Toxic effects of dietary methylmercury (MeHg) on young adult zebrafish
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ABSTRACT: Three-month old zebrafish were fed Biodiet starter (4% body weight per day) with MeHg added at 0, 0.5, 5 and 50 ppm for six weeks. Atomic absorption spectrometry was applied to measure the level of MeHg in the whole fish body. Zebrafish at six weeks were sampled from each group for gene expression analysis by NimbleGen Gene Expression 12X135K zebrafish microarrays. MeHg-exposed trout and zebrafish did not show overt signs of toxicity, nor were significant differences seen in mortality, length, mass, or condition factor. The chronic accumulation of total Hg in zebrafish exhibited dose- and time-dependent patterns. The dysregulated genes in MeHg-treated fish have multiple functional annotations, such as involving metabolism, cellular development, ion binding, stress response, transcriptional regulation, and apoptotic pathways. These results show that numerous molecular pathways involved in the growth and development of multiple organ systems are disrupted by exposure to moderate levels of dietary MeHg. The dysregulated genes will be selected by further analysis and used as biomarkers for MeHg exposure in aquatic environments. This study will allow us to assess the potential impacts of low-level exposure to environmental MeHg in the food chain and on the health of humans and animals. Three-month old zebrafish (Danio rerio, average body 0.149 g) were fed Biodiet Starter (Bio-Oregon) 4% of body weight per day with MeHg added at 0ppm, 0.5ppm, 5ppm and 50ppm (with ethanol as vehicle). Fish at six weeks were sampled from each group for gene expression analysis. Three fish from each treatment group were used for microarray experiments. Total RNA from individual fish was isolated using Trizol reagent (Invitrogen) and further purified using the RNeasy MiniElute cleanup kit (Qiagen). Double-strand cDNA was synthesized from 10ug total RNA of individual fish by using Superscript Double-Stranded cDNA synthesis Kit (Invitrogen). ). One ug double strand DNA was labeled with Cy3 using One-Color DNA labeling Kit (NimbleGen), then hybridized to NimbleGen 12X135K array. The arrays were scanned at 2um on a NimbleGen MS200 scanner with auto-gain adjust. The TIFF images were gridded and extracted using NimbleScan v. 2.6. Expression data were normalized using the Robust Multichip Average (RMA) algorithm.
Project description:Three-month old zebrafish were fed Biodiet starter (4% body weight per day) with MeHg added at 0, 0.5, 5 and 50 ppm for six weeks. Atomic absorption spectrometry was applied to measure the level of MeHg in the whole fish body. Zebrafish at six weeks were sampled from each group for gene expression analysis by NimbleGen Gene Expression 12X135K zebrafish microarrays. MeHg-exposed trout and zebrafish did not show overt signs of toxicity, nor were significant differences seen in mortality, length, mass, or condition factor. The chronic accumulation of total Hg in zebrafish exhibited dose- and time-dependent patterns. The dysregulated genes in MeHg-treated fish have multiple functional annotations, such as involving metabolism, cellular development, ion binding, stress response, transcriptional regulation, and apoptotic pathways. These results show that numerous molecular pathways involved in the growth and development of multiple organ systems are disrupted by exposure to moderate levels of dietary MeHg. The dysregulated genes will be selected by further analysis and used as biomarkers for MeHg exposure in aquatic environments. This study will allow us to assess the potential impacts of low-level exposure to environmental MeHg in the food chain and on the health of humans and animals.
