Open access peer-reviewed chapter

Purification of Rare Earth Amide Salts by Hydrometallurgy and Electrodeposition of Rare Earth Metals Using Ionic Liquids

Written By

Masahiko Matsumiya

Submitted: April 6th, 2016 Reviewed: October 12th, 2016 Published: February 22nd, 2017

DOI: 10.5772/66300

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This paper reports a novel bench-scale hydrometallurgical procedure and electrodeposition using triethyl-pentyl-phosphonium bis(trifluoromethyl-sulfonyl)amide ([P2225][TFSA]) ionic liquids (ILs) for the recovery of rare earth (RE) metals from spent Nd-Fe-B magnets. The hydrometallurgical treatments were carried out at bench scale to produce RE amide salts of high purity. In the leaching process employing 1.7 kg of oxidized Nd-Fe-B fine powder and 14.2 L of an acid medium of 1,1,1-trifluoro-N-[(trifluoromethyl)sulfonyl]methanesulfonamide (H[TFSA]), selective leaching of RE ions (85.7±5.8% Nd) was performed at bench scale. Then, Fe (<99.9%) was successfully separated from RE ions in the deironization process. The total amount of the recovered amide salts through the evaporation treatment using a spray dryer was 3.57 kg. From the CV/EQCM measurements for Nd(III) at 373 K, a clear cathodic peak with the mass increased, and the ηρ decreased was observed at −2.79 V. Considering our previous investigations, the reduction of Nd(III)/Nd(0) was indicated as [Nd(III)(TFSA)5]2− + 3e− → Nd(0) + 5[TFSA]−. In addition, the Mapp value in the range of −2.49 V ~ −2.94 V was 46.8 g mol−1, which was close to the theoretical value for the electrodeposition reaction of Nd(III)/Nd(0), 48.1 g mol−1. Moreover, the electrodeposition of Nd(0) was carried out under the condition of −3.20 V versus Fc/Fc+ at 373 K. The electrodeposits were identified with the metallic Nd in the middle layer investigated by X-ray diffraction and X-ray photoelectron spectroscopy. Finally, we demonstrated that the novel recovery process consisted of hydrometallurgy and electrodeposition using ILs was effective by calculating material flow.


  • electrodeposition
  • hydrometallurgy
  • ionic liquids
  • neodymium metal

1. Introduction

Rare earth (RE) elements are currently regarded to be the most critical elements necessary for sustainable applications, and their RE groups play an important role in the development of future high-tech industries. Significant price fluctuations and high demand have raised their potential recovery from end-of-life products [1]. It is important to recover them from urban mining and secondary products containing permanent magnets.

Hydrometallurgical treatment is widely applied as an effective method for extracting RE components from primary sources and is potential in reclaiming these elements [2]. As listed in Table 1, the various techniques effective for the recovery of RE elements, such as chemical vapor transport [3], solvent extraction [4], electrolytic method [5], and hydrometallurgical processes [6, 7], have been listed, although a number of recovery methods for RE elements on the laboratory scale have not been so widespread. There was almost no information about the plants and processing paths. From the above situation, this study focused on a bench-scale hydrometallurgy to separate and recover RE components from spent Nd-Fe-B magnet. The preliminary research in our procedure is reported in the previous publications [8, 9].

Chemical vapor transport59% Nd and 68% Dy were recovered from
scrap of RE intermetallic materials.
Solvent extraction and
liquid-membrane transport
The selective permeation of Nd and Dy
by IL based supported liquid-membrane
using N,N-dioctyldiglycolamic acid.
ElectrolysisPolarization on Pt electrode led to
recover Nd and Dy metals in fused
Na2SO4 from Nd and Dy oxides
Electrochemical processMass ratio between Nd and Dy was
indicated as 121 from RE-Ni alloys
Hydrometallurgical processThe recovery efficiencies were indicated as
69.7% Nd and 51% Dy from magnetic waste sludge

Table 1.

Various recovery techniques for rare earths.

