QUANTIFYING HISTOLOGICAL DEVELOPMENT IN THE GONADS OF SEXUALLY MATURING FATHEAD MINNOWS (PIMEPHALES PROMELAS): PHASE TWO (original) (raw)
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Aquatic Toxicology, 2006
The Endocrine Modulators Study Group (EMSG) of the European Chemical Industry has proposed an extended fish early-life stage (ELS) test based on OECD test guideline 210 in combination with a fish pair-breeding reproduction study as a possible alternative for fish full life cycle testing. In this paper the androgen methyldihydrotestosterone (MDHT) was tested in an extended ELS test with fathead minnow supplementary to such a test with the weak estrogen 4-tert-pentylphenol (4TPP). Main endpoints were secondary sexual characteristics (SSC), plasma vitellogenin (VTG) induction and gonadal development. Early blastula embryos were exposed to 0, 0.10, 0.32 and 1.0 g MDHT l −1 for up to 114 days post-hatch (dph). A batch of fish exposed to 1.0 g l −1 was transferred to clean water after 30 or 63 dph for the remainder of the study. Ethinylestradiol (EE2) was included as estrogenic reference substance at 0.01 g l −1 . Exposure to MDHT had no significant effect on hatching success or survival, but significantly increased the condition factor of fish exposed for 63 and 114 dph (up to 150% of the control). At 63 dph MDHT exposure induced appearance of tubercles on the snout (a male SSC) of more than 80% of fish. Compared to the controls, plasma VTG was not detectable or significantly lower in fish exposed to MDHT at 0.10 g/l, but not significantly affected at higher MDHT concentrations. Both lower levels of MDHT significantly inhibited the development of female gonads as of 30 dph. Fish exposed to MDHT at 0.32 and 1.0 g l −1 showed higher incidences of mixed sex gonads (10-25%) and smaller testes or dysplasia of gonadal tissue. Dysplasia was present in 80% of the fish continuously exposed to 1.0 g l −1 up to 114 dph, but reversible when fish were transferred to dilution water. Results indicate that suppression of ovarian development was the most sensitive endpoint for MDHT exposure after 30 dph. Other endpoints (e.g., growth and SSC) required exposure during at least up to 63 dph to yield a significant effect. Androgenic effects on VTG production required even longer exposure, i.e., until sufficient number of females had matured.
Aquatic Toxicology, 2006
An extended early-life stage test (based on OECD test guideline 210) was developed to allow the evaluation of a weak environmental oestrogen, 4-tert-pentyphenol (4TPP), on sexual differentiation and gonadal development. Fathead minnow (Pimephales promelas) embryos were exposed to three concentrations of 4TPP (56, 180 and 560 g l −1 ) in a flow-through system, at 25 ± 1 • C, for <107 days post-hatch (dph). In addition, some embryos were exposed to 180 g 4TPP l −1 until 30 or 60 dph, after which they were exposed to dilution water only until 107 dph. At 30, 60 and 107 dph fish were evaluated for growth and gonadal development (via histology), and at 107 dph fish were also evaluated for secondary sexual characteristics (SSC), gonadosomatic index (GSI) and plasma vitellogenin (VTG). There were no effects of 4TPP on hatching success or survival, however, there was a delay in the time taken for embryos to hatch (560 g 4TPP l −1 ). No treatment-related effects were observed on fish growth, with the exception of at 107 dph when the condition factor in female fish was reduced in all 4TPP continuous exposure treatments. Plasma VTG was only elevated in female fish exposed to 180 g 4TPP l −1 and inhibition of gonadal growth (GSI) occurred only in females exposed to 560 g 4TPP l −1 . Histological examination of the gonads revealed delays and disruption in male sexual differentiation and development (180 g 4TPP l −1 ) and no testicular tissue was observed in any fish exposed to 560 g 4TPP l −1 . Mixed gonads (predominately testes with a scattering of primary oocytes) were present in fish exposed to all doses of 180 g 4TPP l −1 at 107 dph. Feminisation of the reproductive ducts (formation of an ovarian like cavity) occurred in the testis of all males exposed to 180 g l −1 , regardless of length of 4TPP exposure. Results indicate that the period of 30-60 dph appears to be the sensitive window for disruption of formation of the reproductive duct and this effect is not reversible when the fish are transferred to dilution water. The data also show that this integrative test is suitable for the detection of a weak environmental oestrogen and comparisons of these results with that of a fish full life-cycle, in medaka, indicate that this test could be a suitable surrogate for a fish full life-cycle. (G.H. Panter). through a variety of mechanisms of action and as a result this has given impetus for the development of screening assays and tests for the detection of EACs, notably in aquatic species. In Europe, the EMSG developed an aquatic research programme to assess the effects of EACs on fish. Within this programme robust and sensitive fish screening assays have already been developed for the evaluation of a range of EACs, using the fathead minnow (Pimephales promelas) . However, although such screening assays will identify the potential endocrine activity of chemicals, further chronic testing will be required to provide more detailed information 0166-445X/$ -see front matter
