Effects of Rhizophagus clarus and biochar on growth, photosynthesis, nutrients, and cadmium (Cd) concentration of maize (Zea mays) grown in Cd-spiked soil

Cadmium (Cd) toxicity in agricultural crops is a widespread problem. Little is known about biochar and arbuscular mycorrhizal fungi (AMF) effect on Cd concentration in maize plant either applied separately or in combination. Current study was performed to demonstrate effects of biochar and Rhizophag...

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Veröffentlicht in:Environmental science and pollution research international 2019-07, Vol.26 (20), p.20689-20700
Hauptverfasser: Rafique, Mazhar, Ortas, Ibrahim, Rizwan, Muhammad, Sultan, Tariq, Chaudhary, Hassan Javed, Işik, Mehmet, Aydin, Oğuzhan
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container_issue 20
container_start_page 20689
container_title Environmental science and pollution research international
container_volume 26
creator Rafique, Mazhar
Ortas, Ibrahim
Rizwan, Muhammad
Sultan, Tariq
Chaudhary, Hassan Javed
Işik, Mehmet
Aydin, Oğuzhan
description Cadmium (Cd) toxicity in agricultural crops is a widespread problem. Little is known about biochar and arbuscular mycorrhizal fungi (AMF) effect on Cd concentration in maize plant either applied separately or in combination. Current study was performed to demonstrate effects of biochar and Rhizophagus clarus on plant growth, photosynthesis activity, nutrients (P, Ca, Mg, Fe, Cu, and Mn), and Cd concentration in maize grown in Cd-spiked soil. The alkaline soil was spiked by Cd factor at three levels: 0 (Cd 0), 5 (Cd 5), and 10 (Cd 10) mg/kg; biochar factor at two levels: 0 and 1%; and mycorrhizal inoculum factor at two levels: MF0 and MF1 ( R. clraus ). Plants were harvested after 70 days of seed germination, and various morphological and physiological parameters, as well as elemental concentration and root colonization, were recorded. Addition of biochar increased plant biomass by 21% (Cd 5) and 93% (Cd 10), MF1 enhanced by 53% (Cd 0) and 69% (Cd 10), while biochar + MF1 enhanced dry plant biomass by 70% (Cd 0) and 94% (Cd 10). Results showed maximum increase of 94% (Cd 10) in plant biomass was observed in Cd-spiked soil. Root colonization decreased proportionally by increasing Cd concentration and at Cd 10, colonization was 36.7% and 31.7% for MF1 and biochar + MF1 treatments, respectively. Besides that, addition of biochar enhanced root attributes (root length, volume, and surface area) by 34–58% compared to control in Cd 10. The MF1 increased these attributes by 11–78% while biochar + MF1 enhanced by 32–61% in Cd-spiked soil. However, biochar + MF1 neutralized Cd stress in maize plant for gaseous attributes (assimilation rate, transpiration rate, intercellular CO 2 , and stomatal conductance). The MF1 enhanced Cd concentration in plant as it was 3.32 mg/kg in Cd 5 and 6.73 mg/kg in Cd 10 treatments while addition of biochar phytostabilized Cd and reduced its concentration in plants by 2.0 mg/kg in Cd 5 and 4.27 mg/kg in Cd 10. The biochar + MF1 had 2.9 mg/kg and 4.8 mg/kg Cd concentration in Cd 5 and Cd 10 plants, respectively. Phosphorus concentration was augmented in shoots (up to 26%) and roots (up to 20%) of maize plant in biochar-amended soil than control plants. In biochar + MF1, concentration of P was 1.01% and 0.73% in Cd 5 and Cd 10, respectively. It is concluded that biochar + MF1 treatment enhances plant biomass while addition of sole biochar reduced Cd uptake, slightly indifferent to earlier treatment.
