Next Article in Journal
Advanced Technologies in Bio/Hydrometallurgy for Recovery and Recycling of Metals
Previous Article in Journal
A Study of Sliver in C-Shaped Grain Selectors during Investment Casting of Single-Crystal Superalloy
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Communication

Study of an Impact Mill-Based Mechanical Method for NdFeB Magnet Recycling

1
Energy Department, Politecnico di Torino, Corso Duca degli Abruzzi 24, 10129 Torino, Italy
2
National Interuniversity Consortium of Materials Science and Technology (INSTM), Via G. Giusti 9, 50121 Florence, Italy
3
Department of Applied Science and Technology, Politecnico di Torino, Viale Teresa Michel 5, 15121 Alessandria, Italy
4
Department of Industrial Engineering, University of Florence, Via di S. Marta 3, 50139 Florence, Italy
*
Author to whom correspondence should be addressed.
Metals 2023, 13(6), 1103; https://doi.org/10.3390/met13061103
Submission received: 19 May 2023 / Revised: 1 June 2023 / Accepted: 10 June 2023 / Published: 12 June 2023
(This article belongs to the Section Powder Metallurgy)

Abstract

:
Nowadays, the circular economy is gaining more and more attention in sectors where the raw material supply is critical for both cost and geo-political reasons. Moreover, the environmental impact issue calls for recycling. From this perspective, the recovery of rare earth elements represents a strategic point. On the other hand, the high cost and the dangerous standard recovery methods that apply to NdFeB magnets limits options for traditional recycling. A new mechanical method is proposed, not requiring hydrogen, high temperature, or chemical processes, but instead using an impact mill designed to operate in vacuum. A traditional impact mill operating in a glove box filled with Ar atmosphere has also been used for comparison. The obtained NdFeB powders were analyzed in terms of magnetic properties and chemical composition, particularly in terms of the oxygen content.

1. Introduction

Decarbonization, reduction of greenhouse gas emissions, and improvement in overall health are the main aims in several countries where some actions concerning environmental policies have been taken. The most popular way of reducing air pollution consists of introducing electric or hybrid vehicles (EV or HEV) [1,2,3]. Different strategies have been proposed and studied regarding this topic, and some tools like life cycle assessment (LCA) are used to analyze the product or processes [4,5,6]. LCA consists of a Life Cycle Inventory (LCI) analysis and Life Cycle Impact Assessment (LCIA), where LCI involves the compilation and quantification of inputs and outputs for a product throughout its life cycle. The adoption of LCA permits understanding and evaluating the magnitude and implication of the potential environmental impacts by considering all the steps related to the product’s life, from the design to its re-use [7]. Therefore, recycling plays an important role in ecological aspects and economic savings. In some industrial sectors recycling is essential, while in other sectors it shows high potential [8], also resolving the problems of raw material supply [9,10].
The introduction of EV or HEV led to the necessity of evaluating new material solutions for battery systems and electrical machines. Nowadays, different types of electric motors are used; one is the permanent magnet synchronous machine (PMSM), which shows high torque density and good dynamic behavior [11,12,13]. However, the PMSM contains Rare Earth elements, which significantly affects the cost of the device [14]. The high cost depends on various aspects: the extraction process is expensive and the price depends on the market and geopolitical situations, as Rare Earth elements are located in a few areas of the planet [15,16,17,18,19]. The Neodymium price variation changed significantly in the last decade: 30 $/kg in 2009, then 300 $/kg in 2011. After that, the price decreased to 60 $/kg in 2018 then increased again until 220 $/kg at the end of 2022, reaching a critical point. The same situation involves the Dysprosium powder used to produce the best NdFeB grade magnets, where the price was 750 $/kg in 2022. Some solutions are proposed to solve this issue [15]: opening new mines, researching new magnetic materials [20,21,22], designing appliances without NdFeB magnets [23], and recycling [24,25,26,27,28]. All listed points have aspects open to criticism: opening new mines faces ecological permission problems in many countries, while new magnetic research is generally based on alloys that are not cost-effective, the use of ferrite magnets (as substitutions for NdFeB) increase volume and weight with an overall reduction of performances, making them not applicable to many industrial sectors.
NdFeB recycling is based on existing recovery techniques [29,30,31,32,33,34,35,36,37]. The hydrometallurgical method is a chemical process in which the material is crushed and leached; its extraction is obtained through particular solvents. This technique is expensive and complex. Another is based on the pyrometallurgical method, which consists of recovering REO (Rare Earth Oxides) at high temperatures (1500 °C). The obtained REO need to be processed again via the typical extraction process of rare earth, which involves transporting REO in a few areas of the planet. The more popular NdFeB recycling technique is hydrogen decrepitation (HD), where the material is crushed by means of the adsorption of hydrogen. There are various dangerous aspects of the process, due to the use of hydrogen and very highly reactive NdFeB powder; for this reason, this method is also considered rather expensive. Moreover, the recycled product should be reused immediately without going through several production chain stages.
This paper analyzes an alternative method for producing NdFeB recycled powder, based on a cheaper mechanical process, without the use of hydrogen. The focus is to develop a more suitable, cheaper, and safer recycling process for industrial criteria. The goal of the research is to develop a reliable process able to guarantee the production of powders ready to be re-used, without changing the chemistry of the starting material. A vacuum impact mill has been designed and used to produce NdFeB powders. The device is a prototype of an attritor capable of working in a vacuum or controlled atmosphere, and it was designed and produced by the authors in Politecnico di Torino. The mill is composed of two chambers, both containing a controlled atmosphere during the operational phase. All of the grinding processes in this work were conducted within a vacuum. The proposed mechanical grinding process is a technique already used for the fracture, surface finish and coating of the powder, continuously. In the proposed work, the process is non-continuous, so when all the magnets are ground and reduced to a powder, the mill can be disassembled and loaded again with new material. Moreover, the activity does not require chemical preparations and does not result in high costs.
For comparison, a conventional impact mill was used, placing it in an inert environment in a glove box filled with Argon gas. NdFeB powders obtained in different conditions have been characterized and tested.

