intraperitoneal injection. The effects of the exposure were assessed by analysing fertilisation success, testis histology, sperm DNA integrity and transcript profiles of the liver and testis. A significant increase in the hepatosomatic index and levels of hepatic vitellogenin transcript were observed following exposure to 5000 mg DEHP kg(-1). Exposure to 5000 mg DEHP kg(-1) also resulted in a reduction in fertilisation success of oocytes spawned by untreated females. However, survival and development of the resulting embryos were unaffected by all treatments, and no evidence of DEHP-induced sperm DNA damage was observed. Exposure to 50 and 5000 mg DEHP kg(-1) caused alterations in the proportion of germ cells at specific stages of spermatogenesis in the testis, including a reduction in the proportion of spermatozoa and an increase in the proportion of spermatocytes, suggesting that DEHP may inhibit the progression of meiosis. In parallel, exposure to 5000 mg DEHP kg(-1) increased the levels of two peroxisome proliferator-activated receptor (PPAR) responsive genes (acyl-coenzyme A oxidase 1 (acox1) and enoyl-coenzyme A, hydratase/3-hydroxyacyl coenzyme A dehydrogenase (ehhadh). These data demonstrated that exposure to high concentrations of DEHP disrupts spermatogenesis in adult zebrafish with a consequent decrease in their ability to fertilise oocytes spawned by untreated females. Furthermore, our data suggest that the adverse effects caused by exposure to DEHP are likely to occur preferentially via PPAR signalling pathways in the testis and oestrogen signalling pathways in the liver. We found no evidence of adverse effects on zebrafish reproductive health following exposure to the concentrations occurring in most aquatic systems, indicating that DEHP alone may not be a causative agent of the reproductive abnormalities seen in wildlife, at least as a result of short-term exposures.

Effects of advanced treatments of wastewater effluents on estrogenic and reproductive health impacts in fish.

Whether the implementation of additional treatments for the removal of estrogens from wastewater treatment works (WwTWs) effluents will eliminate their feminizing effects in exposed wildlife has yet to be established, and this information is crucial for future decisions on investment into WwTWs. Here, granular activated carbon (GAC), ozone (O(3)), and chlorine dioxide (ClO(2)) were investigated for their effectiveness in reducing steroidal estrogen levels in a WwTW effluent and assessments made on the associated estrogenic and reproductive responses in fathead minnows (Pimephales promelas) exposed for 21 days. All treatments reduced the estrogenicity of the standard-treated (STD) effluent, but with different efficacies; ranging between 70-100% for total estrogenicity and 53-100% for individual steroid estrogens. In fish exposed to the GAC- and ClO(2)- (but not O(3)-) treated effluents, there was no induction of plasma vitellogenin (VTG) or reduction in the weight of the fatpad, a secondary sex character in males, as occurred for fish exposed to STD effluent. This finding suggests likely benefits of employing these treatment processes for the reproductive health in wild fish populations living in rivers receiving WwTW discharges. Exposure of pair-breeding minnows to the GAC-treated effluent, however, resulted in a similar inhibition of egg production to that occurring for exposure to the STD effluent (34-40%). These data, together with a lack of effect on egg production of the estrogen, ethinylestradiol (10 ng/L), alone, suggest that chemical/physical properties of the effluents rather than their estrogenicity were responsible for the reproductive effect and that these factor(s) were not remediated for through GAC treatment. Collectively, our findings illustrate the importance of assessing integrative biological responses, rather than biomarkers alone, in the assessment and improvement of WwTW technologies for the protection of wild fish populations.

Dominance hierarchies in zebrafish (Danio rerio) and their relationship with reproductive success.

The zebrafish has considerable potential for use as a model in the study of behavior in social systems, particularly dominance hierarchies, which are widespread in nature and can affect the lifelong success of individuals. There is, however, a paucity of information relating to the characterization of social groups and significance of dominance hierarchies in the zebrafish model. This study set out to bridge this knowledge gap and better characterize dominance and its implications for reproductive success in both male and female zebrafish in colonies comprising of two males and two females. Analyses of four aggressive behaviors (chase, bite, repel, spar) were conducted twice daily over a 5-day period, and fertilized eggs were collected for parentage analyses using DNA microsatellite markers. Dominant-subordinate relationships occurred both between males and between females, and in both sexes, dominance was associated with a greater body size and higher levels of aggression. During the spawning period, dominant females were, however, less aggressive toward their subordinates than dominant males to their subordinates. Aggressive behaviors employed for maintaining dominance did not differ between the sexes, but in females, in contrast with males, the level of aggression directed toward the subordinate fish increased over the study period. Overall, dominance resulted in a greater total reproductive success in males but not in females; however, dominant females sired more offspring with the dominant male. The findings illustrate that energy invested in dominance behavior appears beneficial for both sexes in zebrafish.

