Environment-friendly technology for recovering cathode materials from spent lithium iron phosphate batteries. Issue 8 (August 2020)

• Record Type: Journal Article
• Authors: Bi, Haijun; Zhu, Huabing; Zu, Lei; Gao, Yong; Gao, Song; Bai, Yuxuan
• Is Part Of: Waste management & research. Volume 38:Issue 8(2020:Aug.)
• Page Start: 911
• Page End: 920
• Publication Date: 2020-08
• Subjects: Spent lithium iron phosphate battery -- recovery technology -- discharge and disassembly -- low-temperature heat treatment -- sample screening analysis -- corona electrostatic separation; Factory and trade waste -- Periodicals; Refuse and refuse disposal -- Periodicals; Municipal engineering -- Periodicals; Déchets industriels -- Périodiques; Déchets -- Élimination -- Périodiques; Génie urbain -- Périodiques; 628
• DOI: 10.1177/0734242X20931933
• Languages: English
• ISSNs: 0734-242X

Abstract

The consumption of lithium iron phosphate (LFP)-type lithium-ion batteries (LIBs) is rising sharply with the increasing use of electric vehicles (EVs) worldwide. Hence, a large number of retired LFP batteries from EVs are generated annually. A recovery technology for spent LFP batteries is urgently required. Compared with pyrometallurgical, hydrometallurgical and biometallurgical recycling technologies, physical separating technology has not yet formed a systematic theory and efficient sorting technology. Strengthening the research and development of physical separating technology is an important issue for the efficient use of retired LFP batteries. In this study, spent LFP batteries were discharged in 5 wt% sodium chloride solution for approximately three hours. A specially designed machine was developed to dismantle spent LFP batteries. Extending heat treatment time exerted minimal effect on quality loss. Within the temperature range of 240°C–300°C, temperature change during heat treatment slightly affected mass loss. The change in heat treatment temperature also had negligible effect on the shedding quality of LFP materials. The cathode material and the aluminium foil current collector accounted for a certain proportion in a sieve with a particle size of −1.25 + 0.40 mm. Corona electrostatic separation was performed to separate the metallic particles (with a size range of –1.5 + 0.2 mm) from the nonmetallic particles of crushed spent LFP batteries. No additional reagent was used in the process, and no toxic gases, hazardous solid waste or wastewater were produced. This study provides a complete material recovery process for spent LFP batteries.