Enhancing the production of hydroxyl radicals by Pleurotus eryngii via quinone redox cycling for pollutant removal.
Identifieur interne : 001251 ( Main/Exploration ); précédent : 001250; suivant : 001252Enhancing the production of hydroxyl radicals by Pleurotus eryngii via quinone redox cycling for pollutant removal.
Auteurs : Víctor G Mez-Toribio [Espagne] ; Ana B. García-Martín ; María J. Martínez ; Angel T. Martínez ; Francisco GuillénSource :
- Applied and environmental microbiology [ 1098-5336 ] ; 2009.
Descripteurs français
- KwdFr :
- Acide oxalique (métabolisme), Acide édétique (métabolisme), Benzaldéhydes (métabolisme), Benzoquinones (métabolisme), Composés du fer III (métabolisme), Manganèse (métabolisme), Oxydoréduction (MeSH), Pleurotus (métabolisme), Polluants environnementaux (métabolisme), Radical hydroxyle (métabolisme).
- MESH :
English descriptors
- KwdEn :
- MESH :
- chemical , metabolism : Benzaldehydes, Benzoquinones, Edetic Acid, Environmental Pollutants, Ferric Compounds, Hydroxyl Radical, Manganese, Oxalic Acid.
- metabolism : Pleurotus.
- Oxidation-Reduction.
Abstract
The induction of hydroxyl radical (OH) production via quinone redox cycling in white-rot fungi was investigated to improve pollutant degradation. In particular, we examined the influence of 4-methoxybenzaldehyde (anisaldehyde), Mn(2+), and oxalate on Pleurotus eryngii OH generation. Our standard quinone redox cycling conditions combined mycelium from laccase-producing cultures with 2,6-dimethoxy-1,4-benzoquinone (DBQ) and Fe(3+)-EDTA. The main reactions involved in OH production under these conditions have been shown to be (i) DBQ reduction to hydroquinone (DBQH(2)) by cell-bound dehydrogenase activities; (ii) DBQH(2) oxidation to semiquinone (DBQ(-)) by laccase; (iii) DBQ(-) autoxidation, catalyzed by Fe(3+)-EDTA, producing superoxide (O(2)(-)) and Fe(2+)-EDTA; (iv) O(2)(-) dismutation, generating H(2)O(2); and (v) the Fenton reaction. Compared to standard quinone redox cycling conditions, OH production was increased 1.2- and 3.0-fold by the presence of anisaldehyde and Mn(2+), respectively, and 3.1-fold by substituting Fe(3+)-EDTA with Fe(3+)-oxalate. A 6.3-fold increase was obtained by combining Mn(2+) and Fe(3+)-oxalate. These increases were due to enhanced production of H(2)O(2) via anisaldehyde redox cycling and O(2)(-) reduction by Mn(2+). They were also caused by the acceleration of the DBQ redox cycle as a consequence of DBQH(2) oxidation by both Fe(3+)-oxalate and the Mn(3+) generated during O(2)(-) reduction. Finally, induction of OH production through quinone redox cycling enabled P. eryngii to oxidize phenol and the dye reactive black 5, obtaining a high correlation between the rates of OH production and pollutant oxidation.