doi_str_mv 10.1007/s11356-019-05323-7
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Little is known about biochar and arbuscular mycorrhizal fungi (AMF) effect on Cd concentration in maize plant either applied separately or in combination. Current study was performed to demonstrate effects of biochar and Rhizophagus clarus on plant growth, photosynthesis activity, nutrients (P, Ca, Mg, Fe, Cu, and Mn), and Cd concentration in maize grown in Cd-spiked soil. The alkaline soil was spiked by Cd factor at three levels: 0 (Cd 0), 5 (Cd 5), and 10 (Cd 10) mg/kg; biochar factor at two levels: 0 and 1%; and mycorrhizal inoculum factor at two levels: MF0 and MF1 ( R. clraus ). Plants were harvested after 70 days of seed germination, and various morphological and physiological parameters, as well as elemental concentration and root colonization, were recorded. Addition of biochar increased plant biomass by 21% (Cd 5) and 93% (Cd 10), MF1 enhanced by 53% (Cd 0) and 69% (Cd 10), while biochar + MF1 enhanced dry plant biomass by 70% (Cd 0) and 94% (Cd 10). Results showed maximum increase of 94% (Cd 10) in plant biomass was observed in Cd-spiked soil. Root colonization decreased proportionally by increasing Cd concentration and at Cd 10, colonization was 36.7% and 31.7% for MF1 and biochar + MF1 treatments, respectively. Besides that, addition of biochar enhanced root attributes (root length, volume, and surface area) by 34–58% compared to control in Cd 10. The MF1 increased these attributes by 11–78% while biochar + MF1 enhanced by 32–61% in Cd-spiked soil. However, biochar + MF1 neutralized Cd stress in maize plant for gaseous attributes (assimilation rate, transpiration rate, intercellular CO 2 , and stomatal conductance). The MF1 enhanced Cd concentration in plant as it was 3.32 mg/kg in Cd 5 and 6.73 mg/kg in Cd 10 treatments while addition of biochar phytostabilized Cd and reduced its concentration in plants by 2.0 mg/kg in Cd 5 and 4.27 mg/kg in Cd 10. The biochar + MF1 had 2.9 mg/kg and 4.8 mg/kg Cd concentration in Cd 5 and Cd 10 plants, respectively. Phosphorus concentration was augmented in shoots (up to 26%) and roots (up to 20%) of maize plant in biochar-amended soil than control plants. In biochar + MF1, concentration of P was 1.01% and 0.73% in Cd 5 and Cd 10, respectively. 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All Rights Reserved.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c412t-3f6f86ce6ee49fb4f2f1da517b7d161f24cfcd7ea90403056cb4d2b87c5c8be43</citedby><cites>FETCH-LOGICAL-c412t-3f6f86ce6ee49fb4f2f1da517b7d161f24cfcd7ea90403056cb4d2b87c5c8be43</cites><orcidid>0000-0002-3513-2041</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.1007/s11356-019-05323-7$$EPDF$$P50$$Gspringer$$H</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.1007/s11356-019-05323-7$$EHTML$$P50$$Gspringer$$H</linktohtml><link.rule.ids>314,780,784,27924,27925,41488,42557,51319</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/31104234$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Rafique, Mazhar</creatorcontrib><creatorcontrib>Ortas, Ibrahim</creatorcontrib><creatorcontrib>Rizwan, Muhammad</creatorcontrib><creatorcontrib>Sultan, Tariq</creatorcontrib><creatorcontrib>Chaudhary, Hassan Javed</creatorcontrib><creatorcontrib>Işik, Mehmet</creatorcontrib><creatorcontrib>Aydin, Oğuzhan</creatorcontrib><title>Effects of Rhizophagus clarus and biochar on growth, photosynthesis, nutrients, and cadmium (Cd) concentration of maize (Zea mays) grown in Cd-spiked soil</title><title>Environmental science and pollution research international</title><addtitle>Environ Sci Pollut Res</addtitle><addtitle>Environ Sci Pollut Res Int</addtitle><description>Cadmium (Cd) toxicity in