Arbuscular mycorrhizal fungi alleviate the heavy metal toxicity on sunflower (Helianthus annuus L.) plants cultivated on a heavily contaminated field soil at a WEEE-recycling site.
Identifieur interne : 000974 ( Main/Corpus ); précédent : 000973; suivant : 000975Arbuscular mycorrhizal fungi alleviate the heavy metal toxicity on sunflower (Helianthus annuus L.) plants cultivated on a heavily contaminated field soil at a WEEE-recycling site.
Auteurs : Yu Zhang ; Junli Hu ; Jianfeng Bai ; Junhua Wang ; Rui Yin ; Jingwei Wang ; Xiangui LinSource :
- The Science of the total environment [ 1879-1026 ] ; 2018.
English descriptors
- KwdEn :
- MESH :
- chemical , metabolism : Metals, Heavy, Soil Pollutants.
- drug effects : Helianthus.
- metabolism : Mycorrhizae.
- microbiology : Helianthus.
- chemical , toxicity : Metals, Heavy, Soil Pollutants.
- Biodegradation, Environmental, Plant Roots, Soil.
Abstract
An 8-week pot experiment was conducted to investigate the growth and responses of sunflower (Helianthus annuus L.) to arbuscular mycorrhizal (AM) fungal inoculations on a heavily heavy metal (HM)-contaminated (H) soil and a lightly HM-enriched (L) soil, both of which were collected from a waste electrical and electronic equipment (WEEE)-recycling site. Compared with the L soil, the H soil induced significantly larger (P<0.05) concentrations of Cd, Cu, Pb, Cr, Zn and Ni in sunflower (except for root Cr and shoot Ni), which impaired the thylakoid lamellar folds in leaves. The biomasses and P concentrations of shoots and roots, as well as the total P acquisitions per pot were all significantly decreased (P<0.05). Both Funneliformis mosseae (Fm) and F. caledonium (Fc) inoculation significantly increased (P<0.05) root mycorrhizal colonization. For the L soil, AM fungal inoculations had no significant effects on the soil-plant system, except for a decrease of soil pH and increases of soil available P and DTPA-extractable Zn concentrations with the Fm-inoculated treatment. For the H soil, however, AM fungal inoculations significantly increased (P<0.05) the biomasses and P concentrations of shoots and roots, as well as the total P acquisitions per pot, and significantly reduced (P<0.05) the concentrations of HMs in shoots (except for Cu and Pb with Fm- and Fc- inoculated treatments, respectively) and alleviated the toxicity symptoms of HMs in thylakoid structure of leaves. AM fungal inoculations in the H soil also significantly increased (P<0.05) the shoot uptake of HMs (except for Cr), and tended to decrease the total concentrations of HMs in soils. This suggests the potential application of AM fungi for both reducing HM stress and promoting phytoextraction of HM-contaminated soils caused by WEEE recycling.
DOI: 10.1016/j.scitotenv.2018.01.331
PubMed: 29438937
Links to Exploration step
pubmed:29438937Le document en format XML
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<author><name sortKey="Zhang, Yu" sort="Zhang, Yu" uniqKey="Zhang Y" first="Yu" last="Zhang">Yu Zhang</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</nlm:affiliation>
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<author><name sortKey="Hu, Junli" sort="Hu, Junli" uniqKey="Hu J" first="Junli" last="Hu">Junli Hu</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China. Electronic address: jlhu@issas.ac.cn.</nlm:affiliation>
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<author><name sortKey="Bai, Jianfeng" sort="Bai, Jianfeng" uniqKey="Bai J" first="Jianfeng" last="Bai">Jianfeng Bai</name>
<affiliation><nlm:affiliation>Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China. Electronic address: jfbai@sspu.edu.cn.</nlm:affiliation>
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<author><name sortKey="Wang, Junhua" sort="Wang, Junhua" uniqKey="Wang J" first="Junhua" last="Wang">Junhua Wang</name>
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<author><name sortKey="Yin, Rui" sort="Yin, Rui" uniqKey="Yin R" first="Rui" last="Yin">Rui Yin</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.</nlm:affiliation>
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<author><name sortKey="Wang, Jingwei" sort="Wang, Jingwei" uniqKey="Wang J" first="Jingwei" last="Wang">Jingwei Wang</name>
<affiliation><nlm:affiliation>Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</nlm:affiliation>
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<author><name sortKey="Lin, Xiangui" sort="Lin, Xiangui" uniqKey="Lin X" first="Xiangui" last="Lin">Xiangui Lin</name>