2. Materials and Methods

Hard disks used in computers in the last 15 years have been collected by RISTA s.r.l., an Italian Company working in the field of waste recovery and environmental sustainability. Magnets have been disassembled from the supports through an automatic precision system developed by OSAI Automation System, a leading Italian Company in the field of automation and LASER for industrial processes. The position of the magnets is shown in Figure 1. The variety of the magnets appears in several dimensions (Figure 2) related to different magnetic properties. Diversification of magnets was not implemented, and also the nickel protection coating was not removed [38].
Magnets were demagnetized before the crushing process. This was performed at 350 °C in a vacuum to avoid oxidation.
The crushing and grinding processes were performed using an impact mill (Figure 3). The scheme of its advanced version, that works in vacuum, is reported in Figure 4. Two types of impact mill have been evaluated. The first mill is made by a high-speed DC electric motor and a chamber with blades, which is filled with the recovered magnets to be chopped and transformed into recycled powder. The equipment has been placed in a glove box of approx. 0.5 m3 (Figure 5a,b). Before starting the milling process, an Ar purging of 15 min has been carried out, and Ar backfilling has been adopted throughout the whole process.
The second mill consists of a vacuum impact system designed for this specific purpose (Figure 6a,b). It is made up of different parts. One part consists of a chamber with a high-speed DC motor, electrically and mechanically sealed off from the (second) chamber where the powder is collected, which is then separated by a mechanical grid from a glass storage container for the recycled NdFeB powder. A sealing gasket was used to retain vacuum.
Powders’ granulometry and distribution size have been analyzed with the Malvern Mastersizer 3000, equipped with Aero S for dry dispersion.
The obtained powders were analyzed using X-ray diffraction (XRD) analysis (Bruker New D8 ADVANCE ECO diffractometer equipped with a Cu Kα [1.5406 Å] radiation source) and compared to the NdFeB reference standard (PDF 00-036-1296).
Furthermore, powders were examined by means of X-ray fluorescence (XRD) analysis (Thermo Scientific EDX-7000) to evaluate the amount of neodymium and iron. The oxygen content (wt. %) of the two set of powders was obtained by means of an elemental analyzer (LECO ONH836).
The powders’ magnetic performance has been evaluated by means of a Permanent Magnet Hysteresisgraph (Laboratorio Elettrofisico I-200 A/S, equipped with Powder testing fixture).
All produced powders were stored in vacuum glass bottles. This operation is mandatory to avoid powder oxidation and to facilitate transport. Figure 7 illustrates the scheme from the recovery of NdFeB magnets from hard disks to powder characterization.

3. Experimental Results

After the milling process, powders have been sieved between 50 µm and 500 µm. Their distribution size is reported in Figure 8.