agricultural crops is a widespread problem. Little is known about biochar and arbuscular mycorrhizal fungi (AMF) effect on Cd concentration in maize plant either applied separately or in combination. Current study was performed to demonstrate effects of biochar and Rhizophagus clarus on plant growth, photosynthesis activity, nutrients (P, Ca, Mg, Fe, Cu, and Mn), and Cd concentration in maize grown in Cd-spiked soil. The alkaline soil was spiked by Cd factor at three levels: 0 (Cd 0), 5 (Cd 5), and 10 (Cd 10) mg/kg; biochar factor at two levels: 0 and 1%; and mycorrhizal inoculum factor at two levels: MF0 and MF1 ( R. clraus ). Plants were harvested after 70 days of seed germination, and various morphological and physiological parameters, as well as elemental concentration and root colonization, were recorded. Addition of biochar increased plant biomass by 21% (Cd 5) and 93% (Cd 10), MF1 enhanced by 53% (Cd 0) and 69% (Cd 10), while biochar + MF1 enhanced dry plant biomass by 70% (Cd 0) and 94% (Cd 10). Results showed maximum increase of 94% (Cd 10) in plant biomass was observed in Cd-spiked soil. Root colonization decreased proportionally by increasing Cd concentration and at Cd 10, colonization was 36.7% and 31.7% for MF1 and biochar + MF1 treatments, respectively. Besides that, addition of biochar enhanced root attributes (root length, volume, and surface area) by 34–58% compared to control in Cd 10. The MF1 increased these attributes by 11–78% while biochar + MF1 enhanced by 32–61% in Cd-spiked soil. However, biochar + MF1 neutralized Cd stress in maize plant for gaseous attributes (assimilation rate, transpiration rate, intercellular CO 2 , and stomatal conductance). The MF1 enhanced Cd concentration in plant as it was 3.32 mg/kg in Cd 5 and 6.73 mg/kg in Cd 10 treatments while addition of biochar phytostabilized Cd and reduced its concentration in plants by 2.0 mg/kg in Cd 5 and 4.27 mg/kg in Cd 10. The biochar + MF1 had 2.9 mg/kg and 4.8 mg/kg Cd concentration in Cd 5 and Cd 10 plants, respectively. Phosphorus concentration was augmented in shoots (up to 26%) and roots (up to 20%) of maize plant in biochar-amended soil than control plants. In biochar + MF1, concentration of P was 1.01% and 0.73% in Cd 5 and Cd 10, respectively. It is concluded that biochar + MF1 treatment enhances plant biomass while addition of sole biochar reduced Cd uptake, slightly indifferent to earlier treatment.</description><subject>Alkaline soils</subject><subject>Aquatic Pollution</subject><subject>Arbuscular mycorrhizas</subject><subject>Atmospheric Protection/Air Quality Control/Air Pollution</subject><subject>Biomass</subject><subject>Cadmium</subject><subject>Cadmium - chemistry</subject><subject>Cadmium - metabolism</subject><subject>Cadmium - toxicity</subject><subject>Calcium</subject><subject>Carbon dioxide</subject><subject>Charcoal</subject><subject>Charcoal - analysis</subject><subject>Charcoal - chemistry</subject><subject>Colonization</subject><subject>Conductance</subject><subject>Copper</subject><subject>Corn</subject><subject>Earth and Environmental Science</subject><subject>Ecotoxicology</subject><subject>Environment</subject><subject>Environmental Chemistry</subject><subject>Environmental Health</subject><subject>Environmental science</subject><subject>Fungi</subject><subject>Germination</subject><subject>Glomeromycota - physiology</subject><subject>Inoculum</subject><subject>Magnesium</subject><subject>Manganese</subject><subject>Mycorrhizae - physiology</subject><subject>Nutrients</subject><subject>Nutrients - metabolism</subject><subject>Phosphorus</subject><subject>Photosynthesis</subject><subject>Photosynthesis - drug effects</subject><subject>Plant biomass</subject><subject>Plant