Effects of maternal Cd on the female reproductive functions, gametes development and genes expression of zebrafish
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ABSTRACT:
ORGANISM(S): Danio rerio
SUBMITTER: Ming Yi Chou
PROVIDER: E-GEOD-20926 | biostudies-arrayexpress |
REPOSITORIES: biostudies-arrayexpress
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Project description:The impacts of maternal Cd on zebrafish from female to embryo which included fecundity, gametes development, growth, other reproductive functions, and gene expression of 5hpf embryo were up and down regulated after female pretreated with Cd. The mating rate decreased by 30 %. It can be observed in growth delay during 6-somite stage. The ceratohyal head angle of larvae is widest upon 35.6 μM maternal Cd treatment and it was showed a dose response. Besides, pericardial edema occurred in some 96hpf larvae. There were showed 33 and 37 target genes appeared significantly down and up regulation after microarray assay, respectively. The major effect on gene up regulation was showed at the functional of transcription (occupied 18.9%) and down regulation at the functional of protein biosynthesis (occupied 33.3%). These results demonstrated that maternal Cd influenced the reproduction ability of female and causes development abnormal of embryo.
2013-07-01 | GSE20926 | GEO
Project description:The goal of this experiment was to identify using tissue specific transgenic zebrafish (Fli:EGFP), genes of interest important for embryonic vascular development. Keywords: time course, GFP cell isolation, zebrafish The experiment contained 6 samples. A18, A24 = total RNA isolated from 18 and 24 hpf zebrafish embryo; B2, C and D2=RNA isolated from GFP positive cells sorted at 18, 24 and 28 hpf respectively from Tg(Fli1:EGFP) embryos; E2 = RNA isolated from GFP positive cells sorted at 18 hpf from Tg(Flk:GRCFP) embryos.
2010-05-22 | E-GEOD-12516 | biostudies-arrayexpress
Project description:Purpose: This study aimed to identify differentially expressed genes and transcripts in zebrafish embryos and larvae following benzo[a]pyrene (BaP) exposure. Methods: Adult zebrafish (2 males × 4 females, N=6 replicate tanks for each treatment) were acclimated for 7 days in an 818 Low Temp Illuminated Incubator (Precision Scientific, Chennai, India) at 28.5°C. Next, adult fish were waterborne exposed to control or 50 μg/L (ppb) BaP for 7 days; ethanol was used as vehicle solvent, and final ethanol concentration was 0.1 mL/L (100 ppm) in all treatment groups. This dose of ethanol is not teratogenic to zebrafish. Water was changed and/or re-dosed daily. From day 7 to 11 of the parental exposure, eggs were collected, counted, and raised in normal conditions (control) or continuously exposed to 50 μg/L BaP until 3.3 and 96 hours post fertilization (hpf). At 3.3 or 96 hpf, embryos (200/pool) or larvae (10/pool) were collected and pooled. Total RNA was isolated for transcriptomic RNA sequencing with Illumina HiSeq2000 (2X100bp). RNA-seq reads were uploaded to the galaxy platform https://main.g2.bx.psu.edu/. RNA-seq reads were trimmed, filtered, and aligned to the zebrafish genome (Danio_rerio.Zv9.68) with the Tophat for Illumina tool. Counting and annotation of RNA-seq reads were performed with Partek Genomics Suite version 6.11. Refseq Transcripts (2013-04-10) and Ensembl Transcripts release 70 databases were used for gene and transcript annotation. Differential expression of gene and transcript reads between treatments was analyzed with R package EdgeR. Genes/transcripts with false discovery rate (FDR) less than 0.05 and absolute fold change greater than 1.5 were considered as significant. Differentially expressed genes were defined as genes with altered expression at either gene or transcript level. Results: Differential expression analysis with EdgeR revealed that gene expression was vastly different between 3.3 hpf zebrafish embryos and 96 hpf larvae. Using Refseq annotation, we found that 10644 out of 13950 transcribed zebrafish genes were differentially expressed between the two developmental time-points, with 5961 up-regulated genes and 4683 down-regulated genes in 96 hpf larvae compared with 3.3 hpf embryos. Similarly, using Ensembl annotation, 16529 out of 19886 transcribed zebrafish genes were differentially expressed, with 9318 up-regulated genes and 7211 down-regulated genes in 96 hpf larvae compared with 3.3 hpf embryos. In 3.3 hpf embryos, four genes and seven transcripts were differentially expressed after BaP exposure. In 96 hpf larvae, 447 and 484 zebrafish genes were significantly up- and down-regulated, respectively, by BaP exposure. Conclusions: Parental and developmental BaP exposure caused gene expression changes in zebrafish embryos and larvae.