Project description:Juvenile rainbow trout were fed Biodiet starter (4% body weight per day) with MeHg added at 0, 0.5, 5 and 50 ppm for six weeks. Atomic absorption spectrometry was applied to measure the level of MeHg in the whole fish body. Trout at six weeks were sampled from each group for gene expression analysis by cGRASP 16K cDNA microarrays. MeHg-exposed rainbow trout did not show overt signs of toxicity, nor were significant differences seen in mortality, length, mass, or condition factor. The chronic accumulation of total Hg in trout exhibited dose- and time-dependent patterns. The dysregulated genes have multiple functional annotations, such as involving metabolism, cellular development, ion binding and homeostasis, stress response, immune response, transcriptional regulation, hemolytic development, and apoptotic pathways. These results show that numerous molecular pathways involved in the growth and development of multiple organ systems are disrupted by exposure to moderate levels of dietary MeHg. The dysregulated genes will be selected by further analysis and used as biomarkers for MeHg exposure in aquatic environments. Juvenile rainbow trout (Oncorhynchus mykiss, average body 0.118g) were fed Biodiet Starter (Bio-Oregon) 4% of body weight per day with MeHg added at 0ppm, 0.5ppm, 5ppm and 50ppm (with ethanol as vehicle). Trout at six weeks were sampled from each group for gene expression analysis. Total RNA from individual fish was isolated using Trizol reagent (Invitrogen) and further purified using the RNeasy MiniElute cleanup kit (Qiagen).RNA of ten fish from control group was pooled as a common reference, and total RNA of five individual fish from control and MeHg-treated groups were randomly selected for microarray experiment. cDNA was synthesized from 1 M-NM-<g pooled RNA using SuperScript II Reverse Transcriptase (Invitrogen) according to the manufacturerM-bM-^@M-^Ys protocol. The common reference cDNA targets were labeled with Cy3 and cDNA of individual fish from each group was labeled with Cy5 using the Array 900 Expression Array Detection kit (Genisphere) according to the manufacturerM-bM-^@M-^Ys protocol. The labeled cDNA targets were hybridized to cGRASP 16K cDNA microarrays at 50M-BM-0C for 16 hours. Following the first hybridization, arrays were washed in 2X SSC, 0.2% SDS solution at 50 C 1 x 15 min, 2X SSC 1 x 15 min at room temperature, then 0.2X SSC for 1 x 15 min at room temperature. The fluorescent labeling hybridization (50 C for 4hr) utilized the Genisphere 3DNA Cy3 and Cy5 capture reagents in formamide hybridization buffer. The slides were washed as described above, and the arrays were dried by centrifugation. were scanned using the ScanArray Express (PerkinElmer) at 10 um resolution. The TIFF images of arrays were generated with ScanArray Express software and the intensities of raw data of two-channel arrays were collected by the ImaGene 6.0 (BioDiscovery). Statistical analysis of microarray data was performed using scripts written in R language with LIMMA package.
Project description:Methylmercury (MeHg) is a potent neurotoxin and endocrine disruptor that accumulates in aquatic systems. Previous studies have shown suppression of hormone levels in both male and female fish, suggesting effects on gonadotropin regulation in the brain. We investigated the gene expression profile in adult female zebrafish whole brain induced by acute (96 hr) MeHg exposure. Fish were exposed by injection to 0 or 0.5 M-BM-5g MeHg/g. Gene expression changes in the brain were examined using a two-color 22,000 feature zebrafish microarray. At a significance level of p<0.01, 79 genes were up-regulated and 76 genes were down-regulated in response to MeHg exposure. Individual genes exhibiting altered expression in response to MeHg exposure implicate effects on glutathione metabolism and GABA-A receptors in the mechanism of MeHg neurotoxicity. Gene ontology (GO) terms significantly enriched among altered genes included protein folding, cell redox homeostasis, and steroid biosynthetic process. The most affected biological functions were related to the nervous system development and function, as well as lipid metabolism and molecular transport. These results support the involvement of oxidative stress and effects on protein structure in the mechanism of action of MeHg in the female brain. Future studies will compare the gene expression profile induced in response to MeHg with that induced by other toxins and investigate responsive genes as potential biomarkers of MeHg exposure. Wild-type strain AB-1 zebrafish (Zebrafish International Resource Center, University of Oregon, Eugene, OR) were cultured at the Columbia Environmental Research Center (CERC), USGS, for MeHg exposures. Adult female zebrafish were injected with 0 M-NM-<g/g or 0.5 M-NM-<g/g MeHg in 2 M-BM-5L Na2CO3 (pH 6.98)/g body weight. After 96 hr, fish were anesthetized using ethyl 3-aminobenzoate methanesulfonate (MS-222, Sigma, St. Louis, MO). Whole brains were removed, flash frozen with liquid nitrogen and stored at 80M-BM-0C. For the microarray experiment, two zebrafish brains were pooled per sample. Four pooled samples were taken from fish treated with 0.5 M-NM-<g/g of MeHg, and the other five were taken from control fish treated with sodium carbonate. Array hybridizations were performed using a reference design, where each sample was compared to a reference sample. The reference sample consisted of equal amounts of RNA from control and treated female brains. Five replicates for the control and four replicates for the treated were analyzed. cDNA synthesis, cRNA labeling, amplification and hybridization were performed following the manufacturerM-bM-^@M-^Ys kits and protocols (Agilent Low RNA Input Fluorescent Linear Amplification Kit and Agilent 60-mer oligo microarray processing protocol; Agilent, Palo Alto, CA).
