Project description:Domesticated animal populations often show profound reductions in predator avoidance and fear-related behavior compared to wild populations. These reductions are remarkably consistent and have been observed in a diverse array of taxa including fish, birds, and mammals. Experiments conducted in common environments indicate that these behavioral differences have a genetic basis. In this study, we quantified differences in fear-related behavior between wild and domesticated zebrafish strains and used microarray analysis to identify genes that may be associated with this variation. Compared to wild zebrafish, domesticated zebrafish spent more time near the water surface and were more likely to occupy the front of the aquarium nearest a human observer. Microarray analysis of the brain transcriptome identified high levels of population variation in gene expression, with 1,749 genes significantly differentially expressed among populations. Genes that varied among populations belonged to functional categories that included DNA repair, DNA photolyase activity, response to light stimulus, neuron development and axon guidance, cell death, iron-binding, chromatin reorganization, and homeobox genes. Comparatively fewer genes (112) differed between domesticated and wild strains with notable genes including gpr177 (wntless), selenoprotein P1a, synaptophysin and synaptoporin, and acyl-CoA binding domain containing proteins (acbd3 and acbd4). Microarray analysis identified a large number of genes that differed among zebrafish populations and may underlie behavioral domestication. Comparisons with similar microarray studies of domestication in rainbow trout and canids identified sixteen evolutionarily or functionally related genes that may represent components of shared molecular mechanisms underlying convergent behavioral evolution during vertebrate domestication. However, this conclusion must be tempered by limitations associated with comparisons among microarray studies and the low level of population-level replication inherent to these studies.

Project description:Zebrafish (Danio rerio) were obtained from the Zebrafish Research Facility maintained in the Center for Environmental Biotechnology at the University of Tennessee. Fish husbandry, spawning, and experimental procedures were conducted with approval from the University of Tennessee Institutional Animal Care and Use Committee (Protocol #1690-1007). Water for holding fish and conducting experiments (hereafter referred to as fish water) consisted of MilliQ water (Millipore, Bedford, MA) with ions added: 19 mg/L NaHCO3, 1 mg/L sea salt (Instant Ocean Synthetic Sea Salt, Mentor, OH), 10 mg/L CaSO4, 10 mg/L MgSO4, 2 mg/L KCl. Embryos were obtained by spawning adult fish with no history of contaminant exposure. Fertilization of embryos took place at the same time (Â± 15 min.), such that larvae used in experiments were of similar age at the time of exposure. All activities (maintenance of adult fish, spawning, and experiments) were conducted in an environmental chamber with a temperature of 27Â± 1 ÂºC and 14:10h light:dark photoperiod. Experiment Overall Design: At 72 h post-fertilization, zebrafish larvae were exposed to lyophilized Microcystis and purified MC-LR at concentrations of 100 and 1,000 Âµg/L. Controls consisted of zebrafish system water (negative control) and zebrafish system water containing 0.05% ethanol (vehicle control). Larvae from both control groups as well as 100 Âµg/L MC-LR, 1,000 Âµg/L MC-LR, and lyophilized Microcystis were exposed in groups of 50 with three replicates and were sacrificed after 96 hours for total RNA extraction and subsequent microarray analysis. All larvae were exposed in beakers containing 100 ml of solution. Experiment Overall Design: Water samples for microcystin analysis and water quality measurements were taken during the experiment, and mortality and behavioral observations were recorded at 24-hour intervals. Microcystin analysis was conducted by protein phosphatase inhibition assay. Measured concentrations of microcystin-LR were 140 Â± 12 SD (low concentration) and 1,703 Â± 71 SD (high concentration). The concentration of microcystin-LR in the lyophilized Microcystis treatment was 4.5 Âµg/L. Water quality parameters measured included dissolved oxygen (6.7 mg/L), pH (6.9), total alkalinity (36 mg/L as CaCO3), total hardness (18 mg/L as CaCO3), and ammonia (<0.2 mg/L). No significant mortality or behavioral changes in larvae were observed during the exposure.

Project description:Effects of bisphenol A (BPA) on ovarian transcript profiles as well as targeted endpoints with endocrine/reproductive relevance were examined in two fish species, fathead minnow (Pimephales promelas) and zebrafish (Danio rerio), exposed in parallel using matched experimental designs. Four days of waterborne exposure to 10 µg BPA caused significant vitellogenin induction in both species. However, zebrafish were less sensitive to effects on hepatic gene expression and steroid production than fathead minnow and the magnitude of vitellogenin induction was more modest. The concentration-response at the ovarian transcriptome level was non-monotonic and violated assumptions that underlie proposed methods for estimating hazard thresholds from transcriptomic results. However, the non-monotonic profile was consistent among species and there were nominal similarities in the functions associated with the differentially expressed genes, suggesting potential activation of common pathway perturbation motifs in both species. Overall, the results provide an effective case study for considering the potential application of ecotoxicogenomics to ecological risk assessments and provide novel comparative data regarding effects of BPA in fish. Fish were exposed to 0, 0.01, 0.1, 1.0, 10, or 100 µg BPA/L delivered in a continuous flow (45 ml/min) of sand filtered, UV treated, Lake Superior Water, without the use of carrier solvents. The design employed six replicate tanks per treatment. Three of the replicates were loaded with three male and three female zebrafish per tank, while the remaining three replicates were loaded with three male and three female fathead minnows. Addition of fish to the exposure tanks was staggered by replicate such that all sampling could be completed within 60 min of the desired 96 h exposure duration. After 96 h of exposure, fish were anesthetized in a buffered solution of tricaine methanesulfonate (MS-222; Finquel; Argent, Redmond, WA, USA) and weighed. Blood was collected from the caudal vasculature using microhematocrit tubes, centrifuged to separate the plasma, and plasma was stored at -80oC until analyzed. Liver, gonad, and brain tissues (including pituitary gland) were snap frozen in liquid nitrogen and stored at -80oC until extracted. Total RNA was isolated from ovary tissue of both fathead minnow and zebrafish using RNeasy kits (Qiagen, Valencia, CA, USA). RNA quality was evaluated using an Agilent 2100 Bioanalyzer (Agilent, Wilmington, DE, USA) and RNA was quantified spectrophotometrically (Nanodrop). Total RNA samples were stored at -80oC until used for microarray analyses. Ovarian transcripts from 32 fathead minnows (n=5 per treatment, except for control and 1.0 µg BPA/L, n=6) were analyzed using a custom, 15,000 gene microarray (GEO Platform Accession GPL9248) purchased from Agilent Technologies (Palo Alto, CA, USA). Ovarian transcripts from 34 zebrafish (n=6 per treatment, except 0.01 and 0.1 µg BPA/L, n=5) were analyzed using a commercial 44,000 feature microarray (Agilent design 019161; GEO Platform Accession GPL6457). The same hybridization and scanning procedures were used for both platforms. Briefly, microarrays were hybridized following the manufacturer’s guidelines for One-Color Microarray-Based Gene Expression Analysis (version 5.7; Agilent). Hybridizations were conducted with 1 µg of total RNA. Complementary DNA synthesis, cRNA labeling, amplification, and hybridizations were performed following the manufacturer’s kits and protocols (Quick Amp labeling kit; Agilent). Scanning was conducted at 5 µm resolution using an Axon GenePix® 4000B Microarray Scanner (Molecular Devices Inc., Concord, Ontario, Canada). Data were extracted from microarray array images using Agilent Feature Extraction Software (Agilent; Palo Alto, CA, USA).

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Brain transcriptome variation among behaviorally distinct strains of zebrafish (Danio rerio)

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