Transcriptomic profiling of PBDE-exposed HepaRG cells unveils critical lncRNA- PCG pairs involved in intermediary metabolism
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ABSTRACT:
PROVIDER: PRJNA599419 | ENA |
REPOSITORIES: ENA
Dataset's files
| Action | DRS | |||
|---|---|---|---|---|
| SRR10846474_1.fastq.gz | Fastqsanger.gz | |||
| SRR10846474_2.fastq.gz | Fastqsanger.gz | |||
| SRR10846475_1.fastq.gz | Fastqsanger.gz | |||
| SRR10846475_2.fastq.gz | Fastqsanger.gz | |||
| SRR10846476_1.fastq.gz | Fastqsanger.gz |
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Project description:Purpose: The goal of this study was to investigate how PBDEs regulate both PCGs and lncRNAs in a PXR/CAR ligand-dependent and independent manner Methods: HepaRG cells, which are human-derived hepatic cells that accurately represent gene expression profiles of human liver tissue, were exposed to BDE-47 and BDE-99 at a dose of 25 μM for 24 hours. Differentially expressed lncRNA-PCG pairs were identified through DESeq2 and HOMER; significant canonical pathways were determined through Ingenuity Pathway Analysis (IPA). LncTar was used to predict the binding of 19 lncRNA-PCG pairs with known roles in drug-processing pathways. Results: Genome annotation revealed that the majority of the differentially expressed lncRNAs map to PCG introns. PBDEs regulated overlapping pathways with PXR and CAR such as protein ubiqutination pathway and peroxisome proliferator-activated receptor alpha-retinoid X receptor alpha (PPARα-RXRα) activation but also regulate distinctive pathways involved in intermediary metabolism. PBDEs uniquely down-regulated GDP-L-fucose biosynthesis, suggesting its role in modifying important pathways involved in intermediary metabolism such as carbohydrate and lipid metabolism. Conclusion: There is strong evidence that PBDEs regulate both PCGs and lncRNAs in a PXR/CAR ligand-dependent and independent manner
2020-01-08 | GSE143260 | GEO
Project description:Polybrominated diphenyl ethers (PBDEs) were formally used as flame-retardants and are chemically stable, lipophlic persistent organic pollutants which are known to bioaccumulate in humans. Although its toxicities are well characterized, little is known about the changes in transcriptional regulation caused by PBDE exposure. Long non-coding RNAs (lncRNAs) are increasingly recognized as key regulators of transcriptional and translational processes. It is hypothesized that lncRNAs can regulate nearby protein-coding genes (PCGs) and changes in the transcription of lncRNAs may act in cis to perturb gene expression of its neighboring PCGs. The goals of this study were to 1) characterize PCGs and lncRNAs that are differentially regulated from exposure to PBDEs; 2) identify PCG-lncRNA pairs through genome annotation and predictive binding tools; and 3) determine enriched canonical pathways caused by differentially expressed lncRNA-PCGs pairs. HepaRG cells, which are human-derived hepatic cells that accurately represent gene expression profiles of human liver tissue, were exposed to BDE-47 and BDE-99 at a dose of 25 μM for 24 hours. Differentially expressed lncRNA-PCG pairs were identified through DESeq2 and HOMER; significant canonical pathways were determined through Ingenuity Pathway Analysis (IPA). LncTar was used to predict the binding of 19 lncRNA-PCG pairs with known roles in drug-processing pathways. Genome annotation revealed that the majority of the differentially expressed lncRNAs map to PCG introns. PBDEs regulated overlapping pathways with PXR and CAR such as protein ubiqutination pathway and peroxisome proliferator-activated receptor alpha-retinoid X receptor alpha (PPARα-RXRα) activation but also regulate distinctive pathways involved in intermediary metabolism. PBDEs uniquely down-regulated GDP-L-fucose biosynthesis, suggesting its role in modifying important pathways involved in intermediary metabolism such as carbohydrate and lipid metabolism. In conclusion, we provide strong evidence that PBDEs regulate both PCGs and lncRNAs in a PXR/CAR ligand-dependent and independent manner.