3.1. Chemical and Microstructural Analyses

The presence of oxygen has been investigated through elemental analysis for both impact mill processes. Results are reported in Table 1, where the operation with a vacuum impact mill highlights an oxygen content highly reduced in comparison to the process in the Argon-washed glove box [39].
In order to preserve the magnetic properties of the material, the value of oxygen should be minimized; in fact, the obtained value is similar to a general indication of 0.4%, as reported in the literature [40,41,42]. The result of the vacuum impact mill confirms two things: firstly, the process does not add further oxidation; secondly, the recycled powder can be used immediately and not stored like an REO.
Considering the oxygen contents of the two powders and the magnetic properties of the different systems (ref par 3.2), only results relative to vacuum-processed powders will be reported. Several batches of materials were used that were derived from magnets recovered from landfills. The analyzed lots were found to be free of Dy and Pr. As reported later in the text, this does not affect the basic magnetic characteristics.
Table 2 shows the chemical composition of the powder obtained in vacuum evaluated by XRF.
It is possible to note that Iron and Neodymium are about 63.4% and 28.5%, respectively, which are typical amounts for NdFeB recycled materials [43]. These values correspond to medium Rare Earth element scraps. Additionally, the presence of Nickel is high due to the protective coating, which was not removed before the crushing and grinding process.
The recycled powder was tested through the XRD; the obtained spectrum is shown in Figure 9, blue line. The cell results are as follows: space group is P42/mnm, lattice parameters are a = 8.7865 Å, c = 12.1822 Å. The crystallite size was 96 nm. For verification, the NdFeB standard lattice parameters (PDF 00-036-1296, measured as bulk sample) are reported: space group is P42/mnm, a = 8.7933 Å and c = 12.1799 Å. The experimental spectrum shows the errors with respect to standard lattice parameters of 0.0773% for a and 0.01888% for c. This comparison confirms the similarity of the recycled powder to an NdFeB permanent magnet, evidencing the lack of oxidation effect [44]. Therefore, the magnetic phase is maintained. The comparison of the recycled powder spectrum and NdFeB reference is reported in Figure 9, blue and red lines, respectively.

3.2. Magnetic Characterization and Magnetographic Observation for Recycled Powder

Figure 10 shows the demagnetization curves for two recycled powders obtained through the mechanical process, using impact mills. The exact quantity of powder for both techniques is filled in a particular holder. The holder with powder is magnetized and then characterized by a permanent magnet hysteresisgraph. The obtained results are used to compare the process effect, without estimating the final magnetic properties of a possible magnet. The coercivity fields in a vacuum impact mill increase by 33% with respect to the operation in argon. A slight reduction in remanence has been noted for the process in a vacuum. The difference in the coercivity field is due to the oxygen content, which is 4 times higher than the typical reference value.
With the magnetic characterization of the powders, it is possible to study the density effect on magnetic performances (Figure 11). The density is changed by inserting the powder into a specific cylinder with dimensions 15 mm in diameter and 20 mm in height. Three density values have been implemented. The starting density (low density) corresponds to the density obtained after the powder is added into the calibrated cylinder (Figure 12a,b). The second density measurement (medium density) corresponds to the density obtained after manual powder compaction through the hysteresisgraph joke and dedicated expansion pole (Figure 12b). The third density value (high density) is similar to the second, but also considers an orientation through an external magnetic field.
The demagnetization curves for the three densities of recycled NdFeB powder processed in vacuum are reported in Figure 13. As expected, the low-density sample shows the lowest magnetic characteristic, while the medium density one has a higher magnetic remanence. The demagnetization curve of the high-density recycled powder has the best coercivity properties, at the expense of a reduction in magnetic remanence. After analysis using the magnetographic method described in Figure 14, the presence of residual anisotropy can be observed, especially in Figure 14b,c. This parasitic phenomenon does not permit maximizing the magnetic performance of recycled NdFeB powder. The solution consists of using a specific magnetic orientation with a dedicated tool [45].

