Loading…

Constructing the active surface soil layer with ZVI-biochar amendment for simultaneous immobilization of As and Zn in both contaminated soil and groundwater: Continuous versus intermittent infiltration mode

In this study, the zero valent iron-biochar composite (ZVI-BC) was applied to construct an active surface soil layer for the simultaneous remediation of As-Zn contaminated soil and groundwater, focusing on the influence of the infiltration mode of pumped-up groundwater into soil. The active surface...

Full description

Saved in:
Bibliographic Details
Published in:Journal of hazardous materials 2023-03, Vol.445, p.130518, Article 130518
Main Authors: Chen, Xiang, Xu, Xiaoyun, Wei, Yaqiang, Wang, Xinbing, Cao, Xinde
Format: Article
Language:English
Subjects:
Citations: Items that this one cites
Items that cite this one
Online Access:Get full text
Tags: Add Tag
No Tags, Be the first to tag this record!
cited_by cdi_FETCH-LOGICAL-c365t-a53756d8c4be8ef0824adb3248871a62a0c1bcbabf3f892fb519e37dba9a17293
cites cdi_FETCH-LOGICAL-c365t-a53756d8c4be8ef0824adb3248871a62a0c1bcbabf3f892fb519e37dba9a17293
container_end_page
container_issue
container_start_page 130518
container_title Journal of hazardous materials
container_volume 445
creator Chen, Xiang
Xu, Xiaoyun
Wei, Yaqiang
Wang, Xinbing
Cao, Xinde
description In this study, the zero valent iron-biochar composite (ZVI-BC) was applied to construct an active surface soil layer for the simultaneous remediation of As-Zn contaminated soil and groundwater, focusing on the influence of the infiltration mode of pumped-up groundwater into soil. The active surface soil treated more contaminated groundwater for As (4.45-5.46 L kg-1 soil) than that for Zn (2.52-3.13 L kg-1 soil) under both continuous and intermittent infiltration modes, with about 98% As and 95% Zn removed from groundwater and retained in the soil. As(V) precipitated with Fe(III) due to ZVI oxidation, which was responsible for the As immobilization. The soil under the intermittent infiltration mode was enriched by the Sphingomonas with arsenate reductase gene, which promoted more reduction of As(V) into As(III) and facilitated coprecipitation of As(III) with Fe(III). The Mn oxide determined the sorption of Zn in the active soil layer, where the Hyphomicrobium, one type of manganese oxidizing bacteria, was much higher under the continuous infiltration mode, which accounted for the more Zn immobilization. After the remediation, both As and Zn immobilized in the active surface soil showed high stability, with the average downward migration rate of only 0.207-0.368 cm year-1 within 20-year rainfall exposure. Our findings indicate that this active surface soil layer is applicable for simultaneous immobilization of As and Zn in both contaminated soil and groundwater, and the groundwater intermittent infiltration could be a better option considering the remediation effectiveness, the immobilization mechanism, the long-term stability, and the energetic efficiency. [Display omitted] •The active surface soil was constructed with zero valent iron-biochar composite.•As was adsorbed by ZVI-BC and finally transformed into As-Fe coprecipitates.•The sorption and immobilization of Zn was dominated by Mn oxide in soil.•The downward migration rates of As and Zn immobilized in soil were low.•Intermittent infiltration was optimal for simultaneous immobilization of As and Zn.
