Comparative biodegradation of alkyl halide insecticides by the white rot fungus, Phanerochaete chrysosporium (BKM-F-1767).
Identifieur interne : 000F62 ( Main/Exploration ); précédent : 000F61; suivant : 000F63Comparative biodegradation of alkyl halide insecticides by the white rot fungus, Phanerochaete chrysosporium (BKM-F-1767).
Auteurs : D W Kennedy ; S D Aust ; J A BumpusSource :
- Applied and environmental microbiology [ 0099-2240 ] ; 1990.
Descripteurs français
- KwdFr :
- Aldrine (métabolisme), Basidiomycota (métabolisme), Chlordane (métabolisme), Dieldrine (métabolisme), Dépollution biologique de l'environnement (MeSH), Heptachlore (métabolisme), Insecticides (métabolisme), Lindane (métabolisme), Mirex (métabolisme), Polluants chimiques de l'eau (MeSH), Polluants du sol (MeSH).
- MESH :
English descriptors
- KwdEn :
- MESH :
- chemical , metabolism : Aldrin, Chlordan, Dieldrin, Heptachlor, Hexachlorocyclohexane, Insecticides, Mirex.
- metabolism : Basidiomycota.
- Biodegradation, Environmental, Soil Pollutants, Water Pollutants, Chemical.
Abstract
The ability of Phanerochaete chrysosporium to degrade six alkyl halide insecticides (aldrin, dieldrin, heptachlor, chlordane, lindane, and mirex) in liquid and soil-corncob matrices was compared by using 14C-labeled compounds. Of these, only [14C]lindane and [14C]chlordane underwent extensive biodegradation, as evidenced by the fact that 9.4 to 23.4% of these compounds were degraded to 14CO2 in 30 days in liquid cultures and 60 days in soil-corncob cultures inoculated with P. chrysosporium. Although [14C]aldrin, [14C]dieldrin, [14C]heptachlor, and [14D]mirex were poorly mineralized, substantial bioconversion occurred, as determined by substrate disappearance and metabolite formation. Nonbiological disappearance was observed only with chlordane and heptachlor.
DOI: 10.1128/AEM.56.8.2347-2353.1990
PubMed: 1698348
PubMed Central: PMC184732
Affiliations:
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Of these, only [14C]lindane and [14C]chlordane underwent extensive biodegradation, as evidenced by the fact that 9.4 to 23.4% of these compounds were degraded to 14CO2 in 30 days in liquid cultures and 60 days in soil-corncob cultures inoculated with P. chrysosporium. Although [14C]aldrin, [14C]dieldrin, [14C]heptachlor, and [14D]mirex were poorly mineralized, substantial bioconversion occurred, as determined by substrate disappearance and metabolite formation. Nonbiological disappearance was observed only with chlordane and heptachlor.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" Owner="NLM"><PMID Version="1">1698348</PMID><DateCompleted><Year>1990</Year><Month>10</Month><Day>26</Day></DateCompleted><DateRevised><Year>2020</Year><Month>07</Month><Day>24</Day></DateRevised><Article PubModel="Print"><Journal><ISSN IssnType="Print">0099-2240</ISSN><JournalIssue CitedMedium="Print"><Volume>56</Volume><Issue>8</Issue><PubDate><Year>1990</Year><Month>Aug</Month></PubDate></JournalIssue><Title>Applied and environmental microbiology</Title><ISOAbbreviation>Appl Environ Microbiol</ISOAbbreviation></Journal><ArticleTitle>Comparative biodegradation of alkyl halide insecticides by the white rot fungus, Phanerochaete chrysosporium (BKM-F-1767).</ArticleTitle><Pagination><MedlinePgn>2347-53</MedlinePgn></Pagination><Abstract><AbstractText>The ability of Phanerochaete chrysosporium to degrade six alkyl halide insecticides (aldrin, dieldrin, heptachlor, chlordane, lindane, and mirex) in liquid and soil-corncob matrices was compared by using 14C-labeled compounds. Of these, only [14C]lindane and [14C]chlordane underwent extensive biodegradation, as evidenced by the fact that 9.4 to 23.4% of these compounds were degraded to 14CO2 in 30 days in liquid cultures and 60 days in soil-corncob cultures inoculated with P. chrysosporium. Although [14C]aldrin, [14C]dieldrin, [14C]heptachlor, and [14D]mirex were poorly mineralized, substantial bioconversion occurred, as determined by substrate disappearance and metabolite formation. Nonbiological disappearance was observed only with chlordane and heptachlor.</AbstractText></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Kennedy</LastName><ForeName>D W</ForeName><Initials>DW</Initials><AffiliationInfo><Affiliation>Biotechnology Center, Utah State University, Logan 84322-4430.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Aust</LastName><ForeName>S D</ForeName><Initials>SD</Initials></Author><Author ValidYN="Y"><LastName>Bumpus</LastName><ForeName>J A</ForeName><Initials>JA</Initials></Author></AuthorList><Language>eng</Language><GrantList CompleteYN="Y"><Grant><GrantID>ES 04922</GrantID><Acronym>ES</Acronym><Agency>NIEHS NIH HHS</Agency><Country>United States</Country></Grant></GrantList><PublicationTypeList><PublicationType UI="D003160">Comparative Study</PublicationType><PublicationType UI="D016428">Journal Article</PublicationType><PublicationType UI="D013487">Research Support, U.S. Gov't, 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IdType="pubmed">5646384</ArticleId></ArticleIdList></Reference></ReferenceList></PubmedData></pubmed><affiliations><list></list><tree><noCountry><name sortKey="Aust, S D" sort="Aust, S D" uniqKey="Aust S" first="S D" last="Aust">S D Aust</name><name sortKey="Bumpus, J A" sort="Bumpus, J A" uniqKey="Bumpus J" first="J A" last="Bumpus">J A Bumpus</name><name sortKey="Kennedy, D W" sort="Kennedy, D W" uniqKey="Kennedy D" first="D W" last="Kennedy">D W Kennedy</name></noCountry></tree></affiliations></record>Pour manipuler ce document sous Unix (Dilib)
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