首页|烟秆生物炭吸附去除水中吡虫啉的研究

烟秆生物炭吸附去除水中吡虫啉的研究

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以农业废弃烟秆为原料,通过热解法制备生物炭,研究其对水中典型新烟碱类杀虫剂——吡虫啉(IMI)的吸附去除。结果表明,烟秆生物炭对IMI的吸附效能随烧结温度的升高而增大。900℃烧结2 h的生物炭(BC900)表面含有多种含氧官能团,具有较大的比表面积、丰富的孔隙结构、弱的亲水性和极性,对IMI有最佳的吸附效果,最大理论吸附量为124。87 mg/g;增大BC900投加量以及酸性条件均有利于IMI的吸附,而水中常见阴离子的存在对吸附有抑制作用并遵循以下规律:HCO3->SO42->NO3->Cl-。BC900对IMI的吸附符合准二级动力学方程,等温吸附曲线符合Freundlich模型。吸附机理包括表面吸附、孔隙填充作用、π-π电子受供体相互作用和氢键作用。
Study on adsorptive removal of imidacloprid in water by tobacco stalk biochar
Adsorptive removal of imidacloprid(IMI),a typical neonicotinoid insecticide in water,by bio-char prepared from agriculturally wasted tobacco stalks by pyrolysis was studied.The results showed that the adsorption efficiency of IMI on tobacco stalk biochar increased with the increase of sintering tempera-tures.The biochar(BC900)sintered at 900 ℃ for 2 h owned a variety of oxygen-containing functional groups on its surface,more large specific surface area,rich pore structure,weak hydrophilicity and polari-ty,which had the best adsorption capacity for IMI.Its maximum theoretical adsorption amount was 124.87 mg/g.Moreover,increasing the dosage of BC900 and acidic conditions were benefit to the adsorp-tion of IMI,while the existence of the common anions in water inhibited IMI adsorption and abided by the follow rules:HCO3->SO42->NO3->Cl-.The pseudo-second-order kinetic model and the Freundlich model fitted well with the experimental data.The mechanism of IMI adsorption on BC900 included surface adsorption,pore-filling effect,π-π electron donor-acceptor and hydrogen bonding.

tobacco stalkbiocharadsorptionimidaclopridmechanism

赵兴链、杨莉娜、王媛、董南

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贵州大学资源与环境工程学院,贵州贵阳 550025

贵州大学喀斯特地质资源与环境教育部重点实验室,贵州贵阳 550025

贵州大学化学与化工学院,贵州贵阳 550025

烟秆 生物炭 吸附 吡虫啉 机理

贵州省自然科学基金

黔科合基础-ZK[2021]一般054

2024

应用化工
陕西省石油化工研究设计院 陕西省化工学会

应用化工

CSTPCD北大核心
影响因子:0.411
ISSN:1671-3206
年,卷(期):2024.53(2)
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