Winery biomass waste degradation by sequential sonication and mixed fungal enzyme treatments.
Identifieur interne : 000143 ( Main/Exploration ); précédent : 000142; suivant : 000144Winery biomass waste degradation by sequential sonication and mixed fungal enzyme treatments.
Auteurs : Avinash V. Karpe [Australie] ; Vijay V. Dhamale [Australie] ; Paul D. Morrison [Australie] ; David J. Beale [Australie] ; Ian H. Harding [Australie] ; Enzo A. Palombo [Australie]Source :
- Fungal genetics and biology : FG & B [ 1096-0937 ] ; 2017.
Descripteurs français
- KwdFr :
- Acide gallique (analyse), Acide gallique (métabolisme), Aspergillus niger (enzymologie), Aspergillus niger (métabolisme), Biomasse (MeSH), Cellulase (métabolisme), Champignons (enzymologie), Champignons (métabolisme), Dépollution biologique de l'environnement (MeSH), Fermentation (effets des médicaments et des substances chimiques), Glycolates (analyse), Glycolates (métabolisme), Hydrolases (métabolisme), Laccase (métabolisme), Lignine (métabolisme), Métabolomique (MeSH), Oxidoreductases (métabolisme), Penicillium chrysogenum (enzymologie), Penicillium chrysogenum (métabolisme), Peroxidases (métabolisme), Sonication (MeSH), Vin (MeSH), Vitis (métabolisme).
- MESH :
- analyse : Acide gallique, Glycolates.
- effets des médicaments et des substances chimiques : Fermentation.
- enzymologie : Aspergillus niger, Champignons, Penicillium chrysogenum.
- métabolisme : Acide gallique, Aspergillus niger, Cellulase, Champignons, Glycolates, Hydrolases, Laccase, Lignine, Oxidoreductases, Penicillium chrysogenum, Peroxidases, Vitis.
- Biomasse, Dépollution biologique de l'environnement, Métabolomique, Sonication, Vin.
English descriptors
- KwdEn :
- Aspergillus niger (enzymology), Aspergillus niger (metabolism), Biodegradation, Environmental (MeSH), Biomass (MeSH), Cellulase (metabolism), Fermentation (drug effects), Fungi (enzymology), Fungi (metabolism), Gallic Acid (analysis), Gallic Acid (metabolism), Glycolates (analysis), Glycolates (metabolism), Hydrolases (metabolism), Laccase (metabolism), Lignin (metabolism), Metabolomics (MeSH), Oxidoreductases (metabolism), Penicillium chrysogenum (enzymology), Penicillium chrysogenum (metabolism), Peroxidases (metabolism), Sonication (MeSH), Vitis (metabolism), Wine (MeSH).
- MESH :
- chemical , analysis : Gallic Acid, Glycolates.
- chemical , metabolism : Cellulase, Gallic Acid, Glycolates, Hydrolases, Laccase, Lignin, Oxidoreductases, Peroxidases.
- drug effects : Fermentation.
- enzymology : Aspergillus niger, Fungi, Penicillium chrysogenum.
- metabolism : Aspergillus niger, Fungi, Penicillium chrysogenum, Vitis.
- Biodegradation, Environmental, Biomass, Metabolomics, Sonication, Wine.
Abstract
To increase the efficiency of winery-derived biomass biodegradation, grape pomace was ultrasonicated for 20min in the presence of 0.25M, 0.5Mand1.0MKOH and 1.0MNaOH. This was followed by treatment with a 1:1 (v/v) mix of crude enzyme preparation derived from Phanerochaete chrysosporium and Trametes versicolor for 18h and a further 18h treatment with a 60:14:4:2 percent ratio combination of enzymes derived from Aspergillus niger: Penicillium chrysogenum: Trichoderma harzianum: P. citrinum, repsectively. Process efficiency was evaluated by its comparison to biological only mixed fungal degradation over 16days. Ultrasonication treatment with 0.5MKOH followed by mixed enzyme treatment yielded the highest lignin degradation of about 13%. Cellulase, β-glucosidase, xylanase, laccase and lignin peroxidase activities of 77.9, 476, 5,390.5, 66.7 and 29,230.7U/mL, respectively, were observed during biomass degradation. Gas chromatography-mass spectrometry (GC-MS) analysis of the degraded material identified commercially important compounds such as gallic acid, lithocholic acid, glycolic acid and lactic acid which were generated in considerable quantities. Thus, the combination of sonication pre-treatment and enzymatic degradation has the potential to considerably improve the breakdown of agricultural biomass and produce commercially useful compounds in markedly less time (<40h) with respect to biological only degradation (16days).
