Degradation and mineralization of azo dye reactive blue 222 by sequential Photo-Fenton's oxidation followed by aerobic biological treatment using white rot fungi.
Identifieur interne : 000386 ( Main/Corpus ); précédent : 000385; suivant : 000387Degradation and mineralization of azo dye reactive blue 222 by sequential Photo-Fenton's oxidation followed by aerobic biological treatment using white rot fungi.
Auteurs : Shumaila Kiran ; Shaukat Ali ; Muhammad AsgherSource :
- Bulletin of environmental contamination and toxicology [ 1432-0800 ] ; 2013.
English descriptors
- KwdEn :
- Aerobiosis (MeSH), Azo Compounds (metabolism), Biodegradation, Environmental (MeSH), Biological Oxygen Demand Analysis (MeSH), Coloring Agents (metabolism), Hydrogen Peroxide (metabolism), Iron (metabolism), Minerals (metabolism), Oxidation-Reduction (MeSH), Phanerochaete (metabolism), Photolysis (MeSH), Spectrophotometry, Ultraviolet (MeSH), Spectroscopy, Fourier Transform Infrared (MeSH).
- MESH :
- chemical , metabolism : Azo Compounds, Coloring Agents, Hydrogen Peroxide, Iron, Minerals.
- metabolism : Phanerochaete.
- Aerobiosis, Biodegradation, Environmental, Biological Oxygen Demand Analysis, Oxidation-Reduction, Photolysis, Spectrophotometry, Ultraviolet, Spectroscopy, Fourier Transform Infrared.
Abstract
A two stage sequential Photo-Fenton's oxidation followed by aerobic biological treatment using two white rot fungi P. ostreatus IBL-02 (PO) and P. chrysosporium IBL-03 (PC) was performed to check decolorization and to enhance mineralization of azo dye Reactive Blue 222 (RB222). In the first stage, selected dye was subjected to Photo-Fenton's oxidation with decolorization percentage ≈90 % which was further increased to 96.88 % and 95.23 % after aerobic treatment using two white rot fungi P. ostreatus IBL-02 (PO) and P. chrysosporium IBL-03 (PC), respectively. Mineralization efficiency was accessed by measuring the water quality assurance parameters like COD, TOC, TSS and Phenolics estimation. Reduction in COD, TOC, TSS and Phenolics were found to be 95.34 %, 90.11 %, 90.84 % and 92.22 %, respectively in two stage sequential processes. The degradation products were characterized by UV-visible and FTIR spectral techniques and their toxicity was measured. The results provide evidence that both fungal strains were able to oxidize and mineralize the selected azo dye into non-toxic metabolites.
DOI: 10.1007/s00128-012-0888-0
PubMed: 23272326
Links to Exploration step
pubmed:23272326Le document en format XML
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<author><name sortKey="Kiran, Shumaila" sort="Kiran, Shumaila" uniqKey="Kiran S" first="Shumaila" last="Kiran">Shumaila Kiran</name>
<affiliation><nlm:affiliation>Department of Applied Chemistry, Government College University, Faisalabad, 38000, Pakistan. saba_kirran@yahoo.com</nlm:affiliation>
</affiliation>
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<author><name sortKey="Ali, Shaukat" sort="Ali, Shaukat" uniqKey="Ali S" first="Shaukat" last="Ali">Shaukat Ali</name>
</author>
<author><name sortKey="Asgher, Muhammad" sort="Asgher, Muhammad" uniqKey="Asgher M" first="Muhammad" last="Asgher">Muhammad Asgher</name>
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<sourceDesc><biblStruct><analytic><title xml:lang="en">Degradation and mineralization of azo dye reactive blue 222 by sequential Photo-Fenton's oxidation followed by aerobic biological treatment using white rot fungi.</title>
<author><name sortKey="Kiran, Shumaila" sort="Kiran, Shumaila" uniqKey="Kiran S" first="Shumaila" last="Kiran">Shumaila Kiran</name>
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<author><name sortKey="Ali, Shaukat" sort="Ali, Shaukat" uniqKey="Ali S" first="Shaukat" last="Ali">Shaukat Ali</name>
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<series><title level="j">Bulletin of environmental contamination and toxicology</title>