4. Conclusions

This paper investigated the quality and properties of NdFeB powders obtained from hard disk scraps.
The vacuum milling process represents an industrially viable and safe alternative to generate immediate re-usable powders from Nd-Fe-B magnets, rather than using more complex and expensive processes to recover Nd, Pr and Dy through use of hydrogen and/or chemical solvents. XRD and XRF analyses confirmed the good quality of the recycled powder, without any trace of added oxides. Furthermore, elemental analyses evidenced that a low amount of oxygen is present after operations in a vacuum impact mill, making this technique preferable to washing in an inert atmosphere. This is possible owing to simple equipment: heat treatment in the vacuum at 350 °C, and milling by means of a pump.
Although the presence of residual anisotropy represents a drawback, it does not necessarily imply negative potentiality of the proposed method, since this presence can be reduced with particular arrangements in the stages during the molding processes of the magnets. In this context, further activities will be performed to obtain recycled magnets through the use of dedicated tools, based on magnetic orientation.

Author Contributions

Conceptualization, E.P., F.F., A.C. and M.A.G.; methodology, E.P., F.F., C.I. and C.S.; software, C.I., M.C. and A.C.; validation, L.F., M.A.G. and A.C.; formal analysis, E.P., F.F., M.C. and C.I.; investigation, E.P., F.F., C.S., C.I. and A.C.; resources, L.F., M.A.G. and A.C.; data curation, E.P., C.I., M.C., C.S. and A.C.; writing—original draft preparation, E.P. and L.F.; writing—review and editing, L.F. and M.A.G.; visualization, L.F. and M.A.G.; supervision, M.A.G. and A.C.; project administration, L.F., M.A.G. and A.C.; funding acquisition, M.A.G. All authors have read and agreed to the published version of the manuscript.

Funding

The authors wish to acknowledge the funding of the Ministry of Ecological Transition (Italy) through the Research Project “RIciclo SOstenibile di magneti di terre rare da Raee per Sistemi elettromagnetici ad Alta efficienza”—RISORSA, and the financial support of the Project funded under the National Recovery and Resilience Plan (NRRP), Mission 04 Component 2 Investment 1.5—NextGenerationEU, Call for tender n. 3277 dated 30 December 2021, Award Number: 0001052 dated 23 June 2022 and “Mission 4 Component 2 Investment 1.3—Call for tender No. 341 of 15 March 2023 of Italian Ministry of University and Research (MUR) funded by the European Union—NextGenerationEU—Project code PE_00000004, CUP B83C22004890007, Project title “3A-ITALY—Made-in-Italy circolare e sostenibile”.

Data Availability Statement

Not applicable.