DOI: 10.1128/AEM.02138-08
PubMed: 19376890
PubMed Central: PMC2698368
Affiliations:
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García-Martín</name></author><author><name sortKey="Martinez, Maria J" sort="Martinez, Maria J" uniqKey="Martinez M" first="María J" last="Martínez">María J. Martínez</name></author><author><name sortKey="Martinez, Angel T" sort="Martinez, Angel T" uniqKey="Martinez A" first="Angel T" last="Martínez">Angel T. 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García-Martín</name></author><author><name sortKey="Martinez, Maria J" sort="Martinez, Maria J" uniqKey="Martinez M" first="María J" last="Martínez">María J. Martínez</name></author><author><name sortKey="Martinez, Angel T" sort="Martinez, Angel T" uniqKey="Martinez A" first="Angel T" last="Martínez">Angel T. Martínez</name></author><author><name sortKey="Guillen, Francisco" sort="Guillen, Francisco" uniqKey="Guillen F" first="Francisco" last="Guillén">Francisco Guillén</name></author></analytic><series><title level="j">Applied and environmental microbiology</title><idno type="eISSN">1098-5336</idno><imprint><date when="2009" type="published">2009</date></imprint></series></biblStruct></sourceDesc></fileDesc><profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Benzaldehydes (metabolism)</term><term>Benzoquinones (metabolism)</term><term>Edetic Acid (metabolism)</term><term>Environmental Pollutants (metabolism)</term><term>Ferric Compounds (metabolism)</term><term>Hydroxyl Radical (metabolism)</term><term>Manganese (metabolism)</term><term>Oxalic Acid (metabolism)</term><term>Oxidation-Reduction (MeSH)</term><term>Pleurotus (metabolism)</term></keywords><keywords scheme="KwdFr" xml:lang="fr"><term>Acide oxalique (métabolisme)</term><term>Acide édétique (métabolisme)</term><term>Benzaldéhydes (métabolisme)</term><term>Benzoquinones (métabolisme)</term><term>Composés du fer III (métabolisme)</term><term>Manganèse (métabolisme)</term><term>Oxydoréduction (MeSH)</term><term>Pleurotus (métabolisme)</term><term>Polluants environnementaux (métabolisme)</term><term>Radical hydroxyle (métabolisme)</term></keywords><keywords scheme="MESH" type="chemical" qualifier="metabolism" xml:lang="en"><term>Benzaldehydes</term><term>Benzoquinones</term><term>Edetic Acid</term><term>Environmental Pollutants</term><term>Ferric Compounds</term><term>Hydroxyl Radical</term><term>Manganese</term><term>Oxalic Acid</term></keywords><keywords scheme="MESH" qualifier="metabolism" xml:lang="en"><term>Pleurotus</term></keywords><keywords scheme="MESH" qualifier="métabolisme" xml:lang="fr"><term>Acide oxalique</term><term>Acide édétique</term><term>Benzaldéhydes</term><term>Benzoquinones</term><term>Composés du fer III</term><term>Manganèse</term><term>Pleurotus</term><term>Polluants environnementaux</term><term>Radical hydroxyle</term></keywords><keywords scheme="MESH" xml:lang="en"><term>Oxidation-Reduction</term></keywords><keywords scheme="MESH" xml:lang="fr"><term>Oxydoréduction</term></keywords></textClass></profileDesc></teiHeader><front><div type="abstract" xml:lang="en">The induction of hydroxyl radical (OH) production via quinone redox cycling in white-rot fungi was investigated to improve pollutant degradation. In particular, we examined the influence of 4-methoxybenzaldehyde (anisaldehyde), Mn(2+), and oxalate on Pleurotus eryngii OH generation. Our standard quinone redox cycling conditions combined mycelium from laccase-producing cultures with 2,6-dimethoxy-1,4-benzoquinone (DBQ) and Fe(3+)-EDTA. The main reactions involved in OH production under these conditions have been shown to be (i) DBQ reduction to hydroquinone (DBQH(2)) by cell-bound dehydrogenase activities; (ii) DBQH(2) oxidation to semiquinone (DBQ(-)) by laccase; (iii) DBQ(-) autoxidation, catalyzed by Fe(3+)-EDTA, producing superoxide (O(2)(-)) and Fe(2+)-EDTA; (iv) O(2)(-) dismutation, generating H(2)O(2); and (v) the Fenton reaction. Compared to standard quinone redox cycling conditions, OH production was increased 1.2- and 3.0-fold by the presence of anisaldehyde and