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<sourceDesc><biblStruct><analytic><title xml:lang="en">Arbuscular mycorrhizal fungi alleviate the heavy metal toxicity on sunflower (Helianthus annuus L.) plants cultivated on a heavily contaminated field soil at a WEEE-recycling site.</title>
<author><name sortKey="Zhang, Yu" sort="Zhang, Yu" uniqKey="Zhang Y" first="Yu" last="Zhang">Yu Zhang</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China; Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</nlm:affiliation>
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</author>
<author><name sortKey="Hu, Junli" sort="Hu, Junli" uniqKey="Hu J" first="Junli" last="Hu">Junli Hu</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China. Electronic address: jlhu@issas.ac.cn.</nlm:affiliation>
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<author><name sortKey="Bai, Jianfeng" sort="Bai, Jianfeng" uniqKey="Bai J" first="Jianfeng" last="Bai">Jianfeng Bai</name>
<affiliation><nlm:affiliation>Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China. Electronic address: jfbai@sspu.edu.cn.</nlm:affiliation>
</affiliation>
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<author><name sortKey="Wang, Junhua" sort="Wang, Junhua" uniqKey="Wang J" first="Junhua" last="Wang">Junhua Wang</name>
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<author><name sortKey="Yin, Rui" sort="Yin, Rui" uniqKey="Yin R" first="Rui" last="Yin">Rui Yin</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.</nlm:affiliation>
</affiliation>
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<author><name sortKey="Wang, Jingwei" sort="Wang, Jingwei" uniqKey="Wang J" first="Jingwei" last="Wang">Jingwei Wang</name>
<affiliation><nlm:affiliation>Shanghai Collaborative Innovation Centre for WEEE Recycling, WEEE Research Centre of Shanghai Polytechnic University, Shanghai 201209, China.</nlm:affiliation>
</affiliation>
</author>
<author><name sortKey="Lin, Xiangui" sort="Lin, Xiangui" uniqKey="Lin X" first="Xiangui" last="Lin">Xiangui Lin</name>
<affiliation><nlm:affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.</nlm:affiliation>
</affiliation>
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<series><title level="j">The Science of the total environment</title>
<idno type="eISSN">1879-1026</idno>
<imprint><date when="2018" type="published">2018</date>
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<profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Biodegradation, Environmental (MeSH)</term>
<term>Helianthus (drug effects)</term>
<term>Helianthus (microbiology)</term>
<term>Metals, Heavy (metabolism)</term>
<term>Metals, Heavy (toxicity)</term>
<term>Mycorrhizae (metabolism)</term>
<term>Plant Roots (MeSH)</term>
<term>Soil (MeSH)</term>
<term>Soil Pollutants (metabolism)</term>
<term>Soil Pollutants (toxicity)</term>
</keywords>
<keywords scheme="MESH" type="chemical" qualifier="metabolism" xml:lang="en"><term>Metals, Heavy</term>
<term>Soil Pollutants</term>
</keywords>
<keywords scheme="MESH" qualifier="drug effects" xml:lang="en"><term>Helianthus</term>
</keywords>
<keywords scheme="MESH" qualifier="metabolism" xml:lang="en"><term>Mycorrhizae</term>
</keywords>
<keywords scheme="MESH" qualifier="microbiology" xml:lang="en"><term>Helianthus</term>
</keywords>
<keywords scheme="MESH" type="chemical" qualifier="toxicity" xml:lang="en"><term>Metals, Heavy</term>
<term>Soil Pollutants</term>
</keywords>
<keywords scheme="MESH" xml:lang="en"><term>Biodegradation, Environmental</term>
<term>Plant Roots</term>
<term>Soil</term>
</keywords>
</textClass>
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<front><div type="abstract" xml:lang="en">An 8-week pot experiment was conducted to investigate the growth and responses of sunflower (Helianthus annuus L.) to arbuscular mycorrhizal (AM) fungal inoculations on a heavily heavy metal (HM)-contaminated (H) soil and a lightly HM-enriched (L) soil, both of which were collected from a waste electrical and electronic equipment (WEEE)-recycling site. Compared with the L soil, the H soil induced significantly larger (P<0.05) concentrations of Cd, Cu, Pb, Cr, Zn and Ni in sunflower (except for root Cr and shoot Ni), which impaired the thylakoid lamellar folds in leaves. The biomasses and P concentrations of shoots and roots, as well as the total P acquisitions per pot were all significantly decreased (P<0.05). Both Funneliformis