growth</subject><subject>Plant Roots - growth &amp; 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Ortas, Ibrahim ; Rizwan, Muhammad ; Sultan, Tariq ; Chaudhary, Hassan Javed ; Işik, Mehmet ; Aydin, Oğuzhan</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c412t-3f6f86ce6ee49fb4f2f1da517b7d161f24cfcd7ea90403056cb4d2b87c5c8be43</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2019</creationdate><topic>Alkaline soils</topic><topic>Aquatic Pollution</topic><topic>Arbuscular mycorrhizas</topic><topic>Atmospheric Protection/Air Quality Control/Air Pollution</topic><topic>Biomass</topic><topic>Cadmium</topic><topic>Cadmium - chemistry</topic><topic>Cadmium - metabolism</topic><topic>Cadmium - toxicity</topic><topic>Calcium</topic><topic>Carbon dioxide</topic><topic>Charcoal</topic><topic>Charcoal - analysis</topic><topic>Charcoal - chemistry</topic><topic>Colonization</topic><topic>Conductance</topic><topic>Copper</topic><topic>Corn</topic><topic>Earth and Environmental Science</topic><topic>Ecotoxicology</topic><topic>Environment</topic><topic>Environmental Chemistry</topic><topic>Environmental Health</topic><topic>Environmental science</topic><topic>Fungi</topic><topic>Germination</topic><topic>Glomeromycota - physiology</topic><topic>Inoculum</topic><topic>Magnesium</topic><topic>Manganese</topic><topic>Mycorrhizae - physiology</topic><topic>Nutrients</topic><topic>Nutrients - metabolism</topic><topic>Phosphorus</topic><topic>Photosynthesis</topic><topic>Photosynthesis - drug effects</topic><topic>Plant biomass</topic><topic>Plant growth</topic><topic>Plant Roots - growth &amp; 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Medical Complete (Alumni)</collection><collection>ABI/INFORM Professional Advanced</collection><collection>ABI/INFORM Global</collection><collection>Health &amp; Medical Collection (Alumni Edition)</collection><collection>Medical Database</collection><collection>Science Database</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environmental Science Database</collection><collection>ProQuest One Business</collection><collection>ProQuest One Business (Alumni)</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Environmental Science Collection</collection><collection>ProQuest Central Basic</collection><collection>MEDLINE - Academic</collection><jtitle>Environmental science and pollution research international</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Rafique, Mazhar</au><au>Ortas, Ibrahim</au><au>Rizwan, Muhammad</au><au>Sultan, Tariq</au><au>Chaudhary, Hassan Javed</au><au>Işik, Mehmet</au><au>Aydin, Oğuzhan</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Effects of Rhizophagus clarus and biochar on growth, photosynthesis, nutrients, and cadmium (Cd) concentration of maize (Zea mays) grown in Cd-spiked soil</atitle><jtitle>Environmental science and pollution research international</jtitle><stitle>Environ Sci Pollut Res</stitle><addtitle>Environ Sci Pollut Res Int</addtitle><date>2019-07-01</date><risdate>2019</risdate><volume>26</volume><issue>20</issue><spage>20689</spage><epage>20700</epage><pages>20689-20700</pages><issn>0944-1344</issn><eissn>1614-7499</eissn><abstract>Cadmium (Cd) toxicity in agricultural crops is a widespread problem. Little is known about biochar and arbuscular mycorrhizal fungi (AMF) effect on Cd concentration in maize plant either applied separately or in combination. Current study was performed to demonstrate effects of biochar and Rhizophagus clarus on plant growth, photosynthesis activity, nutrients (P, Ca, Mg, Fe, Cu, and Mn), and Cd concentration in maize grown in Cd-spiked soil. The alkaline soil was spiked by Cd factor at three levels: 0 (Cd 0), 5 (Cd 5), and 10 (Cd 10) mg/kg; biochar