A transformation and auxiliary extraction of Cr during electrokinetic removal of Cr-contaminated multilayer composite soil chamber
Multilayer composite soil chamber was proposed to extract the Cr of contaminated site soil and insight into transformation of Cr fractionation associated with valence states. The variations of current, soil pH and moisture content were explored, as well as the migration of Cr fractionation and redis...
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description | Multilayer composite soil chamber was proposed to extract the Cr of contaminated site soil and insight into transformation of Cr fractionation associated with valence states. The variations of current, soil pH and moisture content were explored, as well as the migration of Cr fractionation and redistribution of Cr. Results indicated that duration of half peak current could be used to adjust treatment time and it varied among different composite ways. Moreover, extraction efficiency of Cr in soil near cathode was relatively higher and reached 60% when citric acid was used. Citric acid could promote the transformation between different Cr fractionations or different valence states. It could also improve the desorption of Cr, and could prevent excessive fluctuations of moisture content at the same time. Cr redistributed acrossed the soil chamber after extraction. When deionized water was used, Cr(VI) significantly migrated toward anode mainly in the form of exchangeable fractionation (EXC) while Fe–Mn oxides fractionation (Fe–Mn) which may be in the form of cationic Cr(III) hydroxides migrated toward cathode. When using citric acid, fractionations that were difficult to migrate of Cr, especially for Fe–Mn in site soils could be activated and became EXC and carbonate fractionation (CAR), then migrated to the anode or cathode. The migration of exchangeable Cr(III) was dramatically enhanced. But the use of citric acid could cause Cr(VI) transformation to Cr(III) near anode. In addition, during the migration process, EXC could go back to Fe–Mn again or transform to residue fractionation (RES). |
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The variations of current, soil pH and moisture content were explored, as well as the migration of Cr fractionation and redistribution of Cr. Results indicated that duration of half peak current could be used to adjust treatment time and it varied among different composite ways. Moreover, extraction efficiency of Cr in soil near cathode was relatively higher and reached 60% when citric acid was used. Citric acid could promote the transformation between different Cr fractionations or different valence states. It could also improve the desorption of Cr, and could prevent excessive fluctuations of moisture content at the same time. Cr redistributed acrossed the soil chamber after extraction. When deionized water was used, Cr(VI) significantly migrated toward anode mainly in the form of exchangeable fractionation (EXC) while Fe–Mn oxides fractionation (Fe–Mn) which may be in the form of cationic Cr(III) hydroxides migrated toward cathode. When using citric acid, fractionations that were difficult to migrate of Cr, especially for Fe–Mn in site soils could be activated and became EXC and carbonate fractionation (CAR), then migrated to the anode or cathode. The migration of exchangeable Cr(III) was dramatically enhanced. But the use of citric acid could cause Cr(VI) transformation to Cr(III) near anode. In addition, during the migration process, EXC could go back to Fe–Mn again or transform to residue fractionation (RES).</description><identifier>ISSN: 0269-4042</identifier><identifier>ISSN: 1573-2983</identifier><identifier>EISSN: 1573-2983</identifier><identifier>DOI: 10.1007/s10653-024-02242-6</identifier><identifier>PMID: 39316230</identifier><language>eng</language><publisher>Dordrecht: Springer Netherlands</publisher><subject>Acidic soils ; Acids ; Activated carbon ; Anodes ; Carbonates ; Cathodes ; Cations ; Chambers ; Chemical Fractionation - methods ; Chromium ; Chromium - chemistry ; Citric acid ; Citric Acid - chemistry ; Deionization ; Earth and Environmental Science ; Electrochemical Techniques ; Electrodes ; Environment ; Environmental Chemistry ; Environmental Health ; Environmental Restoration and Remediation - methods ; Fractionation ; Geochemistry ; Hydrogen-Ion Concentration ; Hydroxides ; Iron ; Moisture content ; Multilayers ; Original Paper ; Public Health ; Soil ; Soil - chemistry ; Soil improvement ; Soil moisture ; Soil pH ; Soil Pollutants - chemistry ; Soil pollution ; Soil Science & Conservation ; Soil water ; Soils ; Terrestrial Pollution ; Trivalent chromium ; Valence ; Water content</subject><ispartof>Environmental geochemistry and health, 2024-11, Vol.46 (11), p.450, Article 450</ispartof><rights>The Author(s), under exclusive licence to Springer Nature B.V. 2024. 