Green and facile method for the recovery of spent Lithium Nickel Manganese Cobalt Oxide (NMC) based Lithium ion batteries
Graphical abstract
LIB recycling using citrus fruits.
Introduction
Technological advancement has greatly increasing the demand for newer lithium ion batteries due to the more use of advanced energy storage devices like electric vehicles, consumer electronics, renewable energy storage, back-up power, medical devices, etc. It was reported that in the year 2006 rechargeable (secondary) batteries covered 11% of the total global battery business and it was growing at the rate of 6% annually (Battery Statistics, 2015). India is the world’s second-largest cellular phone user with over 930.20 million subscribers (547.70 million urban and 382.50 million rural) as on November 2014 (TRAI, 2014).
The removal of the binder is an essential step towards the recovery of metals from spent lithium ion batteries. It can be removed either by the high temperature treatment (Guo et al., 2016) or by using solvents like N-methyl pyrrolidone (NMP), γ-Butyrolactone, dimethylformamide, and dimethyl sulfoxide (Li et al., 2013, Li et al., 2010a). High-temperature treatment process required temperature 500–700 °C and has many issues related to toxic emission and material management (Wang et al., 2016), whereas solvents based techniques have the limitation in terms of toxicity and post management (Chen and Zhou, 2014). So some alternative technique is the need of the hour.
The existing methods for metal recovery from LIB recycling involved: (i) aqueous stream based limited recycling using the liquid stream mixed with soda ash with the hammer mill and shaker table (Meshram et al., 2015a); (ii) supercritical CO2 based recycling of cathode and anode (Bertuol et al., 2016) (iii) pyro and hydrometallurgical processes (Chen et al., 2015a, Pant and Singh, 2014). There was also some limitation over pyro-metallurgical processes towards the recovery of lithium and aluminium and further treatment is needed for the recovery of Li (Hanisch et al., 2015).
The use of strong acids can provide good results in metal leaching but harmful emission like Cl2, SOx and NOx makes its limitation to be a popular technique, also the post management of acids is a complex issue (Zhang et al., 2013). Organic acid has the potential to avoid these adverse environmental impacts. Pure citric, oxalic malic, aspartic, ascorbic, tartaric and iminodiacetic acids (Sun and Qiu, 2012, Li et al., 2013, Nayaka et al., 2016a) can be used as the leaching agent for LIB recycling with incomplete leaching. Use of pure organic acid cannot provide efficient leaching and for improvement H2O2 (1–6 vol.%) be used as a reducing agent (Li et al., 2010b).
To avoids the use of H2O2 like toxicant methods can be modified by using mixture of acids (Table 1) out of which one acid is used as a complexing agent and another as a reducing agent (Li et al., 2012, Nayaka et al., 2016b). Citric and malic acid with a different combination of ascorbic acid/ H2O2 give nearly 100% leaching of Li (Nayaka et al., 2015, Li et al., 2013). Cobalt gives average leaching in between 60% and 97% and best results are with the combination of malic acid and ascorbic acid (Nayaka et al., 2016a).
To develop more environmentally benign process, i.e. avoid the use of H2O2 and mineral acid like toxicant; in an affordable cost we are proposing the use of CJ as a green solvent. Waste resultant from LIBs can cause an inescapable risk for the environment and public health (Pant et al., 2012), while on the other hand it have the harm to improper dispose to the metal resources like Li, Co, Ni and Mn. In year 2005 cobalt in LIB waste was found 12,000 tonnes and respective to this the approximate amount for Li, Mn and Ni contents were 5723, 35,312 and 21,970, respectively (Dewulf et al., 2010). A proper management strategic can reduce the risk of the release of toxic organic compound and also mitigate the risk of resource depletion. The use of CJ for the recovery of metals from waste LIB can make the process safe for the environment with an effective recovery. CJ is a source of mixed organic acid with flavonoids as complexing and reducing agent with different counterions for efficient leaching and binder removal. This study will devote to discover a green recovery of Li, Co, Ni and Mn from LIB using CJ as the innovative waste management.
Section snippets
Experimental
For the metal recovery from waste LIBs of mobile phones (collected from the local scrap market) these were discharge first and then dismantled to separate the cathode and anode film (Scheme 1). Hill lemon, galgal (Citrus pseudolimon Tanaka), a cheap fruit commonly present in a Himachal Pradesh with good quantity, is used for the present study as CJ material. Galgal is light yellow, conical ovate with prominent ridges and smooth surface fruit growing in subhumid-subtropical areas in the upper
Binder removal and recovery of Al and Cu
A typical X-ray diffractogram of cathodes of spent Li-ion batteries before and after treatment was shown in Fig. 1. LiCoO2, Co3O4, Al and carbon were found in the cathode samples as compared with previous reports and JCPDS standards (Freitas et al., 2010). The presence of Co3O4 and LiCoO2 resultant from the reaction was due to the charging–discharging cycles. The role of carbon in both cathode and anode was to increase electric conductivity of the electrode (Contestabile et al., 2001, Lain, 2001
Conclusion
CJ was found to be a good reagent for the metal recycling from the waste LIBs. It plays a good role in removing the binder and provides an efficient leaching for LIB waste with an excellent combination of reducing agents and counterions. Furthermore:
- 1.
The XRD pattern in cathode clearly shows an increment in intensity from 14.005 counts to 38.372 due to the removing defects in the material in case of binder removal;
- 2.
In the FTIR absorption due to fluorocarbon group at 1194 and 866 cm−1 was completely
Acknowledgement
The authors would be thankful to the Department of Biotechnology, Government of India grants no. BT/PR7467/BCE/8/954/2013 for financial assistance, SAIF, IIT Bombay for analytical support and Dr. Jaishree Sanwal, Jawaharlal Nehru Centre for Advanced Scientific Research (JNCASR) for the useful discussion towards the identification of XRD.
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