factor at two levels: 0 and 1%; and mycorrhizal inoculum factor at two levels: MF0 and MF1 ( R. clraus ). Plants were harvested after 70 days of seed germination, and various morphological and physiological parameters, as well as elemental concentration and root colonization, were recorded. Addition of biochar increased plant biomass by 21% (Cd 5) and 93% (Cd 10), MF1 enhanced by 53% (Cd 0) and 69% (Cd 10), while biochar + MF1 enhanced dry plant biomass by 70% (Cd 0) and 94% (Cd 10). Results showed maximum increase of 94% (Cd 10) in plant biomass was observed in Cd-spiked soil. Root colonization decreased proportionally by increasing Cd concentration and at Cd 10, colonization was 36.7% and 31.7% for MF1 and biochar + MF1 treatments, respectively. Besides that, addition of biochar enhanced root attributes (root length, volume, and surface area) by 34–58% compared to control in Cd 10. The MF1 increased these attributes by 11–78% while biochar + MF1 enhanced by 32–61% in Cd-spiked soil. However, biochar + MF1 neutralized Cd stress in maize plant for gaseous attributes (assimilation rate, transpiration rate, intercellular CO 2 , and stomatal conductance). The MF1 enhanced Cd concentration in plant as it was 3.32 mg/kg in Cd 5 and 6.73 mg/kg in Cd 10 treatments while addition of biochar phytostabilized Cd and reduced its concentration in plants by 2.0 mg/kg in Cd 5 and 4.27 mg/kg in Cd 10. The biochar + MF1 had 2.9 mg/kg and 4.8 mg/kg Cd concentration in Cd 5 and Cd 10 plants, respectively. Phosphorus concentration was augmented in shoots (up to 26%) and roots (up to 20%) of maize plant in biochar-amended soil than control plants. In biochar + MF1, concentration of P was 1.01% and 0.73% in Cd 5 and Cd 10, respectively. It is concluded that biochar + MF1 treatment enhances plant biomass while addition of sole biochar reduced Cd uptake, slightly indifferent to earlier treatment.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><pmid>31104234</pmid><doi>10.1007/s11356-019-05323-7</doi><tpages>12</tpages><orcidid>https://orcid.org/0000-0002-3513-2041</orcidid></addata></record>
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identifier ISSN: 0944-1344
ispartof Environmental science and pollution research international, 2019-07, Vol.26 (20), p.20689-20700
issn 0944-1344
1614-7499
language eng
recordid cdi_proquest_miscellaneous_2232085989
source MEDLINE; SpringerLink Journals - AutoHoldings
subjects Alkaline soils
Aquatic Pollution
Arbuscular mycorrhizas
Atmospheric Protection/Air Quality Control/Air Pollution
Biomass
Cadmium
Cadmium - chemistry
Cadmium - metabolism
Cadmium - toxicity
Calcium
Carbon dioxide
Charcoal
Charcoal - analysis
Charcoal - chemistry
Colonization
Conductance
Copper
Corn
Earth and Environmental Science
Ecotoxicology
Environment
Environmental Chemistry
Environmental Health
Environmental science
Fungi
Germination
Glomeromycota - physiology
Inoculum
Magnesium
Manganese
Mycorrhizae - physiology
Nutrients
Nutrients - metabolism
Phosphorus
Photosynthesis
Photosynthesis - drug effects
Plant biomass
Plant growth
Plant Roots - growth & development
Plant Roots - microbiology
Plants (botany)
Research Article
Resistance
Rhizophagus clarus
Seed germination
Shoots
Soil amendment
Soil Pollutants - chemistry
Soil Pollutants - metabolism
Soil Pollutants - toxicity
Stomata
Stomatal conductance
Toxicity
Transpiration
Waste Water Technology
Water Management
Water Pollution Control
Zea mays - growth & development
Zea mays - metabolism
Zea mays - microbiology
title Effects of Rhizophagus clarus and biochar on growth, photosynthesis, nutrients, and cadmium (Cd) concentration of maize (Zea mays) grown in Cd-spiked soil
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