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The variations of current, soil pH and moisture content were explored, as well as the migration of Cr fractionation and redistribution of Cr. Results indicated that duration of half peak current could be used to adjust treatment time and it varied among different composite ways. Moreover, extraction efficiency of Cr in soil near cathode was relatively higher and reached 60% when citric acid was used. Citric acid could promote the transformation between different Cr fractionations or different valence states. It could also improve the desorption of Cr, and could prevent excessive fluctuations of moisture content at the same time. Cr redistributed acrossed the soil chamber after extraction. When deionized water was used, Cr(VI) significantly migrated toward anode mainly in the form of exchangeable fractionation (EXC) while Fe–Mn oxides fractionation (Fe–Mn) which may be in the form of cationic Cr(III) hydroxides migrated toward cathode. When using citric acid, fractionations that were difficult to migrate of Cr, especially for Fe–Mn in site soils could be activated and became EXC and carbonate fractionation (CAR), then migrated to the anode or cathode. The migration of exchangeable Cr(III) was dramatically enhanced. But the use of citric acid could cause Cr(VI) transformation to Cr(III) near anode. In addition, during the migration process, EXC could go back to Fe–Mn again or transform to residue fractionation (RES).</description><subject>Acidic soils</subject><subject>Acids</subject><subject>Activated carbon</subject><subject>Anodes</subject><subject>Carbonates</subject><subject>Cathodes</subject><subject>Cations</subject><subject>Chambers</subject><subject>Chemical Fractionation - methods</subject><subject>Chromium</subject><subject>Chromium - chemistry</subject><subject>Citric acid</subject><subject>Citric Acid - chemistry</subject><subject>Deionization</subject><subject>Earth and Environmental Science</subject><subject>Electrochemical Techniques</subject><subject>Electrodes</subject><subject>Environment</subject><subject>Environmental Chemistry</subject><subject>Environmental Health</subject><subject>Environmental Restoration and Remediation - methods</subject><subject>Fractionation</subject><subject>Geochemistry</subject><subject>Hydrogen-Ion Concentration</subject><subject>Hydroxides</subject><subject>Iron</subject><subject>Moisture content</subject><subject>Multilayers</subject><subject>Original Paper</subject><subject>Public Health</subject><subject>Soil</subject><subject>Soil - chemistry</subject><subject>Soil improvement</subject><subject>Soil moisture</subject><subject>Soil pH</subject><subject>Soil Pollutants - chemistry</subject><subject>Soil pollution</subject><subject>Soil Science & Conservation</subject><subject>Soil water</subject><subject>Soils</subject><subject>Terrestrial Pollution</subject><subject>Trivalent chromium</subject><subject>Valence</subject><subject>Water content</subject><issn>0269-4042</issn><issn>1573-2983</issn><issn>1573-2983</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2024</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp9kcFuFSEUhonR2NtbX8CFIXHjZvQAMwyzbG6qNmnipl0TLnNGqTBcgTHt1icvvVM1ceGCsPi_80POR8hrBu8ZQP8hM5CdaIC39fCWN_IZ2bCuFw0flHhONsDl0LTQ8hNymvMtAAx9q16SEzEIJrmADfl1Tksyc55iCqa4OFMzj9Qsd847k-4p3tXYHoM40V2i45Lc_JWiR1tS_O5mLM7ShCH-NH5lGhvnYoKbTcGRhsUX5809JmpjOMTsCtIcnaf2mwl7TGfkxWR8xldP95bcfLy43n1urr58utydXzWWd7I0UhjODHSjkLxnXFozCDTTCIDAWiZVDSYlsUMxAB9g36reiLFlQhk1DCi25N3ae0jxx4K56OCyRe_NjHHJWjBQvZSi4xV9-w96G5c0198dKSWVrL1bwlfKpphzwkkfkgt1a5qBfjSkV0O6GtJHQ1rWoTdP1cs-4Phn5LeSCogVyIfHTWP6-_Z_ah8A2wSc5w</recordid><startdate>20241101</startdate><enddate>20241101</enddate><creator>Wu, Junnian</creator><creator>Lv, Ziwei</creator><creator>Zheng, Zongqian</creator><creator>Fu, Yupeng</creator><creator>Li, Jiang</creator><general>Springer Netherlands</general><general>Springer Nature B.V</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7ST</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>K9.</scope><scope>L.G</scope><scope>SOI</scope><scope>7X8</scope></search><sort><creationdate>20241101</creationdate><title>A transformation and auxiliary extraction of Cr during electrokinetic removal of Cr-contaminated multilayer composite soil chamber</title><author>Wu, Junnian ; Lv, Ziwei ; Zheng, Zongqian ; Fu, Yupeng ; Li, Jiang</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c256t-63a21a05d3627126ca93eafd00e014168d36f86e5e390290b487a3d4138a899e3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2024</creationdate><topic>Acidic soils</topic><topic>Acids</topic><topic>Activated carbon</topic><topic>Anodes</topic><topic>Carbonates</topic><topic>Cathodes</topic><topic>Cations</topic><topic>Chambers</topic><topic>Chemical Fractionation - methods</topic><topic>Chromium</topic><topic>Chromium - chemistry</topic><topic>Citric acid</topic><topic>Citric Acid - chemistry</topic><topic>Deionization</topic><topic>Earth and Environmental Science</topic><topic>Electrochemical Techniques</topic><topic>Electrodes</topic><topic>Environment</topic><topic>Environmental Chemistry</topic><topic>Environmental Health</topic><topic>Environmental Restoration and Remediation - methods</topic><topic>Fractionation</topic><topic>Geochemistry</topic><topic>Hydrogen-Ion Concentration</topic><topic>Hydroxides</topic><topic>Iron</topic><topic>Moisture content</topic><topic>Multilayers</topic><topic>Original Paper</topic><topic>Public Health</topic><topic>Soil</topic><topic>Soil - chemistry</topic><topic>Soil improvement</topic><topic>Soil moisture</topic><topic>Soil pH</topic><topic>Soil Pollutants - chemistry</topic><topic>Soil pollution</topic><topic>Soil Science & Conservation</topic><topic>Soil water</topic><topic>Soils</topic><topic>Terrestrial Pollution</topic><topic>Trivalent chromium</topic><topic>Valence</topic><topic>Water content</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Wu, Junnian</creatorcontrib><creatorcontrib>Lv, Ziwei</creatorcontrib><creatorcontrib>Zheng, Zongqian</creatorcontrib><creatorcontrib>Fu, Yupeng</creatorcontrib><creatorcontrib>Li, Jiang</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Environment Abstracts</collection><collection>MEDLINE - Academic</collection><jtitle>Environmental geochemistry and health</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Wu, Junnian</au><au>Lv, Ziwei</au><au>Zheng, Zongqian</au><au>Fu, Yupeng</au><au>Li, Jiang</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>A transformation and auxiliary extraction of Cr during electrokinetic removal of Cr-contaminated multilayer composite soil chamber</atitle><jtitle>Environmental geochemistry and health</jtitle><stitle>Environ Geochem Health</stitle><addtitle>Environ Geochem Health</addtitle><date>2024-11-01</date><risdate>2024</risdate><volume>46</volume><issue>11</issue><spage>450</spage><pages>450-</pages><artnum>450</artnum><issn>0269-4042</issn><issn>1573-2983</issn><eissn>1573-2983</eissn><abstract>Multilayer composite soil chamber was proposed to extract the Cr of contaminated site soil and insight into transformation of Cr fractionation associated with valence states. The variations of current, soil pH and moisture content were explored, as well as the migration of Cr fractionation and redistribution of Cr. Results indicated that duration of half peak current could be used to adjust treatment time and it varied among different composite ways. Moreover, extraction efficiency of Cr in soil near cathode was relatively higher and reached 60% when citric acid was used. Citric acid could promote the transformation between different Cr fractionations or different valence states. It could also improve the desorption of Cr, and could prevent excessive fluctuations of moisture content at the same time. Cr redistributed acrossed the soil chamber after extraction. When deionized water was used, Cr(VI) significantly migrated toward anode mainly in the form of exchangeable fractionation (EXC) while Fe–Mn oxides fractionation (Fe–Mn) which may be in the form of cationic Cr(III) hydroxides migrated toward cathode. When using citric acid, fractionations that were difficult to migrate of Cr, especially for Fe–Mn in site soils could be activated and became EXC and carbonate fractionation (CAR), then migrated to the anode or cathode. The migration of exchangeable Cr(III) was dramatically enhanced. But the use of citric acid could cause Cr(VI) transformation to Cr(III) near anode. In addition, during the migration process, EXC could go back to Fe–Mn again or transform to residue fractionation (RES).</abstract><cop>Dordrecht</cop><pub>Springer Netherlands</pub><pmid>39316230</pmid><doi>10.1007/s10653-024-02242-6</doi></addata></record> |
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subjects | Acidic soils Acids Activated carbon Anodes Carbonates Cathodes Cations Chambers Chemical Fractionation - methods Chromium Chromium - chemistry Citric acid Citric Acid - chemistry Deionization Earth and Environmental Science Electrochemical Techniques Electrodes Environment Environmental Chemistry Environmental Health Environmental Restoration and Remediation - methods Fractionation Geochemistry Hydrogen-Ion Concentration Hydroxides Iron Moisture content Multilayers Original Paper Public Health Soil Soil - chemistry Soil improvement Soil moisture Soil pH Soil Pollutants - chemistry Soil pollution Soil Science & Conservation Soil water Soils Terrestrial Pollution Trivalent chromium Valence Water content |
title | A transformation and auxiliary extraction of Cr during electrokinetic removal of Cr-contaminated multilayer composite soil chamber |
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