Transcriptional profile of zebrafish eyes after exposure to 200 ug/L Tetrabromobisphenol A (TBBPA)
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PROVIDER: PRJNA497088 | ENA |
REPOSITORIES: ENA
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Project description:Vertebrate eye devlopment is partially regulated by thyroid hormones. TBBPA is a chemical that interacts with thyroid receptors. We investigated the effects of TBBPA on eye development of zebrafish. We expected TBBPA exposure to cause transcriptional changes of visual-system-related genes, which find their phenotypic anchoring in eye malformations and dysfunction, as observed in our previous studies. Additionally, the reversibility of effects after recovery in clean water for three days was investigated.
2019-05-09 | GSE121336 | GEO
Project description:To identify liver transcripts differentially expressed due to treatment with tetrabromobisphenol A-bis(2,3-dibromopropyl ether) (TBBPA-DBPE), we collected RNA from male Harlan Sprague Dawley rats exposed to 0, 0.1, 0.94, 9.4, 94.3 or 943 mg/kg TBBPA.DBPE, 5 days after exposure for animals 7 weeks of age. These samples were interrogated with the Affymetrix Rat Genome 230 2.0 GeneChip array. A total of 0,0,0,0,0, and 0 gene transcripts were differentially expressed due to TBBPA.DBPE treatment after exposure to 0.1, 0.94, 9.4, 94.3 or 943 mg/kg TBBPA.DBPE (false discovery rate (FDR) < 0.05).
2020-07-15 | GSE153363 | GEO
Project description:Halogenated flame retardants (HFRs) Tetrabromobisphenol A (TBBPA), Tetrabromobisphenol S (TBBPS) and Tetrachlorobisphenol (TCBPA) are wildly applied in manufacturing industry to improve the fire safety of the products. Recent reports demonstrated that TBBPA, TBBPS and TCBPA can be detected in pregnant women serum at nanomolar-level. Considering TBBPA have also been detected in the cord serum and the structural similarity of the 3 HFRs, it is necessary to pay attention to their development toxicity. Liver is the important detoxic organ but also target of TBBPA since it has been demonstrated that TBBPA exposure lead to increased liver weight in mouse and rat. So the developmental hepatic toxicity of the 3 HFRs were studied in this current research with the transcriptomic and human embryonic stem cells hepatic differentiation based toxicity evaluation system. A hepatic differentiation specific lineage development map and cell lineage - gene expression annotations were made and used for easily assessing the lineage alternations caused by toxicant treatment. Together with GO and KEGG analysis, this study mainly demonstrated that, the 3 HFRs have many common disruptive effect on hepatic differentiation, while only TCBPA significantly inhibited hepatic differentiation. The up-regulation of genes related to cell cycle and FGF10 signaling pathway at relatively late stage of hepatic differentiation indicates the proliferation of hepatoblasts were promoted by the 3 HFRs, likely via up-regulating the FGF10 signaling pathway. The proliferating promoting effect may partly explain why liver gain weight in rodents exposed to TBBPA.
2023-04-03 | GSE148518 | GEO
Project description:Tetrabromobisphenol A (TBBPA) biodegradation in acidogenic systems: one step further on where and who
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Project description:To further study the transcriptome of THP-1 human monocytes after exposure to S-Nitrosoglutathione (GSNO), we investigate whole genome microarray expression to identify genes regulated by exposure or not to GSNO. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 50 ug / mL of S-Nitrosoglutathione-loaded polymeric Eudragit RL nanoparticles (GSNO-loaded ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of GSNO-loaded ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 200 ug / mL of empty polymeric Eudragit RL nanoparticles (empty ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 200 ug / mL of empty ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 24 h to 50 ug / mL of S-Nitrosoglutathione-loaded polymeric Eudragit RL nanoparticles (GSNO-loaded ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of GSNO-loaded ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 24 h to 50 ug / mL of empty polymeric Eudragit RL nanoparticles (empty ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of empty ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 50 ug / mL of empty polymeric Eudragit RL nanoparticles (empty ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of empty ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 200 ug / mL of S-Nitrosoglutathione-loaded polymeric Eudragit RL nanoparticles (GSNO-loaded ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 200 ug / mL of GSNO-loaded ENP.
