Arbuscular mycorrhizal inoculum sources influence bacterial, archaeal, and fungal communities' structures of historically dioxin/furan-contaminated soil but not the pollutant dissipation rate.
Identifieur interne : 000812 ( Main/Curation ); précédent : 000811; suivant : 000813Arbuscular mycorrhizal inoculum sources influence bacterial, archaeal, and fungal communities' structures of historically dioxin/furan-contaminated soil but not the pollutant dissipation rate.
Auteurs : H. Meglouli [France] ; A. Lounès-Hadj Sahraoui [France] ; M. Magnin-Robert [France] ; B. Tisserant [France] ; M. Hijri [Canada] ; J. Fontaine [France]Source :
- Mycorrhiza [ 1432-1890 ] ; 2018.
Descripteurs français
- KwdFr :
- Consortiums microbiens (effets des médicaments et des substances chimiques), Dioxines (analyse), Dépollution biologique de l'environnement (MeSH), Furanes (analyse), Medicago sativa (microbiologie), Microbiologie du sol (MeSH), Mycobiome (effets des médicaments et des substances chimiques), Mycorhizes (effets des médicaments et des substances chimiques), Mycorhizes (métabolisme), Plant (croissance et développement), Plant (effets des médicaments et des substances chimiques), Plant (microbiologie), Polluants environnementaux (analyse), Racines de plante (effets des médicaments et des substances chimiques), Racines de plante (microbiologie), Sol (composition chimique).
- MESH :
- analyse : Dioxines, Furanes, Polluants environnementaux.
- composition chimique : Sol.
- croissance et développement : Plant.
- effets des médicaments et des substances chimiques : Consortiums microbiens, Mycobiome, Mycorhizes, Plant, Racines de plante.
- microbiologie : Medicago sativa, Plant, Racines de plante.
- métabolisme : Mycorhizes.
- Dépollution biologique de l'environnement, Microbiologie du sol.
English descriptors
- KwdEn :
- Biodegradation, Environmental (MeSH), Dioxins (analysis), Environmental Pollutants (analysis), Furans (analysis), Medicago sativa (microbiology), Microbial Consortia (drug effects), Mycobiome (drug effects), Mycorrhizae (drug effects), Mycorrhizae (metabolism), Plant Roots (drug effects), Plant Roots (microbiology), Seedlings (drug effects), Seedlings (growth & development), Seedlings (microbiology), Soil (chemistry), Soil Microbiology (MeSH).
- MESH :
- chemical , analysis : Dioxins, Environmental Pollutants, Furans.
- chemical , chemistry : Soil.
- drug effects : Microbial Consortia, Mycobiome, Mycorrhizae, Plant Roots, Seedlings.
- growth & development : Seedlings.
- metabolism : Mycorrhizae.
- microbiology : Medicago sativa, Plant Roots, Seedlings.
- Biodegradation, Environmental, Soil Microbiology.
Abstract
Little is known about the influence of arbuscular mycorrhizal fungi (AMF) inoculum sources on phytoremediation efficiency. Therefore, the aim of this study was to compare the effects of two mycorrhizal inocula (indigenous and commercial inocula) in association with alfalfa and tall fescue on the plant growth, the bacterial, fungal, and archaeal communities, and on the removal of dioxin/furan (PCDD/F) from a historically polluted soil after 24 weeks of culture in microcosms. Our results showed that both mycorrhizal indigenous and commercial inocula were able to colonize plant roots, and the growth response depends on the AMF inoculum. Nevertheless, the improvement of root dry weight in inoculated alfalfa with indigenous inoculum and in inoculated tall fescue with commercial inoculum was clearly correlated with the highest mycorrhizal colonization of the roots in both plant species. The highest shoot dry weight was obtained in inoculated alfalfa and tall fescue with the commercial inoculum. AMF inoculation differently affected the number of bacterial and archaeal OTUs and bacterial diversity, with elevated bacterial and archaeal OTUs and bacterial diversity observed with indigenous inoculum. Mycorrhizal inoculation increases the abundance of bacterial OTUs (in particular with indigenous inoculum) and microbial richness but it does not improve PCDD/F dissipation. Vegetation had no effect on the abundance of microbial OTUs nor on richness but stimulated specific communities (Planctomycetia and Gammaproteobacteria) likely to be involved in the dissipation of PCDD/F. The reduction of toxic equivalency PCDD/F concentration also could be explained by the stimulation of soil microbial activities estimated with dehydrogenase and fluorescein diacetate hydrolase.