Environmental health impacts of equine estrogens derived from hormone replacement therapy.

Many factors have been considered in evaluations of the risk-benefit balance of hormone replacement therapy (HRT), used for treating menopausal symptoms in women, but not its potential risks for the environment We investigated the possible environmental health implications of conjugated equine estrogens (CEEs), the most common components of HRT, including their discharge into the environment, their uptake, potency, and ability to induce biological effects in wildlife. Influents and effluents from four U.K. sewage treatment works (STWs), and bile of effluent-exposed fish, were screened for six equine estrogens. In vitro estrogen receptor (ER) activation assays were applied in humans and fish to compare their potencies, followed by in vivo exposures of fish to equine estrogens and evaluation of bioaccumulation, estrogenic responses, and ER gene expression. The equine estrogen equilenin (Eqn), and its metabolite 17beta-dihydroequilenin (17beta-Eqn), were detected by tandem GC-MSMS in all STW influent samples and 83% of STW effluent samples analyzed, respectively, at low concentrations (0.07-2.6 ng/L) and were taken-up into effluent-exposed fish. As occurs in humans, these estrogens bound to and activated the fish ERs, with potencies at ERalpha 2.4-3490% of thatfor 17beta-estradiol. Exposure of fish for 21 days to Eqn and 17beta-Eqn induced estrogenic responses including hepatic growth and vitellogenin production at concentrations as low as 0.6-4.2 ng/L. Associated with these effects were inductions of hepatic ERalpha and ERbeta1 gene expression, suggesting ER-mediated mechanism(s) of action. These data provide evidence for the discharge of equine estrogens from HRT into the aquatic environment and highlight a strong likelihood that these compounds contribute to feminization in exposed wildlife.

Variability in measures of reproductive success in laboratory-kept colonies of zebrafish and implications for studies addressing population-level effects of environmental chemicals.

Laboratory tests that quantify reproductive success using model fish species are used to investigate for population-level effects of endocrine disrupting chemicals (EDCs) and other chemicals discharged into the environment. Even for the zebrafish (Danio rerio), however, one of the most widely used laboratory models, surprisingly little is known about the normal variability in measures of reproductive success and this information is crucial for robust test design. In this study, the dynamics of breeding and inherent variability in egg output/viability and sperm quality were characterized among individuals/colonies and over time in 34 colonies of laboratory-kept zebrafish over a 20-day study period. For this work, a '6 x 6' (six males and six females) colony size was adopted, as this is both environmentally relevant and optimal when considering egg output and animal welfare combined: an initial experiment showed egg output per female increased with decreasing colony size however, there was also a parallel increase in aggressive behavior. Both egg output and viability in '6 x 6' colonies were highly variable among colonies (with co-efficients of variation (CVs) of 30 and 11%, respectively) and over the 20-day study duration (considering egg output and viability of all the colonies combined, the CVs were 20 and 12%, respectively). The patterns of egg production also differed among the '6 x 6' colonies, and they included a cyclical output, a consistent daily output, an infrequent egg output with intermittent days of very high egg output, and an output with no obvious pattern. Sperm quality, measured as percentage motility and curvilinear velocity (VCL), was variable both among individuals within '6 x 6' colonies and across colonies, with percentage motility being the most variable parameter (mean CVs of 82% inter-individual within colonies and 49% inter-colony). Sperm quality did not, however, vary over a 24h period. A minimum number of six replicate '6 x 6' colonies, assessed daily for a period of 4 days, was required per treatment to detect a 40% change in egg output. The minimum numbers of individual males required per treatment to detect a 40% change in sperm quality using the breeding system adopted were 32 males for percentage motility and 12 males for VCL, equivalent to six and two '6 x 6' colonies, respectively. These data demonstrate the need for high levels of replication when testing for effects of EDCs on reproductive output in the zebrafish model in an environmentally relevant ('6 x 6') breeding matrix.

The kisspeptin/gonadotropin-releasing hormone pathway and molecular signaling of puberty in fish.

