Joshua
Vauloup
a,
Cécile
Bouilhac
a,
Nicolas
Coppey
c,
Patrick
Lacroix-Desmazes
a,
Bernard
Fraisse
a,
Lorenzo
Stievano
ab,
Laure
Monconduit
*ab and
Moulay Tahar
Sougrati
*ab
aICGM, Univ Montpellier, CNRS, ENSCM, Montpellier, France. E-mail: Laure.monconduit@umontpellier.fr
bRéseau sur le Stockage Electrochimique de l'Energie (RS2E), CNRS FR3459, Amiens, France
cSNAM, Avenue Jean Jaurès 12110, Viviez, France
First published on 15th July 2024
Lithium-ion batteries (LIBs) stand as the dominant power source for electric vehicles owing to their mature technology and exceptional performance. Consequently, metallic components of LIB cathode materials (Ni, Co, Li, and Mn) are assuming strategic significance. The imperative recycling of these metals has necessitated the development of novel technologies that can curtail secondary pollution arising from prevailing hydrometallurgical procedures, including issues such as wastewater generation and excessive energy and chemical consumption. In this study, we present an optimised mechanochemical process tailored for the magnetic recovery of cobalt from LiCoO2, which is a crucial component of LIBs. Our methodology involves the initial reduction of cobalt, facilitated by aluminium, followed by a selective extraction process that leverages the magnetic properties of the obtained species. A systematic exploration of milling parameters was undertaken to comprehensively understand their influence on chemical reactions and to improve reduction efficiency. This research represents a significant stride towards fostering sustainable practices in the realm of LIB cathode material recycling, addressing critical concerns related to resource management and environmental impact.
As the lifespan of LIBs is currently estimated to be around ten years, a huge quantity of end-of-life (EoL) LIBs must be handled to ensure the complete recovery of strategic components and avoid soil, water and air pollution due to their disposal.1,2 In fact, the worldwide EV inventory has undergone rapid expansion, starting from fewer than 1600000 units in 2015 to exceeding 17400000 units in 2021.1 Moreover, metals used in LIB cathode materials (Co, Li, Mn, Ni, etc.) are considered strategic resources by several countries, and regulations concerning LIB recycling are evolving to ensure sustainable metal supplies for producing new LIBs.3–5 Beyond resource scarcity and economic safety issues, recycling LIBs is beneficial in terms of energy consumption compared with the use of virgin resources.6 Indeed, the metal extraction industry is known to be energy-intensive, and the large amounts of chemicals that can be released into the environment serve as additional sources of pollution. The production of cathode materials for LIBs using metal intermediates from LIB recycling has been proven to be twofold less energy-intensive than that using virgin raw materials.7 Some studies have also highlighted that the production of cathode materials containing high-value metals, such as Ni and Co, from spent LIBs is economically more beneficial than using virgin materials.3,8 This is because the average concentration of strategic metals in LIBs is 100- to 1000-fold higher than that in natural ores. For example, Co and Li contents are 5–20 wt% (based on the whole LIB) and 2–7 wt%, respectively.9,10
Recycling these metals while reducing secondary pollution caused by the current recycling processes is an urgent and important challenge.11 The most common process for metal recovery is hydrometallurgy, either alone or in combination with pyrometallurgy.2 It involves acid leaching of metal oxides followed by multiple separation and purification steps to selectively recover metals with sufficiently high purity for them to be reused. This process is combined with pre-treatment steps, such as discharging, dismantling, crushing, pyrolysis, sieving, magnetic separation and other physical separation methods. Many combinations of these steps are possible with different arrangements according to the proprietary industrial routes. However, hydrometallurgical processes generate significant amounts of wastewater, are energy intensive and consume a large quantity of chemicals.12,13
While LIB recycling is expected to be the major source of battery elements by 2040 in the EU,14 today, it is still in its infancy with a capacity of only 0.05–0.08 million tons per year (1.4 Mton per year by 2035).15 Currently, the recycling rate of metals from LIBs is low at 22% for cobalt and less than 1% for Li; the recycling of the latter is not economically viable using conventional pyro and hydrometallurgical processes.16 To date, a majority of spent LIBs on the market are those extracted from portable devices. However, with the fast development of the EV market, the flow of spent LIBs will increase significantly in the coming years (5 times). The capacity of the existing recycling plants is not sufficient to handle the increasing volume of spent LIBs. Therefore, the share of recycled LIBs is expected to decrease in the coming years.2 Moreover, to achieve closed-loop recycling of cathode materials, metals have to be selectively recovered with high purity to meet the battery-grade specifications. The quality of recycled metals is closely linked to the method used for sorting the input feed, as well as the steps and the technologies employed in the recycling process because a great variety of LIB compositions exists in the market.2,17