mosseae (Fm) and F. caledonium (Fc) inoculation significantly increased (P<0.05) root mycorrhizal colonization. For the L soil, AM fungal inoculations had no significant effects on the soil-plant system, except for a decrease of soil pH and increases of soil available P and DTPA-extractable Zn concentrations with the Fm-inoculated treatment. For the H soil, however, AM fungal inoculations significantly increased (P<0.05) the biomasses and P concentrations of shoots and roots, as well as the total P acquisitions per pot, and significantly reduced (P<0.05) the concentrations of HMs in shoots (except for Cu and Pb with Fm- and Fc- inoculated treatments, respectively) and alleviated the toxicity symptoms of HMs in thylakoid structure of leaves. AM fungal inoculations in the H soil also significantly increased (P<0.05) the shoot uptake of HMs (except for Cr), and tended to decrease the total concentrations of HMs in soils. This suggests the potential application of AM fungi for both reducing HM stress and promoting phytoextraction of HM-contaminated soils caused by WEEE recycling.</div>
</front>
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<Abstract><AbstractText>An 8-week pot experiment was conducted to investigate the growth and responses of sunflower (Helianthus annuus L.) to arbuscular mycorrhizal (AM) fungal inoculations on a heavily heavy metal (HM)-contaminated (H) soil and a lightly HM-enriched (L) soil, both of which were collected from a waste electrical and electronic equipment (WEEE)-recycling site. Compared with the L soil, the H soil induced significantly larger (P<0.05) concentrations of Cd, Cu, Pb, Cr, Zn and Ni in sunflower (except for root Cr and shoot Ni), which impaired the thylakoid lamellar folds in leaves. The biomasses and P concentrations of shoots and roots, as well as the total P acquisitions per pot were all significantly decreased (P<0.05). Both Funneliformis mosseae (Fm) and F. caledonium (Fc) inoculation significantly increased (P<0.05) root mycorrhizal colonization. For the L soil, AM fungal inoculations had no significant effects on the soil-plant system, except for a decrease of soil pH and increases of soil available P and DTPA-extractable Zn concentrations with the Fm-inoculated treatment. For the H soil, however, AM fungal inoculations significantly increased (P<0.05) the biomasses and P concentrations of shoots and roots, as well as the total P acquisitions per pot, and significantly reduced (P<0.05) the concentrations of HMs in shoots (except for Cu and Pb with Fm- and Fc- inoculated treatments, respectively) and alleviated the toxicity symptoms of HMs in thylakoid structure of leaves. AM fungal inoculations in the H soil also significantly increased (P<0.05) the shoot uptake of HMs (except for Cr), and tended to decrease the total concentrations of HMs in soils. This suggests the potential application of AM fungi for both reducing HM stress and promoting phytoextraction of HM-contaminated soils caused by WEEE recycling.</AbstractText>
<CopyrightInformation>Copyright © 2018 Elsevier B.V. All rights reserved.</CopyrightInformation>
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<AuthorList CompleteYN="Y"><Author ValidYN="Y"><LastName>Zhang</LastName>
<ForeName>Yu</ForeName>
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</AffiliationInfo>
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<Author ValidYN="Y"><LastName>Bai</LastName>
<ForeName>Jianfeng</ForeName>
<Initials>J</Initials>
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<Author ValidYN="Y"><LastName>Yin</LastName>
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<AffiliationInfo><Affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.</Affiliation>
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<ForeName>Jingwei</ForeName>
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<AffiliationInfo><Affiliation>State Key Laboratory of Soil and Sustainable Agriculture, Joint Open Laboratory of Soil and the Environment, Hong Kong Baptist University & Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.</Affiliation>
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<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
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<Keyword MajorTopicYN="N">Funneliformis caledonium</Keyword>
<Keyword MajorTopicYN="N">Funneliformis mosseae</Keyword>
<Keyword MajorTopicYN="N">P acquisition</Keyword>
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