The mechanisms underlying the initiation of puberty in fish are poorly understood, and whether the Kiss1 receptor (Kiss1r; previously designated G protein-coupled receptor 54; GPR54) and its ligands, kisspeptins, play a significant role, as has been established in mammals, is not yet known. We determined (via real-time PCR) temporal patterns of expression in the brain of kiss1r, gnrh2, and gnrh3 and a suite of related genes in the hypothalamo-pituitary-gonadal (HPG) axis and analyzed them against the timing of gonadal germ cell development in male and female fathead minnow (Pimephales promelas). Full- or partial-length cDNAs for kiss1r (736 bp), gnrh2 (698 bp), and gnrh3 (804 bp) cloned from fathead minnow were found to be expressed only in the brain, testis, and ovary of adult fish. Localization of kiss1r, gnrh2, and gnrh3 within the brain provided evidence for their physiological roles and a likely hypophysiotropic role for GnRH3 in this species (which, like other cyprinids, does not appear to express gnrh1). In both sexes, kiss1r expression in the brain increased at the onset of puberty and reached maximal expression in males when spermatagonia type B appeared in the testis and in females when cortical alveolus-stage oocytes first appeared in the ovary, the timings of which differed for the two sexes. However, kiss1r expression was considerably lower during more advanced stages of spermatogenesis and oogenesis. The expression of kiss1r closely aligned with that of the gnrh genes (gnrh3 in particular), suggesting the Kiss1r/kisspeptin system in fish has a similar role in puberty to that occurring in mammals, and this hypothesis was supported by the induction of gnrh3 (2.25-fold) and kiss1r (1.5-fold) in early-mid pubertal fish injected with mammalian kisspeptin-10 (2 nmol/g wet weight). An intriguing finding, and contrasting that in mammals, was an elevated expression of esr1, ar, and cyp19a2 (genes involved in sex steroid signaling) in the brain at the onset of puberty, and in females slightly in advance of the elevation in the expression of kiss1r.

Health impacts of estrogens in the environment, considering complex mixture effects.

BACKGROUND: Environmental estrogens in wastewater treatment work (WwTW) effluents are well established as the principal cause of reproductive disruption in wild fish populations, but their possible role in the wider health effects of effluents has not been established. OBJECTIVES: We assessed the contribution of estrogens to adverse health effects induced in a model fish species by exposure to WwTW effluents and compared effects of an estrogen alone and as part of a complex mixture (i.e., spiked into effluent). METHODS: Growth, genotoxic, immunotoxic, metabolic, and endocrine (feminized) responses were compared in fathead minnows (Pimephales promelas) exposed for 21 days to a potent estrogenic effluent, a weakly estrogenic effluent before and after spiking with a steroidal estrogen [17 alpha-ethinyl-estradiol (EE2)], and to EE2 alone. RESULTS: In addition to endocrine disruption, effluent exposure induced genotoxic damage, modulated immune function, and altered metabolism; many of these effects were elicited in a sex-specific manner and were proportional to the estrogenic potencies of the effluents. A key finding was that some of the responses to EE2 were modified when it was present in a complex mixture (i.e., spiked into effluent), suggesting that mixture effects may not be easily modeled for effluent discharges or when the chemicals impact on a diverse array of biological axes. CONCLUSION: These data reveal a clear link between estrogens present in effluents and diverse, adverse, and sex-related health impacts. Our findings also highlight the need for an improved understanding of interactive effects of chemical toxicants on biological systems for understanding health effects of environmental mixtures.

Appropriate 'housekeeping' genes for use in expression profiling the effects of environmental estrogens in fish.

BACKGROUND: Attempts to develop a mechanistic understanding of the effects of environmental estrogens on fish are increasingly conducted at the level of gene expression. Appropriate application of real-time PCR in such studies requires the use of a stably expressed 'housekeeping' gene as an internal control to normalize for differences in the amount of starting template between samples. RESULTS: We sought to identify appropriate genes for use as internal controls in experimental treatments with estrogen by analyzing the expression of eight functionally distinct 'housekeeping' genes (18S ribosomal RNA [18S rRNA], ribosomal protein l8 [rpl8], elongation factor 1 alpha [ef1a], glucose-6-phosphate dehydrogenase [g6pd], beta actin [bactin], glyceraldehyde-3-phosphate dehydrogenase [gapdh], hypoxanthine phosphoribosyltransferase 1 [hprt1], and tata box binding protein [tbp]) following exposure to the environmental estrogen, 17alpha-ethinylestradiol (EE2), in the fathead minnow (Pimephales promelas). Exposure to 10 ng/L EE2 for 21 days down-regulated the expression of ef1a, g6pd, bactin and gapdh in the liver, and bactin and gapdh in the gonad. Some of these effects were gender-specific, with bactin in the liver and gapdh in the gonad down-regulated by EE2 in males only. Furthermore, when ef1a, g6pd, bactin or gapdh were used for normalization, the hepatic expression of two genes of interest, vitellogenin (vtg) and cytochrome P450 1A (cyp1a) following exposure to EE2 was overestimated. CONCLUSION: Based on the data presented, we recommend 18S rRNA, rpl8, hprt1 and/or tbp, but not ef1a, g6pd, bactin and/or gapdh, as likely appropriate internal controls in real-time PCR studies of estrogens effects in fish. Our studies show that pre-validation of control genes considering the scope and nature of the experiments to be performed, including both gender and tissue type, is critical for accurate assessments of the effects of environmental estrogens on gene expression in fish.

