Biochar-induced changes in soil properties affected immobilization/mobilization of metals/metalloids in contaminated soils
Purpose Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable biochar properties and soil types helps elucidating the meticulous roles of biochar in immobilizing/mobilizing metals/metalloids in contaminated so...
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Published in | Journal of soils and sediments Vol. 17; no. 3; pp. 717 - 730 |
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Main Authors | , , , , , |
Format | Journal Article |
Language | English |
Published |
Berlin/Heidelberg
Springer Berlin Heidelberg
01.03.2017
Springer Nature B.V |
Subjects | |
Online Access | Get full text |
ISSN | 1439-0108 1614-7480 |
DOI | 10.1007/s11368-015-1339-4 |
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Abstract | Purpose
Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable biochar properties and soil types helps elucidating the meticulous roles of biochar in immobilizing/mobilizing metals/metalloids in contaminated soils.
Materials and methods
Six biochars were produced from widely available agricultural wastes (i.e., soybean stover, peanut shells and pine needles) at two pyrolysis temperatures of 300 and 700 °C, respectively. The Pb-, Cu-, and Sb-contaminated shooting range soils and Pb-, Zn-, and As-contaminated agricultural soils were amended with the produced biochars. The mobility of metals/metalloids was assessed by the standard batch leaching test, principal component analysis and speciation modeling.
Results and discussion
The changes in soil properties were correlated to feedstock types and pyrolysis temperatures of biochars based on the principal component analysis. Biochars produced at 300 °C were more efficient in decreasing Pb and Cu mobility (>93 %) in alkaline shooting range soil via surface complexation with carboxyl groups and Fe-/Al-minerals of biochars as well as metal-phosphates precipitation. By contrast, biochars produced at 700 °C outperformed their counterparts in decreasing Pb and Zn mobility (100 %) in acidic agricultural soil by metal-hydroxides precipitation due to biochar-induced pH increase. However, Sb and As mobility in both soils was unfavorably increased by biochar amendment, possibly due to the enhanced electrostatic repulsion and competition with phosphate.
Conclusions
It is noteworthy that the application of biochars is not equally effective in immobilizing metals or mobilizing metalloids in different soils. We should apply biochar to multi-metal contaminated soil with great caution and tailor biochar production for achieving desired outcome and avoiding adverse impact on soil ecosystem. |
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AbstractList | Purpose Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable biochar properties and soil types helps elucidating the meticulous roles of biochar in immobilizing/mobilizing metals/metalloids in contaminated soils. Materials and methods Six biochars were produced from widely available agricultural wastes (i.e., soybean stover, peanut shells and pine needles) at two pyrolysis temperatures of 300 and 700 °C, respectively. The Pb-, Cu-, and Sb-contaminated shooting range soils and Pb-, Zn-, and As-contaminated agricultural soils were amended with the produced biochars. The mobility of metals/metalloids was assessed by the standard batch leaching test, principal component analysis and speciation modeling. Results and discussion The changes in soil properties were correlated to feedstock types and pyrolysis temperatures of biochars based on the principal component analysis. Biochars produced at 300 °C were more efficient in decreasing Pb and Cu mobility (>93 %) in alkaline shooting range soil via surface complexation with carboxyl groups and Fe-/Al-minerals of biochars as well as metal-phosphates precipitation. By contrast, biochars produced at 700 °C outperformed their counterparts in decreasing Pb and Zn mobility (100 %) in acidic agricultural soil by metal-hydroxides precipitation due to biochar-induced pH increase. However, Sb and As mobility in both soils was unfavorably increased by biochar amendment, possibly due to the enhanced electrostatic repulsion and competition with phosphate. Conclusions It is noteworthy that the application of biochars is not equally effective in immobilizing metals or mobilizing metalloids in different soils. We should apply biochar to multi-metal contaminated soil with great caution and tailor biochar production for achieving desired outcome and avoiding adverse impact on soil ecosystem. Purpose Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable biochar properties and soil types helps elucidating the meticulous roles of biochar in immobilizing/mobilizing metals/metalloids in contaminated soils. Materials and methods Six biochars were produced from widely available agricultural wastes (i.e., soybean stover, peanut shells and pine needles) at two pyrolysis temperatures of 300 and 700 °C, respectively. The Pb-, Cu-, and Sb-contaminated shooting range soils and Pb-, Zn-, and As-contaminated agricultural soils were amended with the produced biochars. The mobility of metals/metalloids was assessed by the standard batch leaching test, principal component analysis and speciation modeling. Results and discussion The changes in soil properties were correlated to feedstock types and pyrolysis temperatures of biochars based on the principal component analysis. Biochars