Therefore, more advanced and efficient LIB recycling technologies are necessary to support the existing methods and fulfill the upcoming legislation targets towards limiting secondary pollution emissions. A technology that has garnered growing interest in the last decades is mechanochemistry (MC), which entails the activation of chemical reactions through mechanical energy. It usually works at room temperature and, most often, without a solvent. Therefore, it is energy-saving18 and involves less reagent consumption.19 These benefits are currently being explored for several processes of LIB recycling.20 Different strategies have been proposed, such as MC-assisted leaching with organic acids,21–25 ball milling as pre-treatment for the activation of the recycling feed,26,27 reducing the cobalt and/or nickel species to activate leaching,28–34 and solid-state chlorination to form water-soluble metal salts using organic wastes35 or inorganic salts.36–38 MC has also been investigated in other innovative processes, such as ammonia leaching36 and the direct synthesis of new materials from spent cathodes.39,40 Another promising MC-based technique is the direct recycling of cathode materials by relithiation, as no chemical separation steps are needed.41 In this study, the strategy is to use MC for converting LCO to cobalt metal, which can then be selectively recovered by magnetic separation. This process has already been proposed by Dolokto et al. using aluminium as the reducing agent.42,43 This work focuses on the influence of the ball milling parameters to elucidate the mechanisms of cobalt reduction and thereby optimise the energy consumption of this process. Understanding the mechanism is also beneficial to predicting scale-up issues. The magnetic separation step is not discussed here. The original cobalt quantification method was employed for quantifying metallic cobalt in the milled powder. Aluminium was chosen because of its low redox potential (−1.68 V vs. ESH for Al(III)/Al(0); 1.82 and −0.28 V vs. ESH for Co(III)/Co(II) and Co(II)/Co(0), respectively, at 25 °C in 1 M aqueous solution). Moreover, unlike Co, Al is currently not considered a critical resource and costs much less than Co. Lastly, Al is already present in spent LIBs as the cathode current collector and/or in the casing, which might render this process economically and environmentally attractive.
(1) |
From the LCO amount, the initial cobalt mass in the as-milled powder was determined. From this value, the cobalt fraction converted to Co metal was easily calculated using eqn (2):
(2) |
The SEM-EDX analysis of the powder after 5 h of milling (Fig. 2) confirmed the presence of Fe and Cr as contaminants. The use of SS jar leads to extensive scratching and the consequent formation of ferromagnetic pollutants, which contaminate the cobalt. For this reason, ZrO2 jar and balls were used subsequently in this study. It is worth noting that Dolotko et al.43 used SS jars and balls to reduce cobalt with Al in their previous studies. However, even though they employed a 3D high-energy ball mill, they did not observe any Fe or CoFe alloy in the milled powder. The milling materials were not damaged in their case, as the milling duration was shorter (less than 3 h).
As the kinetics was slower when an equimolar amount of Al was used, faster kinetics might be expected if more energy was brought to the system. To ascertain this possibility, milling speed, filling rate and the ball number and diameter were the parameters explored.
Fig. 4a presents the LCO to Co metal conversion efficiency as a function of milling time based on the magnetometry analysis of the milled powders (3 g, Al + LCO) using 50 balls of 5 mm diameter and milling/rest cycle = 15 min/10 min. Under these conditions, about 60% of LCO was converted to Co metal after 1 h at 600 rpm, whereas no reaction occurred in the same milling time at 500 and 400 rpm. However, a similar conversion efficiency was observed when the milling time was extended to 2 h at both rotating speeds. Since no difference was observed between 400 and 500 rpm, these two conditions could be distinguished only by changing other parameters, such as the number and/or the size of the balls. For instance, the use of larger balls (7 balls of 10 mm diameter) and a shorter rest time (10 min rest every 60 min milling) allowed the differentiation of reaction kinetics between 400 and 500 rpm; complete conversion (110%) was observed after 2 h at 500 rpm, while no reaction (3%) occurred at 400 rpm (Fig. 4b). It is noteworthy that the conversion to Co metal exceeded 100% (500 rpm, 2 h) due to the uncertainty of the SQUID measurements, which were carried out with small quantities of samples (10–30 mg) in which controlling homogeneity is difficult.