Acknowledgments

Authors would like to thank RISTA and OSAI for the co-operation in the research activity, and in particular Fabrizio Rista, Marco Rinaldi and Alice Tori for their precious help. The part of research activities developed by Emir Pošković has been conducted through the Operative National Program (PON) for Research and Innovation 2014–2020, M.D. 1062 (10 August 2021), Action IV.6- “Research contracts on Green topics”.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Lepoutre, A.; Bouscayrol, A.; Irimia, C.; Husar, C.; Kalogiannis, T.; Ahmed, M.; Martis, C.; Zuber, D.; Phetsinorath, D.; Gao, F.; et al. Calculation of the GHG emissions of a European research project on electrified vehicles. In Proceedings of the 2021 IEEE Vehicle Power and Propulsion Conference (VPPC), Gijon, Spain, 25–28 October 2021; pp. 1–5. [Google Scholar] [CrossRef]
  2. Freire, F.; Marques, P. Electric vehicles in Portugal: An integrated energy, greenhouse gas and cost life-cycle analysis. In Proceedings of the 2012 IEEE International Symposium on Sustainable Systems and Technology (ISSST), Boston, MA, USA, 16–18 May 2012; pp. 1–6. [Google Scholar]
  3. Helmers, E.; Dietz, J.; Hartard, S. Electric car life cycle assessment based on real-world mileage and the electric conversion scenario. Int. J. Life Cycle Assess. 2015, 22, 15–30. [Google Scholar] [CrossRef]
  4. Faludi, J.; Bayley, C.; Bhogal, S.; Iribarne, M. Comparing environmental impacts of additive manufacturing vs traditional machining via life-cycle assessment. Rapid Prototyp. J. 2015, 21, 14–33. [Google Scholar] [CrossRef] [Green Version]
  5. Schillingmann, H.; Gehler, S.; Henke, M. Life cycle assessment of electrical machine production considering resource requirements and sustainability. In Proceedings of the 2021 11th International Electric Drives Production Conference (EDPC), Erlangen, Germany, 7–9 December 2021; pp. 1–7. [Google Scholar] [CrossRef]
  6. Tintelecan, A.; Dobra, A.C.; Martis, C. Literature Review—Electric Vehicles Life Cycle Assessment. In Proceedings of the 2020 ELEKTRO, Taormina, Italy, 25–28 May 2020; pp. 1–6. [Google Scholar] [CrossRef]
  7. Ayyappan, G.; Narayanan, N.K.; Raghavan, M.R.; Pandi, V.R.; Angel, T.; Babu, B.R. Electrical Motor Maintenance Techniques and Life Cycle Assessment—A Review with Case Studies. In Proceedings of the 2019 2nd International Conference on Power and Embedded Drive Control (ICPEDC), Chennai, India, 21–23 August 2019; pp. 167–172. [Google Scholar] [CrossRef]
  8. Rassõlkin, A.; Kallaste, A.; Orlova, S.; Gevorkov, L.; Vaimann, T.; Belahcen, A. Re-Use and Recycling of Different Electrical Machines. Latv. J. Phys. Tech. Sci. 2018, 55, 13–23. [Google Scholar]
  9. Andersson, M.; Ljunggren Söderman, M.; Sandén, B. Are scarce metals in cars functionally recycled? Waste Manag. 2017, 60, 407–416. [Google Scholar] [CrossRef]
  10. Efstratiadis, V.S.; Michailidis, N. Sustainable Recovery, Recycle of Critical Metals and Rare Earth Elements from Waste Electric and Electronic Equipment (Circuits, Solar, Wind) and Their Reusability in Additive Manufacturing Applications: A Review. Metals 2022, 12, 794. [Google Scholar] [CrossRef]
  11. Isfahani, A.H.; Vaez-Zadeh, S. Line start permanent magnet synchronous motors: Challenges and opportunities. Energy 2009, 34, 1755–1763. [Google Scholar] [CrossRef]
  12. Tintelecan, A.; Dobra, A.C.; Martis, C. Life Cycle Assessment Comparison of Synchronous Motor and Permanent Magnet Synchronous Motor. In Proceedings of the 2020 International Conference and Exposition on Electrical And Power Engineering (EPE), Iasi, Romania, 22–23 October 2020; pp. 205–210. [Google Scholar] [CrossRef]
  13. Nordelöf, A.; Grunditz, E.; Lundmark, S.; Tillman, A.-M.; Alatalo, M.; Thiringer, T. Life cycle assessment of permanent magnet electric traction motors. Transp. Res. Part D: Transp. Environ. 2019, 67, 263–274. [Google Scholar] [CrossRef]
