A Short-Term Study Investigating the Estrogenic Potency of Diethylstilbesterol in the Fathead Minnow (Pimephales promelas): Exposure Phase
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ABSTRACT:
ORGANISM(S): Pimephales promelas
PROVIDER: GSE36465 | GEO | 2012/09/20
SECONDARY ACCESSION(S): PRJNA155607
REPOSITORIES: GEO
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Project description:Diethylstilbestrol (DES) is a synthetic estrogen that has been banned for use in humans, but still is employed in livestock and aquaculture operations in some parts of the world. Detectable concentrations of DES in effluent and surface waters have been reported to range from slightly below 1 to greater than 10 ng/L. Little is known, however, concerning the toxicological potency of DES in fish. In this study, sexually-mature fathead minnows (Pimephales promelas) of both sexes were exposed to 1, 10 or 100 ng DES/L water in a flow-through system. Tissue concentrations of DES and changes in a number of estrogen-responsive endpoints, including alterations to the hepatic transcriptome in females, were measured in the fish at the end of a 4-d exposure, and after a 4-d depuration/recovery period in clean water. The objectives of the study were to measure accumulation of DES in fish tissues, characterize effects of the chemical on physiological endpoints related to reproductive performance, and to evaluate DES's potency relative to concentrations reported in aquatic environments. The current series includes n=11 microarrays associated with recovery-phase samples (collected from fish exposed continuously for 4 d, and then held in control water for an additional 4 days before tissues were collected).
2012-09-20 | GSE36466 | GEO
Project description:Diethylstilbestrol (DES) is a synthetic estrogen that has been banned for use in humans, but still is employed in livestock and aquaculture operations in some parts of the world. Detectable concentrations of DES in effluent and surface waters have been reported to range from slightly below 1 to greater than 10 ng/L. Little is known, however, concerning the toxicological potency of DES in fish. In this study, sexually-mature fathead minnows (Pimephales promelas) of both sexes were exposed to 1, 10 or 100 ng DES/L water in a flow-through system. Tissue concentrations of DES and changes in a number of estrogen-responsive endpoints, including alterations to the hepatic transcriptome in females, were measured in the fish at the end of a 4-d exposure, and after a 4-d depuration/recovery period in clean water. The objectives of the study were to measure accumulation of DES in fish tissues, characterize effects of the chemical on physiological endpoints related to reproductive performance, and to evaluate DES's potency relative to concentrations reported in aquatic environments. The current series includes n=11 microarrays associated with recovery-phase samples (collected from fish exposed continuously for 4 d, and then held in control water for an additional 4 days before tissues were collected). Fish were exposed to 0, 1, 10, or 100 ng DES/L delivered in a continuous flow (45 ml/min) of sand filtered, UV treated, Lake Superior Water, without the use of carrier solvents. Flow of DES into the test system was initiated without fish present and continued for 1 d. Exposures then were started by placing three male and three female sexually-mature fathead minnows into each tank. There were eight replicate tanks for the control and 100 ng/L treatments, and six replicate tanks for the 1 and 10 ng/L groups. The fish were held at 25+1M-BM-:C under a 16:8 L:D photoperiod and were fed frozen adult brine shrimp twice daily (San Francisco Bay Brand, Newark, CA, USA). Fish used for the experiment were from an on-site culture, and all procedures involving animals conformed to guidelines approved by the local Animal Care and Use Committee. After the 4-d exposure, fish from three tanks from each treatment (n=9 per sex) were sampled for determination of various biological endpoints. At this time fish from two additional tanks from the control and 100 ng/L treatments also were sampled for determination of DES tissue residues (n=6 per sex). Delivery of DES to the test system was subsequently stopped, and fish from the remaining three tanks per treatment group were sampled 4 d later (n= 9 per sex). The fathead minnows were euthanized with buffered MS-222 (Argent, Redmond, VA, USA) and weighed. Fish were scored for occurrence and relative expression of nuptial tubercles, which in males can be reduced by ER agonists. Blood was collected from the caudal vein/artery with a microhematocrit tube, and plasma was separated by centrifugation and stored at -80M-BM-:C. Gonads were removed from males and a subsample (8.5M-BM-13.0 mg; meanM-BM-1SD) was immediately immersed in tissue culture media for determination of ex vivo steroid production. Livers were removed from both sexes and flash-frozen for gene expression analyses using microarray (females) or real-time QPCR (males). Hepatic transcripts from three females per treatment group, in each phase of the experiment (except n=2 from recovery phase 10 ng/L) were analyzed using a custom 15,000 feature microarray (GEO Platform Accession GPL9248). Data sets for the exposure phase (n=12 microarrays) and recovery phase (n=11) were normalized independently using Fastlo (Ballman et al., 2004) implemented in R (http://www.r-project.org/), but analyzed using parallel approaches.
