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CHARACTERIZING TOXICITY PATHWAYS OF FLUOXETINE TO PREDICT ADVERSE OUTCOMES IN ADULT PIMEPHALES PROMELAS

ABSTRACT: Fluoxetine (FLX) is the most common selective serotonin reuptake inhibitor pharmaceutical used for the treatment of psychological disorders such as depression and anxiety. Increased prescription use of FLX by human populations has led to its pseudo-persistence in effluent-receiving waterways. Despite emerging concerns of FLX becoming a potential threat to the aquatic environment, there is currently limited information on effects of FLX on aquatic wildlife, including its specific mechanism of action and associated toxicity pathways in fish. The main goal of this study was to identify and validate key molecular toxicity pathways that are predictive of apical endpoints induced by exposure to FLX using the fathead minnow (Pimephales promelas), a model species common to North American freshwater systems. Adult fathead minnows were exposed to three concentrations of FLX (2.42, 10.7, and 56.7 µg/L) and a control for 21 days. After 96 hours, a subset of fish was sampled, and liver and brain tissue were collected to characterize molecular toxicity pathways using whole transcriptome and proteome analyses. In addition, at the end of the 21-day exposure, individuals were assessed for apical outcomes of regulatory relevance including histopathology and fecundity. Differential gene expression observed in the liver of fish exposed to the highest FLX treatment and revealed dysregulation of pathways associated with biosynthesis and metabolism of fatty acids, which may be an upstream molecular response that led to lipid-type vacuolation of hepatocytes, as observed in the histology analysis. Whole proteome analysis of the same fish revealed dysregulation of PPAR signalling, which may be associated with the enrichment of lipid-related pathways observed in the transcriptome. In addition, there was an indication of pathway enrichment of transcription- and translation-related pathways in the proteome. Common dysregulated genes in the brain of the treated fish were related to cellular signalling processes that are influenced by serotonin levels and shown to be involved in reproductive behaviour and, in turn, reproductive success. This was confirmed through a significant decrease in fecundity following the 21-day exposure. Pathways to measurable adverse outcomes are complex, however, this research does provide some important clues to the mechanistic toxicity that FLX inflicts.

ORGANISM(S): Pimephales promelas

PROVIDER: GSE182913 | GEO | 2022/02/27

REPOSITORIES: GEO

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Project description:Propranolol is a beta-adrenergic receptor antagonist (Î²-blocker) that has been detected in United States wastewater effluents at concentrations ranging from 0.026 to 1.90 Âµg/l. In mammals, there is evidence that Î²-blockers can cause sexual dysfunction, and alter serotonergic pathways which may impact reproductive behavior but little is known about the effects on fish behavior. The present study tested the effects of propranolol on fecundity and on reproductive behavior of the fathead minnow, Pimephales promelas, a fish that exhibits male parental care. Sexually mature fathead minnows were housed at a ratio of one male and two females per tank and exposed to nominal concentrations of 0, 0.1, 1, 10 Âµg/l for 21 days. Measured concentrations (Â±SD) of propranolol were 0.05Â±0.02, 0.88Â±0.34 and 4.11Â±1.19 Âµg/l. There were no statistically significant differences in fecundity, fertilization rate, hatchability and time to hatch. Propranolol exposure was not associated with a change in nest rubbing behavior, time spent in the nest or approaching the females. There was a significant difference in the number of visits to the nest with males receiving low and medium propranolol treatments. The microarray analysis showed that there were 335 genes up-regulated and 400 genes down-regulated in the brain after exposure to the highest dose of propranolol. Among those genes, myoglobin and calsequestrin transcripts (fold change=10.84 and 5.49, respectively) were highly up-regulated. Ontological analyses indicated changes in genes involved in calcium ion transport, transcription, proteolysis and apoptosis/anti-apoptosis. The results showed that exposure to propranolol at concentrations as high as 4.11 Âµg/l did not significantly impact reproductive behavior or spawning abilities of fathead minnow but did alter the regulation of genes within the brain of fish. Effects of propanolol exposure were investigated in the brain of adult male fathead minnow exposed to 10 Âµg/L of propanolol or a solvent control solution (0.01% ethanol). For each treatment, the brain of four different fish were analyzed.