In conclusion, increasing the rotation speed increases the kinetic energy of the balls and consequently the impact energy of the balls, as well as the distance browsed by the balls in the same period. Therefore, for a given milling time, more energy (determined by the rotation speed, the number and diameter of the balls, the rest time) will be released by the balls when the rotation speed is higher, and cobalt reduction will occur faster.46
The last experiment shows that the use of balls with a bigger size improves LCO reduction without increasing the rotation speed (which is costly). An attempt was then made to further decrease the rotation speed using balls of the same size. Fig. 5 shows the (a) Co metal quantification and (b) XRD patterns of a powder milled at 300 rpm. In this case, a P/B ratio of 0.08 was used to bring more energy to the powder and thereby facilitate the conversion reaction at such a low speed. The complete conversion of LCO occurred between 5 and 8 h, with a 70% selectivity to Co metal and the formation of CoO and LiAlO2. This change was accompanied by a progressive temperature increase until the conversion reaction was triggered. Since the reaction is exothermic, the heat produced by the reaction might be transferred to the rest of the sample, producing a rapid local increase in temperature that suddenly accelerates LCO conversion.
To get better insights into this effect, the outside temperature of the bowl was monitored during milling. Fig. 6 shows the bowl temperature evolution and the amount of cobalt obtained from LCO conversion as functions of milling time. The exothermic peak observed between 2 and 3 hours corresponds to LCO reduction. The influence of the exothermicity of LCO reduction is discussed in detail later in the article (vide infra).
Fig. 7a shows the temperature evolution of the bowl at two different P/B ratios. The powder mass was kept constant at 3 g, and the number of 10 mm balls was varied from 7 to 10 balls corresponding to the P/B ratios of 0.15 and 0.10, respectively. Temperature monitoring evidenced a faster reaction when a higher number of balls was used, with an exothermic peak observed after 75 min of reaction with 10 balls, while it appeared only after 130 min with 7 balls (Fig. 7a). A similar behaviour was observed while studying the magnetic moment of the milled powder to determine the cobalt reduction efficiency, as shown in Fig. 7b. A reduction yield of 50% was measured after 2 h of milling with 7 balls, whereas no reaction was observed with 5 balls in the same reaction time. In conclusion, the lower the number of balls, the slower the reaction as there are less contact points and less friction to activate the reaction.
As seen in Fig. 7b, a conversion drop occurred after 2 h of milling with 7 balls. This phenomenon is probably due to the oxidation of the Co metal by its reaction with the oxygen brought into the jar when it was opened for sampling. The formation of CoO during milling was confirmed by XRD analysis (Fig. 7c). Furthermore, XRD also detected the progressive consumption of LCO and Al, confirming the partial reduction of cobalt after 1 h. After 2 h, no LCO and Al were detected, while hexagonal Co metal and LiAlO2 were formed. With further milling, the peaks of Co decreased in intensity and that of CoO prevailed. Therefore, limiting sampling and air exposure during the milling process is fundamental for studying the Co reduction more accurately. Thus, temperature monitoring is a better way to study the reaction kinetics as the bowl remains closed.
As mentioned above, experiments were also carried out with a constant number of balls (50 of 5 mm diameter) by varying the mass of the powder (3 and 5 g) under the same milling conditions (500 rpm, milling/rest time = 15 min/10 min). However, no difference was observed by XRD between these two experiments. LCO and Al disappeared completely after 1 h, and the reaction was too fast to differentiate between the two conditions. The only difference was in the morphology of the obtained powder (Fig. S8†); for a higher amount of powder (5 g), sheet-like millimeter-size agglomerates were observed, whereas for 3 g, the milled powder was more homogeneous. As the heat released is proportional to the amount of reagent, with 5 g, the heat released was higher than that obtained with 3 g, and therefore, the reaction was more intense with a fast cobalt reduction reaction, leading to Co metal agglomerates.
The temperature of the jars was recorded as a function of milling time using four different amounts of powder (1, 2, 3 and 5 g). The results shown in Fig. 8 highlight a remarkable difference in reaction kinetics, with an exothermic peak at 40 min (40 °C), 60 min (46 °C), 100 min (50 °C) and 170 min (58 °C) for 1, 2, 3 and 5 g, respectively. Reaction activation was the fastest at the lowest P/B ratio. Nevertheless, even though the reaction with the highest powder mass was slower, the temperature build-up was higher. This phenomenon is due to the high exothermicity of the LCO reduction reaction using Al metal to produce LiAlO2 and Co metal (−510.5 kJ mol−1, see ESI† for additional details).