2012-09-20 | E-GEOD-36466 | biostudies-arrayexpress
Project description:Diethylstilbestrol (DES) is a synthetic estrogen that has been banned for use in humans, but still is employed in livestock and aquaculture operations in some parts of the world. Detectable concentrations of DES in effluent and surface waters have been reported to range from slightly below 1 to greater than 10 ng/L. Little is known, however, concerning the toxicological potency of DES in fish. In this study, sexually-mature fathead minnows (Pimephales promelas) of both sexes were exposed to 1, 10 or 100 ng DES/L water in a flow-through system. Tissue concentrations of DES and changes in a number of estrogen-responsive endpoints, including alterations to the hepatic transcriptome in females, were measured in the fish at the end of a 4-d exposure, and after a 4-d depuration/recovery period in clean water. The objectives of the study were to measure accumulation of DES in fish tissues, characterize effects of the chemical on physiological endpoints related to reproductive performance, and to evaluate DES's potency relative to concentrations reported in aquatic environments. The current series includes n=12 microarrays associated with exposure-phase samples (collected from fish exposed continuously for 4 d). Fish were exposed to 0, 1, 10, or 100 ng DES/L delivered in a continuous flow (45 ml/min) of sand filtered, UV treated, Lake Superior Water, without the use of carrier solvents. Flow of DES into the test system was initiated without fish present and continued for 1 d. Exposures then were started by placing three male and three female sexually-mature fathead minnows into each tank. There were eight replicate tanks for the control and 100 ng/L treatments, and six replicate tanks for the 1 and 10 ng/L groups. The fish were held at 25+1M-BM-:C under a 16:8 L:D photoperiod and were fed frozen adult brine shrimp twice daily (San Francisco Bay Brand, Newark, CA, USA). Fish used for the experiment were from an on-site culture, and all procedures involving animals conformed to guidelines approved by the local Animal Care and Use Committee. After the 4-d exposure, fish from three tanks from each treatment (n=9 per sex) were sampled for determination of various biological endpoints. At this time fish from two additional tanks from the control and 100 ng/L treatments also were sampled for determination of DES tissue residues (n=6 per sex). Delivery of DES to the test system was subsequently stopped, and fish from the remaining three tanks per treatment group were sampled 4 d later (n= 9 per sex). The fathead minnows were euthanized with buffered MS-222 (Argent, Redmond, VA, USA) and weighed. Fish were scored for occurrence and relative expression of nuptial tubercles, which in males can be reduced by ER agonists. Blood was collected from the caudal vein/artery with a microhematocrit tube, and plasma was separated by centrifugation and stored at -80M-BM-:C. Gonads were removed from males and a subsample (8.5M-BM-13.0 mg; meanM-BM-1SD) was immediately immersed in tissue culture media for determination of ex vivo steroid production. Livers were removed from both sexes and flash-frozen for gene expression analyses using microarray (females) or real-time QPCR (males). Hepatic transcripts from three females per treatment group, in each phase of the experiment (except n=2 from recovery phase 10 ng/L) were analyzed using a custom 15,000 feature microarray (GEO Platform Accession GPL9248). Data sets for the exposure phase (n=12 microarrays) and recovery phase (n=11) were normalized independently using Fastlo (Ballman et al., 2004) implemented in R (http://www.r-project.org/), but analyzed using parallel approaches.