Mn(2+), respectively, and 3.1-fold by substituting Fe(3+)-EDTA with Fe(3+)-oxalate. A 6.3-fold increase was obtained by combining Mn(2+) and Fe(3+)-oxalate. These increases were due to enhanced production of H(2)O(2) via anisaldehyde redox cycling and O(2)(-) reduction by Mn(2+). They were also caused by the acceleration of the DBQ redox cycle as a consequence of DBQH(2) oxidation by both Fe(3+)-oxalate and the Mn(3+) generated during O(2)(-) reduction. Finally, induction of OH production through quinone redox cycling enabled P. eryngii to oxidize phenol and the dye reactive black 5, obtaining a high correlation between the rates of OH production and pollutant oxidation.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" Owner="NLM"><PMID Version="1">19376890</PMID><DateCompleted><Year>2009</Year><Month>06</Month><Day>25</Day></DateCompleted><DateRevised><Year>2018</Year><Month>11</Month><Day>13</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1098-5336</ISSN><JournalIssue CitedMedium="Internet"><Volume>75</Volume><Issue>12</Issue><PubDate><Year>2009</Year><Month>Jun</Month></PubDate></JournalIssue><Title>Applied and environmental microbiology</Title><ISOAbbreviation>Appl Environ Microbiol</ISOAbbreviation></Journal><ArticleTitle>Enhancing the production of hydroxyl radicals by Pleurotus eryngii via quinone redox cycling for pollutant removal.</ArticleTitle><Pagination><MedlinePgn>3954-62</MedlinePgn></Pagination><ELocationID EIdType="doi" ValidYN="Y">10.1128/AEM.02138-08</ELocationID><Abstract><AbstractText>The induction of hydroxyl radical (OH) production via quinone redox cycling in white-rot fungi was investigated to improve pollutant degradation. In particular, we examined the influence of 4-methoxybenzaldehyde (anisaldehyde), Mn(2+), and oxalate on Pleurotus eryngii OH generation. Our standard quinone redox cycling conditions combined mycelium from laccase-producing cultures with 2,6-dimethoxy-1,4-benzoquinone (DBQ) and Fe(3+)-EDTA. The main reactions involved in OH production under these conditions have been shown to be (i) DBQ reduction to hydroquinone (DBQH(2)) by cell-bound dehydrogenase activities; (ii) DBQH(2) oxidation to semiquinone (DBQ(-)) by laccase; (iii) DBQ(-) autoxidation, catalyzed by Fe(3+)-EDTA, producing superoxide (O(2)(-)) and Fe(2+)-EDTA; (iv) O(2)(-) dismutation, generating H(2)O(2); and (v) the Fenton reaction. Compared to standard quinone redox cycling conditions, OH production was increased 1.2- and 3.0-fold by the presence of anisaldehyde and Mn(2+), respectively, and 3.1-fold by substituting Fe(3+)-EDTA with Fe(3+)-oxalate. A 6.3-fold increase was obtained by combining Mn(2+) and Fe(3+)-oxalate. These increases were due to enhanced production of H(2)O(2) via anisaldehyde redox cycling and O(2)(-) reduction by Mn(2+). They were also caused by the acceleration of the DBQ redox cycle as a consequence of DBQH(2) oxidation by both Fe(3+)-oxalate and the Mn(3+) generated during O(2)(-) reduction. Finally, induction of OH production through quinone redox cycling enabled P. eryngii to oxidize phenol and the dye reactive black 5, obtaining a high correlation between the rates of OH production and pollutant oxidation.</AbstractText></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Gómez-Toribio</LastName><ForeName>Víctor</ForeName><Initials>V</Initials><AffiliationInfo><Affiliation>Centro de Investigaciones Biológicas, Consejo Superior de Investigaciones Científicas, Madrid, Spain.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>García-Martín</LastName><ForeName>Ana B</ForeName><Initials>AB</Initials></Author><Author ValidYN="Y"><LastName>Martínez</LastName><ForeName>María J</ForeName><Initials>MJ</Initials></Author><Author ValidYN="Y"><LastName>Martínez</LastName><ForeName>Angel T</ForeName><Initials>AT</Initials></Author><Author ValidYN="Y"><LastName>Guillén</LastName><ForeName>Francisco</ForeName><Initials>F</Initials></Author></AuthorList><Language>eng</Language><PublicationTypeList><PublicationType UI="D016428">Journal Article</PublicationType><PublicationType UI="D013485">Research