DOI: 10.1007/s00572-018-0852-x
PubMed: 29987429
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Meglouli</name><affiliation wicri:level="1"><nlm:affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</nlm:affiliation><country xml:lang="fr">France</country><wicri:regionArea>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais</wicri:regionArea></affiliation></author><author><name sortKey="Lounes Hadj Sahraoui, A" sort="Lounes Hadj Sahraoui, A" uniqKey="Lounes Hadj Sahraoui A" first="A" last="Lounès-Hadj Sahraoui">A. Lounès-Hadj Sahraoui</name><affiliation wicri:level="1"><nlm:affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</nlm:affiliation><country xml:lang="fr">France</country><wicri:regionArea>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais</wicri:regionArea></affiliation></author><author><name sortKey="Magnin Robert, M" sort="Magnin Robert, M" uniqKey="Magnin Robert M" first="M" last="Magnin-Robert">M. Magnin-Robert</name><affiliation wicri:level="1"><nlm:affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</nlm:affiliation><country xml:lang="fr">France</country><wicri:regionArea>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais</wicri:regionArea></affiliation></author><author><name sortKey="Tisserant, B" sort="Tisserant, B" uniqKey="Tisserant B" first="B" last="Tisserant">B. Tisserant</name><affiliation wicri:level="1"><nlm:affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</nlm:affiliation><country xml:lang="fr">France</country><wicri:regionArea>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais</wicri:regionArea></affiliation></author><author><name sortKey="Hijri, M" sort="Hijri, M" uniqKey="Hijri M" first="M" last="Hijri">M. Hijri</name><affiliation wicri:level="1"><nlm:affiliation>Institut de Recherche en Biologie Végétale, Département de Sciences Biologiques, Université de Montréal, Montréal, QC, Canada.</nlm:affiliation><country xml:lang="fr">Canada</country><wicri:regionArea>Institut de Recherche en Biologie Végétale, Département de Sciences Biologiques, Université de Montréal, Montréal, QC</wicri:regionArea></affiliation></author><author><name sortKey="Fontaine, J" sort="Fontaine, J" uniqKey="Fontaine J" first="J" last="Fontaine">J. Fontaine</name><affiliation wicri:level="1"><nlm:affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France. fontaine@univ-littoral.fr.</nlm:affiliation><country xml:lang="fr">France</country><wicri:regionArea>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais</wicri:regionArea></affiliation></author></analytic><series><title level="j">Mycorrhiza</title><idno type="eISSN">1432-1890</idno><imprint><date when="2018" type="published">2018</date></imprint></series></biblStruct></sourceDesc></fileDesc><profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Biodegradation, Environmental (MeSH)</term><term>Dioxins (analysis)</term><term>Environmental Pollutants (analysis)</term><term>Furans (analysis)</term><term>Medicago sativa (microbiology)</term><term>Microbial Consortia (drug effects)</term><term>Mycobiome (drug effects)</term><term>Mycorrhizae (drug effects)</term><term>Mycorrhizae (metabolism)</term><term>Plant Roots (drug effects)</term><term>Plant Roots (microbiology)</term><term>Seedlings (drug effects)</term><term>Seedlings (growth & development)</term><term>Seedlings (microbiology)</term><term>Soil (chemistry)</term><term>Soil Microbiology (MeSH)</term></keywords><keywords scheme="KwdFr" xml:lang="fr"><term>Consortiums microbiens (effets des médicaments et des substances chimiques)</term><term>Dioxines (analyse)</term><term>Dépollution biologique de l'environnement (MeSH)</term><term>Furanes (analyse)</term><term>Medicago sativa (microbiologie)</term><term>Microbiologie du sol (MeSH)</term><term>Mycobiome (effets des médicaments et des substances chimiques)</term><term>Mycorhizes (effets des médicaments et des substances chimiques)</term><term>Mycorhizes (métabolisme)</term><term>Plant (croissance et développement)</term><term>Plant (effets des médicaments et des substances chimiques)</term><term>Plant (microbiologie)</term><term>Polluants environnementaux (analyse)</term><term>Racines de plante (effets des médicaments et des substances chimiques)</term><term>Racines de plante (microbiologie)</term><term>Sol (composition chimique)</term></keywords><keywords scheme="MESH" type="chemical" qualifier="analysis" xml:lang="en"><term>Dioxins</term><term>Environmental Pollutants</term><term>Furans</term></keywords><keywords