DOI: 10.1016/j.fgb.2016.08.008
PubMed: 27599392
Affiliations:
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Karpe</name><affiliation wicri:level="1"><nlm:affiliation>Department of Chemistry and Biotechnology, Swinburne University of Technology, PO Box 218, Hawthorn, Victoria 3122, Australia; Land and Water, Commonwealth Scientific and Industrial Research Organization (CSIRO), PO Box 2583, Brisbane, Queensland 4001, Australia.</nlm:affiliation><country xml:lang="fr">Australie</country><wicri:regionArea>Department of Chemistry and Biotechnology, Swinburne University of Technology, PO Box 218, Hawthorn, Victoria 3122, Australia; Land and Water, Commonwealth Scientific and Industrial Research Organization (CSIRO), PO Box 2583, Brisbane, Queensland 4001</wicri:regionArea><wicri:noRegion>Queensland 4001</wicri:noRegion></affiliation></author><author><name sortKey="Dhamale, Vijay V" sort="Dhamale, Vijay V" uniqKey="Dhamale V" first="Vijay V" last="Dhamale">Vijay V. 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This was followed by treatment with a 1:1 (v/v) mix of crude enzyme preparation derived from Phanerochaete chrysosporium and Trametes versicolor for 18h and a further 18h treatment with a 60:14:4:2 percent ratio combination of enzymes derived from Aspergillus niger: Penicillium chrysogenum: Trichoderma harzianum: P. citrinum, repsectively. Process efficiency was evaluated by its comparison to biological only mixed fungal degradation over 16days. Ultrasonication treatment with 0.5MKOH followed by mixed enzyme treatment yielded the highest lignin degradation of about 13%. Cellulase, β-glucosidase, xylanase, laccase and lignin peroxidase activities of 77.9, 476, 5,390.5, 66.7 and 29,230.7U/mL, respectively, were observed during biomass degradation. Gas chromatography-mass spectrometry (GC-MS) analysis of the degraded material identified commercially important compounds such as gallic acid, lithocholic acid, glycolic acid and lactic acid which were generated in considerable quantities. Thus, the combination of sonication pre-treatment and enzymatic degradation has the potential to considerably improve the breakdown of agricultural biomass and produce commercially useful compounds in markedly less time (<40h) with respect to biological only degradation (16days).</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" Owner="NLM"><PMID Version="1">27599392</PMID><DateCompleted><Year>2018</Year><Month>02</Month><Day>14</Day></DateCompleted><DateRevised><Year>2018</Year><Month>02</Month><Day>26</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1096-0937</ISSN><JournalIssue CitedMedium="Internet"><Volume>102</Volume><PubDate><Year>2017</Year><Month>05</Month></PubDate></JournalIssue><Title>Fungal genetics and biology : FG & B</Title><ISOAbbreviation>Fungal Genet Biol</ISOAbbreviation></Journal><ArticleTitle>Winery biomass waste degradation by sequential sonication and mixed fungal enzyme treatments.</ArticleTitle><Pagination><MedlinePgn>22-30</MedlinePgn></Pagination><ELocationID EIdType="pii" ValidYN="Y">S1087-1845(16)30098-6</ELocationID><ELocationID EIdType="doi" ValidYN="Y">10.1016/j.fgb.2016.08.008</ELocationID><Abstract><AbstractText>To increase the efficiency of winery-derived biomass biodegradation, grape pomace was ultrasonicated for 20min in the presence of 0.25M, 0.5Mand1.0MKOH and 1.0MNaOH. This was followed by treatment with a 1:1 (v/v) mix of crude enzyme preparation derived from Phanerochaete chrysosporium and Trametes versicolor for 18h and a further 18h treatment with a 60:14:4:2 percent ratio combination of enzymes derived from Aspergillus niger: Penicillium chrysogenum: Trichoderma harzianum: P. citrinum, repsectively. Process efficiency was evaluated by its comparison to biological only mixed fungal degradation over 16days. Ultrasonication treatment with 0.5MKOH followed by mixed enzyme treatment yielded the highest lignin degradation of about 13%. Cellulase, β-glucosidase, xylanase, laccase and lignin peroxidase activities of 77.9, 476, 5,390.5, 66.7 and 29,230.7U/mL, respectively, were observed during biomass degradation. Gas chromatography-mass spectrometry (GC-MS) analysis of the degraded material identified commercially important compounds such as gallic acid, lithocholic acid, glycolic acid and lactic acid which were generated in considerable quantities. Thus, the combination of sonication pre-treatment and enzymatic degradation has the potential to considerably improve the breakdown of agricultural biomass and produce commercially useful compounds in markedly less time (<40h) with respect to biological only degradation (16days).