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钽铌冶炼厂含氟废水资源化治理技术
引用本文:杜璞欣,宋卫锋,刘勇,周吉奎,吕先谨. 钽铌冶炼厂含氟废水资源化治理技术[J]. 化工环保, 2012, 40(5): 487-493. DOI: 10.3969/j.issn.1006-1878.2020.05.005
作者姓名:杜璞欣  宋卫锋  刘勇  周吉奎  吕先谨
作者单位:1.广东工业大学 环境科学与工程学院,广东 广州 510006;2.广东省资源综合利用研究所,广东 广州 510650;3.稀有金属分离与综合利用国家重点实验室,广东 广州 510650;4.广东省矿产资源开发和综合利用重点实验室,广东 广州 510650
基金项目:广东省省级科技计划项目 (2015B020235003); 广东省科学院发展专项资金项目(2018GDASCX-0109)
摘    要:采用合金膜电渗析法分离富集钽铌冶炼厂含氟废水中的F-和SO42-。最优的工艺运行条件为:膜对电压0.500 V,膜面流速4.09 cm/s。在此条件下电渗析30 min,F-去除率达97.53%,SO42-去除率接近100%。优化条件下运行电渗析器,一段淡水中大部分的F-和SO42-均被去除,可以直接回用。一段电渗析的浓水再经多段电渗析浓缩,以LiOH·H2O沉淀F-得到LiF产品,该LiF产品纯度达99.06%,满足GB/T 22666—2008标准的3级品要求。LiF收率为84.92%,F-整体回收率为79.45%。

关 键 词:钽铌冶炼  含氟废水  电渗析  氟化锂  
收稿时间:2020-02-03

Resource recovery technology of fluorine-containing wastewater intantalum and niobium smelting plant
DU Puxin,SONG Weifeng,LIU Yong,ZHOU Jikui,Lv Xianjin. Resource recovery technology of fluorine-containing wastewater intantalum and niobium smelting plant[J]. Environmental Protection of Chemical Industry, 2012, 40(5): 487-493. DOI: 10.3969/j.issn.1006-1878.2020.05.005
Authors:DU Puxin  SONG Weifeng  LIU Yong  ZHOU Jikui  Lv Xianjin
Affiliation:1. School of Environmental Science and Engineering,Guangdong University of Technology,Guangzhou 510006,China;2. Guangdong Institute of Resources Comprehensive Utilization,Guangzhou 510650,China;3. State Key Laboratory of Rare Metals Separation and Comprehensive Utilization,Guangzhou 510650,China;4. GuangdongKey Laboratory of Mineral Resources Development and Comprehensive Utilization,Guangzhou 510650,China
Abstract:F- and SO42- in fluorine-containing wastewater in a tantalum and niobium smelting plant were separated and enriched by alloy membrane electrodialysis. The optimal process operation conditions are as followsvoltage on a pair of membranes 0.500 V,membrane surface velocity 4.09 cm/s. When the wastewater was treated by electrodialysis under these conditions for 30 min,the F- removal rate reached 97.53% and the SO42- removal rate was close to 100%. Running the electrodialyzer under optimized conditions,most of the F- and SO42- in the diluted solution of the first-stage process were removed and could be reused directly. The concentrated water of the first-stage electrodialysis was then subjected to multiple stages of electrodialysis and LiF was obtained by F-precipitation with LiOH·H2O. The purity of the product reaches 99.06%,which meets the Grade 3 standard of GB/T 22666-2008. The yield of LiF is 84.92%,and the overall recovery rate of F- is 79.45%.
Keywords:tantalum and niobium smelting  fluorine-containing wastewater  electrodialysis  lithium fluoride  
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