Pyrometallurgical treatment using high-temperature molten salts (HTMSs) is generally known as a conventional method for the recovery of RE metals. However, the HTMSs such as fluorides [10, 11] consumes a large amount of thermal energy owing to the high melting points of molten salts; thus, the recovery method of RE metals from HTMS baths is inappropriate as a next-generation technique. From the standpoint of saving energy, the development of a recovery process for RE metals with reduced energy consumption is hopeful in the near future. For this purpose, we have proposed an electrowinning-recovery method of the REs using ILs, which have unique physicochemical properties, such as high ionic conductivity, a wide electrochemical window, low vapor pressure, and incombustibility [12]. The electrochemical behaviors and the electrodepositions of RE metals such as La, Sm, Eu, and Yb in ILs are reported [13, 14]. We have already demonstrated the electrochemical behaviors and the electrodepositions of Nd [1518] and Dy metals [19, 20] using hydrophobic ILs, such as triethyl-pentyl-phosphonium bis(trifluoromethyl-sulfonyl) amide [P2225][TFSA] and 2-hydroxyethyl-trimethyl-ammonium bis(trifluoromethyl-sulfonyl) amide [N1112OH][TFSA]. In addition, we have developed the wet separation processes such as the solvent extraction using the hydrophobic ILs [2123] and the precipitation separation [8, 9]. The wet separation process was combined with the electrodeposition for the recovery of the Nd and Dy metals from the practical wastes of Nd-Fe-B magnets.

For the purpose of the analysis of reduction behavior of Nd(III) in ILs, in situ investigation using an electrochemical quartz crystal microbalance (EQCM) was conducted in this study. The EQCM technique is based on the piezoelectric properties of a quartz crystal and can detect a nano-level mass change in a quartz crystal electrode during electrochemical experiments from the resonance frequency of the quartz [24]. Although a conventional oscillator technique, namely self-excited or active technique EQCM, was inoperative in some ILs due to their high viscosity, the possibility of applying EQCM measurements with the use of separately excited or passive technique in highly viscous fluids including ILs was recently demonstrated and the cases of successful application have been reported [2530]. On the EQCM measurement, the resonance resistance can also be measured and reflects a product of the viscosity and the density of the media near the quartz crystal electrode [28] and the viscoelasticity of the electrodeposits [26, 27, 31, 32]. Thus, the change in the mass and the viscoelasticity of the electrodeposits on the electrode and the product of the viscosity and the density of the electrolyte near the electrode, relating to the concentration of a soluble species particularly in the case of ILs [25, 26] and corresponding to the electrochemical behavior, can simultaneously be observed by using the EQCM measurements, and very useful information for the specific examination of the electrode reaction can be acquired.

In this study as a new attempt, the electrochemical behavior of Nd(III) in ILs was analyzed by EQCM measurement at elevated temperatures because it is desirable to decrease the overpotential of the electrodeposition and to increase the diffusion rate of the metallic species by lowering the viscosity by means of elevating the temperature. There were a few reports about the theoretical equations: the Sauerbrey equation [24] and Kanazawa-Gordon [33]. However, these equations were not applied at elevated temperatures [25, 34]; therefore, we have demonstrated that the applicability of EQCM method in a medium temperature range around 373 K was revealed in the previous study [35]. In addition, we discuss the electroreduction behavior of Nd(III) in ILs on the potentiostatic condition in this study.

Considering the fundamental electrochemical investigations, the electrodeposition on the condition of constant potential was carried out on a relatively large scale. The Nd metal recovered by electrodeposition is applicable in the production of new Nd-Fe-B magnets because Nd metal of high purity is obtained by polishing the oxide layer after electrodeposition using ILs. Finally, we demonstrated the effectiveness of hydrometallurgy and electrodeposition process through the material flow.


2. Experimental

2.1. Pretreatment process

The spent Nd-Fe-B magnets were recovered from voice coil motors (VCMs) that were heated in an electric furnace at 623 K for 3 h for the demagnetization treatment. After demagnetization, the magnetic flux density was measured using a digital TESLA meter. The residual magnetic force field of this sample was almost zero, and the percentage of demagnetization was >99.9%. Then, the Ni-Cu-Ni triple layer on the Nd-Fe-B sample was removed by a grinding machine. After the stripping of the layer, fragments of Nd-Fe-B sample were pulverized using a stamp mill. The fine powders obtained were sieved to less than 150 μm and heated at 90 K h−1 to 1133 K, which was kept for 3 h in an electric furnace in order to oxidize the Nd-Fe-B components. After the roasting process, these fine powders were reground again by the automatic grinder. The surface area and the particle size (D50) of oxidized Nd-Fe-B sample measured by the Brunauer-Emmett-Teller (BET) method were 0.630 m2 g−1 and 59.43 μm, respectively.