</AbstractText><CopyrightInformation>Copyright © 2016 Elsevier Inc. All rights reserved.</CopyrightInformation></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Karpe</LastName><ForeName>Avinash V</ForeName><Initials>AV</Initials><AffiliationInfo><Affiliation>Department of Chemistry and Biotechnology, Swinburne University of Technology, PO Box 218, Hawthorn, Victoria 3122, Australia; Land and Water, Commonwealth Scientific and Industrial Research Organization (CSIRO), PO Box 2583, Brisbane, Queensland 4001, Australia.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Dhamale</LastName><ForeName>Vijay V</ForeName><Initials>VV</Initials><AffiliationInfo><Affiliation>Department of Chemistry and Biotechnology, Swinburne University of Technology, PO Box 218, Hawthorn, Victoria 3122, Australia.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Morrison</LastName><ForeName>Paul D</ForeName><Initials>PD</Initials><AffiliationInfo><Affiliation>Australian Centre for Research on Separation Science, School of Applied Sciences, RMIT University, PO Box 2547, Melbourne, Victoria 3000, Australia.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Beale</LastName><ForeName>David J</ForeName><Initials>DJ</Initials><AffiliationInfo><Affiliation>Land and Water, Commonwealth Scientific and Industrial Research Organization (CSIRO), PO Box 2583, Brisbane, Queensland 4001, Australia.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Harding</LastName><ForeName>Ian H</ForeName><Initials>IH</Initials><AffiliationInfo><Affiliation>Department of Chemistry and Biotechnology, Swinburne University of Technology, PO Box 218, Hawthorn, Victoria 3122, Australia.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Palombo</LastName><ForeName>Enzo A</ForeName><Initials>EA</Initials><AffiliationInfo><Affiliation>Department of Chemistry and Biotechnology, Swinburne University of Technology, PO Box 218, Hawthorn, Victoria 3122, Australia. Electronic address: epalombo@swin.edu.au.</Affiliation></AffiliationInfo></Author></AuthorList><Language>eng</Language><PublicationTypeList><PublicationType UI="D016428">Journal Article</PublicationType></PublicationTypeList><ArticleDate DateType="Electronic"><Year>2016</Year><Month>09</Month><Day>04</Day></ArticleDate></Article><MedlineJournalInfo><Country>United States</Country><MedlineTA>Fungal Genet Biol</MedlineTA><NlmUniqueID>9607601</NlmUniqueID><ISSNLinking>1087-1845</ISSNLinking></MedlineJournalInfo><ChemicalList><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D006016">Glycolates</NameOfSubstance></Chemical><Chemical><RegistryNumber>0WT12SX38S</RegistryNumber><NameOfSubstance UI="C031149">glycolic acid</NameOfSubstance></Chemical><Chemical><RegistryNumber>632XD903SP</RegistryNumber><NameOfSubstance UI="D005707">Gallic Acid</NameOfSubstance></Chemical><Chemical><RegistryNumber>9005-53-2</RegistryNumber><NameOfSubstance UI="D008031">Lignin</NameOfSubstance></Chemical><Chemical><RegistryNumber>EC 1.-</RegistryNumber><NameOfSubstance UI="D010088">Oxidoreductases</NameOfSubstance></Chemical><Chemical><RegistryNumber>EC 1.10.3.2</RegistryNumber><NameOfSubstance UI="D042845">Laccase</NameOfSubstance></Chemical><Chemical><RegistryNumber>EC 1.11.1.-</RegistryNumber><NameOfSubstance UI="D010544">Peroxidases</NameOfSubstance></Chemical><Chemical><RegistryNumber>EC 1.11.1.-</RegistryNumber><NameOfSubstance UI="C042858">lignin peroxidase</NameOfSubstance></Chemical><Chemical><RegistryNumber>EC 3.