Project description:Production, usage and disposal of the munitions constituent (MC) cyclotrimethylenetrinitramine (RDX) has led to environmental releases on military facilities. The chemical attributes of RDX are conducive for leaching to surface water which may put aquatic organisms at risk of exposure. Because RDX has been observed to cause aberrant neuromuscular effects across a wide range of animal phyla, we assessed the effects of RDX on central nervous system (CNS) function in the representative aquatic ecotoxicological model species, fathead minnow (Pimephales promelas). A brain-tissue based cDNA library enriched for transcripts differentially expressed in response to RDX exposure was developed for fathead minnow and was transitioned to custom cDNA-based microarrays. All 4,128 cDNAs were sequenced, quality filtered and assembled yielding 3,018 unique sequences and 945 significant blastx matches (E ≤ 10-5). Bioassays were conducted exposing fathead minnows to RDX at 0.625, 1.25, 2.5, 5, 10 mg/L or an acetone-spike control for 10d. Overt toxicity of RDX in fathead minnow occurred only at the highest exposure concentration resulting in 50% mortality. Conversely, Bayesian analysis of microarray data indicated significant changes in transcript expression in fathead minnow brain tissue at RDX concentrations as low as 0.625 mg/L. In total, 154 microarray targets representing 44 unique transcript identities were differentially expressed in RDX exposures, the majority of which were validated by RT-qPCR. Investigation of molecular pathways, gene ontology and individual gene functions indicated that RDX exposures affected metabolic processes involved in: oxygen transport, neurological function, calcium binding / signaling, energy metabolism, cell cycle / cell proliferation, oxidative stress and ubiquitination. In total, our study indicated that RDX exposure affected molecular processes critical to CNS function in fathead minnow. 10 Day RDX Exposure, Brain Tissue Investigation: Sub-adult fathead minnows were exposed to RDX in a 10d dose-series experiment (0.625, 1.25, 2.5, 5.0, or 10 mg/L RDX) which included an acetone-spike control (1% acetone). Each experimental treatment included 8 replicate fish (48 total fish) and endpoints included mortality, total weight and neurotoxicogenomics. The 1.25mg/L dose was not included in the microarray experiment. Please see attached PDF file for detailed 'Balanced, Interwoven Loop Design'.

Project description:Metformin, along with its biotransformation product guanylurea, are commonly observed in municipal wastewaters and subsequent surface waters. Previous studies in fish have identified metformin as a potential endocrine active compound but there are inconsistencies in the literature with regard to effects. To further investigate the potential reproductive toxicity of metformin and guanylurea to fish, a series of experiments were performed with reproductively mature fathead minnows (Pimephales promelas). First, explants of mature fathead minnow ovary tissue were exposed to 0.001-100 µM metformin or guanylurea to investigate whether they can directly perturb steroidogenesis. Second, spawning pairs of fathead minnows were exposed to metformin (0.41, 4.1, 41 µg/L) or guanylurea (1.0, 10, 100 µg/L) for 23 d to assess impacts on reproduction. Lastly, male fathead minnows were exposed to 41 µg/L metformin, 100 µg/L guanylurea, or a mixture of both compounds, with samples collected over a 96 h time course to investigate potential impacts to the hepatic transcriptome or metabolome. Neither metformin or guanylurea effected estradiol or testosterone by ovary tissue exposed in vitro. In the 23 d exposure, neither compound significantly impacted transcription of endocrine-related genes in male liver or gonad, circulating steroid concentrations in male or female fish, or fecundity of spawning pairs. In the 96 h time course, 100 µg guanylurea/L elicited more differential gene expression than 41 µg metformin/L , and showed the greatest impacts after 96 h. A number of DEGs up-regulated after 24 h were subsequently down-regulated after 96 h, demonstrating time-dependent impacts of guanylurea on the liver. Overall, metformin and guanylurea did not elicit effects consistent with reproductive toxicity in adult fathead minnows at environmentally relevant concentrations. Where effects were identified using ‘omics approaches, guanylurea induced greater impacts than metformin.

Project description:Cyclooxygenase (COX) inhibition is of concern in fish because COX inhibitors (e.g., ibuprofen) are ubiquitous in aquatic systems/fish tissues, and can disrupt synthesis of prostaglandins that modulate a variety of essential biological functions including reproduction. Transcriptomic data and publicly available high throughput toxicity data were utilized to develop putative adverse outcome pathways (AOPs) for molecular initiating event (MIE) of COX inhibition. Effects of a waterborne exposure to indomethacin (IN; 100 Âµg/L), ibuprofen (IB; 200 Âµg/L) and celecoxib (CX; 20 Âµg/L) on liver metabolome and ovarian gene expression (using oligonucleotide microarrays) in sexually mature fathead minnows were examined. Metabolomic profiles of IN, IB and CX were not significantly different from control or one another. Exposure to IB and CX resulted in differential expression of comparable numbers of genes (IB = 433, CX= 545). In contrast, 2558 genes were differentially expressed in IN-treated fish. Functional analyses (canonical pathway and gene set enrichment) indicated extensive effects of IN on prostaglandin synthesis pathway, oocyte meiosis and several other processes consistent with physiological roles of prostaglandins. Transcriptomic data was congruent with apical endpoint data - IN reduced plasma prostaglandin F2 alpha concentrations, and ovarian COX activity, whereas IB and CX did not. Putative AOPs pathways for COX inhibition (MIE) leading to reproductive failure (adverse outcome) via reduction of: 1) ovulation, 2) reproductive behaviors mediated by exogenous and endogenous prostaglandins, and 3) oocyte maturation were developed. Adult fathead minnow were exposed to either 100 Âµg/L indomethacin, 200 Âµg/L ibuprofen, 20 Âµg/L celecoxib or UV-treated Lake Superior (control) water for 96 hours. After exposure, microarray analyses were conducted using the female gonads (n=7-8 per treatment) and metabolomic analyses were conducted using the livers of all the exposed fish.

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CHARACTERIZING TOXICITY PATHWAYS OF FLUOXETINE TO PREDICT ADVERSE OUTCOMES IN ADULT PIMEPHALES PROMELAS

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