scheme="MESH" type="chemical" qualifier="chemistry" xml:lang="en"><term>Soil</term></keywords><keywords scheme="MESH" qualifier="analyse" xml:lang="fr"><term>Dioxines</term><term>Furanes</term><term>Polluants environnementaux</term></keywords><keywords scheme="MESH" qualifier="composition chimique" xml:lang="fr"><term>Sol</term></keywords><keywords scheme="MESH" qualifier="croissance et développement" xml:lang="fr"><term>Plant</term></keywords><keywords scheme="MESH" qualifier="drug effects" xml:lang="en"><term>Microbial Consortia</term><term>Mycobiome</term><term>Mycorrhizae</term><term>Plant Roots</term><term>Seedlings</term></keywords><keywords scheme="MESH" qualifier="effets des médicaments et des substances chimiques" xml:lang="fr"><term>Consortiums microbiens</term><term>Mycobiome</term><term>Mycorhizes</term><term>Plant</term><term>Racines de plante</term></keywords><keywords scheme="MESH" qualifier="growth & development" xml:lang="en"><term>Seedlings</term></keywords><keywords scheme="MESH" qualifier="metabolism" xml:lang="en"><term>Mycorrhizae</term></keywords><keywords scheme="MESH" qualifier="microbiologie" xml:lang="fr"><term>Medicago sativa</term><term>Plant</term><term>Racines de plante</term></keywords><keywords scheme="MESH" qualifier="microbiology" xml:lang="en"><term>Medicago sativa</term><term>Plant Roots</term><term>Seedlings</term></keywords><keywords scheme="MESH" qualifier="métabolisme" xml:lang="fr"><term>Mycorhizes</term></keywords><keywords scheme="MESH" xml:lang="en"><term>Biodegradation, Environmental</term><term>Soil Microbiology</term></keywords><keywords scheme="MESH" xml:lang="fr"><term>Dépollution biologique de l'environnement</term><term>Microbiologie du sol</term></keywords></textClass></profileDesc></teiHeader><front><div type="abstract" xml:lang="en">Little is known about the influence of arbuscular mycorrhizal fungi (AMF) inoculum sources on phytoremediation efficiency. Therefore, the aim of this study was to compare the effects of two mycorrhizal inocula (indigenous and commercial inocula) in association with alfalfa and tall fescue on the plant growth, the bacterial, fungal, and archaeal communities, and on the removal of dioxin/furan (PCDD/F) from a historically polluted soil after 24 weeks of culture in microcosms. Our results showed that both mycorrhizal indigenous and commercial inocula were able to colonize plant roots, and the growth response depends on the AMF inoculum. Nevertheless, the improvement of root dry weight in inoculated alfalfa with indigenous inoculum and in inoculated tall fescue with commercial inoculum was clearly correlated with the highest mycorrhizal colonization of the roots in both plant species. The highest shoot dry weight was obtained in inoculated alfalfa and tall fescue with the commercial inoculum. AMF inoculation differently affected the number of bacterial and archaeal OTUs and bacterial diversity, with elevated bacterial and archaeal OTUs and bacterial diversity observed with indigenous inoculum. Mycorrhizal inoculation increases the abundance of bacterial OTUs (in particular with indigenous inoculum) and microbial richness but it does not improve PCDD/F dissipation. Vegetation had no effect on the abundance of microbial OTUs nor on richness but stimulated specific communities (Planctomycetia and Gammaproteobacteria) likely to be involved in the dissipation of PCDD/F. The reduction of toxic equivalency PCDD/F concentration also could be explained by the stimulation of soil microbial activities estimated with dehydrogenase and fluorescein diacetate hydrolase.</div></front></TEI><pubmed><MedlineCitation Status="MEDLINE" Owner="NLM"><PMID Version="1">29987429</PMID><DateCompleted><Year>2019</Year><Month>04</Month><Day>08</Day></DateCompleted><DateRevised><Year>2019</Year><Month>04</Month><Day>08</Day></DateRevised><Article PubModel="Print-Electronic"><Journal><ISSN IssnType="Electronic">1432-1890</ISSN><JournalIssue CitedMedium="Internet"><Volume>28</Volume><Issue>7</Issue><PubDate><Year>2018</Year><Month>Oct</Month></PubDate></JournalIssue><Title>Mycorrhiza</Title><ISOAbbreviation>Mycorrhiza</ISOAbbreviation></Journal><ArticleTitle>Arbuscular mycorrhizal inoculum sources influence bacterial, archaeal, and fungal communities' structures of historically dioxin/furan-contaminated soil but not the pollutant dissipation rate.