Gene expression profiles revealing the mechanisms of anti-androgen- and estrogen-induced feminization in fish.

Environmental anti-androgens are increasingly being recognized as potential contributing factors in the chemically induced feminization of wild fish because, by blocking androgen action, they can produce phenotypic effects similar to environmental estrogens. The molecular mechanisms by which anti-androgens and estrogens exert feminizing effects, however, have not been systematically compared. Using a targeted approach, we profiled the expression responses of a suite of 22 genes involved in reproduction, growth and development (processes controlled by androgens and estrogens) in the liver and gonad in adult male and female fathead minnow (Pimephales promelas) exposed to the model anti-androgen flutamide and the model synthetic estrogen 17alpha-ethinylestradiol (EE(2)). Both flutamide (320 microg/L) and EE(2) (10ng/L) produced phenotypic effects indicative of feminization (induction of plasma vitellogenin, reduced gonadosomatic index, and reduced secondary sex characters), although for the chosen test concentrations EE(2) was the more potent. For the genes studied, flutamide and EE(2) produced distinct expression profiles, suggesting that they largely operate via distinct molecular mechanisms. As examples, in liver EE(2) (but not flutamide) exposure up-regulated estrogen receptor (ER) alpha mRNA, whereas flutamide exposure increased ERbeta and ERgamma mRNAs in males and resulted in decreased androgen receptor (AR) mRNA in females. In the testis, flutamide up-regulated genes coding for enzymes involved in androgen biosynthesis (cytochrome P450 17 [CYP17] and 11beta-hydroxysteroid dehydrogenase [11beta-HSD]) implying an inhibitory action on androgen negative feedback pathways. EE(2), in contrast, inhibited the expression of enzymes involved in androgen biosynthesis (CYP17, 11beta-HSD and 17beta-hydroxysteroid dehydrogenase [17beta-HSD]). There were also some commonalities in the molecular mechanisms of flutamide and EE(2) action, including the down-regulation of gonadal sex steroid receptor expression (gonadal AR and ovarian ERalpha), increased expression of genes coding for estrogen-producing enzymes (cytochrome P450 19A and B [CYP19A and CYP19B]), decreased expression of genes involved in testis differentiation (anti-Mullerian hormone [AMH] and doublesex and mab-3 related transcription factor 1 [DMRT1]), and decreased expression of hepatic genes which mediate wider physiological processes such as somatic growth (growth hormone [GH], GH receptor [GHR], insulin-like growth factor-I [IGF-I], IGF-I receptor [IGF-IR], thyroid hormone receptor alpha [TRalpha] and beta [TRbeta]).

Gene expression profiling for understanding chemical causation of biological effects for complex mixtures: a case study on estrogens.

Gene expression profiling offers considerable potential for identifying chemical causation of effects induced in exposures to complex mixtures, and for understanding the mechanistic basis for their phenotypic effects. We characterized gene expression responses in livers and gonads of fathead minnow (Pimephales promelas) exposed (for 14-21 days) to estrogenic wastewater treatment works final effluents with varying potencies and assessed the extent to which these expression profiles mapped with those induced by individual steroid estrogens present in the effluents (17beta-estradiol and 17alpha-ethinylestradiol) and, thus, were diagnostic of estrogen exposure. For these studies, we adopted a targeted approach (via real-time PCR) with a suite of 12 genes in liver and 21 genes in gonad known to play key roles in reproduction, growth and development (processes controlled by estrogens) and responses were compared with effects on phenotypic end points indicative of feminization. Gene responses to effluent were induced predominantly in a linear (monotonic) concentration-dependent manner but were complex with many genes responding differently between tissue types and sexes. The gene expression profiles for the estrogenic effluents and the individual steroid estrogens had many common features. There were marked differences in the profiles between the two effluents, however, that were not explained by differences in their estrogenic potencies, suggesting that these may have arisen as a consequence of differences in the contents of other chemicals, which may act directly or indirectly with the estrogen-response pathway to alter estrogen-induced gene expression. These data demonstrate that the patterns of gene expression induced by estrogenic effluents, although complex, can be diagnostic for some of the estrogens they contain and provide insights into the mechanistic basis for the phenotypic effects seen.