2012-09-20 | E-GEOD-36465 | biostudies-arrayexpress
Project description:The phenylpyrazole fipronil is a widely used insecticide designed to inhibit γ -amino-butyric acid (GABA) receptors, the major inhibitory neurotransmitter in the central nervous system. Fipronil has been detected in some water systems in the ng/L range, and is reported to be neurotoxic. To address the risks associated with fipronil exposure, we measured morphological, physiological, and molecular responses in zebrafish (Danio rerio) embryos following a 48 hour exposure (20 ng/L – 2 mg/L). Survival was not different than controls following treatments below 200 µg fipronil/L but was ~20% higher with concentrations above 200 µg fipronil/L. Once the embryos hatched, they underwent a 7 day depuration phase. At 9 days post-fertilization (9 dpf), body length and notochord length were not different than controls for any dose. To assess sub-lethal effects, transcriptome profiling was conducted in 9 dpf larvae following 48 hour exposure + 7 dpf depuration to environmentally relevant concentrations of fipronil (200 ng fipronil/L), as well as two higher concentrations of the pesticide (200 µg fipronil/L and 2 mg fipronil/L). Transcriptome profiling revealed that all three concentrations affected pathways related to chromosome condensation and the metabolism of estrogens and androgens as well as genes related to methylation. In addition, 200 ng fipronil/L down-regulated genes related to the circadian clock, histone and DNA methylation, and histone acetylation, while the highest dose increased networks related to immune function (e.g. lectin-induced complement pathway and the alternative complement pathway). The two highest concentrations of fipronil increased the expression of transcriptional networks associated with mitochondrial respiratory chain dysfunction and mitochondrial protein transport. As such, we exposed 24 hpf embryos to fipronil for 24 hours and measured oxygen consumption rate to assess mitochondrial function. There were no differences in basal and maximal respiration in the embryos nor ATP production, and fipronil did not affect mitochondrial bioenergetics. This study suggests that fipronil at environmentally relevant concentrations does not adversely affect the survival or morphology of fish embryos, however sub-lethal endpoints should be examined to more fully characterize the long term effects of fipronil exposure in larval fish.
2018-01-31 | GSE99608 | GEO
Project description:17α-Ethinylestradiol (EE2) is a ubiquitous aquatic contaminant shown to decrease fish fertility at low concentrations, especially in fish exposed during development. The mechanisms of the decreased fertility are not fully understood. In this study, we perform transcriptome analysis by RNA sequencing of testes from zebrafish with previously reported lowered fertility due to exposure to low concentrations of EE2 during development. Fish were exposed to 1.2 and 1.6 ng/L (measured concentration) of EE2 from fertilization to 80 days of age, followed by 82 days of remediation in clean water.
2017-12-09 | E-MTAB-6251 | biostudies-arrayexpress
Project description:17-ethinylestradiol (EE2) is a synthetic estrogen commonly used as an active substance in oral contraceptives. It is frequently found in waste water effluent and raise concern due to its persistent nature. EE2 binds to estrogen receptors with similar affinity to oestradiol and acts as one of the most potent hormone mimics found in the environment. Estrogen is involved in many aspects of the development of the neuroendocrine system influencing both brain structure and behavior. We and others have reported a significant effect on non-reproductive behaviors in adult fish and in recent studies we found that developmental exposure to EE2 resulted in an anxiogenic phenotype as adults even after a long remediation period. In this study we aim to study possible mechanisms behind the behavior alterations of zebrafish developmentally exposed to EE2 by sequencing the whole brain transcriptome. Zebrafish embryos were exposed to 0, 2.14 and 7.34 ng/L EE2 from 1 day to 80 days post fertilization. After the exposure period a remediation period of 120 days followed before the fish were sampled. 3 male brains from the control group (0 ng/L) and the 2.14 ng/L group were sampled and 3 female brains from the control group (0 ng/L) and 7.34 ng/L were sampled.