  14. Grunditz, E.A.; Lundmark, S.T.; Alatalo, M.; Thiringer, T.; Nordelöf, A. Three traction motors with different magnet materials—Influence on cost, losses, vehicle performance, energy use and environmental impact. In Proceedings of the 2018 Thirteenth International Conference on Ecological Vehicles and Renewable Energies (EVER), Monte Carlo, Monaco, 10–12 April 2018; pp. 1–13. [Google Scholar]
  15. Ilankoon, I.M.S.K.; Dushyantha, N.P.; Mancheri, N.; Edirisinghe, P.M.; Neethling, S.J.; Ratnayake, N.P.; Rohitha, L.P.S.; Dis-sanayake, D.M.D.O.K.; Premasiri, H.M.R.; Abeysinghe, A.M.K.B.; et al. Constraints to rare earth elements supply diversification: Evidence from an industry survey. J. Clean. Prod. 2021, 331, 129932. [Google Scholar] [CrossRef]
  16. Massari, S.; Ruberti, M. Rare earth elements as critical raw materials: Focus on international markets and future strategies. Resour. Policy 2013, 38, 36–43. [Google Scholar] [CrossRef]
  17. Baldi, L.; Peri, M.; Vandone, D. Clean energy industries and rare earth materials: Economic and financial issues. Energy Policy 2014, 66, 53–61. [Google Scholar] [CrossRef] [Green Version]
  18. Habib, K. A product classification approach to optimize circularity of critical resources – the case of NdFeB magnets. J. Clean. Prod. 2019, 230, 90–97. [Google Scholar] [CrossRef]
  19. Zhanheng, C. Global rare earth resources and scenarios of future rare earth industry. J. Rare Earths 2011, 29, 1–6. [Google Scholar]
  20. Kontos, S.; Ibrayeva, A.; Leijon, J.; Mörée, G.; Frost, A.E.; Schönström, L.; Gunnarsson, K.; Svedlindh, P.; Leijon, M.; Eriksson, S. An Overview of MnAl Permanent Magnets with a Study on Their Potential in Electrical Machines. Energies 2020, 13, 5549. [Google Scholar] [CrossRef]
  21. Ferraris, L.; Ferraris, P.; Poskovic, E.; Tenconi, A. Theoretic and Experimental Approach to the Adoption of Bonded Magnets in Fractional Machines for Automotive Applications. IEEE Trans. Ind. Electron. 2011, 59, 2309–2318. [Google Scholar] [CrossRef]
  22. Ferraris, L.; Franchini, F.; La Cascia, D.; Poskovic, E. Adoption of bonded magnets in place of sintered NdFeB: Performance and economic considerations on a small power generator. In Proceedings of the IEEE EPE ECCE Europe Conference, Geneva, Switzerland, 8–10 September 2015. [Google Scholar] [CrossRef]
  23. Riba, J.-R.; López-Torres, C.; Romeral, L.; Garcia, A. Rare-earth-free propulsion motors for electric vehicles: A technology review. Renew. Sustain. Energy Rev. 2016, 57, 367–379. [Google Scholar] [CrossRef] [Green Version]
  24. Schulze, R.; Buchert, M. Estimates of global REE recycling potentials from NdFeB magnet material. Resour. Conserv. Recycl. 2016, 113, 12–27. [Google Scholar] [CrossRef]
  25. Binnemans, K.; Jones, P.T.; Blanpain, B.; Van Gerven, T.; Yang, Y.; Walton, A.; Buchert, M. Recycling of rare earths: A critical review. J. Clean. Prod. 2013, 51, 1–22. [Google Scholar] [CrossRef]
  26. Liu, R.; Buchert, M.; Dittrich, S.; Manhart, A.; Merz, C.; Schuler, D. Application of rare earths in consumer electronics and challenges for recycling. In Proceedings of the IEEE ICCE Conference, Berlin, Germany, 6–8 September 2011; pp. 286–290. [Google Scholar] [CrossRef]
  27. Zakotnik, M.; Tudor, C.O.; Talens Peiró, L.; Afiuny, P.; Skomski, R.; Hatch, G.P. Analysis of energy usage in Nd–Fe–B magnet to magnet recycling. Environ. Technol. Innov. 2016, 5, 117–126. [Google Scholar] [CrossRef]
  28. Jin, H.; Song, B.D.; Yih, Y.; Sutherland, J. A bi-objective network design for value recovery of neodymium-iron-boron magnets: A case study of the United States. J. Clean. Prod. 2018, 211, 257–269. [Google Scholar] [CrossRef]
  29. Lixandru, A.; Poenaru, I.; Güth, K.; Gauß, R.; Gutfleisch, O. A systematic study of HDDR processing conditions for the recycling of end-of-life Nd-Fe-B magnets. J. Alloys Compd. 2017, 724, 51–61. [Google Scholar] [CrossRef]
  30. Zakotnik, M.; Harris, I.R.; Williams, A.J. Multiple recycling of NdFeB-type sintered magnets. J. Alloys Compd. 2009, 469, 314–321. [Google Scholar] [CrossRef]
  31. Zakotnik, M.; Harris, I.R.; Williams, A.J. Possible methods of recycling NdFeB-type sintered magnets using the HD/degassing process. J. Alloys Compd. 2008, 450, 525–531. [Google Scholar] [CrossRef]