2013-12-19 | GSE51186 | GEO
Project description:Tetrabromobisphenol A (TBBPA) and its substitutes and derivatives have been widely used as halogenated flame retardants (HFRs), in the past few decades. As a consequence, these compounds are frequently detected in the environment, as well as human bodily fluids, especially umbilical cord blood and breast milk. This has raised awareness of their potential risks to fetuses and infants. In this study, we employed human embryonic stem cell differentiation models to assess the potential developmental toxicity of six TBBPA-like compounds, at human relevant nanomolar concentrations. To mimic early embryonic development, we utilized embryoid body-based 3D differentiation in presence of the six HFRs. Transcriptomics data showed that HFR exposure over 16 days of differentiation only interfered with the expression of a few genes, indicating those six HFRs may not have specific tissue/organ targets during embryonic development. Nevertheless, further analyses revealed that some cardiac-related genes were dysregulated. Since the heart is also the first organ to develop, we employed a cardiac differentiation model to analyze the six HFRs' potential developmental toxicity in more depth. Overall, HFRs of interest did not significantly disturb the canonical WNT pathway, which is an essential signal transduction pathway for cardiac development. In addition, the six HFRs showed only mild changes in gene expression levels for cardiomyocyte markers, such as NKX2.5, MYH7, and MYL4, as well as a significant down-regulation of some but not all the epicardial and smooth muscle cell markers selected. Taken together, our results show that the six studied HFRs, at human relevant concentrations, may impose negligible effects on embryogenesis and heart development. Nevertheless, higher exposure doses might affect the early stages of heart development.
2023-02-02 | GSE193176 | GEO
Project description:To further study the transcriptome of THP-1 human monocytes after exposure to S-Nitrosoglutathione (GSNO), we investigate whole genome microarray expression to identify genes regulated by exposure or not to GSNO. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 50 ug / mL of S-Nitrosoglutathione-loaded polymeric Eudragit RL nanoparticles (GSNO-loaded ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of GSNO-loaded ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 200 ug / mL of empty polymeric Eudragit RL nanoparticles (empty ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 200 ug / mL of empty ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 24 h to 50 ug / mL of S-Nitrosoglutathione-loaded polymeric Eudragit RL nanoparticles (GSNO-loaded ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of GSNO-loaded ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 24 h to 50 ug / mL of empty polymeric Eudragit RL nanoparticles (empty ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of empty ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 50 ug / mL of empty polymeric Eudragit RL nanoparticles (empty ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 50 ug / mL of empty ENP. To further study the transcriptome of THP-1 human monocytes after exposure for 4 h to 200 ug / mL of S-Nitrosoglutathione-loaded polymeric Eudragit RL nanoparticles (GSNO-loaded ENP), we investigate whole genome microarray expression to identify genes regulated by exposure or not to 200 ug / mL of GSNO-loaded ENP. Changes in gene expression in THP-1 cells incubated without (control) or with 50 uM GSNO for 4 h, were measured. Five biological replicates were performed as controls: F_01; F_07; F_13; S_01; S_02. Four biological replicates were performed in GSNO exposed cells: S_13; S_14; S_15; S_16. Changes in gene expression in THP-1 cells incubated without (control) or with 50 ug / mL of GSNO-loaded ENPs (300 nm) for 4 h were measured. Five biological replicates were performed as controls: F_01; F_07; F_13; S_01; S_02. Three biological replicates were performed in 50 ug / mL of GSNO-loaded ENP exposed cells: S_06; S_07; S_08. Changes in gene expression in THP-1 cells incubated without (control) or with 200 ug / mL of empty ENPs (300 nm) for 4 h were measured. Five biological replicates were performed as controls: F_01; F_07; F_13; S_01; S_02. Three biological replicates were performed in 200 ug / mL of empty ENP exposed cells: S_17; S_19; S_20. Changes in gene expression in THP-1 cells incubated without (control) or with 50 ug / mL of GSNO-loaded ENPs (300 nm) for 24 h were measured. Five biological replicates were performed as controls: F_04; F_10; F_16; S_03; S_04. Four biological replicates were performed in 50 ug / mL of GSNO-loaded ENP exposed cells: S_09; S_10; S_11; S_12. Changes in gene expression in THP-1 cells incubated without (control) or with 50 ug / mL of empty ENPs (300 nm) for 24 h were measured. Five biological replicates were performed as controls: F_04; F_10; F_16; S_03; S_04. Three biological replicates were performed in 50 ug / mL of empty ENP exposed cells: F_05; F_11; F_17. Changes in gene expression in THP-1 cells incubated without (control) or with 50 ug / mL of empty ENPs (300 nm) for 4 h were measured. Five biological replicates were performed as controls: F_01; F_07; F_13; S_01; S_02. Three biological replicates were performed in 50 ug / mL of empty ENP exposed cells: F_02; F_08; F_14. Changes in gene expression in THP-1 cells incubated without (control) or with 200 ug / mL of GSNO-loaded ENPs (300 nm) for 4 h were measured. Five biological replicates were performed as controls: F_01; F_07; F_13; S_01; S_02. Four biological replicates were performed in 200 ug / mL of GSNO-loaded ENP exposed cells: S_21; S_22; S_23; S_24.
2013-12-19 | E-GEOD-51186 | biostudies-arrayexpress
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