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<profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Aerobiosis (MeSH)</term>
<term>Azo Compounds (metabolism)</term>
<term>Biodegradation, Environmental (MeSH)</term>
<term>Biological Oxygen Demand Analysis (MeSH)</term>
<term>Coloring Agents (metabolism)</term>
<term>Hydrogen Peroxide (metabolism)</term>
<term>Iron (metabolism)</term>
<term>Minerals (metabolism)</term>
<term>Oxidation-Reduction (MeSH)</term>
<term>Phanerochaete (metabolism)</term>
<term>Photolysis (MeSH)</term>
<term>Spectrophotometry, Ultraviolet (MeSH)</term>
<term>Spectroscopy, Fourier Transform Infrared (MeSH)</term>
</keywords>
<keywords scheme="MESH" type="chemical" qualifier="metabolism" xml:lang="en"><term>Azo Compounds</term>
<term>Coloring Agents</term>
<term>Hydrogen Peroxide</term>
<term>Iron</term>
<term>Minerals</term>
</keywords>
<keywords scheme="MESH" qualifier="metabolism" xml:lang="en"><term>Phanerochaete</term>
</keywords>
<keywords scheme="MESH" xml:lang="en"><term>Aerobiosis</term>
<term>Biodegradation, Environmental</term>
<term>Biological Oxygen Demand Analysis</term>
<term>Oxidation-Reduction</term>
<term>Photolysis</term>
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<front><div type="abstract" xml:lang="en">A two stage sequential Photo-Fenton's oxidation followed by aerobic biological treatment using two white rot fungi P. ostreatus IBL-02 (PO) and P. chrysosporium IBL-03 (PC) was performed to check decolorization and to enhance mineralization of azo dye Reactive Blue 222 (RB222). In the first stage, selected dye was subjected to Photo-Fenton's oxidation with decolorization percentage ≈90 % which was further increased to 96.88 % and 95.23 % after aerobic treatment using two white rot fungi P. ostreatus IBL-02 (PO) and P. chrysosporium IBL-03 (PC), respectively. Mineralization efficiency was accessed by measuring the water quality assurance parameters like COD, TOC, TSS and Phenolics estimation. Reduction in COD, TOC, TSS and Phenolics were found to be 95.34 %, 90.11 %, 90.84 % and 92.22 %, respectively in two stage sequential processes. The degradation products were characterized by UV-visible and FTIR spectral techniques and their toxicity was measured. The results provide evidence that both fungal strains were able to oxidize and mineralize the selected azo dye into non-toxic metabolites.</div>
</front>
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<ArticleTitle>Degradation and mineralization of azo dye reactive blue 222 by sequential Photo-Fenton's oxidation followed by aerobic biological treatment using white rot fungi.</ArticleTitle>
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<Abstract><AbstractText>A two stage sequential Photo-Fenton's oxidation followed by aerobic biological treatment using two white rot fungi P. ostreatus IBL-02 (PO) and P. chrysosporium IBL-03 (PC) was performed to check decolorization and to enhance mineralization of azo dye Reactive Blue 222 (RB222). In the first stage, selected dye was subjected to Photo-Fenton's oxidation with decolorization percentage ≈90 % which was further increased to 96.88 % and 95.23 % after aerobic treatment using two white rot fungi P. ostreatus IBL-02 (PO) and P. chrysosporium IBL-03 (PC), respectively. Mineralization efficiency was accessed by measuring the water quality assurance parameters like COD, TOC, TSS and Phenolics estimation. Reduction in COD, TOC, TSS and Phenolics were found to be 95.34 %, 90.11 %, 90.84 % and 92.22 %, respectively in two stage sequential processes. The degradation products were characterized by UV-visible and FTIR spectral techniques and their toxicity was measured. The results provide evidence that both fungal strains were able to oxidize and mineralize the selected azo dye into non-toxic metabolites.</AbstractText>
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