-</RegistryNumber><NameOfSubstance UI="D006867">Hydrolases</NameOfSubstance></Chemical><Chemical><RegistryNumber>EC 3.2.1.4</RegistryNumber><NameOfSubstance UI="D002480">Cellulase</NameOfSubstance></Chemical></ChemicalList><CitationSubset>IM</CitationSubset><MeshHeadingList><MeshHeading><DescriptorName UI="D001234" MajorTopicYN="N">Aspergillus niger</DescriptorName><QualifierName UI="Q000201" MajorTopicYN="N">enzymology</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D001673" MajorTopicYN="Y">Biodegradation, Environmental</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D018533" MajorTopicYN="Y">Biomass</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D002480" MajorTopicYN="N">Cellulase</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D005285" MajorTopicYN="N">Fermentation</DescriptorName><QualifierName UI="Q000187" MajorTopicYN="N">drug effects</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D005658" MajorTopicYN="N">Fungi</DescriptorName><QualifierName UI="Q000201" MajorTopicYN="Y">enzymology</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D005707" MajorTopicYN="N">Gallic Acid</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="N">analysis</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D006016" MajorTopicYN="N">Glycolates</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="N">analysis</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D006867" MajorTopicYN="N">Hydrolases</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D042845" MajorTopicYN="N">Laccase</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D008031" MajorTopicYN="N">Lignin</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D055432" MajorTopicYN="N">Metabolomics</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D010088" MajorTopicYN="N">Oxidoreductases</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D010408" MajorTopicYN="N">Penicillium chrysogenum</DescriptorName><QualifierName UI="Q000201" MajorTopicYN="N">enzymology</QualifierName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D010544" MajorTopicYN="N">Peroxidases</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D013010" MajorTopicYN="Y">Sonication</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D027843" MajorTopicYN="N">Vitis</DescriptorName><QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D014920" MajorTopicYN="N">Wine</DescriptorName></MeshHeading></MeshHeadingList><KeywordList Owner="NOTNLM"><Keyword MajorTopicYN="Y">Enzyme activities</Keyword><Keyword MajorTopicYN="Y">Fungi</Keyword><Keyword MajorTopicYN="Y">Grape biomass</Keyword><Keyword MajorTopicYN="Y">Lignin degradation</Keyword><Keyword MajorTopicYN="Y">Metabolomics</Keyword><Keyword MajorTopicYN="Y">Ultrasonication</Keyword></KeywordList></MedlineCitation><PubmedData><History><PubMedPubDate PubStatus="received"><Year>2016</Year><Month>03</Month><Day>16</Day></PubMedPubDate><PubMedPubDate PubStatus="revised"><Year>2016</Year><Month>08</Month><Day>25</Day></PubMedPubDate><PubMedPubDate PubStatus="accepted"><Year>2016</Year><Month>08</Month><Day>30</Day></PubMedPubDate><PubMedPubDate PubStatus="pubmed"><Year>2016</Year><Month>9</Month><Day>8</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="medline"><Year>2018</Year><Month>2</Month><Day>15</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate><PubMedPubDate PubStatus="entrez"><Year>2016</Year><Month>9</Month><Day>8</Day><Hour>6</Hour><Minute>0</Minute></PubMedPubDate></History><PublicationStatus>ppublish</PublicationStatus><ArticleIdList><ArticleId IdType="pubmed">27599392</ArticleId><ArticleId IdType="pii">S1087-1845(16)30098-6</ArticleId><ArticleId IdType="doi">10.1016/j.fgb.2016.08.008</ArticleId></ArticleIdList></PubmedData></pubmed><affiliations><list><country><li>Australie</li></country></list><tree><country name="Australie"><noRegion><name sortKey="Karpe, Avinash V" sort="Karpe, Avinash V" uniqKey="Karpe A" first="Avinash V" last="Karpe">Avinash V. Karpe</name></noRegion><name sortKey="Beale, David J" sort="Beale, David J" uniqKey="Beale D" first="David J" last="Beale">David J. Beale</name><name sortKey="Dhamale, Vijay V" sort="Dhamale, Vijay V" uniqKey="Dhamale V" first="Vijay V" last="Dhamale">Vijay V. Dhamale</name><name sortKey="Harding, Ian H" sort="Harding, Ian H" uniqKey="Harding I" first="Ian H" last="Harding">Ian H. Harding</name><name sortKey="Morrison, Paul D" sort="Morrison, Paul D" uniqKey="Morrison P" first="Paul D" last="Morrison">Paul D. Morrison</name><name sortKey="Palombo, Enzo A" sort="Palombo, Enzo A" uniqKey="Palombo E" first="Enzo A" last="Palombo">Enzo A. Palombo</name></country></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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