doi_str_mv 10.1016/j.jhazmat.2022.130518
format article
fullrecord <record><control><sourceid>pubmed_cross</sourceid><recordid>TN_cdi_crossref_primary_10_1016_j_jhazmat_2022_130518</recordid><sourceformat>XML</sourceformat><sourcesystem>PC</sourcesystem><els_id>S0304389422023123</els_id><sourcerecordid>36493652</sourcerecordid><originalsourceid>FETCH-LOGICAL-c365t-a53756d8c4be8ef0824adb3248871a62a0c1bcbabf3f892fb519e37dba9a17293</originalsourceid><addsrcrecordid>eNqFUc1uFSEUJkZjr9VH0PACc4Vhft2YpqnapIkbddHN5ACHXm4GaIC5TfuQPpNMprp1QQ45fH_kI-Q9Z3vOePfxuD8e4MlB3tesrvdcsJYPL8iOD72ohBDdS7JjgjWVGMbmjLxJ6cgY433bvCZnomtG0bX1jvy-DD7luKhs_R3NB6RQriekaYkGVJnBznSGR4z0weYDvf11XUkb1AEiBYdel5OpCZEm65Y5g8ewJGqdC9LO9gmyDZ4GQy8SBa_prafWUxmKlAo-g7MeMurNZwXcxbB4_VCW8RMt6UqwZVU8YUyrsC8Pzua82lpv7Jzj5uGCxrfklYE54bvneU5-frn6cfmtuvn-9fry4qZS5du5glb0bacH1Ugc0LChbkBLUTfD0HPoamCKSyVBGmGGsTay5SOKXksYgff1KM5Ju-mqGFKKaKb7aB3Ex4mzae1nOk7P_UxrP9PWT-F92Hj3i3So_7H-FlIAnzcAlvQni3FKyqJXqG1ElScd7H8s_gC2Yauw</addsrcrecordid><sourcetype>Aggregation Database</sourcetype><iscdi>true</iscdi><recordtype>article</recordtype></control><display><type>article</type><title>Constructing the active surface soil layer with ZVI-biochar amendment for simultaneous immobilization of As and Zn in both contaminated soil and groundwater: Continuous versus intermittent infiltration mode</title><source>ScienceDirect Freedom Collection 2022-2024</source><creator>Chen, Xiang ; Xu, Xiaoyun ; Wei, Yaqiang ; Wang, Xinbing ; Cao, Xinde</creator><creatorcontrib>Chen, Xiang ; Xu, Xiaoyun ; Wei, Yaqiang ; Wang, Xinbing ; Cao, Xinde</creatorcontrib><description>In this study, the zero valent iron-biochar composite (ZVI-BC) was applied to construct an active surface soil layer for the simultaneous remediation of As-Zn contaminated soil and groundwater, focusing on the influence of the infiltration mode of pumped-up groundwater into soil. The active surface soil treated more contaminated groundwater for As (4.45-5.46 L kg-1 soil) than that for Zn (2.52-3.13 L kg-1 soil) under both continuous and intermittent infiltration modes, with about 98% As and 95% Zn removed from groundwater and retained in the soil. As(V) precipitated with Fe(III) due to ZVI oxidation, which was responsible for the As immobilization. The soil under the intermittent infiltration mode was enriched by the Sphingomonas with arsenate reductase gene, which promoted more reduction of As(V) into As(III) and facilitated coprecipitation of As(III) with Fe(III). The Mn oxide determined the sorption of Zn in the active soil layer, where the Hyphomicrobium, one type of manganese oxidizing bacteria, was much higher under the continuous infiltration mode, which accounted for the more Zn immobilization. After the remediation, both As and Zn immobilized in the active surface soil showed high stability, with the average downward migration rate of only 0.207-0.368 cm year-1 within 20-year rainfall exposure. Our findings indicate that this active surface soil layer is applicable for simultaneous immobilization of As and Zn in both contaminated soil and groundwater, and the groundwater intermittent infiltration could be a better option considering the remediation effectiveness, the immobilization mechanism, the long-term stability, and the energetic efficiency. [Display omitted] •The active surface soil was constructed with zero valent iron-biochar composite.•As was adsorbed by ZVI-BC and finally transformed into As-Fe coprecipitates.•The sorption and immobilization of Zn was dominated by Mn oxide in soil.•The downward migration rates of As and Zn immobilized in soil were low.