Cloning and characterization of cDNAs for hormones and/or receptors of growth hormone, insulin-like growth factor-I, thyroid hormone, and corticosteroid and the gender-, tissue-, and developmental-specific expression of their mRNA transcripts in fathead minnow (Pimephales promelas).

Growth hormone (GH), insulin-like growth factor-I (IGF-I), thyroid hormones, and corticosteroids play central roles in a wide range of body functions but, in fish, information on their interactions is limited. These axes of the endocrine system are also potential targets for disruption of signaling pathways by hormone-mimicking chemicals, but have received little study. Molecular approaches offer an effective way to help unravel these endocrine interactions but require the appropriate gene-specific assays to do so. In this study, the cDNAs for a suite of hormones and/or receptors involved in signaling for the effects of GH and IGF-I [GH, GH receptor (GHR), IGF-I, IGF-I receptor (IGF-IR)], thyroid hormones [thyroid hormone receptor alpha (TRalpha) and beta (TRbeta)], and corticosteroids [glucocorticoid receptor (GR)] were cloned from the fathead minnow (Pimephales promelas; fhm), and the tissue-, developmental-, and gender-related expression of their mRNA transcripts established. By polymerase chain reaction (PCR) strategy, we obtained full-length 1123-bp GH, 817-bp IGF-I, 1584-bp TRbeta, and 2571-bp GR cDNAs, coding for 210 amino acid (aa) GH, 161 aa IGF-I, 378 aa TRbeta, and 745 aa GR putative proteins, and partial-length 158-bp GHR, 811-bp IGF-IR, and 446-bp TRalpha cDNAs. Real-time PCR analyses revealed broad tissue expression for the target mRNAs; all targets were expressed in brain, pituitary, gill, liver, gonad, intestine, and muscle, with the exception of GH that was expressed only in the pituitary and gonad. Expression patterns in both juvenile and adult fhm were complex, with both temporal-, tissue-, and sex-specific characteristics. For example, hepatic expressions of GHR, IGF-I, and IGF-IR were far higher in males than in females, possibly reflecting the sex-related dimorphism in growth that occurs in this species, and TRalpha and TRbeta showed divergent expression patterns during development (where TRbeta predominated) and in adult tissues implying some distinct roles for the two TR subtypes.

Multiple molecular effect pathways of an environmental oestrogen in fish.

Complex interrelationships in the signalling of oestrogenic effects mean that environmental oestrogens present in the aquatic environment have the potential to disrupt physiological function in fish in a more complex manner than portrayed in the present literature. Taking a broader approach to investigate the possible effect pathways and the likely consequences of environmental oestrogen exposure in fish, the effects of 17beta-oestradiol (E(2)) were studied on the expression of a suite of genes which interact to mediate growth, development and thyroid and interrenal function (growth hormone GH (gh), GH receptor (ghr ), insulin-like growth factor (IGF-I) (igf1), IGF-I receptor (igf1r ), thyroid hormone receptors-alpha (thra) and -beta (thrb) and glucocorticoid receptor (gr )) together with the expression analyses of sex-steroid receptors and ten other genes centrally involved in sexual development and reproduction in fathead minnow (fhm; Pimephales promelas). Exposure of adult fhm to 35 ng E(2)/l for 14 days induced classic oestrogen biomarker responses (hepatic oestrogen receptor 1 and plasma vitellogenin), and impacted on the reproductive axis, feminising "male" steroidogenic enzyme expression profiles and suppressing genes involved in testis differentiation. However, E(2) also triggered a cascade of responses for gh, ghr, igf1, igf1r, thra, thrb and gr in the pituitary, brain, liver, gonad and gill, with potential consequences for the functioning of many physiological processes, not just reproduction. Molecular responses to E(2) were complex, with most genes showing differential responses between tissues and sexes. For example, igf1 expression increased in brain but decreased in gill on exposure to E(2), and responded in an opposite way in males compared with females in liver, gonad and pituitary. These findings demonstrate the importance of developing a deeper understanding of the endocrine interactions for unravelling the mechanisms of environmental oestrogen action and predicting the likely health consequences.