2015-09-04 | GSE64198 | GEO
Project description:The glucocorticoid receptor (GR) regulates gene expression upon activation by glucocorticoid (GC) hormones. In zebrafish, two GR splice variants exist: the canonical GR M-NM-1-isoform (GRM-NM-1), and the GR M-NM-2-isoform (GRM-NM-2). The exact function of GRb remains elusive. We have investigated the transcriptional role of GRa and GRb in the zebrafish embryo model by injecting mebryos with two splice-blocking morpholinos (one leading to knockdown of both GR M-NM-1- and M-NM-2-isoforms, and another targeting the alternative splicing of the GR pre-mRNA in favor of the GR M-NM-2-isoform) and with GRM-NM-2 mRNA (resulting in specific GRM-NM-2 overexpression). Transcriptome profiling was performed on total RNA isolated from 30 hpf embryos. Our results show that GRb does not act as a dominant-negative inhibitor of GRa, and that GRa regulates two distinct gene clusters, which are mainly involved in the metabolism of the embryo. This microarray study was designed to determine the effect of knockdown and overexpression of GRa and GRb. For this purpose, wild type (AB/TL) zebrafish embryos were injected at the 1-2 cell stage with a standard control morpholino (SC-MO), a splice-blocking morpholino leading to knockdown of both GR M-NM-1- and M-NM-2-isoforms (MO1), a splice-blocking morpholino targeting the alternative splicing of the GR pre-mRNA in favor of the GR M-NM-2-isoform (MO2), or GRb mRNA. At 24 hpf, each group was treated with dexamathasone (or vehicle) for 6 hr. This resulted in 8 treament groups: SC-MO/veh, SC-MO/dex, MO1/veh, MO1/dex, MO2/veh, MO2/dex, GRb mRNA/veh, GRb mRNA/dex. After the incubation period, embryos were collected and RNA was isolated from 20 embryos per treatment group (30 hpf). Three individual experiments were performed, and the resulting triplicate samples were analyzed by microarray, using a common reference approach.
2014-11-18 | E-GEOD-63360 | biostudies-arrayexpress
Project description:Purpose: This study aimed to identify differentially expressed genes and transcripts in zebrafish embryos and larvae following benzo[a]pyrene (BaP) exposure. Methods: Adult zebrafish (2 males × 4 females, N=6 replicate tanks for each treatment) were acclimated for 7 days in an 818 Low Temp Illuminated Incubator (Precision Scientific, Chennai, India) at 28.5°C. Next, adult fish were waterborne exposed to control or 50 μg/L (ppb) BaP for 7 days; ethanol was used as vehicle solvent, and final ethanol concentration was 0.1 mL/L (100 ppm) in all treatment groups. This dose of ethanol is not teratogenic to zebrafish. Water was changed and/or re-dosed daily. From day 7 to 11 of the parental exposure, eggs were collected, counted, and raised in normal conditions (control) or continuously exposed to 50 μg/L BaP until 3.3 and 96 hours post fertilization (hpf). At 3.3 or 96 hpf, embryos (200/pool) or larvae (10/pool) were collected and pooled. Total RNA was isolated for transcriptomic RNA sequencing with Illumina HiSeq2000 (2X100bp). RNA-seq reads were uploaded to the galaxy platform https://main.g2.bx.psu.edu/. RNA-seq reads were trimmed, filtered, and aligned to the zebrafish genome (Danio_rerio.Zv9.68) with the Tophat for Illumina tool. Counting and annotation of RNA-seq reads were performed with Partek Genomics Suite version 6.11. Refseq Transcripts (2013-04-10) and Ensembl Transcripts release 70 databases were used for gene and transcript annotation. Differential expression of gene and transcript reads between treatments was analyzed with R package EdgeR. Genes/transcripts with false discovery rate (FDR) less than 0.05 and absolute fold change greater than 1.5 were considered as significant. Differentially expressed genes were defined as genes with altered expression at either gene or transcript level. Results: Differential expression analysis with EdgeR revealed that gene expression was vastly different between 3.3 hpf zebrafish embryos and 96 hpf larvae. Using Refseq annotation, we found that 10644 out of 13950 transcribed zebrafish genes were differentially expressed between the two developmental time-points, with 5961 up-regulated genes and 4683 down-regulated genes in 96 hpf larvae compared with 3.3 hpf embryos. Similarly, using Ensembl annotation, 16529 out of 19886 transcribed zebrafish genes were differentially expressed, with 9318 up-regulated genes and 7211 down-regulated genes in 96 hpf larvae compared with 3.3 hpf embryos. In 3.3 hpf embryos, four genes and seven transcripts were differentially expressed after BaP exposure. In 96 hpf larvae, 447 and 484 zebrafish genes were significantly up- and down-regulated, respectively, by BaP exposure. Conclusions: Parental and developmental BaP exposure caused gene expression changes in zebrafish embryos and larvae. Illumina HiSeq2000 deep sequencing was used to generate transcriptomic profiles for BaP-exposed 3.3 hpf zebrafish embryos (n=3 for control, n=3 for BaP) and 96 hpf larvae (n=2 for control, n=2 for BaP).
2015-09-04 | E-GEOD-64198 | biostudies-arrayexpress
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2011-09-30 | E-GEOD-30497 | biostudies-arrayexpress
Project description:The goal of this study is to compare gene expression levels in the livers of larval Tg(fabp10:nls-mcherry) exposed to 1 mM inorganic arsenic from 4-120 hpf to the unexposed siblings. Samples were collected from Tg(fabp10:nls-mcherry) zebrafish larvae that were derived from incrossed parents of the same strain. The background of transgenic lines were typically from mixed outcrosses of the transgenics to AB, TAB5, and TAB14 strains when regenerating the lines as the working stocks aged. All samples were collected at approximately 120 hpf - natural spawning at 8:30-9:00AM EST on day zero, samples were collected at 8-10AM EST on day 5.
2017-11-12 | GSE104953 | GEO