| S-EPMC7043721 | biostudies-literature
Project description:Liver gene transcripts patterns were used to characterize toxicity from exposure to polybrominated diphenyl ethers (PBDEs), flame retardant components. In this study, Wistar Han dams were exposed by gavage to the PBDE mixture (DE71) starting at gestation day 6 (GD 6) and continuing to weaning on postnatal day 21 (PND 21). Offspring from the dams began PBDE direct dosing on PND 12 and were dosed daily through PND 21. After weaning, they were dosed 5 days per week for another 13 weeks. Liver samples were collected at PND 22 and week 13 for liver gene expression analysis and interrogated with the Affymetrix Rat Genome 230 2.0 Array. PBDE treatment induced 1,066 liver gene transcript changes in females and 1,200 transcriptional changes in males at PND 22 (false discovery rate (FDR) < 0.01), but only 263 liver transcriptional changes at 13 weeks in male rats (FDR <0.05). No significant differences in dose response were found between male and female pups. There were a total of 6 groups and 5x replication for each group, for 30 total samples that were analyzed. The groups were (1) pup-male-CTL, (2) pup-female-CTL, (3) pup-male-PBDE, (4) pup-female-PBDE, (5) rat-male-CTL, (6) rat-male-PBDE. We generated the following pairwise comparisons using R/maanova: malePups(PBDE vs CTL), femalePups(PBDE vs CTL), maleRats(PBDE vs CTL), CTLpups(male vs female), PBDEpups(male vs female). We also performed ANOVA test for SEX-by-DOSE (pups) and AGE-by-DOSE (males). For pups, genes with an FDR≤1% were selected; for rats, genes with FDR < 5% were selected.
2011-10-04 | E-GEOD-32156 | biostudies-arrayexpress
Project description:To identify liver transcripts differentially expressed between control samples and animals exposed to PBDE-47, we collected RNA from male pups at postnatal day 4 (PND4) after the Wistar Han dams were exposed to 0, 0.1, 15, or 50 mg/kg PBDE-47. These samples were interrogated with the Affymetrix Rat Genome 230 2.0 GeneChip array. A total of 7, 50, and 149 gene transcripts were differentially expressed between control samples and 0.1, 15, and 50 mg/kg PBDE-47 (using a false discovery rate (FDR) threshold of 0.05). These transcripts were mapped to 2, 40, and 139 genes using Ingenuity Pathway Analysis.
2020-07-22 | GSE154912 | GEO
Project description:Liver gene transcripts patterns were used to characterize toxicity from exposure to polybrominated diphenyl ethers (PBDEs), flame retardant components. In this study, Wistar Han dams were exposed by gavage to the PBDE mixture (DE71) starting at gestation day 6 (GD 6) and continuing to weaning on postnatal day 21 (PND 21). Offspring from the dams began PBDE direct dosing on PND 12 and were dosed daily through PND 21. After weaning, they were dosed 5 days per week for another 13 weeks. Liver samples were collected at PND 22 and week 13 for liver gene expression analysis and interrogated with the Affymetrix Rat Genome 230 2.0 Array. PBDE treatment induced 1,066 liver gene transcript changes in females and 1,200 transcriptional changes in males at PND 22 (false discovery rate (FDR) < 0.01), but only 263 liver transcriptional changes at 13 weeks in male rats (FDR <0.05). No significant differences in dose response were found between male and female pups.