Project description:Investigation of whole genome gene expression level changes in zebrafish liver under naphthalene treatedï¼?high-concentration group and low-concentration groupï¼?, compared to the solvent control group revealed that 76 genes and 88 genes were differentially expressed respectively in the fish caged at the low-concentration and high-concentration. KEGG pathway and GO analysis of the differentially expressed genes, showed significant enrichment in several meaningful categories. Healthy 5-month-old adult zebrafish (AB strain) maintenance and chemical exposure to 84μg/L and 840μg/L naphthalene and 0.005% Dimethyl sulfoxide as the solvent control were performed according to published research protocols. Prior to exposure, the fish were acclimatized in 50L aerated fresh water in glass tanks for 2 weeks, under controlled environmental conditions with the water temperature maintained at 26±0.5â?? for 16-h light and 8-h dark photoperiod. After 21 d of treatment, adult zebrafish livers were removed by dissection, and immediately transferred to RNA-later Stabilization Reagent(Qiagen,76106) , prior to storage at 4â?? for histopathological and microarray analysis. NimbleGen Gene Expression 12X135K zebrafish microarrays and One-Color DNA labeling Kit (NimbleGen, WI) were used for genome-wide expression analysis of naphthalene-treated zebrafish.
Project description:Juvenile zebrafish were fed Biodiet starter (4% body weight per day) for 42 d with TCDD added at 0 ppb, 0.1 ppb, 1 ppb, 10 ppb or 100 ppb. Fish were collected, sexed, weighed and length measured at 0, 7, 14, 28 or 42 d for TCDD assessment, histopathologic and microarray analysis. Microarray experiments were conducted using 0 and 100 ppb-TCDD treated male and female sexed zebrafish at 7, 14, 28 and 42 d. NimbleGen Gene Expression 12X135K zebrafish microarrays and One-Color DNA labeling Kit (NimbleGen, WI) were used for genome-wide expression analysis of TCDD-treated zebrafish. TCDD accumulated in a dose- and time-dependent manner and 100 ppb TCDD caused TCDD accumulation in female (15.49 ppb) and male (18.04 ppb) fish at 28 d post exposure. TCDD caused multiple lesions in liver, kidney, intestine and ovary of zebrafish and functional dysregulation such as depletion of glycogen in liver, retrobulbar edema, degeneration of neurosensory epithelium, underdevelopment of intestine, and diminution in the fraction of ovarian follicles containing vitellogenic oocytes. At 42d, no mature female fish were observed.
Project description:Adult F0 female zebrafish were fed with control diet or diets containing 5-AZA, MeHg or TCDD. After breeding with unexposed males to produce the F1 generation, livers were sampled from the F0 females. F1 generation embryos were unexposed to test chemicals, were sampled, then bred to produce F2 fish, also unexposed to test chemicals. Methylated DNA immunoprecipitation was carried out on liver samples from F0 and F1 and F2 embryos and MeDIP samples were labeled with Cy5 and hybridised to a zebrafish CGI tiling array versus Cy3-labled zebrafish genomic DNA. The objective was to determine DNA methylation changes following chemical exposure and whether these persisted transgenerationally.