</ArticleTitle><Pagination><MedlinePgn>635-650</MedlinePgn></Pagination><ELocationID EIdType="doi" ValidYN="Y">10.1007/s00572-018-0852-x</ELocationID><Abstract><AbstractText>Little is known about the influence of arbuscular mycorrhizal fungi (AMF) inoculum sources on phytoremediation efficiency. Therefore, the aim of this study was to compare the effects of two mycorrhizal inocula (indigenous and commercial inocula) in association with alfalfa and tall fescue on the plant growth, the bacterial, fungal, and archaeal communities, and on the removal of dioxin/furan (PCDD/F) from a historically polluted soil after 24 weeks of culture in microcosms. Our results showed that both mycorrhizal indigenous and commercial inocula were able to colonize plant roots, and the growth response depends on the AMF inoculum. Nevertheless, the improvement of root dry weight in inoculated alfalfa with indigenous inoculum and in inoculated tall fescue with commercial inoculum was clearly correlated with the highest mycorrhizal colonization of the roots in both plant species. The highest shoot dry weight was obtained in inoculated alfalfa and tall fescue with the commercial inoculum. AMF inoculation differently affected the number of bacterial and archaeal OTUs and bacterial diversity, with elevated bacterial and archaeal OTUs and bacterial diversity observed with indigenous inoculum. Mycorrhizal inoculation increases the abundance of bacterial OTUs (in particular with indigenous inoculum) and microbial richness but it does not improve PCDD/F dissipation. Vegetation had no effect on the abundance of microbial OTUs nor on richness but stimulated specific communities (Planctomycetia and Gammaproteobacteria) likely to be involved in the dissipation of PCDD/F. The reduction of toxic equivalency PCDD/F concentration also could be explained by the stimulation of soil microbial activities estimated with dehydrogenase and fluorescein diacetate hydrolase.</AbstractText></Abstract><AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Meglouli</LastName><ForeName>H</ForeName><Initials>H</Initials><AffiliationInfo><Affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Lounès-Hadj Sahraoui</LastName><ForeName>A</ForeName><Initials>A</Initials><AffiliationInfo><Affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Magnin-Robert</LastName><ForeName>M</ForeName><Initials>M</Initials><AffiliationInfo><Affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Tisserant</LastName><ForeName>B</ForeName><Initials>B</Initials><AffiliationInfo><Affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Hijri</LastName><ForeName>M</ForeName><Initials>M</Initials><AffiliationInfo><Affiliation>Institut de Recherche en Biologie Végétale, Département de Sciences Biologiques, Université de Montréal, Montréal, QC, Canada.</Affiliation></AffiliationInfo></Author><Author ValidYN="Y"><LastName>Fontaine</LastName><ForeName>J</ForeName><Initials>J</Initials><Identifier Source="ORCID">http://orcid.org/0000-0001-7873-5056</Identifier><AffiliationInfo><Affiliation>Unité de Chimie Environnementale et Interactions sur le Vivant (UCEIV), Université du Littoral Côte d'Opale, SFR Condorcet FR CNRS 3417, 50, Rue Ferdinand Buisson, 62228, Calais, France. fontaine@univ-littoral.fr.</Affiliation></AffiliationInfo></Author></AuthorList><Language>eng</Language><PublicationTypeList><PublicationType UI="D016428">Journal Article</PublicationType></PublicationTypeList><ArticleDate DateType="Electronic"><Year>2018</Year><Month>07</Month><Day>09</Day></ArticleDate></Article><MedlineJournalInfo><Country>Germany</Country><MedlineTA>Mycorrhiza</MedlineTA><NlmUniqueID>100955036</NlmUniqueID><ISSNLinking>0940-6360</ISSNLinking></MedlineJournalInfo><ChemicalList><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D004147">Dioxins</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D004785">Environmental Pollutants</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D005663">Furans</NameOfSubstance></Chemical><Chemical><RegistryNumber>0</RegistryNumber><NameOfSubstance UI="D012987">Soil</NameOfSubstance></Chemical><Chemical><RegistryNumber>UC0XV6A8N9</RegistryNumber><NameOfSubstance UI="C039281">furan</NameOfSubstance></Chemical></ChemicalList><CitationSubset>IM</CitationSubset><MeshHeadingList><MeshHeading><DescriptorName UI="D001673" MajorTopicYN="Y">Biodegradation, Environmental</DescriptorName></MeshHeading><MeshHeading><DescriptorName UI="D004147" MajorTopicYN="N">Dioxins</DescriptorName><QualifierName UI="Q000032" MajorTopicYN="Y">analysis</QualifierName></MeshHeading><MeshHeading><DescriptorName UI="D004785" MajorTopicYN="N">Environmental Pollutants</DescriptorName><QualifierName UI="Q000032" 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