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过程工程学报 ›› 2020, Vol. 20 ›› Issue (8): 929-937.DOI: 10.12034/j.issn.1009-606X.219323

• 反应与分离 • 上一篇    下一篇

从熔盐电解废渣中回收钪和氟

付云枫, 王玮玮*   

  1. 中国恩菲工程技术有限公司,北京 100038
  • 收稿日期:2019-10-22 修回日期:2019-12-17 出版日期:2020-08-24 发布日期:2020-08-24
  • 通讯作者: 王玮玮 wangweiwei@enfi.com.cn
  • 基金资助:
    国家博士后自然基金资助项目

Recovery of scandium and fluorine from molten salt electrolysis waste residues

Yunfeng FU, Weiwei WANG*   

  1. The China ENFI Engineering Co., Ltd., Beijing 100038, China
  • Received:2019-10-22 Revised:2019-12-17 Online:2020-08-24 Published:2020-08-24
  • Supported by:
    Postdoctoral Science Foundation of China

摘要: 为无害化处理熔盐电解法制备铝钪中间合金过程产生的熔盐电解废渣并回收其中的有价元素,针对熔盐电解废渣氟盐高、稀土元素钪含量低的特点,提出了一种氢氧化钠?硫酸两步浸取的全湿法处理熔盐电解废渣,回收氟、钪的新工艺。利用X射线衍射仪(XRD)、X射线荧光光谱仪(XRF)、离子色谱仪(IC)、电感耦合等离子体原子发射光谱仪(ICP-OES)、扫描电镜(SEM)对碱浸?酸浸过程中氟、钪元素的走向分布进行了系统考察。结果表明,碱浸过程中熔盐电解废渣中的氟转化成溶解度较低的氟化钠,通过水洗使氟几乎全部进入溶液,而钪留在碱浸水洗渣中,实现了氟、钪分离。利用碱浸水洗渣中的铝以难溶于酸的?-Al2O3形式存在的特性,通过酸浸将碱浸水洗渣中的钪溶解,实现了钪和铝的分离与回收。通过研究碱浸、酸浸过程中浸出剂浓度、液固比、浸出温度和时间等工艺参数对浸出率的影响,得到最佳工艺参数:碱浸过程氢氧化钠浓度100 g/L,液固质量比12:1,温度90℃,浸出时间1.5 h;酸浸过程硫酸浓度1.5 mol/L,液固质量比6:1,温度90℃,浸出时间50 min。碱浸后熔盐电解废渣中可溶性铝和氟的浸出率分别达97.12%和98.71%,氟化钠产品纯度达到98.70%,酸浸过程钪的浸出率达到92.01%。

关键词: 氟盐废渣, 稀土回收, 钪, 湿法浸出

Abstract: To realize the detoxification treatment of the fluorine-containing waste residue from the production of an Al–Sc master alloy by molten salt electrolysis and recover valuable elements, based on the characteristics of a high fluoride and low scandium content in mineralogical compositions, the two-stage hydrometallurgical leaching of electrolytic slag from the Al–Sc alloy prepared by molten salt electrolysis was conducted for the recovery of fluorine and scandium. X-Ray diffraction (XRD), X-ray fluorescence (XRF), ion chromatograph (IC), inductively coupled plasma atomic emission spectrometer (ICP-OES), scanning electron microscope (SEM) were employed to investigate the trend and distribution of fluorine, scandium, and aluminum in detail. Results revealed that during the alkali leaching process, the fluorine in the molten salt slag was converted into sodium fluoride with low solubility, and almost all of the fluorine can be dissolved into the solution by washing with water. The scandium in the molten salt slag remained in the alkali leaching slag; therefore, the separation of fluorine and scandium was realized. By utilizing the insolubility of α-Al2O3 in less concentrated sulfuric acid at a low temperature, the alkali leaching slag was then leached by sulfuric acid to separate and recover scandium from α-Al2O3. Effects of the leaching agent concentration, liquid to solid ratio, leaching temperature, time, and other process parameters on the leaching rates in the alkali leaching and acid leaching processes were investigated. The optimum reaction conditions were determined to be a sodium hydroxide concentration of 100 g/L, a liquid to solid ratio of 12:1, a leaching temperature of 90℃, and a leaching time of 1.5 h for the alkali leaching process, and the sulfuric acid concentration of 1.5 mol/L, a liquid to solid ratio of 6:1, a leaching temperature of 90℃, and a leaching time of 50 min for the acid leaching process. Under the optimized parameters, the leaching rates of soluble aluminum and fluorine in the molten salt residue after alkali leaching were 97.12% and 98.71%, respectively. The purity of the sodium fluoride product reached 98.70%. Furthermore, the leaching rate of scandium reached 92.01% during the subsequent acid leaching process.

Key words: flouride-containing waste residue, recovery of rare earth, scandium, hydrometallurgical leaching