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活性污泥法去除水溶液中溶解态硫化物:机理与特性。

Removal of dissolved sulfides in aqueous solution by activated sludge: mechanism and characteristics.

机构信息

Environmental Simulation and Pollution Control State Key Joint Laboratory, School of Environment, Tsinghua University, Beijing 100084, China.

Environmental Simulation and Pollution Control State Key Joint Laboratory, School of Environment, Tsinghua University, Beijing 100084, China; Graduate School at Shenzhen, Tsinghua University, Shenzhen 518055, PR China.

出版信息

J Hazard Mater. 2017 Feb 15;324(Pt B):732-738. doi: 10.1016/j.jhazmat.2016.11.048. Epub 2016 Nov 18.

Abstract

Activated sludge recycling has been developed as a novel technique to directly prevent volatile sulfides emission from wastewater influents. In this study, mechanisms and characteristics of dissolved sulfides removal in aqueous solution by activated sludge were investigated. When DO content in water was 0.49mg/L, 70% of removed dissolved sulfides were released back from the activated sludge by lowering pH to 1. The SEM/EDS result revealed that removed sulfur was fixed in activated sludge and the XPS result showed that fixed sulfur had an oxidation state of -2. FTIR results showed that primary amine group (R-NH) could be one of the radical groups bonding sulfides. All these results verified that sulfides removal by activated sludge is primarily attributed to adsorption, rather than biodegradation, under low DO conditions in 40min. The equilibrium isotherm data fit the Langmuir isotherm model well. The maximum adsorption capacity (q) ranged in 25-38mg/g at temperatures of 10-40°C. The adsorption kinetic data fit the pseudo-second-order model well. The amounts of adsorbed sulfides at equilibrium (q) were positively proportional to temperature, initial sulfides concentration and agitation speed. These results indicate that sulfides adsorption could be a chemical sorption or ion exchange process.

摘要

活性污泥再循环已被开发为一种从废水中直接防止挥发性硫化物排放的新技术。在这项研究中,研究了活性污泥在水溶液中去除溶解态硫化物的机制和特性。当水中的 DO 含量为 0.49mg/L 时,通过将 pH 值降低到 1,可以将 70%的已去除的溶解态硫化物从活性污泥中释放回水中。SEM/EDS 结果表明,去除的硫被固定在活性污泥中,XPS 结果表明固定的硫的氧化态为-2。FTIR 结果表明,伯胺基(R-NH)可能是与硫化物结合的自由基基团之一。所有这些结果都证实了在 40 分钟内,低 DO 条件下,活性污泥对硫化物的去除主要归因于吸附,而不是生物降解。平衡等温线数据很好地符合 Langmuir 等温线模型。在 10-40°C 的温度下,最大吸附容量(q)范围为 25-38mg/g。吸附动力学数据很好地符合拟二级动力学模型。平衡时吸附的硫化物量(q)与温度、初始硫化物浓度和搅拌速度呈正相关。这些结果表明,硫化物的吸附可能是一种化学吸附或离子交换过程。

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