2.2. Bench-scale leaching

The fine powders of oxidized Nd-Fe-B sample (1.7 kg) were leached in 14.2 L of a 1.0 M aqueous solution of 1,1,1-trifluoro-N-[(trifluoromethyl)sulfonyl]methanesulfonamide (HN(SO2CF3)2, H[TFSA]). The leaching solution was heated at 323 K, stirring at 500 rpm. The leaching behavior was researched from the potential (E)-pH diagram for Fe-H2O and Nd-H2O systems. Therefore, the oxidation-reduction potential (ORP) and pH in the leaching solution were measured by a high-precision digital meter (MM-60R, DKK-TOA Corp.). The quantification of Fe2+ was available for the complexation of [Fe(phen)3]2+ using 1,10-phenanthroline. The concentration of Fe2+ was measured by an ultraviolet-visible-near-infrared (UV-Vis-NIR) spectrometer (Perkin Elmer, Lambda750) at 508 nm [36, 37]. The concentration of Fe3+ was calculated from the total amount of Fe2+ and Fe3+ ions obtained from inductively coupled plasma atomic emission spectroscopy (ICP-AES) analysis (ICPE-9000, Shimadzu Co.). All of the precise concentrations for metallic species were quantitatively determined from ICP-AES analysis.

2.3. Bench-scale deironization and preparation of RE salts

Dried oxygen gas was introduced into the leaching solution with a flow rate of 5.0 L min−1 after the leaching process. The oxidizing agent for Fe2+ was effective in the leaching solution at pH > 3.2. Some kinds of alkali metal hydroxides [8, 9] were acted as precipitation agents in the previous study, and the perfect removal of the iron components was successfully carried out at laboratory scale. The deironization treatment without precipitation agents is important as a further development, because the additive materials contaminated the final RE salts. Considering the leaching process, reuse of the oxidized Nd-Fe-B powder as a precipitation agent is desirable, because RE2O3 in the oxidized Nd-Fe-B sample was selectively leached in the H[TFSA] solution. The oxidized Nd-Fe-B fine powder was also available for sediment formation of [Fe(OH)x]3−xprecipitates in this study. A small amount of the oxide Nd-Fe-B powder was introduced carefully into leaching solution while the alternation in pH was measured. The best terminal point of the precipitation reaction for [Fe(OH)x]3−xwas found to be pH = 4.92–4.93 because no iron component was detected in the leaching solution. It was important to develop a rapid solid-liquid separation technique because [Fe(OH)x]3−xprecipitates are colloidal and the separation from colloidal precipitates is very difficult. Therefore, hematite (α-Fe2O3) containing oxidized Nd-Fe-B sample was applied as a seed crystal in the formation of [Fe(OH)x]3−xprecipitates. The formation of [Fe(OH)x]3−xprecipitates with a large particle size greatly contributed to the filtration in solid-liquid separation. Finally, the [Fe(OH)x]3−xprecipitates were completely removed from the leaching solution.

After the deironization treatment, a turquoise filtrate was obtained; the color of the solution was based on the RE components. The evaporation treatment of the filtrate was carried out by a spray dryer (SD-1000, EYELA Co., Ltd.). In the operation of the spray dryer, the inlet temperature was maintained at 473 ± 1.6 K and dried nitrogen gas was introduced through the evaporation part at 105 ± 5.0 kPa. Then, the H[TFSA] filtrate was introduced using a roller pump at 150 mL h−1. In order to recover the dried M(TFSA)nsalts, the recovery part was heated at 413 ± 1.5 K with a heating mantle. The amount of M(TFSA)nsalts for one batch and the total amount of M(TFSA)nsalts were >300 g and 3.57 kg, respectively. The amount of metallic components in the M(TFSA)nsalts was measured by ICP-AES analysis.