Aquatic Toxicology, 1999
Environmental contaminants with estrogenic activity have recently received attention because of their potential effects on the reproductive efficiency of humans and wildlife. This study was conducted with the endogenous estrogen, 17 b-estradiol (E2), to establish the histologic response of the fathead minnow (Pimephales promelas) as a model organism. Sexually mature fathead minnows were exposed for 14 days to waterborne concentrations of 1000, 100, 10, 2, 1, 0.5, 0.25, 0.125, 0.1 or 0.0625 nM E2. Exposure to E2 caused a reduction in size of the prominent male secondary sex characteristics, the fatpads and nuptial breeding tubercles. Histological lesions observed in the testes included proliferation of Sertoli cells and degenerative changes. Electron microscopy of seminiferous tubules and their Sertoli cells revealed large phagolysosomes filled with degenerating spermatozoa and other cellular debris. Females had ovaries in which most of the follicles were in the primary stage of development. There were also more atretic follicles and fewer secondary and Graafian follicles than in unexposed females. These findings demonstrate components of sexually mature fish which may be altered by compounds that mimic E2. To determine if lesions observed in males were permanent, 50 sexually mature males and females were exposed to a single concentration of 10 nM E2 for 10 days. Samples were collected from males on the final day of E2 exposure and over a period of 16 weeks after the exposure was stopped. No E2-induced lesions were observed beyond 16 weeks post E2 exposure. Results of these studies suggest that histological lesions could occur at ecologically-relevant exposures to 'estrogenic' compounds. However, certain lesions caused by exposure of adult fathead minnows are not permanent.
Environmental Toxicology and Chemistry, 2011
Vitellogenin (VTG) is a precursor of egg-yolk protein and is therefore present at high concentrations in the plasma of female fish. In male fish, VTG concentrations are usually undetectable or low, but can be induced upon exposure to oestrogenic substances either via the water or the diet. This work was carried o ut to determine the reason for apparently elevated VTG concentrations in unexposed stock male fathead minnow maintained in our laboratory. The results showed clear ly that some of the food given to the fish was oestrogenic and that replacement of this with non-oestrogenic food led to a significant reduction in the basal VTG levels measured in male fish after a 6 month period. This reduction in male VTG concentrations drastically increased the sensitivity of the VTG test in further studies carried out with these fish. Moreover, a review of published concentrations of V TG in unexposed male fathead minnow suggests that this problem may exist in other laboratories. The fathead minnow is a standard ecotoxicological fish test specie s and so these findings will be of interest to any laboratory carrying out fish tests on endocrine disrupting chemicals.
Environmental hormones and their impacts on sex differentiation in fathead minnows
Aquatic Toxicology, 2015
Runoff from lands fertilized with animal manure from concentrated animal feeding operations (CAFOs) is a source of hormones to surface water. In this study we tested the hypothesis that larval fathead minnows exposed to sex steroids singly or in a "typical" CAFO mixture during sex differentiation would respond with changes in the expression of a set of target genes, leading to gonadal abnormalities later in life. In the first experiment, a static daily-renewal system was used to expose larvae during the period of 10-20 days post-hatch (dph) to either 5 ng/L 17-trenbolone (17-TRB) or 5 ng/L 17␣-ethinylestradiol (EE 2 ). In a second experiment, fish were exposed from 0 to 45 dph in a flow-through system to a CAFO mixture composed of steroids and degradates (2-16 ng/L), atrazine and degradates (15-250 ng/L), and nitrate (3-11 mg/L). In the single hormone experiment, expression of genes involved in steroidogenesis (cyp19a, cyp17, and star) was decreased in females. In contrast, no differences in gene expression were observed in fish exposed to the CAFO mixture. However, the majority (84%) of treated males had testes containing an ovarian cavity, indicative of feminization, compared to 0% in the control males. Overall, our results show that: (1) changes in gene expression after single hormone exposures are sex-specific, with females more responsive than males; and (2) phenotypic alterations in testicular development can be elicited by a simulated "CAFO" mixture when fathead minnows are exposed during the first 45 days of development. More research is needed to further discern the complex response of fish to steroid mixtures, especially those associated with runoff from land-applied CAFO waste.
