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生物炭衍生污泥对土壤中重金属吸附和固定的影响。

Effects of Biochar-Derived Sewage Sludge on Heavy Metal Adsorption and Immobilization in Soils.

作者信息

Zhou Dan, Liu Dan, Gao Fengxiang, Li Mengke, Luo Xianping

机构信息

Jiangxi Key Laboratory of Mining & Metallurgy Environmental Pollution Control, Jangxi University of Science and Technology, Ganzhou 341000, China.

Key Laboratory of Ionic-Type Rare Earth Resources Development and Application, Ministry of Education, Ganzhou 341000, China.

出版信息

Int J Environ Res Public Health. 2017 Jun 23;14(7):681. doi: 10.3390/ijerph14070681.

Abstract

The object of this study was to evaluate the effect of sewage sludge biochar on adsorption and mobility of Cr, Mn, Cu, and Zn. Biochar (BC400) was produced via pyrolysis of municipal sewage sludge at 400 °C. Maximum adsorption capacities () for Zn, Cr, Mn, and Cu were 5.905, 5.724, 5.681, and 5.342 mg·g, respectively, in the mono-metal solution and 2.475, 8.204, 1.01, and 5.415 mg·g, respectively, in the multi-metal solution. The adsorption capacities for Mn, Cu, and Zn decreased in the multi-metal solution due to competitive adsorption, whereas the capacity for Cr increased. Surface precipitation is an important mechanism in the sorption of these metals on BC400. The 360-day incubation experiment showed that BC400 application reduced metal mobility in contaminated soils, which was attributed to the substantial decreases in the acid-soluble fractions of Cr, Mn, Cu, and Zn (72.20%, 70.38%, 50.43%, and 29.78%, respectively). Furthermore, the leaching experiment using simulated acid rain indicated that the addition of BC400 enhanced the acid buffer capacity of contaminated soil, and the concentration of Cr, Mn, Cu, and Zn in the leachate was lower than in untreated soil. Overall, this study indicates that sewage sludge biochar application reduces the mobility of heavy metal in co-contaminated soil, and this adsorption experiment is suitable for the evaluation of biochar properties for remediation.

摘要

本研究的目的是评估污水污泥生物炭对铬、锰、铜和锌吸附及迁移性的影响。生物炭(BC400)通过城市污水污泥在400℃下热解制备。在单金属溶液中,锌、铬、锰和铜的最大吸附容量()分别为5.905、5.724、5.681和5.342 mg·g,在多金属溶液中分别为2.475、8.204、1.01和5.415 mg·g。由于竞争吸附,多金属溶液中锰、铜和锌的吸附容量降低,而铬的容量增加。表面沉淀是这些金属在BC400上吸附的重要机制。360天的培养实验表明,施用BC400降低了污染土壤中金属的迁移性,这归因于铬、锰、铜和锌酸溶态部分的大幅降低(分别为72.20%、70.38%、50.43%和29.78%)。此外,使用模拟酸雨的淋溶实验表明,添加BC400提高了污染土壤的酸缓冲能力,淋滤液中铬、锰、铜和锌的浓度低于未处理土壤。总体而言,本研究表明,施用污水污泥生物炭可降低复合污染土壤中重金属的迁移性,且该吸附实验适用于评估生物炭修复性能。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4788/5551119/ea6b44068e9e/ijerph-14-00681-g001.jpg

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