2.4. Electrochemical analysis

The resistance of a quartz oscillator and resonance frequency were observed using an EQCM system, (Seiko EG&G, QCA922) applying AT-cut platinum-coated [9 MHz, ϕ = 5.0 mm, Seiko EG&G, QA-A9M-PT(P)] with a well-type cell (Seiko EG&G, QA-CL4PK) as shown in Figure 1. The employed O-rings (Seiko EG&G, P-S75B) had a high resistance for heat and low expansibility. The temperature of the EQCM system was elevated using a heating mantle controlled by a thermostat with a proportional-integral-derivative (PID) controller. The temperature was slowly increased at a rate of 1.0–1.5 K min−1 to prevent the strain occurring in the crystal structure of the quartz. The bath temperature was measured using a K-type thermocouple (ϕ = 1.6 mm). The cell covered with the heating mantle was connected to the EQCM system with an extension cord (Seiko EG&G, QCA922-10-EX10). In terms of the functionality of EQCM technique at elevated temperatures, the relationship between the viscosity and the density of Nd(III) samples, ηρvalues, the shifts of the resonance frequency, and the resistance before and after contacting the samples with the quartz have been already revealed in the previous study [35].

The voltammetric measurements were carried out using an electrochemical analyzer (ALS-440A, BAS Inc.,) with the EQCM system employing the Pt-coated quartz oscillator as a working electrode. Two Pt wires with 0.5 mm inside diameter were used as a counter and a quasi-reference electrode (QRE). The counter electrode was surrounded by a Vycor glass filter at the bottom in order to prevent the diffusion of decomposition components from the anode into the electrolyte. The Pt QRE showed a high stability and a good reproducibility of the potential at elevated temperatures. The potential was compensated for the IL standard using a ferrocene (Fc)/ferrocenium (Fc+) redox couple. Before all the electrochemical measurements, the dissolved oxygen was removed from the electrolytes by bubbling Ar gas for 30 min, and the measurements were conducted under flowing Ar gas in the cell with a rate of 20 ml min−1. Cyclic voltammetry (CV) of 0.01 M Fc in [P2225][TFSA] was carried out at 298 K with a sweep rate of 1.0 mV s−1 after iRcompensation (RC constant: 977.3) in order to confirm EQCM behavior while there was an outer-sphere electron-transfer reaction of Fc/Fc+. The electrochemical behavior of Nd(III) in [P2225][TFSA] was investigated by CV measurements of 0.05 M Nd(III) in [P2225][TFSA] at 373 K with a sweep rate of 2.0 mV s−1. For the analysis of the electrodeposition behavior of Nd(0) from Nd(III) in [P2225][TFSA], the controlled potential electrolysis (CPE) under −3.20 V vs. Fc/Fc+ was performed at 373 K using 0.05 and 0.10 M Nd(III) in [P2225][TFSA] as electrolytes.

Figure 1.

The schematic illustration of EQCM cell with separate system: (a) Ar flow, (b) K-type thermocouple1 (for recording by a data logger), (c) Pt wire (counter electrode), (d) heating mantle, (e) separated electrolyte, (f) Vycor glass, (g) quartz oscillator coated with Pt (working electrode), (h) K-type thermocouple2 (for controlling temperature by PID), (i) Pt wire (quasi-reference electrode), (j) main electrolyte, (k) heat insulator.

2.5. Electrodeposition

A schematic illustration of the electrodeposition cell is shown in Figure 2. In the electrodeposition with the three-electrode system, a copper substrate with a surface area of 2.0 × 10−2 m2 and a platinum were employed as the working electrode and quasi-reference electrode, respectively. Fe rod was employed as a counter electrode and was surrounded with a glass tube via a Vycor glass filter at the bottom to prevent the diffusion of dissolved [Fe(TFSA)3] complexes from the anode into the electrolyte. The electrolytic bath was stirred at 500 rpm, because the current during electrodeposition decreased immediately to the limiting current when the bath was not stirred. The overpotential was constant at −3.20 V versus Fc/Fc+ at 373 K during potentiostatic electrodeposition in a glovebox. After electrodeposition, the electrodeposits were leached into a super-dehydrated acetone (>99.5%, Wako Pure Chemical Industries, Ltd., water content <10 ppm) in a glovebox to remove the electrolyte thoroughly. The surface morphology of the electrodeposits was observed by scanning electron microscopy (SEM) and the composition of the electrodeposits was analyzed by energy dispersive X-ray analysis (EDX) (JSM-6510LA, JED-2300, JEOL, Ltd.). The metallic state and the crystallinity of the electrodeposits were evaluated by X-ray photoelectron spectroscopy (XPS) (Quantera SXM, ULVAC-PHI, Inc) and X-ray diffraction (XRD) (RINT-2500, Rigaku Co.), respectively.

