Project description:In the present study OMICs analysis was employed to investigate the early molecular responses of zebrafish embryos to exposure to the fungicide difenoconazole. Difenoconazole, a sterol biosynthesis inhibitor according to Fungicide Resistance Action Committee (FRAC) classification, may also induce adverse effects on non-target organisms inhabiting the environment. Early molecular responses in terms of transcriptome and proteome analysis were investigated and refined to select potentially substance specific biomarker candidates for early prediction of difenoconazole toxicity in zebrafish embryos.
Project description:In the present study transcriptome analysis was employed to investigate the early molecular responses to exposure to the fungicide difenoconazole, a sterol biosynthesis inhibitor according to Fungicide Resistance Action Committee (FRAC) classification. Zebrafish embryos were exposed to difenoconazole according to OECD guidelines (OECD test No. 236). At the end of exposure time (96 hours), simultaneous RNA and protein extraction from 10 embryos was performed using a Macherey & Nagel RNA/protein extraction kit. The obtained RNA extracts were sequenced using Illumina HiSeq 4000 System and the obtained sequences went through bioinformatic analysis pipeline to Identify and count the detected gene sequences followed by differential gene expression analysis. Finally, potential substance specific biomarker candidates were refined and selected based on the differential expression patterns and the biological functions investigation of the detected DEGs.
Project description:In the present study transcriptome analysis was employed to investigate the early molecular responses to exposure to the fungicide difenoconazole, a sterol biosynthesis inhibitor according to Fungicide Resistance Action Committee (FRAC) classification. Zebrafish embryos were exposed to difenoconazole according to OECD guidelines (OECD test No. 236). At the end of exposure time (96 hours), simultaneous RNA and protein extraction from 10 embryos was performed using a Macherey & Nagel RNA/protein extraction kit. The obtained RNA extracts were sequenced using Illumina HiSeq 4000 System and the obtained sequences went through bioinformatic analysis pipeline to Identify and count the detected gene sequences followed by differential gene expression analysis. Finally, potential substance specific biomarker candidates were refined and selected based on the differential expression patterns and the biological functions investigation of the detected DEGs.
Project description:In the present study OMICs analysis was employed to investigate the early molecular responses of zebrafish embryos to exposure to the fungicide metalaxyl. Metalaxyl, a nucleic acid metabolism inhibitor according to Fungicide Resistance Action Committee (FRAC) classification, may also induce adverse effects on non-target organisms inhabiting the environment. Early molecular responses in terms of transcriptome and proteome analysis were investigated and refined to select potentially substance specific biomarker candidates for early prediction of metalaxyl toxicity in zebrafish embryos.
2024-01-02 | PXD045444 | Pride
Project description:transcriptomics of difenoconazole and dimethomorph on zebrafish embryos
Project description:The aim of this mRNA expression profiling experiment was to screen for ecotoxicogenomic fingerprints in zebrafish (Danio rerio) embryos as aquatic vertebrate non-target model exposed to sub lethal concentrations of the heavily used organophosphate insecticide Fipronil (CAS 2921-88-2). The Insecticide Resistance Action Committee (IRAC) classified Fipronil after its mode of action (MoA) in the target organism as an acetylcholinesterase (AChE) inhibitor (Group 1B). The goal is to identify toxicogenomic profiles with predictive character and potential molecular key events (KE) explaining upstream adverse effects in aquatic non-target organisms. This will provide useful information to refine and improve existing adverse outcome pathways (AOP). Furthermore, integrating the obtained profiles for this and other tested chemicals in a collective database will enable us in the future to derive predictions about the ecotoxicological hazard for chemcials with unknown apical effects, based on similarly altered transcriptomic and proteomic profiles. In a modified version of the zebrafish embryo toxicity test (OECD 236), 15 fertilized eggs were exposed to two different sub lethal concentrations of Fipronil for 96 hours under semi-static conditions. Each test comprised of a low exposure (LE, 0.075 mg/L), high exposure (HE, 0.3 mg/L) and negative control (NC) group and was performed in triplicates. At 96 hours post fertilization (hpf), 10 larvae were randomly picked for each sample and pooled for RNA and protein extraction with NucleoSpin RNA/Protein kit (Macherey-Nagel). RNA quality was assessed with a 2100 Bioanalyzer system (Agilent) before coding RNA was purified (PolyA selection with TruSeq RNA Library Prep Kit v2) and sequenced on an Illumina HiSeq 4000 System (Illumina) in 50 bp single read mode, producing roughly 30 million reads per sample. Adapter sequences were removed with trimmomatic and sequences were aligned to the D.rerio reference genome GRCz11 with STAR. Counting of feature mapped reads was performed through featureCounts. Library gene count tables were then merged to a single count matrix as input for differential gene expression analysis with DESeq2.