Project description:Juvenile rainbow trout were fed Biodiet starter (4% body weight per day) with MeHg added at 0, 0.5, 5 and 50 ppm for six weeks. Atomic absorption spectrometry was applied to measure the level of MeHg in the whole fish body. Trout at six weeks were sampled from each group for gene expression analysis by cGRASP 16K cDNA microarrays. MeHg-exposed rainbow trout did not show overt signs of toxicity, nor were significant differences seen in mortality, length, mass, or condition factor. The chronic accumulation of total Hg in trout exhibited dose- and time-dependent patterns. The dysregulated genes have multiple functional annotations, such as involving metabolism, cellular development, ion binding and homeostasis, stress response, immune response, transcriptional regulation, hemolytic development, and apoptotic pathways. These results show that numerous molecular pathways involved in the growth and development of multiple organ systems are disrupted by exposure to moderate levels of dietary MeHg. The dysregulated genes will be selected by further analysis and used as biomarkers for MeHg exposure in aquatic environments.
Project description:Juvenile zebrafish were fed Biodiet starter (4% body weight per day) for 42 d with TCDD added at 0 ppb, 0.1 ppb, 1 ppb, 10 ppb or 100 ppb. Fish were collected, sexed, weighed and length measured at 0, 7, 14, 28 or 42 d for TCDD assessment, histopathologic and microarray analysis. Microarray experiments were conducted in TCDD-treated (at 0, 0.1, 1, 10 and 100 ppb) for male and female sexed zebrafish at 28 d. NimbleGen Gene Expression 12X135K zebrafish microarrays and One-Color DNA labeling Kit (NimbleGen, WI) were used for genome-wide expression analysis of TCDD-treated zebrafish. TCDD accumulated in a dose- and time-dependent manner and 100 ppb TCDD caused TCDD accumulation in female (15.49 ppb) and male (18.04 ppb) fish at 28 d post exposure. TCDD caused multiple lesions in liver, kidney, intestine and ovary of zebrafish and functional dysregulation such as depletion of glycogen in liver, retrobulbar edema, degeneration of neurosensory epithelium, underdevelopment of intestine, and diminution in the fraction of ovarian follicles containing vitellogenic oocytes. Microarray gene expression analysis comparing control to post TCDD diet revealed dysregulated genes located in pathways associated with cardiac necrosis/cell death, cardiac fibrosis, renal necrosis/cell death and liver necrosis/cell death. These baseline toxicological effects provide evidence for the potential biomarkers, mechanisms and pathology of TCDD induced dysregulation.
Project description:Methylmercury (MeHg) is an environmental neurotoxicant known to cause adverse effects in fish, such as locomotor abnormalities, visual deficits or teratogenesis. However, very few studies have investigated the effects of environmentally realistic MeHg exposures on the gene expression of fish embryos. Since the primary source of MeHg exposure in wild fish is through the diet, this study analyzed differential gene expression in zebrafish embryos from parents that had been subjected to environmentally relevant dietary MeHg exposures (0, 1, 3, and 10ppm) throughout their whole life cycle.
Project description:In order to investigate the underlying mechanisms of methylmecury (MeHg)-mediated toxicity to Atlantic cod (Gadus morhua), we analyzed the liver proteome of fish exposed in vivo to MeHg (0, 0.5, 2 mg/kg body weight) for 2 weeks. Label-free quantitative mass spectrometry enabled quantification of 1143 proteins, and 125 were differentially regulated between MeHg-treated samples and controls. Six proteins among the top differentially regulated (T23O, GLNA EPS8L2, APOA4, RAP1B, CZTZ) were analyzed using selected reaction monitoring (SRM). Supported by bioinformatics analyses, we conclude that MeHg disrupts mainly redox homeostasis and energy generating metabolic pathways in cod liver, the latter potentially modulated through MeHg-induced oxidative stress.