Figure 2.

The schematic illustration of the electrodeposition cell with three-electrode system, (a) Fe rod (anode), (b) Teflon cap, (c) heat insulator, (d) soda-lime glass tube, (e) [P2225][TFSA], (f) Vycor glass filter, (g) K-type thermocouple, (h) Pt wire (Q.R.E.), (i) Cu substrate (cathode), (j) heating mantle, (k) stirrer, and (l) [P2225][TFSA] including M(TFSA)nor Nd(TFSA)3.


3. Results and discussion

3.1. Leaching behavior at bench scale

The leaching reactions of the oxidized Nd-Fe-B sample were represented as follows:


The leaching behavior in H[TFSA] solution using the oxidized Nd-Fe-B fine powder as a precipitation agent is shown in Figure 3. The leaching percentage of Nd and Fe for 66h in the H[TFSA] solution were 85.7±5.8% and 5.8±0.1%, respectively. A drastic increase in the pH value was observed at the initial stage of the leaching process, which indicates that leaching reaction Eq. (1) mainly occurred in this system. The leaching behavior accounted for the potential (E)-pH diagrams of Fe-H2O and Nd-H2O systems as shown in Figure 4. The actual measurement data in the bench scale is also plotted in the potential (E)-pH diagram. From the E-pH diagram, at E = ~0.75 and pH < 1.0, the most stable states of Fe and Nd components were found to be solid Fe2O3 and Nd3+ ion, respectively. This result indicated that the selective leaching of Nd3+ (leaching percentage > 90%) was carried out at bench scale.

Figure 3.

The leaching behavior of each metallic component in H[TFSA] solution at bench scale.

Figure 4.

Potential(E)-pH diagram of Fe-H2O and Nd-H2O systems. Leaching time ○:3 h, ●:15 h, □:18 h, ■:21 h.

3.2. Deironization and purification of RE amide salts at bench scale

The effective treatment for deironization is precipitation separation through the oxidation from Fe2+ to Fe3+ by oxygen bubbling, because [Fe(OH)x]3−xprecipitates are formed under acidic pH conditions [8, 9]. The precipitation reaction using the oxidized Nd-Fe-B sample was expressed as follows:


[Fe(OH)x]3−xis generally a colloidal precipitate, and it is very difficult to separate from the H[TFSA] solution. Therefore, we applied a seed crystal method, and hematite (α-Fe2O3) in oxidized Nd-Fe-B sample was employed as a seed crystal for the formation of [Fe(OH)x]3−xprecipitates. The precipitate with a large particle size greatly facilitated the filtration in the solid-liquid separation treatment. From the ICP-AES analysis, the separation percentage of Fe component was confirmed to be >99.9%. This result allowed us to conclude that the oxidized Nd-Fe-B sample was applicable for perfect removal of iron component as a seed crystal.

Run no.Flow rate /mL 
Blower flow
rate/m3 min−1
Volume of
H[TFSA] aq./mL
Amount of
Total: 3571.5 gAve.: 91.7%

Table 2.

The refining condition of leaching solution by spray dryer.