produced at 300 °C were more efficient in decreasing Pb and Cu mobility (>93 %) in alkaline shooting range soil via surface complexation with carboxyl groups and Fe-/Al-minerals of biochars as well as metal-phosphates precipitation. By contrast, biochars produced at 700 °C outperformed their counterparts in decreasing Pb and Zn mobility (100 %) in acidic agricultural soil by metal-hydroxides precipitation due to biochar-induced pH increase. However, Sb and As mobility in both soils was unfavorably increased by biochar amendment, possibly due to the enhanced electrostatic repulsion and competition with phosphate. Conclusions It is noteworthy that the application of biochars is not equally effective in immobilizing metals or mobilizing metalloids in different soils. We should apply biochar to multi-metal contaminated soil with great caution and tailor biochar production for achieving desired outcome and avoiding adverse impact on soil ecosystem. Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable biochar properties and soil types helps elucidating the meticulous roles of biochar in immobilizing/mobilizing metals/metalloids in contaminated soils. Six biochars were produced from widely available agricultural wastes (i.e., soybean stover, peanut shells and pine needles) at two pyrolysis temperatures of 300 and 700 degree C, respectively. The Pb-, Cu-, and Sb-contaminated shooting range soils and Pb-, Zn-, and As-contaminated agricultural soils were amended with the produced biochars. The mobility of metals/metalloids was assessed by the standard batch leaching test, principal component analysis and speciation modeling. The changes in soil properties were correlated to feedstock types and pyrolysis temperatures of biochars based on the principal component analysis. Biochars produced at 300 degree C were more efficient in decreasing Pb and Cu mobility (>93 %) in alkaline shooting range soil via surface complexation with carboxyl groups and Fe-/Al-minerals of biochars as well as metal-phosphates precipitation. By contrast, biochars produced at 700 degree C outperformed their counterparts in decreasing Pb and Zn mobility (100 %) in acidic agricultural soil by metal-hydroxides precipitation due to biochar-induced pH increase. However, Sb and As mobility in both soils was unfavorably increased by biochar amendment, possibly due to the enhanced electrostatic repulsion and competition with phosphate. It is noteworthy that the application of biochars is not equally effective in immobilizing metals or mobilizing metalloids in different soils. We should apply biochar to multi-metal contaminated soil with great caution and tailor biochar production for achieving desired outcome and avoiding adverse impact on soil ecosystem. |
Author | Lee, Sang Soo Tsang, Daniel C. W. Ahmad, Mahtab Al-Wabel, Mohammad I. Ok, Yong Sik Lee, Sung Eun |
Author_xml | – sequence: 1 givenname: Mahtab surname: Ahmad fullname: Ahmad, Mahtab organization: Korea Biochar Research Center, Kangwon National University, Soil Sciences Department, College of Food and Agricultural Sciences, King Saud University – sequence: 2 givenname: Sang Soo surname: Lee fullname: Lee, Sang Soo organization: Korea Biochar Research Center, Kangwon National University – sequence: 3 givenname: Sung Eun surname: Lee fullname: Lee, Sung Eun organization: School of Applied Biosciences, Kyungpook National University – sequence: 4 givenname: Mohammad I. surname: Al-Wabel fullname: Al-Wabel, Mohammad I. organization: Soil Sciences Department, College of Food and Agricultural Sciences, King Saud University – sequence: 5 givenname: Daniel C. W. surname: Tsang fullname: Tsang, Daniel C. W. email: dan.tsang@polyu.edu.hk organization: Department of Civil and Environmental Engineering, Hong Kong Polytechnic University – sequence: 6 givenname: Yong Sik surname: Ok fullname: Ok, Yong Sik email: soilok@kangwon.ac.kr organization: Korea Biochar Research Center, Kangwon National University |
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Keywords | Soil remediation Bioavailability Black carbon Plant biomass Charcoal Soil contamination |
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Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable... Purpose Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable... Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable biochar... PURPOSE: Remediation of metal contaminated soil with biochar is attracting extensive interest in recent years. Understanding the significance of variable... |
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SubjectTerms | Agricultural land Agricultural pollution agricultural soils agricultural wastes antimony Arachis hypogaea arsenic biochar Biochar for a Sustainable Environment Biomass Bioremediation Charcoal conifer needles copper Earth and Environmental Science electrostatic interactions Environment Environmental Physics feedstocks Heavy metals Hydroxides Leaching Lead Metals Mobility peanut hulls phosphates Pine needles polluted soils principal component analysis Principal components analysis Pyrolysis remediation Soil conditioners Soil contamination soil ecosystems Soil properties Soil Science & Conservation Soil types Soybeans Speciation Stover temperature zinc |
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Title | Biochar-induced changes in soil properties affected immobilization/mobilization of metals/metalloids in contaminated soils |
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