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Frontiers of Chemical Science and Engineering

ISSN 2095-0179

ISSN 2095-0187(Online)

CN 11-5981/TQ

Postal Subscription Code 80-969

2018 Impact Factor: 2.809

Front. Chem. Sci. Eng.    2020, Vol. 14 Issue (4) : 639-650    https://doi.org/10.1007/s11705-019-1806-3
RESEARCH ARTICLE
Investigation of solution chemistry to enable efficient lithium recovery from low-concentration lithium-containing wastewater
Chunlong Zhao1,2, Mingming He2, Hongbin Cao2, Xiaohong Zheng2, Wenfang Gao2, Yong Sun3, He Zhao2, Dalong Liu4, Yanling Zhang1, Zhi Sun2()
1. State Key Laboratory of Advanced Metallurgy, University of Science and Technology Beijing, Beijing 100083, China
2. Beijing Engineering Research Center of Process Pollution Control, Key Laboratory of Green Process and Engineering, Institute of Process Engineering, Chinese Academy of Sciences, Beijing 100190, China
3. University of Nottingham Ningbo China, Ningbo 315100, China
4. Henan Bingsheng Biotechnology Company Limited, Kaifeng 475103, China
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Abstract

In the production of lithium-ion batteries (LIBs) and recycling of spent LIBs, a large amount of low-concentration lithium-containing wastewater (LCW) is generated. The recovery of Li from this medium has attracted significant global attention from both the environmental and economic perspectives. To achieve effective Li recycling, the features of impurity removal and the interactions among different ions must be understood. However, it is generally difficult to ensure highly efficient removal of impurity ions while retaining Li in the solution for further recovery. In this study, the removal of typical impurity ions from LCW and the interactions between these species were systematically investigated from the thermodynamic and kinetics aspects. It was found that the main impurities (e.g., Fe3+, Al3+, Ca2+, and Mg2+) could be efficiently removed with high Li recovery by controlling the ionic strength of the solution. The mechanisms of Fe3+, Al3+, Ca2+, and Mg2+ removal were investigated to identify the controlling steps and reaction kinetics. It was found that the precipitates are formed by a zero-order reaction, and the activation energies tend to be low with a sequence of fast chemical reactions that reach equilibrium very quickly. Moreover, this study focused on Li loss during removal of the impurities, and the corresponding removal rates of Fe3+, Al3+, Ca2+, and Mg2+ were found to be 99.8%, 99.5%, 99%, and 99.7%, respectively. Consequently, high-purity Li3PO4 was obtained via one-step precipitation. Thus, this research demonstrates a potential route for the effective recovery of Li from low-concentration LCW and for the appropriate treatment of acidic LCW.

Keywords lithium-containing wastewater      lithium phosphate      precipitation      impurity ion     
Corresponding Author(s): Zhi Sun   
Just Accepted Date: 05 May 2019   Online First Date: 25 June 2019    Issue Date: 22 May 2020
 Cite this article:   
Chunlong Zhao,Mingming He,Hongbin Cao, et al. Investigation of solution chemistry to enable efficient lithium recovery from low-concentration lithium-containing wastewater[J]. Front. Chem. Sci. Eng., 2020, 14(4): 639-650.
 URL:  
https://academic.hep.com.cn/fcse/EN/10.1007/s11705-019-1806-3
https://academic.hep.com.cn/fcse/EN/Y2020/V14/I4/639
Metal ion Li+ Na+ Fe3+ Al3+ Ca2+ Mg2+
Concentration /(mg?L-1) 2000 2000 80 400 300 300
Tab.1  Initial concentration of different ions in the Li-containing wastewater
Fig.1  Schematic diagram of the experimental device
Metal ion Li+ Na+ Fe3+ Al3+ Ca2+ Mg2+
Concentration /(mg?L1) 1900 5500 <1 <3 200 270
Tab.2  Concentration of different ions after removing Fe and Al
Fig.2  E-pH diagram for the (a) Fe-H2O and Al-H2O, (b) Ca-C-H2O and Mg-H2O systems, and (c) Li-P-H2O systems (at 1 atm pressure and 298 K, c(Fe3+) = 0.001432 mol?L1, c(Al3+) = 0.0148 mol?L1, c(Ca2+) = 0.0075 mol?L1, c(Mg2+) = 0.0125 mol?L1, c(Li+) = 1 mol?L1
Fig.3  Effect of ionic strength on the rate of Li+ loss
Fig.4  Zero-order control model for kinetics of removal of (a) Fe3+, (b) Al3+, (c) Ca2+, and (d) Mg2+ at different temperatures
T /K Fe Al Ca Mg
k
/(mmol·min1)
R2 k
/(mmol·min1)
R2 k
/(mmol·min1)
R2 k
/(mmol·min1)
R2
298 0.3134 0.9992 1.4240 0.9825 0.9834 0.9957 2.5675 0.9806
303 0.3298 0.9977 1.4750 0.9886 1.0358 0.9997 2.6468 0.9866
313 0.3438 0.9913 1.5538 0.9918 1.0806 0.9981 2.7351 0.9869
323 0.3583 0.9725 1.6255 0.9963 1.1361 0.9886 2.8496 0.9873
Tab.3  Kinetics parameters for ion removal—calculated by applying the zero-order chemical reaction model
Fig.5  Arrhenius plot for the removal of (a) Fe3+, (b) Al3+, (c) Ca2+, and (d) Mg2+ in the temperature range of 298K–323 K
Fig.6  (a) XRD pattern of residue after removing Fe3+ and Al3+ (1) and after baking at 600°C for 2 h (2); (b) simultaneous TG/DSC curves for the residue after removing Fe3+ and Al3+
Fig.7  (a) XRD pattern of the residue after removing Ca2+ and Mg2+ and (b) curves for simultaneous TG/DSC analysis of residue after removing Ca2+ and Mg2+
Fig.8  Mechanisms of removing (a) Fe3+ and Al3+, and (b) Ca2+ and Mg2+
Content Li3PO4 CaO MgO Al2O3 Na2O Fe2O3
Composition /wt-% 99.081 0.049 0.007 0.032 0.828 0.003
Tab.4  Mass fraction of metals in precipitated Li3PO4
Fig.9  XRD pattern of recycled Li3PO4
Fig.10  SEM image of precipitated Li3PO4
Element First step
recovery efficiency
Second step recovery efficiency Precipitation efficiency Total recovery rate Main product
Li 95.87% 95.49% 92.04% 84.26% Li3PO4
Tab.5  Global recovery rates of Li in this research
Fig.11  Simplified flow-sheet for recovery Li from low-concentration LCW
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