After the solid-liquid separation, the evaporation treatment of filtrate was performed using an improved spray dryer to effectively recover dried M(TFSA)n(M = Pr, Nd, Dy, B, Al, K, and trace elements) salts. The refining conditions of the H[TFSA] solution for the oxidized Nd-Fe-B sample are listed in Table 2. The total amount of recovered M(TFSA)nand the average recovery yield were 3571.5 g and 91.7%, respectively. The obtained M(TFSA)nsalt was a fine pale purple powder, and the water content in the M(TFSA)nsalt was less than 10 ppm. The composition of the recovered M(TFSA)nsalts is tabulated in Table 3. The stoichiometric number of M(TFSA)nand average molecular weight were 3.00 and 943.68, respectively. In addition, the average RE component in M(TFSA)nwas 96.81%. This series of results allowed us to conclude that the separation factor of Fe in the deironization treatment was >99.9% and the recovery yield of M(TFSA)nsalts was 82.4–96.8% using a spray dryer at bench scale.

Run no.Pr   Nd   Dy   RE*   Fe   B   Molecular weight
of M(TFSA)n

Table 3.

The composition (wt.%) of recovered M(TFSA)nsalts on the condition of Table 1.

*RE indicates the summation of the composition for Pr, Nd, and Dy.

**nindicates the stoichiometric number of M(TFSA)nsalts.

3.3. Theory

A frequency shift (Δf) observed on the EQCM analyzer includes effects relating to the mass change (Δm) in the quartz crystal electrode (Δfm) and the viscosity (η) and the density (ρ) of the liquid adjacent to the quartz (Δfηρ).


The relationship between Δfmand Δmis expressed by the Sauerbrey equation [24].


where f0 is the fundamental resonance frequency, Ais the surface area of the electrode (0.196 cm2), μqis the shear modulus of quartz (2.95 × 1010 kg m−1 s−2 at 298 K), and ρqis the density of quartz (2.65 × 103 kg m−3 at 298 K). On the other hand, Δfηρis proportional to the square root of the product of the liquid viscosity and density, (ηρ)1/2 demonstrated by Kanazawa-Gordon [33].


Although a frequency shift by the aqueous solution contacting the quartz is small, in the case of employing ILs as the electrolyte, it is necessary to consider the influence of Δfηρdue to the exceedingly high viscosity of ILs. In the EQCM measurements, the resonance resistance (R) can simultaneously be measured, and (ηρ)1/2 is also estimated from Rvalue [38].


where kis an electromechanical coupling factor and often used when the electrical model of the quartz crystal oscillator is converted to a mechanical model. The kvalue was estimated from the shifts in the resonance frequency and the resistances before and after the liquid sample came into contact with the quartz according to Eqs. (6) and (7), respectively, for each measurement in this study. Δfmis isolated from the total shift of frequency (Δf) by using Eqs. (4), (6), and (7). In addition, the apparent molar mass, Mapp, of the electrodeposited species can be calculated by using Δmestimated from Δfm, the electrical charge Qpassed during electrodeposition, and the Faraday constant F.


The theoretical value of Mapp based on the reduction reaction of Nd(III) + 3e → Nd(0) was 48.1 g mol−1. The theoretical equations of the EQCM measurements related to the frequency response are based on the analysis of an admittance spectrum of the quartz crystal near its resonance frequency [39]. The responses of the resonance frequency and the resistance to (ηρ)1/2 of the adjacent liquid to the quartz crystal are derived from the solutions of the equation, describing the steady-state shear waves in the AT-cut quartz oscillator under the condition that the transverse velocity of the surface of the quartz oscillator is identical with that of the adjacent liquid and that the force exerted by the liquid on the quartz is equal and opposite to the force exerted by the quartz on the liquid [33, 38]. Strictly speaking, the estimation of Δmfrom Δfmby Eq. (4) is valid for thin and rigid films coated on the quartz. Moreover, Δfηρand Rreflect not only the viscosity and the density of contacting liquid with the quartz but also the roughness, the viscoelastic properties, and the films [31, 32]. By considering these parameters in combination, it is possible to discuss detailed states on the surface of the quartz electrode accompanied by the electrochemical behaviors.