2011-10-05 | GSE32156 | GEO
Project description:Test articles used: DE-71 (Pentabromodiphenyl Ether Mixture [Technical Grade), CAS Number 32534-81-9, DTXSID2024246); PBDE-47 (CAS Number 5436-43-1); PB (Phenobarbital, CAS Number 50-06-6 ); PCB (PCB126, CAS Number 57465-28-8)
2019-01-05 | GSE124431 | GEO
Project description:Affymetrix high-density oligonucleotide microarray analysis was performed to analyse hydroxylated polybrominated diphenyl ethers (OH-PBDE)-induced gene expression changes in H295R adrenocortical carcinoma cells. Cells were treated with growth medium in the presence or absence of 10 µM 2-OH-BDE47 or 2-OH-BDE85 for 24 hours before the gene expression changes were investigated. Experiment Overall Design: Gene expression changes in response to hydroxylated polybrominated diphenyl ethers (OH-PBDEs) were analysed by Microarray technology in H295R adrenocortical carcinoma cells. Cells were treated with 10 µM of 2-OH-BDE47 or 2-OH-BDE85 (or growth medium alone) for 24 hours before the OH-PBDE-induced gene expression changes were investigated. Control, 2-OH-BDE47- and 2-OH-BDE85-treated samples were collected from three independent experiments each.
2009-01-02 | E-GEOD-8588 | biostudies-arrayexpress
Project description:To identify the molecular mechanisms and environmental inducers contributing to reprogramming of hepatocytes into progenitors in HCC context, we used the HepaRG cell line as model.
2013-12-05 | GSE52989 | GEO
Project description:Polycomb group (PcG) proteins maintain the silenced state of key developmental genes in animals, but how these proteins are recruited to specific regions of the genome is still poorly understood. In Drosophila, PcG proteins are recruited to Polycomb response elements (PREs) that include combinations of sites for sequence specific DNA binding “PcG recruiters,” including Pho, Cg, and Spps. To understand their roles in PcG recruitment, we compared Pho-, Cg-, and Spps-binding sites against H3K27me3 and key PcG proteins by ChIP-seq in wild-type and mutant third instar larvae. H3K27me3 in canonical Polycomb domains is decreased after the reduction of any recruiter. Reduction of Spps and Pho, but not Cg, causes the redistribution of H3K27me3 to heterochromatin. Regions with dramatically depleted H3K27me3 after Spps knockout are usually accompanied by decreased Pho binding, suggesting their cooperative binding. PcG recruiters, the PRC2 component E(z), and the PRC1 components Psc and Ph cobind thousands of active genes outside of H3K27me3 domains. This study demonstrates the importance of distinct PcG recruiters for the establishment of unique Polycomb domains. Different PcG recruiters can act both cooperatively and independently at specific PcG target genes, highlighting the complexity and diversity of PcG recruitment mechanisms.
2018-03-07 | GSE102339 | GEO
Project description:Polybrominated diphenyl ethers (PBDEs) are commonly used as flame retardants in a variety of commercial and household products. They have been detected in the environment and accumulate in mammalian tissues and fluids. PBDE toxicity is thought to be associated with endocrine disruption, developmental neurotoxicity and changes in fetal development. Although humans are exposed to PBDEs, our knowledge of the effects of PBDE metabolites on human cells with respect to health risk is insufficient. Two hydroxylated PBDEs (OH-PBDEs), 2-OH-BDE47 and 2-OH-BDE85, were investigated for their effects on cell viability/proliferation, DNA damage, cell cycle distribution and gene expression profiling in H295R adrenocortical carcinoma cells. We show that the two agents are cytotoxic in a dose-dependent manner only at micromolar concentrations, with 2-OH-BDE85 being more toxic than 2-OH-BDE47. However, no DNA damage was observed for either chemical, suggesting that the biological effects of OH-PBDEs occur primarily via non-genotoxic routes. Furthermore, no evidence of aryl hydrocarbon receptor (AHR)-mediated, dioxin-like toxicity was observed. Instead, we report that a micromolar concentration of OH-PBDEs induces transcriptional changes associated with endoplasmic reticulum stress and the unfolded protein response. We discuss whether OH-PBDE bioaccumulation could result in impairment of the adrenocortical secretory function.
2008-12-25 | GSE8588 | GEO