Fig. 8 External bowl temperature as a function of milling time with varying powder mass. Milling conditions: 450 rpm, 7 × 10 mm balls, no rest time, and nAl/nCo = 1.0. |
The effect of milling time was studied by SQUID magnetometry while all the other parameters were kept constant. With a lower rest time of 10 min for every 30 min of milling, the reduction yield improved quickly to around 50% after 1 h, while no metallic cobalt was measured by this time with 10 min of rest time for every 15 min of milling (fixed conditions: 500 rpm, 3 g of powder, nAl/nCo = 1.0, P/B = 0.15, 50 × 5 mm balls). The reduction yield of Co metal was only measured after 2 h of milling (around 55%). These results show that temperature build-up within the cell is an important parameter influencing the conversion of LCO to Co metal.
These results were confirmed by the comparison of the external wall temperatures of the milling jar, as shown in Fig. 9, between two different milling experiments carried out at 500 rpm with 7 balls of 10 mm diameter, 3 g of powder and a P/B ratio of 0.15. A sudden and steep increase in temperature was observed after 60 min of continuous milling without rest, whereas the increase in temperature was lower and observed only after 75 min when a rest of 10 min was applied after every 15 min of milling. In summary, the application of regular rest times during milling is a crucial parameter as it allows heat dissipation and slows down the reaction, confirming that reaction activation is not only dependent on the milling time but also on the temperature build-up in the system. This temperature increase helps in reaching the activation threshold, thereby triggering LCO reduction, which then produces more heat and leads to a rapid reaction in the entire mass of powder. These results confirm the results presented in Fig. 6 (vide supra), which shows that the LCO conversion is strongly correlated with the reaction temperature within the jar.
The control of temperature build-up by changing the milling parameters, however, is also important to obtain a homogeneous powder and to avoid damage to the jar and the balls. For example, before milling at 500 rpm with milling/rest cycles of 15/10 min, no structural change was observed by XRD (Fig. 10a). This means that no reaction occurred, and the composition of the milled powder is homogeneous in terms of composition, even if it appeared agglomerated, as observed through SEM (Fig. 10c, S8, S9, Tables S1, S2 and S3†). After 3 h of milling, the reaction occurred suddenly, producing sheet-like particles measuring a few centimetres. Their SEM-EDX analysis (Fig. 10e) revealed that the sheets consisted of Co metal covered on the surface by small particles enriched in Al. Such large Co sheets could damage the balls during milling, as shown in Fig. 10d, and some ZrO2 particles were also detected.
In order to avoid damage to both the milling jar and the balls, temperature build-up and the milling energy have to be controlled. With a shorter rest time, the reaction will be more violent, and more resistant (bigger) balls should be used to decrease the number of reaction activation sites, as well as the temperature build-up. Regarding the milling speed, a compromise had to be made between energy consumption and the processing time for LCO reduction. For example, at 500 rpm, with 7 balls of 10 mm diameter, 3 g of powder and 15/10 min milling/rest cycles, LCO conversion to Co metal was possible after 2 h (Fig. 11). Nevertheless, to limit energy consumption, the reaction time can be still decreased by removing the rest time and using a smaller number of balls and/or a slower rotation speed if the reaction is too violent. Another strategy would be to decrease the amount of powder to limit heat release. In this case, however, a smaller amount of cathode material will be treated and the energy required per mass of powder will be higher.
A summary of the different reaction pathways as a function of the milling conditions is shown in Fig. 12. Notably, the renewal of the oxygenated atmosphere caused by powder sampling for the characterisation of the intermediate states impacts the formation of Co metal. The maximum production of Co metal requires no air exposure during milling and equimolar amounts of LCO and Al. LCO conversion is faster for high milling energy but the high temperature increase may damage the milling materials. Therefore, milling speed, rest time, powder amount, and the number of balls have to be balanced to limit temperature increase and avoid ZrO2 pollution from the ball mill. The as-formed LiAlO2 side product can be leached for Li+ recovery.48,49 This material can be easily valorised to produce coatings for cathode materials towards improving their electrochemical performance.50–52
The triggering mechanism of the reaction is still under investigation. XRD refinement of the milled powder sample before LCO conversion was performed to study the evolution of lattice parameters. No significant change in the lattice parameters of LCO and Al was observed with variation in milling time (Fig. S11†). Further work is under process, such as the study of the amorphisation of the reagents, which is supposed to be correlated with the triggering of cobalt reduction in addition to temperature build-up to reach the activation energy threshold.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4mr00018h |
This journal is © The Royal Society of Chemistry 2024 |