微波制备碱木质素生物炭对Zn<sup>2+</sup>的吸附性能及机理

陈龙; 李凯; 涂智; 周羽; 张继龙; 弭宝彬; 武芳芳

doi:10.13205/j.hjgc.202308013

微波制备碱木质素生物炭对Zn²⁺的吸附性能及机理

doi: 10.13205/j.hjgc.202308013

陈龙¹,
李凯¹,
涂智²,
周羽¹,
张继龙¹,
弭宝彬³,
武芳芳^1, ,

1. 湖南农业大学化学与材料科学学院, 长沙 410125;
2. 湖南省农业科学院蔬菜研究所, 长沙 410125;
3. 中机国际工程设计研究院有限责任公司, 长沙 410021

基金项目:

湖南省教育厅重点科研项目(20A245)

湖南省自然科学基金面上项目(2021JJ30410,2022JJ30348)

湖南省科技人才托举工程项目(2022TJ-N15)

详细信息

作者简介:
陈龙(1997-),男,硕士,主要研究方向为农林废弃生物质热解及生物炭环境应用。1752910282@qq.com

通讯作者:
武芳芳(1987-),女,副教授,主要研究方向为生物质综合利用技术及生物炭环境治理工程。wufangfang@hunau.edu.cn

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出版历程
- 收稿日期: 2022-06-14
- 网络出版日期: 2023-11-15

ADSORPTION PERFORMANCE AND MECHANISM OF Zn²⁺ ON MICROWAVE-PREPARED ALKALI LIGNIN BIOCHAR

1. School of Chemistry and Materials Science, Hunan Agricultural University, Changsha 410125, China;
2. Institute of Vegetable Research, Hunan Academy of Agricultural Sciences, Changsha 410125, China;
3. China Machinery International Engineering Design & Research Institute Co., Ltd, Changsha 410021, China

摘要

摘要: 碱木质素是造纸工业的主要副产品。为探索碱木质素资源化利用的可行途径,以碱木质素为原料,在微波热解条件下制备得到生物炭,并研究了生物炭对水体中Zn²⁺的吸附性能和吸附机理。结果表明:在炭化温度为400 ℃,投加量为0.4 g/L,Zn²⁺初始浓度为200 mg/L,pH为5的吸附条件下,碱木质素生物炭对Zn²⁺的平衡吸附量达到313.7~326.7 mg/g,为最佳吸附效果;准二级动力学模型和Langmuir模型能更好地拟合碱木质素生物炭对Zn²⁺的吸附过程,说明生物炭的吸附速率受化学吸附机制的控制,且由Langmuir模型拟合得到生物炭对Zn²⁺的最大吸附量(q_m)为371.3~412.3 mg/g;吸附机理研究表明,碱木质素生物炭对Zn²⁺的吸附机理包括矿物共沉淀作用、DOM吸附作用、表面络合作用(含氧官能团络合和Zn²⁺-π配位作用)和离子交换作用。此外,生物炭吸附机理量化分析结果表明,矿物共沉淀和表面络合作用对生物炭吸附量的贡献分别为81.8%~85.6%和7.6%~9.9%。
- 碱木质素 /
- 生物炭 /
- Zn²⁺ /
- 吸附 /
- 机理定量分析
Abstract: Alkali lignin is the major by-product of the paper-making industry. In order to explore a feasible way for resource utilization of alkali lignin, biochar was prepared from alkali lignin under microwave pyrolysis, and the adsorption performance and mechanism of biochar were further investigated in this paper. The results showed that the best adsorption effect of biochar was achieved under the adsorption condition of a charring temperature of 400 ℃, a biochar dosage of 0.4 g/L, an initial Zn²⁺ concentration of 200 mg/L, and solution pH=5; the adsorption process could be well described by the Langmuir model and the quasi-secondary kinetic model, indicating that the adsorption process was dominated by chemisorption, and the maximum adsorption capacity (q_m) of biochar calculated from the Langmuir fitting reached 371.3 to 412.3 mg/g; the adsorption mechanism analysis of biochar revealed that the mechanisms mainly include mineral co-precipitation, DOM interaction, surface complexation (O-functional group complexation and Zn²⁺-π complexation), and ionic exchange. In addition, the results of quantitative analysis of the adsorption mechanism showed that mineral co-precipitation and surface complexation contributed 81.8%~85.6% and 7.6%~9.9% to the adsorption capacities of biochars, respectively.
- alkali lignin /
- biochar /
- Zn²⁺ /
- adsorption /
- quantitative analysis of mechanism

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