2017-10-02 | E-MTAB-5173 | biostudies-arrayexpress
Project description:17alpha-ethinylestradiol (EE2), used for birth control in humans, is a potent estrogen that is found in wastewater at low concentrations (ng/L). EE2 has the ability to interfere with the endocrine system of fish, affecting reproduction which can result in population level effects. The objective of this study was to determine if dietary exposure to EE2 would alter gene expression patterns and key pathways in the liver and ovary and whether these could be associated with reproductive endpoints in female largemouth bass (LMB) during egg development. Female LMB received 70 ng EE2/g feed (feed administered at 1% of body weight) for 60 days. EE2 dietary exposure significantly reduced plasma vitellogenin concentrations by 70%. Hepatosomatic and gonadosomatic indices were also decreased with EE2 feeding by 38.5% and 40%, respectively. Transcriptomic profiling revealed that there were more changes in steady-state mRNA levels in the liver compared to the ovary. Genes associated with reproduction were differentially expressed such as vitellogenin in the liver and aromatase in the gonad. In addition, a set of genes related with oxidative stress (e.g., glutathione reductase and glutathione peroxidase) were identified as altered in the liver and genes associated with the immune system (e.g., complement component 1, and macrophage-inducible C-type lectin) were altered in the gonad. In a follow-up study with 0.2 ng EE2/g feed for 60 days, similar phenotypic and gene expression changes were observed that support these findings with the higher concentrations. This study provides new insights into how dietary exposure to EE2 interferes with endocrine signaling pathways in female LMB during a critical period of reproductive oogenesis.
2011-03-24 | GSE28143 | GEO
Project description:Aquatic organisms are continuously exposed to complex mixtures of chemicals, many of which can interfere with their endocrine system, resulting in impaired reproduction, development or survival, among others. In order to analyze the effects and mechanisms of action of estrogen/anti-estrogen mixtures, we exposed male fathead minnows (Pimephales promelas) for 48 hours via the water to 2, 5, 10, and 50 ng 17α- ethinylestradiol (EE2)/L, 100 ng ZM 189,154/L (a potent antiestrogen known to block activity of all estrogen receptors) or mixtures of 5 or 50 ng EE2/L with 100 ng ZM 189,154/L. We analyzed gene expression changes in the gonad, as well as hormone and vitellogenin plasma levels. Steroidogenesis was down-regulated by EE2 as reflected by the reduced plasma levels of testosterone in the exposed fish and down-regulation of genes in the steroidogenic pathway. Microarray analysis of testis of fathead minnows treated with 5 ng EE2/L or with the mixture of 5 ng EE2/L and 100 ng ZM 189,154/L indicated that some of the genes whose expression was changed by EE2 were blocked by ZM 189,154, while others were either not blocked or enhanced by the mixture, generating two distinct expression patterns. Gene ontology and pathway analysis programs were used to determine categories of genes for each expression pattern. Our results suggest that response to estrogens occurs via multiple mechanisms, including canonical binding to soluble estrogen receptors, membrane estrogen receptors, and other mechanisms that are not blocked by pure antiestrogens.
2009-01-03 | GSE14235 | GEO
Project description:FHMs were exposed to three concentrations of phenanthrene (average measured 29, 287, 1006 ng/L) and fish were sampled after 48hr.
2013-08-27 | GSE44839 | GEO
Project description:Polar cod (Boreogadus saida), a key arctic fish species spawning during the polar night, may be at risk for crude oil exposure during this potential sensitive life stage. This study investigates the effects of crude oil exposure on Polar cod during spawning season. Wild-caught polar cod were exposed to crude oil water accommodated fraction (WAF) (start concentrations of sum of 44 polycyclic aromatic hydrocarbon (sum 44 PAHs) at 12.5 μg/L) from pre-spawning to post-spawning. The exposure system consisted of an oiled-rock-column system where running though sweater delivers WAF in the fish tank at decreasing concentrations over time. Samples were taken at three time-points (pre-spawning, spawning window, and post-spawning) and used to evaluate changes in reproductive endpoints such as gonad histology, plasma steroid hormones and sperm motility. For RNA-extraction and sequencing, liver samples from both oil-exposed and control groups of female fish (n = 5 per group) were taken at 47 days after experiment start and submitted for sequencing. RNA-seq analysis showed that hundreds of genes were differentially expressed in the liver.
2024-09-08 | E-MTAB-12354 | biostudies-arrayexpress