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Degradation of atrazine and 2,4-dichlorophenoxyacetic acid by mycorrhizal fungi at three nitrogen concentrations in vitro.

Identifieur interne : 000D92 ( Main/Curation ); précédent : 000D91; suivant : 000D93

Degradation of atrazine and 2,4-dichlorophenoxyacetic acid by mycorrhizal fungi at three nitrogen concentrations in vitro.

Auteurs : P K Donnelly ; J A Entry ; D L Crawford

Source :

RBID : pubmed:8368851

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English descriptors

Abstract

Nine mycorrhizal fungi and free-living saprophytic microorganisms were tested for their ability to degrade two chlorinated aromatic herbicides at two herbicide concentrations and three nitrogen concentrations. Radiolabelled 2,4-dichlorophenoxyacetic acid (2,4-D) and 2-chloro-4-ethylamino-6-isopropylamino-s-triazine (atrazine) were used as substrates at concentrations of 1 and 4 mM. After 8 weeks, none of the cultures tested grew at 4 mM 2,4-D. However, when the 2,4-D concentration was reduced to 1 mM, Phanerochaete chrysosporium 1767 had the highest level of 2,4-D mineralization and degradation under all nitrogen conditions. All cultures tested grew at both atrazine concentrations. In all cases, the ericoid mycorrhizal fungus Hymenoscyphus ericae 1318 had the highest level of atrazine carbon incorporated into its tissue. In general, as the nitrogen concentration increased, the total herbicide degradation increased. All of the cultures, except for Rhizopogon vinicolor 7534 and Sclerogaster pacificus 9011, showed increased degradation at 4 mM compared with 1 mM atrazine. The ability to degrade these two herbicides thus appeared to be dependent on the fungus and the herbicide, with no correlation to fungal ecotype (mycorrhizal versus free living).

DOI: 10.1128/AEM.59.8.2642-2647.1993
PubMed: 8368851
PubMed Central: PMC182332

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P K Donnelly
<affiliation>
<nlm:affiliation>Department of Bacteriology and Biochemistry, University of Idaho, Moscow 83843.</nlm:affiliation>
<wicri:noCountry code="subField">Moscow 83843</wicri:noCountry>
</affiliation>

Le document en format XML

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<term>2,4-Dichlorophenoxyacetic Acid (metabolism)</term>
<term>Atrazine (metabolism)</term>
<term>Biodegradation, Environmental (MeSH)</term>
<term>Fungi (growth & development)</term>
<term>Fungi (metabolism)</term>
<term>Nitrogen (MeSH)</term>
<term>Plants (microbiology)</term>
<term>Soil Pollutants (metabolism)</term>
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<keywords scheme="KwdFr" xml:lang="fr">
<term>Acide 2,4-dichlorophénoxy-acétique (métabolisme)</term>
<term>Atrazine (métabolisme)</term>
<term>Azote (MeSH)</term>
<term>Champignons (croissance et développement)</term>
<term>Champignons (métabolisme)</term>
<term>Dépollution biologique de l'environnement (MeSH)</term>
<term>Plantes (microbiologie)</term>
<term>Polluants du sol (métabolisme)</term>
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<keywords scheme="MESH" type="chemical" qualifier="metabolism" xml:lang="en">
<term>2,4-Dichlorophenoxyacetic Acid</term>
<term>Atrazine</term>
<term>Soil Pollutants</term>
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<term>Champignons</term>
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<term>Plantes</term>
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<term>Plants</term>
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<keywords scheme="MESH" qualifier="métabolisme" xml:lang="fr">
<term>Acide 2,4-dichlorophénoxy-acétique</term>
<term>Atrazine</term>
<term>Champignons</term>
<term>Polluants du sol</term>
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<keywords scheme="MESH" xml:lang="en">
<term>Biodegradation, Environmental</term>
<term>Nitrogen</term>
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<div type="abstract" xml:lang="en">Nine mycorrhizal fungi and free-living saprophytic microorganisms were tested for their ability to degrade two chlorinated aromatic herbicides at two herbicide concentrations and three nitrogen concentrations. Radiolabelled 2,4-dichlorophenoxyacetic acid (2,4-D) and 2-chloro-4-ethylamino-6-isopropylamino-s-triazine (atrazine) were used as substrates at concentrations of 1 and 4 mM. After 8 weeks, none of the cultures tested grew at 4 mM 2,4-D. However, when the 2,4-D concentration was reduced to 1 mM, Phanerochaete chrysosporium 1767 had the highest level of 2,4-D mineralization and degradation under all nitrogen conditions. All cultures tested grew at both atrazine concentrations. In all cases, the ericoid mycorrhizal fungus Hymenoscyphus ericae 1318 had the highest level of atrazine carbon incorporated into its tissue. In general, as the nitrogen concentration increased, the total herbicide degradation increased. All of the cultures, except for Rhizopogon vinicolor 7534 and Sclerogaster pacificus 9011, showed increased degradation at 4 mM compared with 1 mM atrazine. The ability to degrade these two herbicides thus appeared to be dependent on the fungus and the herbicide, with no correlation to fungal ecotype (mycorrhizal versus free living).</div>
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<Title>Applied and environmental microbiology</Title>
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<ArticleTitle>Degradation of atrazine and 2,4-dichlorophenoxyacetic acid by mycorrhizal fungi at three nitrogen concentrations in vitro.</ArticleTitle>
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<AbstractText>Nine mycorrhizal fungi and free-living saprophytic microorganisms were tested for their ability to degrade two chlorinated aromatic herbicides at two herbicide concentrations and three nitrogen concentrations. Radiolabelled 2,4-dichlorophenoxyacetic acid (2,4-D) and 2-chloro-4-ethylamino-6-isopropylamino-s-triazine (atrazine) were used as substrates at concentrations of 1 and 4 mM. After 8 weeks, none of the cultures tested grew at 4 mM 2,4-D. However, when the 2,4-D concentration was reduced to 1 mM, Phanerochaete chrysosporium 1767 had the highest level of 2,4-D mineralization and degradation under all nitrogen conditions. All cultures tested grew at both atrazine concentrations. In all cases, the ericoid mycorrhizal fungus Hymenoscyphus ericae 1318 had the highest level of atrazine carbon incorporated into its tissue. In general, as the nitrogen concentration increased, the total herbicide degradation increased. All of the cultures, except for Rhizopogon vinicolor 7534 and Sclerogaster pacificus 9011, showed increased degradation at 4 mM compared with 1 mM atrazine. The ability to degrade these two herbicides thus appeared to be dependent on the fungus and the herbicide, with no correlation to fungal ecotype (mycorrhizal versus free living).</AbstractText>
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<Citation>Microbiol Sci. 1987 Oct;4(10):300-3</Citation>
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<ArticleId IdType="pubmed">3153591</ArticleId>
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<Citation>Appl Environ Microbiol. 1989 Oct;55(10):2717-9</Citation>
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