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作 者:Chaoyang Zhang Zili Jiang Wanxue Sun Yuyuan Tang Zhanying Zhang Changrong Shi Xiuxiu Ruan
机构地区:[1]School of Environmental and Chemical Engineering,Shanghai University,No.99 Shangda Road,Shanghai 200444,People’s Republic of China. [2]Center of Green Urban Mining and Industry Ecology,Shanghai University,No.99 Shangda Road,Shanghai 200444,People’s Republic of China. [3]School of Mechanical,Medical and Process Engineering,Faculty of Engineering,Queensland University of Technology,Brisbane,QLD 4000,Australia. [4]Centre for Agriculture and the Bioeconomy,Queensland University of Technology,Brisbane,QLD 4000,Australia.
出 处:《Biochar》2024年第1期1230-1245,共16页生物炭(英文)
基 金:supported by the National Key Research and Development Program of China(No.2020YFC1808103);Science&Technology Commission of Shanghai Municipality(No.22002400500);National Natural Science Foundation of China(20907029 and 21577085);Natural Science Fund Projects of Shanghai Municipal Science and Technology Commission(No.14ZR1415600).
摘 要:To reveal the influence of the diversity of precursors on the formation of environmental persistent free radicals(EPFRs),pomelo peel(PP)and its physically divided portion,pomelo cuticle(PC),and white fiber(WF)were used as precursors to prepare six hydrochars:PPH-Fe,PCH-Fe,WFH-Fe,PPH,PCH,and WFH with and without Fe(III)addition during hydrothermal carbonization(HTC).PPH-Fe and WFH-Fe had higher EPFRs content(9.11×10^(18)and 8.25×10^(18)spins·g^(−1))compared to PPH and WFH(3.33×10^(18)and 2.96×10^(18)spins·g^(−1)),indicating that iron-doping favored EPFRs formation.However,PCH-Fe had lower EPFRs content(2.78×10^(18)spins·g^(−1))than PCH(7.95×10^(18)spins·g^(−1)),possibly due to excessive iron leading to the consumption of the generated EPFRs.For another reason,the required Fe(III)amount for EPFRs formation might vary among different precursors.PC has a lower concentration of phenolic compounds but 68-97%fatty acids,while WF and PP are rich in cellulose and lignin.In the Fenton-like reaction,oxygen-centered radicals of hydrochar played a significant role in activating H_(2)O_(2)and efficiently degrading bisphenol A(BPA).Mechanisms of reactive oxygen species(ROS)generation in hydrochar/H_(2)O_(2)system were proposed.EPFRs on hydrochar activate H_(2)O_(2)via electron transfer,creating·OH and 1O2,leading to BPA degradation.More importantly,the embedded EPFRs on the hydrochar’s inner surface contributed to the prolonged Fenton-like reactivity of PPH-Fe stored for 45 days.This study demonstrates that by optimizing precursor selection and iron doping,hydrochars can be engineered to maximize their EPFRs content and reactivity,providing a cost-effective solution for the degradation of hazardous pollutants.
关 键 词:Pomelo peel Hydrochar Environmental persistent free radicals(EPFRs) CATALYSIS FENTON-LIKE BPA degradation
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