Support, Non-U.S. Gov't</PublicationType></PublicationTypeList><ArticleDate DateType="Electronic"><Year>2009</Year><Month>04</Month><Day>17</Day></ArticleDate></Article><MedlineJournalInfo><Country>United States</Country><MedlineTA>Appl Environ Microbiol</MedlineTA><NlmUniqueID>7605801</NlmUniqueID><ISSNLinking>0099-2240</ISSNLinking></MedlineJournalInfo><ChemicalList><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D001547">Benzaldehydes</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D016227">Benzoquinones</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D004785">Environmental Pollutants</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D005290">Ferric Compounds</NameOfSubstance></Chemical><Chemical><RegistryNumber>1Z701W789S</RegistryNumber><NameOfSubstance UI="C030511">2,6-dimethoxy-1,4-benzoquinone</NameOfSubstance></Chemical><Chemical><RegistryNumber>3352-57-6</RegistryNumber><NameOfSubstance UI="D017665">Hydroxyl Radical</NameOfSubstance></Chemical><Chemical><RegistryNumber>3T006GV98U</RegistryNumber><NameOfSubstance UI="C004532">quinone</NameOfSubstance></Chemical><Chemical><RegistryNumber>42Z2K6ZL8P</RegistryNumber><NameOfSubstance UI="D008345">Manganese</NameOfSubstance></Chemical><Chemical><RegistryNumber>9E7R5L6H31</RegistryNumber><NameOfSubstance UI="D019815">Oxalic Acid</NameOfSubstance></Chemical><Chemical><RegistryNumber>9G34HU7RV0</RegistryNumber><NameOfSubstance UI="D004492">Edetic Acid</NameOfSubstance></Chemical><Chemical><RegistryNumber>9PA5V6656V</RegistryNumber><NameOfSubstance UI="C024896">4-anisaldehyde</NameOfSubstance></Chemical><Chemical><RegistryNumber>KJ3C78Y22Z</RegistryNumber><NameOfSubstance UI="C019179">Fe(III)-EDTA</NameOfSubstance></Chemical></ChemicalList><CitationSubset>IM</CitationSubset><MeshHeadingList><MeshHeading><DescriptorName UI="D001547" MajorTopicYN="N">Benzaldehydes</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D016227" MajorTopicYN="N">Benzoquinones</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D004492" MajorTopicYN="N">Edetic Acid</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D004785" MajorTopicYN="N">Environmental Pollutants</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D005290" 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MajorTopicYN="Y">metabolism</QualifierName></MeshHeading></MeshHeadingList></MedlineCitation><PubmedData><History><PubMedPubDate PubStatus="entrez"><Year>2009</Year><Month>4</Month><Day>21</Day><Hour>9</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="pubmed"><Year>2009</Year><Month>4</Month><Day>21</Day><Hour>9</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="medline"><Year>2009</Year><Month>6</Month><Day>26</Day><Hour>9</Hour><Minute>0</Minute></PubMedPubDate></History><PublicationStatus>ppublish</PublicationStatus><ArticleIdList><ArticleId IdType="pubmed">19376890</ArticleId><ArticleId IdType="pii">AEM.02138-08</ArticleId><ArticleId IdType="doi">10.1128/AEM.02138-08</ArticleId><ArticleId IdType="pmc">PMC2698368</ArticleId></ArticleIdList><ReferenceList><Reference><Citation>Curr Microbiol. 1997 Jan;34(1):1-5</Citation><ArticleIdList><ArticleId IdType="pubmed">8939793</ArticleId></ArticleIdList></Reference><Reference><Citation>Proc Natl Acad Sci U S A. 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García-Martín</name><name sortKey="Guillen, Francisco" sort="Guillen, Francisco" uniqKey="Guillen F" first="Francisco" last="Guillén">Francisco Guillén</name><name sortKey="Martinez, Angel T" sort="Martinez, Angel T" uniqKey="Martinez A" first="Angel T" last="Martínez">Angel T. Martínez</name><name sortKey="Martinez, Maria J" sort="Martinez, Maria J" uniqKey="Martinez M" first="María J" last="Martínez">María J. Martínez</name></noCountry><country name="Espagne"><region name="Communauté de Madrid"><name sortKey="G Mez Toribio, Victor" sort="G Mez Toribio, Victor" uniqKey="G Mez Toribio V" first="Víctor" last="G Mez-Toribio">Víctor G Mez-Toribio</name></region></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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