  32. Horikawa, T.; Miura, K.; Itoh, M.; Machida, K.I. Effective recycling for Nd-Fe-B sintered magnet scraps. J. Alloys Compd. 2006, 408–412, 1386–1390. [Google Scholar] [CrossRef]
  33. Itoh, M.; Masuda, M.; Suzuki, S.; Machida, K.-I. Recycling of rare earth sintered magnets as isotropic bonded magnets by melt-spinning. J. Alloys Compd. 2004, 374, 393–396. [Google Scholar] [CrossRef]
  34. Tanvar, H.; Dhawan, N. Microwave-Assisted Carbothermic Reduction of Discarded Rare Earth Magnets for Recovery ofNeodymium and Iron Values. J. Miner. Met. Mater. Soc. 2021, 73, 54–62. [Google Scholar] [CrossRef]
  35. Di Piazza, S.; Cecchi, G.; Cardinale, A.M.; Carbone, C.; Mariotti, M.G.; Giovine, M.; Zotti, M. Penicillium expansum Link strain for a biometallurgical method to recover REEs from WEEE. Waste Manag. 2017, 60, 596–600. [Google Scholar] [CrossRef]
  36. Emil-Kaya, E.; Stopic, S.; Gürmen, S.; Friedrich, B. Production of rare earth element oxide powders by solution combustion: A new approach for recycling of NdFeB magnets. RSC Adv. 2022, 12, 31478–31488. [Google Scholar] [CrossRef]
  37. Chung, H.; Prasakti, L.; Stopic, S.R.; Feldhaus, D.; Cvetković, V.S.; Friedrich, B. Recovery of Rare Earth Elements from Spent NdFeB Magnets: Metal Extraction by Molten Salt Electrolysis (Third Part). Metals 2023, 13, 559. [Google Scholar] [CrossRef]
  38. Orefice, M.; Eldosouky, A.; Škulj, I.; Binnemans, K. Removal of metallic coatings from rare-earth permanent magnets by solutions of bromine in organic solvents. RSC Adv. 2019, 9, 14910–14915. [Google Scholar] [CrossRef] [Green Version]
  39. Meakin, J. Targeted Hydrogen Decrepitation of Ndfeb Magnets from Large Commercial Assemblies. Master’s Thesis, School of Metallurgy and Materials, University of Birmingham, Birmingham, UK, 2013. [Google Scholar]
  40. Fidler, J.; Schrefl, T.; Hoefinger, S.; Hajduga, M. Recent developments in hard magnetic bulk materials. J. Phys. Condens. Matter 2004, 16, S455–S470. [Google Scholar] [CrossRef] [Green Version]
  41. Method for Producing Sintered Ndfeb Magnet. European Patent EP2071597B1, 23 July 2007.
  42. Corfield, M.R.; Harris, I.R.; Williams, A.J. Influence of oxygen content on grain growth in Pr–Fe–B/Nd–Fe–B sintered magnets. J. Alloys Compd. 2008, 463, 180–188. [Google Scholar] [CrossRef]
  43. Zhang, Y.; Gu, F.; Su, Z.; Liu, S.; Anderson, C.; Jiang, T. Hydrometallurgical Recovery of Rare Earth Elements from NdFeB Permanent Magnet Scrap: A Review. Metals 2020, 10, 841. [Google Scholar] [CrossRef]
  44. Li, D.; Horikawa, T.; Liu, J.; Itoh, M.; Machida, K.-I. Electromagnetic wave absorption properties of iron/rare earth oxide composites dispersed by amorphous carbon powder. J. Alloys Compd. 2006, 408–412, 1429–1433. [Google Scholar] [CrossRef]
  45. Nlebedim, I.; Ucar, H.; Hatter, C.B.; McCallum, R.; McCall, S.K.; Kramer, M.; Paranthaman, M.P. Studies on in situ magnetic alignment of bonded anisotropic Nd-Fe-B alloy powders. J. Magn. Magn. Mater. 2017, 422, 168–173. [Google Scholar] [CrossRef] [Green Version]
Figure 1. Hard disk drive with the magnet position.
Figure 1. Hard disk drive with the magnet position.
Metals 13 01103 g001
Figure 2. Different sizes of the recovered NdFeB magnets (some high-mu shields on the left).
Figure 2. Different sizes of the recovered NdFeB magnets (some high-mu shields on the left).
Metals 13 01103 g002
Figure 3. Proposed mechanical technique: impact mill.
Figure 3. Proposed mechanical technique: impact mill.
Metals 13 01103 g003
Figure 4. Vacuum impact mill scheme.
Figure 4. Vacuum impact mill scheme.
Metals 13 01103 g004
Figure 5. Impact mill in glove-box and the washing in Argon: exterior aspect of the glove box (a) and the impact mill used with this configuration (b).
Figure 5. Impact mill in glove-box and the washing in Argon: exterior aspect of the glove box (a) and the impact mill used with this configuration (b).
Metals 13 01103 g005
Figure 6. Vacuum impact mill: mill (a) and system connection with the pump (b).
Figure 6. Vacuum impact mill: mill (a) and system connection with the pump (b).