Project description:The aim of this mRNA expression profiling experiment was to screen for ecotoxicogenomic fingerprints in zebrafish (Danio rerio) embryos as aquatic vertebrate non-target model exposed to sub lethal concentrations of the heavily used organophosphate insecticide Chlorpyrifos (CAS 2921-88-2). The Insecticide Resistance Action Committee (IRAC) classified Chlorpyrifos after its mode of action (MoA) in the target organism as an acetylcholinesterase (AChE) inhibitor (Group 1B). The goal is to identify toxicogenomic profiles with predictive character and potential molecular key events (KE) explaining upstream adverse effects in aquatic non-target organisms. This will provide useful information to refine and improve existing adverse outcome pathways (AOP). Furthermore, integrating the obtained profiles for this and other tested chemicals in a collective database will enable us in the future to derive predictions about the ecotoxicological hazard for chemcials with unknown apical effects, based on similarly altered transcriptomic and proteomic profiles. In a modified version of the zebrafish embryo toxicity test (OECD 236), 15 fertilized eggs were exposed to two different sub lethal concentrations of 6PTU for 96 hours under semi-static conditions. Each test comprised of a low exposure (LE, 0.75 mg/L), high exposure (HE, 3 mg/L) and negative control (NC) group and was performed in triplicates. At 96 hours post fertilization (hpf), 10 larvae were randomly picked for each sample and pooled for RNA and protein extraction with NucleoSpin RNA/Protein kit (Macherey-Nagel). RNA quality was assessed with a 2100 Bioanalyzer system (Agilent) before coding RNA was purified (PolyA selection with TruSeq RNA Library Prep Kit v2) and sequenced on an Illumina HiSeq 4000 System (Illumina) in 50 bp single read mode, producing roughly 30 million reads per sample. Adapter sequences were removed with trimmomatic and sequences were aligned to the D.rerio reference genome GRCz11 with STAR. Counting of feature mapped reads was performed through featureCounts. Library gene count tables were then merged to a single count matrix as input for data normalization and differential gene expression analysis with DESeq2.
Project description:The aim of this mRNA expression profiling experiment was to screen for ecotoxicogenomic fingerprints in zebrafish (Danio rerio) embryos (96 hpf) as aquatic vertebrate non-target model exposed to sub lethal concentrations of the carbamate insecticide Carbaryl (CAS 63-25-2). The Insecticide Resistance Action Committee (IRAC) classified Carbaryl after its mode of action (MoA) in the target organism as an acetylcholinesterase (AChE) inhibitor (Group 1A). The goal is to identify toxicogenomic profiles with predictive character and potential molecular key events (KE) explaining upstream adverse effects in aquatic non-target organisms. This will provide useful information to refine and improve existing adverse outcome pathways (AOP). Furthermore, integrating the obtained profiles for this and other tested chemicals in a collective database will enable us in the future to derive predictions about the ecotoxicological hazard for chemcials with unknown apical effects, based on similarly altered transcriptomic and proteomic profiles. In a modified version of the zebrafish embryo toxicity test (OECD 236), 15 fertilized eggs were exposed to two different sub lethal concentrations of Carbaryl for 96 hours under semi-static conditions. Each test comprised of a low exposure (LE, 275 µg/L), high exposure (HE, 1100 µg/L) and negative control (NC) group and was performed in triplicates. At 96 hours post fertilization (hpf), 10 larvae were randomly picked for each sample and pooled for RNA and protein extraction with NucleoSpin RNA/Protein kit (Macherey-Nagel). RNA quality was assessed with a 2100 Bioanalyzer system (Agilent) before coding RNA was purified (PolyA selection with TruSeq RNA Library Prep Kit v2) and sequenced on an Illumina HiSeq 4000 System (Illumina) in 50 bp single read mode, producing roughly 30 million reads per sample. Adapter sequences were removed with trimmomatic and sequences were aligned to the D.rerio reference genome GRCz11 with STAR. Counting of feature mapped reads was performed through featureCounts. Library gene count tables were then merged to a single count matrix as input for differential gene expression analysis with DESeq2.
Project description:The aim of this mRNA expression profiling experiment was to screen for ecotoxicogenomic fingerprints in zebrafish (Danio rerio) embryos as aquatic vertebrate non-target model exposed to sub lethal concentrations of the heavily used neonicotinoid insecticide Imidacloprid (CAS 138261-41-3). The Insecticide Resistance Action Committee (IRAC) classified Imidacloprid after its mode of action (MoA) in the target organism as a nicotinic acetylcholine receptor (nAChR) competitive modulator (Group 4A) The goal is to identify toxicogenomic profiles with predictive character and potential molecular key events (KE) explaining upstream adverse effects in aquatic non-target organisms. This will provide useful information to refine and improve existing adverse outcome pathways (AOP). Furthermore, integrating the obtained profiles for this and other tested chemicals in a collective database will enable us in the future to derive predictions about the ecotoxicological hazard for chemcials with unknown apical effects, based on similarly altered transcriptomic and proteomic profiles. In a modified version of the zebrafish embryo toxicity test (OECD 236), 15 fertilized eggs were exposed to two different sub lethal concentrations of Imidacloprid for 96 hours under semi-static conditions. Each test comprised of a low exposure (LE, 0.015 mg/L), medium exposure (ME, 0.03 mg/L), high exposure (HE, 0.06 mg/L) and negative control (NC) group and was performed in triplicates. At 96 hours post fertilization (hpf), 10 larvae were randomly picked for each sample and pooled for RNA and protein extraction with NucleoSpin RNA/Protein kit (Macherey-Nagel). RNA quality was assessed with a 2100 Bioanalyzer system (Agilent) before coding RNA was purified (PolyA selection with TruSeq RNA Library Prep Kit v2) and sequenced on an Illumina HiSeq 4000 System (Illumina) in 50 bp single read mode, producing roughly 30 million reads per sample. Adapter sequences were removed with trimmomatic and sequences were aligned to the D.rerio reference genome GRCz11 with STAR. Counting of feature mapped reads was performed through featureCounts. Library gene count tables were then merged to a single count matrix as input for data normalization and differential gene expression analysis with DESeq2.