机构地区:[1]School of Environmental and Chemical Engineering,Foshan University,528000 Foshan,Guangdong,China [2]Agronomy College,Shenyang Agricultural University,110866 Shenyang,China [3]Key Laboratory of Biochar and Soil Improvement,Ministry of Agriculture and Rural Affairs,110866 Shenyang,China [4]Department of Chemistry and Biotechnology,Center for Translational Atomaterials,Swinburne University of Technology,3122 Hawthorn,VIC,Australia [5]Future Industries Institute,University of South Australia,Mawson Lakes,SA 5095,Australia [6]Department of Separation Science,LUT School of Engineering Science,LUT University,Sammonkatu 12,FI-50130 Mikkeli,Finland [7]School of Agriculture and Environment,The University of Western Australia,6001 Perth,WA,Australia [8]The UWA Institute of Agriculture,The University of Western Australia,6001 Perth,WA,Australia [9]Institute of Agricultural Resources and Environment,Guangdong Academy of Agricultural Sciences,510640 Guangzhou,China [10]State Key Laboratory of Environmental Criteria and Risk Assessment,Chinese Research Academy of Environmental Sciences,100012 Beijing,China [11]Department of Biology,Hong Kong Baptist University,Kowloon Tong,Hong Kong SAR,China [12]School of Environment,Tsinghua University,100084 Beijing,China [13]Guangdong Green Technologies Co.,Ltd,528100 Foshan,China
出 处:《Biochar》2022年第1期561-576,共16页生物炭(英文)
基 金:the National Key Research and Development Program of China(2020YFC1807704);the National Natural Science Foundation of China(21876027);the Science and Technology Innovation Project of Foshan,China(1920001000083).
摘 要:Removal of antimonite[Sb(Ⅲ)]from the aquatic environment and reducing its biotoxicity is urgently needed to safeguard environmental and human health.Herein,crawfish shell-derived biochars(CSB),pyrolyzed at 350,500,and 650℃,were used to remediate Sb(Ⅲ)in aqueous solutions.The adsorption data best fitted to the pseudo-second-order kinetic and Langmuir isotherm models.Biochar produced at 350℃(CSB350)showed the highest adsorption capacity(27.7 mg g^(−1)),and the maximum 78%oxidative conversion of Sb(Ⅲ)to Sb(V).The adsorption results complemented with infrared(FTIR),X-ray photoelectron(XPS),and near-edge X-ray absorption fine structure(NEXAFS)spectroscopy analyses indicated that the adsorption of Sb(Ⅲ)on CSB involved electrostatic interaction,surface complexation with oxygen-containing functional groups(C=O,O=C-O),π-πcoordination with aromatic C=C and C-H groups,and H-bonding with-OH group.Density functional theory calculations verified that surface complexation was the most dominant adsorption mechanism,whilstπ-πcoordination and H-bonding played a secondary role.Furthermore,electron spin resonance(ESR)and mediated electrochemical reduction/oxidation(MER/MEO)analyses confirmed that Sb(Ⅲ)oxidation at the biochar surface was governed by persistent free radicals(PFRs)(•O_(2)^(−)and•OH)and the electron donating/accepting capacity(EDC/EAC)of biochar.The abundance of preferable surface functional groups,high concentration of PFRs,and high EDC conferred CSB350 the property of an optimal adsorbent/oxidant for Sb(Ⅲ)removal from water.The encouraging results of this study call for future trials to apply suitable biochar for removing Sb(Ⅲ)from wastewater at pilot scale and optimize the process.
关 键 词:SORPTION Heavy metal SYNCHROTRON Density functional theory Contaminated water
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