Ecotoxicology, 2002
Sexual differentiation in fish occurs after hatching during early life-stages and is believed to be a time when the gonad has a heightened sensitivity to disruption by chemicals that mimic hormones. In this study fathead minnows (Pimephales promelas) were exposed to an environmentally relevant concentration of ethinylestradiol (EE2) for short intervals in fish early life-stages and vitellogenic and gonadal responses were measured at 30 and 100 dph (sexual maturity), respectively. All EE2 exposure regimes induced vitellogenin (VTG) synthesis and disruption in duct development (a feminization) in males, with a window of enhanced sensitivity between 10 and 15 dph (where 60% of the males had feminized ducts). There was an altered pattern in sex cell development in males (inhibition of spermatogenesis) in the solvent controls (ethanol 0.1 ml/l) and all EE2 treatments when compared with the dilution water controls. Furthermore, fewer spermatozoa were observed in the testis of males exposed to EE2 from 15 to 20 dph and fertilized eggs (<24 h post-fertilization) -20 dph, compared with both the solvent and dilution water controls. These data show that short exposures of embryos/very early life-stage fathead minnows to an environmentally relevant concentration of EE2 lead to alterations in gonadal development that potentially have reproductive consequences and thus population level effects.
Aquatic Toxicology, 2011
Exogenous treatment of fish with natural sex hormones and their mimics has been shown to influence gonadal differentiation resulting in biased phenotypic sex-ratios. This has lead to the development of the Fish Sexual Development Test (FSDT) as a method for the detection of endocrine active chemicals. Proposed test organisms include the medaka, zebrafish (ZF) and stickleback, although the guideline also allows for inclusion of species such as the fathead minnow (FHM), provided the test duration allows for sufficient sexual differentiation. However, although the processes underlying sexual differentiation are known to differ for each of these species, it is not known how, or if, these differences would influence the results of the FSDT. In the experiments reported here, responses of the ZF and FHM to prochloraz, a sterol biosynthesis inhibitor and androgen antagonist, were characterized and compared. Exposure to 320 g/L of prochloraz, from embryo until 60 (ZF) or 95-125 (FHM) days post hatch inhibited somatic growth of both species, but while a negative impact on ZF larval survival was observed (LOEC 32 g/L) there was no evidence for an effect on FHM larval survival. Prochloraz influenced sexual differentiation in both species by decreasing the proportion of females (LOEC 100 g/L (ZF), 320 g/L (FHM)) and delaying completion of sexual differentiation; manifest as an increased incidence of ovotestis in the ZF (LOEC 100 g/L) and as an increased number of fish with undifferentiated gonads in the FHM (LOEC 320 g/L). However, while exposure to 320 g/L prochloraz delayed maturation of the differentiated FHM testis, there was no such effect in the ZF. These results demonstrate that the different strategy of sexual differentiation in the ZF and FHM influences the profile of responses of their gonads to the masculinising effects of prochloraz, but does not affect their overall sensitivity.
Sex-Specific Gonadal and Gene Expression Changes throughout Development in Fathead Minnow
Sexual Development
Although fathead minnows (Pimephales promelas) are commonly used as a model fish in endocrine disruption studies, past studies have not characterized sex-specific baseline expression of genes involved in sex differentiation during development in this species. Using a sex-linked DNA marker to verify gender, we evaluated the expression over time of genes involved in sex differentiation (dmrt1, cyp19a, cyp17, star, esr1, ar) in developing fathead minnows (10-45 days post hatch). Evaluation of these molecular markers in combination with gender identification help us to better understand the mechanisms regulating sex differentiation in fathead minnows and how endocrine-disrupting chemicals may alter these processes. © 2013 S. Karger AG, Basel.
Environmental estrogenic effects and gonadal development in wild goldfish ( Carassius auratus
Environmental Monitoring and Assessment, 2009
Serum vitellogenin (VTG) contents of wild goldfish (Carassius auratus) were investigated as a sensitive biomarker for artificial estrogenic compounds in aquatic environments. Goldfish was sampled from a pristine area, a river situated 5 km downstream from a sewage treatment works (STW), and also from the Young-San River in Korea. The female yolk precursor protein VTG was not detected when gonadosomatic index (GSI) was less than 0.85%, while VTG levels of >10 μg/ml were found in males whose GSI was less than 1.53%. In male goldfish sampled from STW and the Young-San River, the higher VTG corresponded to lower GSI. This study suggested a trend that gonad development was connected to VTG levels in both sexes, and the application of GSI and histological analysis provide an attractive possibility that it could be included in the panel of markers used for estrogenic activity investigation of aquatic environments.