Metals 13 01103 g006
Figure 7. The scheme represents different steps of the proposed technique: supply of disused hard disks, recovery of NdFeB magnets, crushing with two different impact mills, and recycled powder characterization.
Figure 7. The scheme represents different steps of the proposed technique: supply of disused hard disks, recovery of NdFeB magnets, crushing with two different impact mills, and recycled powder characterization.
Metals 13 01103 g007
Figure 8. Distribution size of milled powders.
Figure 8. Distribution size of milled powders.
Metals 13 01103 g008
Figure 9. Comparison between Experimental XRD spectrum of recycled powder in vacuum impact mill (numbers denote the Miller’s indices, (hkl)) and NdFeB bulk reference standard.
Figure 9. Comparison between Experimental XRD spectrum of recycled powder in vacuum impact mill (numbers denote the Miller’s indices, (hkl)) and NdFeB bulk reference standard.
Metals 13 01103 g009
Figure 10. Demagnetization curves for two impact mill processes.
Figure 10. Demagnetization curves for two impact mill processes.
Metals 13 01103 g010
Figure 11. The density variation for the same volume cylinder of recycled NdFeB powder.
Figure 11. The density variation for the same volume cylinder of recycled NdFeB powder.
Metals 13 01103 g011
Figure 12. The specific cylinder with dedicated tools: brass cylinder and separators discs with dedicated extension poles (a); insert in hysteresisgraph joke (b).
Figure 12. The specific cylinder with dedicated tools: brass cylinder and separators discs with dedicated extension poles (a); insert in hysteresisgraph joke (b).
Metals 13 01103 g012
Figure 13. Demagnetization curves of the three powder densities for recycled NdFeB: low density 3.11 g/cm3, medium density 4.52 g/cm3, and high density 4.81 g/cm3.
Figure 13. Demagnetization curves of the three powder densities for recycled NdFeB: low density 3.11 g/cm3, medium density 4.52 g/cm3, and high density 4.81 g/cm3.
Metals 13 01103 g013
Figure 14. Magnetographic observation for three different densities: 3.11 g/cm3 (a), 4.52 g/cm3 (b), 4.81 g/cm3 (c). The presence of residual anisotropy (b,c).
Figure 14. Magnetographic observation for three different densities: 3.11 g/cm3 (a), 4.52 g/cm3 (b), 4.81 g/cm3 (c). The presence of residual anisotropy (b,c).
Metals 13 01103 g014
Table 1. Elementary analyses (LECO-ONH) as a function of different processes with impact mills.
Table 1. Elementary analyses (LECO-ONH) as a function of different processes with impact mills.
Type of Impact Mill Operation Oxygen Content wt.%
Operation in a glove box (Argon)1.59
Operation in Vacuum Impact Mill0.375
Table 2. XRF composition of recycled powder in vacuum impact mill.
Table 2. XRF composition of recycled powder in vacuum impact mill.
ElementsComposition %
Fe63.394
Nd28.514
Ni5.653
V1.053
La0.987
Cu0.182
Ca0.087
Nb0.057
Zr0.039
Os0.020
Mo0.013
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Pošković, E.; Franchini, F.; Ceroni, M.; Innocenti, C.; Ferraris, L.; Sangregorio, C.; Caneschi, A.; Actis Grande, M. Study of an Impact Mill-Based Mechanical Method for NdFeB Magnet Recycling. Metals 2023, 13, 1103. https://doi.org/10.3390/met13061103

AMA Style

Pošković E, Franchini F, Ceroni M, Innocenti C, Ferraris L, Sangregorio C, Caneschi A, Actis Grande M. Study of an Impact Mill-Based Mechanical Method for NdFeB Magnet Recycling. Metals. 2023; 13(6):1103. https://doi.org/10.3390/met13061103

Chicago/Turabian Style

Pošković, Emir, Fausto Franchini, Marta Ceroni, Claudia Innocenti, Luca Ferraris, Claudio Sangregorio, Andrea Caneschi, and Marco Actis Grande. 2023. "Study of an Impact Mill-Based Mechanical Method for NdFeB Magnet Recycling" Metals 13, no. 6: 1103. https://doi.org/10.3390/met13061103

APA Style

Pošković, E., Franchini, F., Ceroni, M., Innocenti, C., Ferraris, L., Sangregorio, C., Caneschi, A., & Actis Grande, M. (2023). Study of an Impact Mill-Based Mechanical Method for NdFeB Magnet Recycling. Metals, 13(6), 1103. https://doi.org/10.3390/met13061103

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop