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Cell line stimulated with recombinant cytokines interleukin-1b and interferon gamma.

ABSTRACT: Interleukin 1b and interferon g are two cytokines that are central to the inflammatory response. They both have a broad range of activity, each directing the immune response to be towards either the innate response (IL-1b and IFN-g) or the cellular response (IFN-g), however invivo there is a lot of subtle interactions. Microarray analysis has been used to characterize the transcriptional response to recombinant rainbow trout IL-1b and IFN-g in a rainbow trout macrophage cell line RTS-11. The use of the cell line removes the host response and the interference of other cellular factors that occur when performing whole fish experiments, or even primary cultures. RNA was extracted from stimulated or control cells following 6h incubation, this was used to hybridize to a 16K v1 salmonid cDNA array constructed by GRASP consortium. Keywords: Dual label cDNA microarray

ORGANISM(S): Salmo salar Oncorhynchus mykiss

PROVIDER: GSE5091 | GEO | 2007/06/16

SECONDARY ACCESSION(S): PRJNA95339

REPOSITORIES: GEO

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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:We investigated the effects of chronic TCDD exposure on global gene expression in developing rainbow trout (Oncorhynchus mykiss). Juvenile rainbow trout (0.18M-BM-10.01g) were fed Biodiet starter with TCDD added at 0, 0.1, 1, 10 and 100ppb, and ten fish were sampled and pooled from each group for microarray experiments at 28 days after initiation of the exposure. Gene expression analysis was performed using the Genomics Research on All Salmonids Project (cGRASP) 16K cDNA microarrays. TCDD-responsive whole body transcripts identified in the microarray experiments have putative functions involved in various biological processes including cellular process, metabolic process, biological regulation, and response to stimulus. In addition, TCDD caused leisons in multiple organ systems in juvenile rainbow, including skin, oropharynx, liver, gas bladder, intestine, pancreas, nose and kidney. Juvenile rainbow trout (0.18M-BM-10.01g) were fed Biodiet starter (Bio-Oregon) (4% body weight per day) with TCDD added at 0, 0.1, 1, 10 and 100 ppb. Fish were sampled after 28 days. Total RNA from individual fish was isolated using TRIzol reagent (Invitrogen). Total RNA of ten control trout were pooled as a common reference which were labeled with Cy3. Total RNA of ten fish of each treatment were labeled wih Cy5. cDNA were synthesized using SuperScript II Reverse Transcriptase (Invitrogen) (1 M-NM-<g pooled RNA per synthesis). Targets were labeled using the Array 900 Expression Array Detection kit (Genisphere) following the manufacture protocol. 1M-BM-5g RNA of pooled ten control fish were labled with Cy3 and 1M-BM-5g RNA of pooled ten TCDD-treated fish were labled with Cy5, then day-swap was performed. Two arrays were run for each comparison. Microarrays were scanned at 10 M-BM-5m resolution using a ScanArray Express (PerkinElmer Life Sciences, Inc, Boston, MA). The photomultiplier tube settings (PMT) for Cy3 and Cy5 were 70 and 65-66, respectively. TIFF images of arrays were generated with ScanArray Express software (PerkinElmer). Fluorescence intensity data for Cy3 and Cy5 channels were extracted from TIFF images using ImaGene 7.5 software (BioDiscovery Inc., El Segundo, CA). Background correction, data transformation (setting background corrected values < 0.01 to 0.01), Lowess normalization, and analysis (e.g. fold-change calculations) were performed using GeneSpring GX 7.3 (Agilent Technologies, Palo Alto, CA)

Project description:This study compared changes in gene expression in an oviparous female fish, the rainbow trout (Oncorhynchus mykiss), under two different photoperiod treatments, a natural photoperiod (NP) and a shortened photoperiod (SP; 60% of NP). Gene expression in the liver, ovary and pituitary were measured at one-four week intervals over the course of the reproductive cycle in each treatment. Total RNA was harvested from these tissues, cDNA prepared, and hybridized on the 16K GRASP cDNA microarray. Established indices of reproductive development (ovulation, gonadosomatic index, mean oocyte diameter, and plasma hormone levels) were also measured. The SP fish failed to ovulate and their reproductive trajectory was clearly different from the NP group, which ovulated as expected. A comparative examination of the reproductive indices in both groups shows that ovarian development initiated in the SP group and proceeded relatively normally for about two-thirds of the reproductive cycle. Plasma follicle-stimulating hormone levels were higher in the SP fish from the cycle onset. This may have dampened E2 synthesis, preventing the positive feedback signal on the pituitary for the normal, rapid increase in luteinizing hormone late in the cycle. Transcriptome analysis used an unsupervised k-means hierarchical clustering method to visualize changes in gene expression in the different organs from the NP fish that were assumed to represent the normal pattern leading to successful ovary development. In the NP, fish four, five, and six unique gene clusters were identified in the liver, ovary, and pituitary, respectively. These clusters ranged in size from 22 genes in one of the pituitary clusters to 302 genes in the liver. These clusters were then applied to the SP fish to determine if and how they were altered. The expression patterns of most genes in the SP fish were notably altered from the first time point. A SP in female rainbow trout initiated a rapid change in tr anscript levels within the liver, ovary, and pituitary, leading to ovarian failure and apparently disrupting normal endocrine signaling between the pituitary and ovary.

Project description:The Infectious Hematopoietic Necrosic Virus (IHNV) DNA vaccine is based on the viral glycoprotein gene (G gene) and induces a non-specific anti-viral immune response and long-term specific immunity against IHNV in salmonid fishes. This study characterized gene expression responses associated with the early anti-viral response. Homozygous rainbow trout were injected intra-muscularly (I.M.) with vector DNA or the IHNV DNA vaccine. Gene expression at the I.M. site was evaluated using a 16,000 feature salmon cDNA microarray. Eighty different transcripts were significantly modulated in the vector DNA group while 910 transcripts were modulated in the IHNV DNA vaccinated group relative to control group. Quantitative reverse transcriptase PCR was used to examine expression of selected genes at the I.M. site and in other secondary tissues. In the localized response (I.M. site), the magnitudes of gene expression changes were higher in the vaccinate group relative to the vector DNA group for the majority of genes analyzed. At secondary systemic sites (e.g. gill, kidney and spleen) evaluated with RT-PCR of specific genes, the main difference was the up-regulation of the type I IFN-related genes in only the IHNV DNA vaccinated group. Keywords: disease vaccine response Gene expression at the site of I.M injection was evaluated 7 days post-injection in clonal rainbow trout. Gene expression was compared across three treatments, with replicate clonal rainbow trout individuals (Hot Creek strain) within each treatment. Treatments included injection with 1X PBS (control group), plasmid vector only (without IHNV G gene; hereafter referred to as vector group), and the pIHNV vaccine (vaccine group). Three clonal individuals from the control, three individuals from the vector group, and four individuals from the vaccine group were labeled with Cy3 and used for individual hybridizations to ten slides, comparing hybridization of each individual to a major reference RNA pool. The major reference pool consisted of three unhandled clonal rainbow trout and constituted a pool of RNA from the anterior kidney, spleen, liver and muscle and was labelled with Cy5. Total RNA was extracted from samples, amplified, and hybridized to 16,000 feature Atlantic salmon cDNA arrays developed by the Genomic Research for Atlantic Salmon project. Differential expression was compared among control, vector, and vaccine groups.

Project description:We investigated the effects of chronic TCDD exposure on global gene expression in developing rainbow trout (Oncorhynchus mykiss). Juvenile rainbow trout(0.18M-BM-10.01g) were fed Biodiet starter with TCDD added at 0, 0.1, 1, 10 and 100ppb, and ten fish were sampled and pooled from 10 ppb group at 7, 14, 28 and 42 days for microarray experiments after initiation of the exposure. Gene expression analysis was performed using the Genomics Research on All Salmonids Project (cGRASP) 16K cDNA microarrays. TCDD-responsive whole body transcripts identified in the microarray experiments have putative functions involved in various biological processes including response to stimulus, cell wall organization or biogenesis, growth and cell proliferation. In addition, TCDD caused leisons in multiple organ systems in juvenile rainbow, including skin, oropharynx, liver, gas bladder, intestine, pancreas, nose and kidney. Juvenile rainbow trout (0.18M-BM-10.01g) were fed Biodiet starter (Bio-Oregon) (4% body weight per day) with TCDD added at 0, 0.1, 1, 10 and 100 ppb. Fish were sampled and from 10 ppb group at 7, 14, 28 and 42 days for microarray experiments after initiation of the exposure. Total RNA from individual fish was isolated using TRIzol reagent (Invitrogen).Total RNA of ten control trout were pooled as a common reference which were labeled with Cy3. Total RNA of ten fish of each treatment were labeled wih Cy5. cDNA were synthesized using SuperScript II Reverse Transcriptase (Invitrogen) (1 M-NM-<g pooled RNA per synthesis). Targets were labeled using the Array 900 Expression Array Detection kit (Genisphere) following the manufacture protocol. 1M-BM-5g RNA of pooled ten control fish were labled with Cy3 and 1M-BM-5g RNA of pooled ten TCDD-treated fish were labled with Cy5, then day-swap was performed. Two arrays were run for each comparison. Microarrays were scanned at 10 M-BM-5m resolution using a ScanArray Express (PerkinElmer Life Sciences, Inc, Boston, MA). The photomultiplier tube settings (PMT) for Cy3 and Cy5 were 70 and 65-66, respectively. TIFF images of arrays were generated with ScanArray Express software (PerkinElmer). Fluorescence intensity data for Cy3 and Cy5 channels were extracted from TIFF images using ImaGene 7.5 software (BioDiscovery Inc., El Segundo, CA). Background correction, data transformation (setting background corrected values < 0.01 to 0.01), Lowess normalization, and analysis (e.g. fold-change calculations) were performed using GeneSpring GX 7.3 (Agilent Technologies, Palo Alto, CA)

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Cell line stimulated with recombinant cytokines interleukin-1b and interferon gamma.

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