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用铝土矿残渣(赤泥)从水溶液中去除 Cr(Ⅲ):活性成分的鉴定和柱试验。

Removal of Cr (Ⅲ) from aqueous solution by using bauxite residue (red mud): Identification of active components and column tests.

机构信息

State Key Laboratory of Pollution Control and Resource Reuse, College of Environmental Science and Engineering, UNEP-TONGJI Institute of Environment for Sustainable Development, Tongji University, Siping Rd 1239, Shanghai, 200092, China; Shanghai Institute of Pollution Control and Ecological Security, Key Laboratory of Yangtze River Water Environment, Ministry of Education, Shanghai, 200092, China.

State Key Laboratory of Pollution Control and Resource Reuse, College of Environmental Science and Engineering, UNEP-TONGJI Institute of Environment for Sustainable Development, Tongji University, Siping Rd 1239, Shanghai, 200092, China; Shanghai Institute of Pollution Control and Ecological Security, Key Laboratory of Yangtze River Water Environment, Ministry of Education, Shanghai, 200092, China.

出版信息

Chemosphere. 2020 Apr;245:125560. doi: 10.1016/j.chemosphere.2019.125560. Epub 2019 Dec 10.

Abstract

Bauxite residue is the by-product of the aluminium industry with an annual output of more than 200 million metric tons in China. Its treatment is still a big problem because more than 96% of that is stockpiled on land causing environmental pollution and threatening the human health. This study used bauxite residue to remove Cr (Ⅲ) from aqueous solution and analyzed the removal mechanism. The removal time was dependent on the initial concentrations of Cr (Ⅲ) and different active components acted on different reaction period. Reaction time increased from <5 min to >2 h with an increase of Cr (Ⅲ) concentration from 5 to 100 and 170 mg/L. The existing forms of adsorbed-Cr were iron oxide-bound Cr (40.80%-87.85%), sulfide-bound Cr (4.04%-20.28%) and residue (6.60%-33.72%). All the components started to react as soon as bauxite residue was added. Cr did not precipitate in the presence of high alkalinity bauxite residue due to the slow release of alkalinity maintaining pH < 6, thus producing Cr(OH), Cr(OH) and Cr(OH) by hydrolysis without precipitation. FeO and Al-containing components were the main active phases for Cr (Ⅲ) removal, with the reaction time lasting more than 2 h and producing CaAlCrO, AlCr, (Si, Al)O, Fe(Cr, Al)O, FeCrSiO, MgCrFeO and MgCrFeO. Finally, bauxite residue was granulated and used for column tests. Cr (Ⅲ) wastewater (1 and 50 mg/L) was treated and the effluent can meet the first level of the Shanghai standard (0.1 mg/L) defined by Integrated Wastewater Discharge Standard (DB 31/199-2009).

摘要

铝土矿残渣是铝工业的副产品,中国每年的产量超过 2 亿吨。其处理仍然是一个大问题,因为超过 96%的铝土矿残渣被储存在土地上,造成环境污染,威胁人类健康。本研究使用铝土矿残渣从水溶液中去除 Cr(Ⅲ),并分析了去除机制。去除时间取决于 Cr(Ⅲ)的初始浓度,不同的活性成分作用于不同的反应期。当 Cr(Ⅲ)浓度从 5 增加到 100 和 170mg/L 时,反应时间从<5min 增加到>2h。吸附-Cr 的存在形式为氧化铁结合态 Cr(40.80%-87.85%)、硫化物结合态 Cr(4.04%-20.28%)和残渣(6.60%-33.72%)。铝土矿残渣一加入,所有成分就开始反应。由于高碱度铝土矿残渣的碱度释放缓慢,使 pH<6,Cr 不会沉淀,从而通过水解产生 Cr(OH)、Cr(OH)和 Cr(OH),而不沉淀。FeO 和含 Al 的成分是去除 Cr(Ⅲ)的主要活性相,反应时间超过 2h,生成 CaAlCrO、AlCr、(Si,Al)O、Fe(Cr,Al)O、FeCrSiO、MgCrFeO 和 MgCrFeO。最后,将铝土矿残渣造粒并用于柱试验。处理 Cr(Ⅲ)废水(1 和 50mg/L),出水可达到《综合污水排放标准》(DB 31/199-2009)规定的上海市一级标准(0.1mg/L)。

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