•Intermittent infiltration was optimal for simultaneous immobilization of As and Zn.</description><identifier>ISSN: 0304-3894</identifier><identifier>EISSN: 1873-3336</identifier><identifier>DOI: 10.1016/j.jhazmat.2022.130518</identifier><identifier>PMID: 36493652</identifier><language>eng</language><publisher>Netherlands: Elsevier B.V</publisher><subject>Active soil layer ; As and Zn ; Charcoal ; Ferric Compounds ; Groundwater ; Immobilization ; Soil ; Soil Pollutants - analysis ; Zinc</subject><ispartof>Journal of hazardous materials, 2023-03, Vol.445, p.130518, Article 130518</ispartof><rights>2022 Elsevier B.V.</rights><rights>Copyright © 2022 Elsevier B.V. All rights reserved.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c365t-a53756d8c4be8ef0824adb3248871a62a0c1bcbabf3f892fb519e37dba9a17293</citedby><cites>FETCH-LOGICAL-c365t-a53756d8c4be8ef0824adb3248871a62a0c1bcbabf3f892fb519e37dba9a17293</cites><orcidid>0000-0002-2315-4219</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/36493652$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Chen, Xiang</creatorcontrib><creatorcontrib>Xu, Xiaoyun</creatorcontrib><creatorcontrib>Wei, Yaqiang</creatorcontrib><creatorcontrib>Wang, Xinbing</creatorcontrib><creatorcontrib>Cao, Xinde</creatorcontrib><title>Constructing the active surface soil layer with ZVI-biochar amendment for simultaneous immobilization of As and Zn in both contaminated soil and groundwater: Continuous versus intermittent infiltration mode</title><title>Journal of hazardous materials</title><addtitle>J Hazard Mater</addtitle><description>In this study, the zero valent iron-biochar composite (ZVI-BC) was applied to construct an active surface soil layer for the simultaneous remediation of As-Zn contaminated soil and groundwater, focusing on the influence of the infiltration mode of pumped-up groundwater into soil. The active surface soil treated more contaminated groundwater for As (4.45-5.46 L kg-1 soil) than that for Zn (2.52-3.13 L kg-1 soil) under both continuous and intermittent infiltration modes, with about 98% As and 95% Zn removed from groundwater and retained in the soil. As(V) precipitated with Fe(III) due to ZVI oxidation, which was responsible for the As immobilization. The soil under the intermittent infiltration mode was enriched by the Sphingomonas with arsenate reductase gene, which promoted more reduction of As(V) into As(III) and facilitated coprecipitation of As(III) with Fe(III). The Mn oxide determined the sorption of Zn in the active soil layer, where the Hyphomicrobium, one type of manganese oxidizing bacteria, was much higher under the continuous infiltration mode, which accounted for the more Zn immobilization. After the remediation, both As and Zn immobilized in the active surface soil showed high stability, with the average downward migration rate of only 0.207-0.368 cm year-1 within 20-year rainfall exposure. Our findings indicate that this active surface soil layer is applicable for simultaneous immobilization of As and Zn in both contaminated soil and groundwater, and the groundwater intermittent infiltration could be a better option considering the remediation effectiveness, the immobilization mechanism, the long-term stability, and the energetic efficiency. [Display omitted] •The active surface soil was constructed with zero valent iron-biochar composite.•As was adsorbed by ZVI-BC and finally transformed into As-Fe coprecipitates.•The sorption and immobilization of Zn was dominated by Mn oxide in soil.•The downward migration rates of As and Zn immobilized in soil were low.•Intermittent infiltration was optimal for simultaneous immobilization of As and Zn.</description><subject>Active soil layer</subject><subject>As and Zn</subject><subject>Charcoal</subject><subject>Ferric Compounds</subject><subject>Groundwater</subject><subject>Immobilization</subject><subject>Soil</subject><subject>Soil Pollutants - analysis</subject><subject>Zinc</subject><issn>0304-3894</issn><issn>1873-3336</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><recordid>eNqFUc1uFSEUJkZjr9VH0PACc4Vhft2YpqnapIkbddHN5ACHXm4GaIC5TfuQPpNMprp1QQ45fH_kI-Q9Z3vOePfxuD8e4MlB3tesrvdcsJYPL8iOD72ohBDdS7JjgjWVGMbmjLxJ6cgY433bvCZnomtG0bX1jvy-DD7luKhs_R3NB6RQriekaYkGVJnBznSGR4z0weYDvf11XUkb1AEiBYdel5OpCZEm65Y5g8ewJGqdC9LO9gmyDZ4GQy8SBa_prafWUxmKlAo-g7MeMurNZwXcxbB4_VCW8RMt6UqwZVU8YUyrsC8Pzua82lpv7Jzj5uGCxrfklYE54bvneU5-frn6cfmtuvn-9fry4qZS5du5glb0bacH1Ugc0LChbkBLUTfD0HPoamCKSyVBGmGGsTay5SOKXksYgff1KM5Ju-mqGFKKaKb7aB3Ex4mzae1nOk7P_UxrP9PWT-F92Hj3i3So_7H-FlIAnzcAlvQni3FKyqJXqG1ElScd7H8s_gC2Yauw</recordid><startdate>20230305</startdate><enddate>20230305</enddate><creator>Chen, Xiang</creator><creator>Xu, Xiaoyun</creator><creator>Wei, Yaqiang</creator><creator>Wang, Xinbing</creator><creator>Cao, Xinde</creator><general>Elsevier 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><orcidid>https://orcid.org/0000-0002-2315-4219</orcidid></search><sort><creationdate>20230305</creationdate><title>Constructing the active surface soil layer with ZVI-biochar amendment for simultaneous immobilization of As and Zn in both contaminated soil and groundwater: Continuous versus intermittent infiltration mode</title><author>Chen, Xiang ; Xu, Xiaoyun ; Wei, Yaqiang ; Wang, Xinbing ; Cao, Xinde</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c365t-a53756d8c4be8ef0824adb3248871a62a0c1bcbabf3f892fb519e37dba9a17293</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2023</creationdate><topic>Active soil layer</topic><topic>As and Zn</topic><topic>Charcoal</topic><topic>Ferric Compounds</topic><topic>Groundwater</topic><topic>Immobilization</topic><topic>Soil</topic><topic>Soil Pollutants - analysis</topic><topic>Zinc</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Chen, Xiang</creatorcontrib><creatorcontrib>Xu, Xiaoyun</creatorcontrib><creatorcontrib>Wei, Yaqiang</creatorcontrib><creatorcontrib>Wang, Xinbing</creatorcontrib><creatorcontrib>Cao, Xinde</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><jtitle>Journal of hazardous materials</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Chen, Xiang</au><au>Xu, Xiaoyun</au><au>Wei, Yaqiang</au><au>Wang, Xinbing</au><au>Cao, Xinde</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Constructing the active surface soil layer with ZVI-biochar amendment for simultaneous immobilization of As and Zn in both contaminated soil and groundwater: Continuous versus intermittent infiltration mode</atitle><jtitle>Journal of hazardous materials</jtitle><addtitle>J Hazard Mater</addtitle><date>2023-03-05</date><risdate>2023</risdate><volume>445</volume><spage>130518</spage><pages>130518-</pages><artnum>130518</artnum><issn>0304-3894</issn><eissn>1873-3336</eissn><abstract>In this study, the zero valent iron-biochar composite (ZVI-BC) was applied to construct an active surface soil layer for the simultaneous remediation of As-Zn contaminated soil and groundwater, focusing on the influence of the infiltration mode of pumped-up groundwater into soil. The active surface soil treated more contaminated groundwater for As (4.45-5.46 L kg-1 soil) than that for Zn (2.52-3.13 L kg-1 soil) under both continuous and intermittent infiltration modes, with about 98% As and 95% Zn removed from groundwater and retained in the soil. As(V) precipitated with Fe(III) due to ZVI oxidation, which was responsible for the As immobilization. The soil under the intermittent infiltration mode was enriched by the Sphingomonas with arsenate reductase gene, which promoted more reduction of As(V) into As(III) and facilitated coprecipitation of As(III) with Fe(III). The Mn oxide determined the sorption of Zn in the active soil layer, where the Hyphomicrobium, one type of manganese oxidizing bacteria, was much higher under the continuous infiltration mode, which accounted for the more Zn immobilization. After the remediation, both As and Zn immobilized in the active surface soil showed high stability, with the average downward migration rate of only 0.207-0.368 cm year-1 within 20-year rainfall exposure. Our findings indicate that this active surface soil layer is applicable for simultaneous immobilization of As and Zn in both contaminated soil and groundwater, and the groundwater intermittent infiltration could be a better option considering the remediation effectiveness, the immobilization mechanism, the long-term stability, and the energetic efficiency. [Display omitted] •The active surface soil was constructed with zero valent iron-biochar composite.•As was adsorbed by ZVI-BC and finally transformed into As-Fe coprecipitates.•The sorption and immobilization of Zn was dominated by Mn oxide in soil.•The downward migration rates of As and Zn immobilized in soil were low.•Intermittent infiltration was optimal for simultaneous immobilization of As and Zn.</abstract><cop>Netherlands</cop><pub>Elsevier B.V</pub><pmid>36493652</pmid><doi>10.1016/j.jhazmat.2022.130518</doi><orcidid>https://orcid.org/0000-0002-2315-4219</orcidid></addata></record>
fulltext fulltext
identifier ISSN: 0304-3894
ispartof Journal of hazardous materials, 2023-03, Vol.445, p.130518, Article 130518
issn 0304-3894
1873-3336
language eng
recordid cdi_crossref_primary_10_1016_j_jhazmat_2022_130518
source ScienceDirect Freedom Collection 2022-2024
subjects Active soil layer
As and Zn
Charcoal
Ferric Compounds
Groundwater
Immobilization
Soil
Soil Pollutants - analysis
Zinc
title Constructing the active surface soil layer with ZVI-biochar amendment for simultaneous immobilization of As and Zn in both contaminated soil and groundwater: Continuous versus intermittent infiltration mode
url http://sfxeu10.hosted.exlibrisgroup.com/loughborough?ctx_ver=Z39.88-2004&ctx_enc=info:ofi/enc:UTF-8&ctx_tim=2025-01-01T03%3A08%3A21IST&url_ver=Z39.88-2004&url_ctx_fmt=infofi/fmt:kev:mtx:ctx&rfr_id=info:sid/primo.exlibrisgroup.com:primo3-Article-pubmed_cross&rft_val_fmt=info:ofi/fmt:kev:mtx:journal&rft.genre=article&rft.atitle=Constructing%20the%20active%20surface%20soil%20layer%20with%20ZVI-biochar%20amendment%20for%20simultaneous%20immobilization%20of%20As%20and%20Zn%20in%20both%20contaminated%20soil%20and%20groundwater:%20Continuous%20versus%20intermittent%20infiltration%20mode&rft.jtitle=Journal%20of%20hazardous%20materials&rft.au=Chen,%20Xiang&rft.date=2023-03-05&rft.volume=445&rft.spage=130518&rft.pages=130518-&rft.artnum=130518&rft.issn=0304-3894&rft.eissn=1873-3336&rft_id=info:doi/10.1016/j.jhazmat.2022.130518&rft_dat=%3Cpubmed_cross%3E36493652%3C/pubmed_cross%3E%3Cgrp_id%3Ecdi_FETCH-LOGICAL-c365t-a53756d8c4be8ef0824adb3248871a62a0c1bcbabf3f892fb519e37dba9a17293%3C/grp_id%3E%3Coa%3E%3C/oa%3E%3Curl%3E%3C/url%3E&rft_id=info:oai/&rft_id=info:pmid/36493652&rfr_iscdi=true