3.4. Electrochemical analysis

For the investigation of the reduction behavior for Nd(III) in [P2225][TFSA], cyclic voltammetry with EQCM measurements (CV/EQCM) were carried out at elevated temperatures. The EQCM behavior was confirmed in advance by CV/EQCM at 298 K measuring Fc/Fc+ redox couple in [P2225][TFSA]. The potential difference, ΔEp, between the anode and cathode peak was 67 mV after iRcompensation. The ΔEp value was close to the theoretical value; 59 mV in a reversible and one-electron reaction at 298 K and thus the observation of the electrochemical behavior was confirmed with high precision. Moreover, there were no significant alternations for the mass and ηρvalues in this reversible reaction. The results indicated that no changes of Δmand Δηρwere detected during the outer-sphere electron-transfer reaction and consistent with the Ref. [26].

The CV/EQCM results for Nd(III) in [P2225][TFSA] at 373 K were shown in Figure 5. A clear cathodic peak with the mass increased and the ηρdecreased was observed at −2.79 V. Considering our previous investigations [1518], the reduction of Nd(III)/Nd(0) was indicated as follows:


The Mapp value in the range of −2.49 V ~ −2.94 V calculated from the mass change was 46.8 g mol−1, which was close to the theoretical value for the electrodeposition reaction of Nd(III)/Nd(0), 48.1 g mol−1. Moreover, the observed decrease of the ηρvalue indicated that the concentration of Nd(III) near the electrode was locally decreased by consuming Nd(III) in the electrodeposition reduction of Nd(III)/Nd(0). This is based on the ηρchange in the IL system that largely depends on the concentration of the metal ion. Therefore, these results are an evidence for the electrodeposition reaction of Nd(III)/Nd(0). At a more negative potential than −2.79 V, the mass and ηρincreased with the comparatively low values of Mapp for 0.05 M Nd(III) in [P2225][TFSA]. This behavior indicated that the cathodic decomposition products from IL were generated on the electrode surface. A part of side chain of [P2225]+ would be decomposed on the cathode considering the Mapp value estimated in this potential range (−2.96 V ~ −3.30 V). In addition, in the range of 0 ~ −2.0 V the mass unexpectedly increased during slight current and no change in the ηρvalue for 0.05 M Nd(III) in [P2225][TFSA]. There was no observation of mass increase in the EQCM analysis for neat [P2225][TFSA] in this potential. Therefore, it was deduced that the reaction would be the formation of divalent species; Nd(II) [Nd(III) + e → Nd(II)]. The related disproportionation reaction [2Nd(III) + Nd(0) → 3Nd(II)] would occur in the IL system.

Figure 5.

CV/EQCM analysis for 0.05 M Nd(III) in [P2225][TFSA] at 373 K with 2.0 mV s−1; (a) voltammogram, (b) the mass change, and (c) the change inηρvalues.

The controlled potential electrolysis with EQCM measurements (CPE/EQCM) at −3.20 V was conducted with 0.05 and 0.10 M Nd(III) in [P2225][TFSA] at 373 K. The parameters of Δmand Δηρwere plotted as a function of the charge density Qdpassed during CPE as shown in Figure 6. The calculated values of Mapp in 0.05 and 0.10 M Nd(III) at the initial stage of CPE/EQCM analysis were 49.1 and 49.6 g mol−1, respectively, which were close to the theoretical value when the reduction of Nd(III)/Nd(0) occurred, 48.1 g mol−1, so that the electrodeposition of Nd(0) metal was also proved from the CPE/EQCM analysis. The total values of Mapp in 0.10 M solution, 18.4 ~ 29.8 g mol−1, were larger than those in 0.05 M solution, 7.7 ~ 18.6 g mol−1. These results indicated that the competition reaction for Nd(III)/Nd(0) reduction and IL decomposition would occur and depend on the Nd(III) concentration. The value of ηρafter 0.45 C cm−2 increased and the IL decomposition was also deduced from this result because the ηρchange implied that the quantity of the soluble species increase near the electrode and/or the viscoelastic film might be formed on the electrode surface [27, 31, 32, 40] by the IL decomposition.

Figure 6.

CPE/EQCM analysis for 0.05 and 0.10 M Nd(III) in [P2225][TFSA] induced on 3.20 V at 373 K; (a) the mass change and (b) the change inηρvalues.

Run no.Overpotential,
η/V vs. Fc/Fc+
charge, Q/C
Weight change,
Current efficiency,

Table 4.

The potentiostatic electrodeposition condition using [P2225][TFSA] including M(TFSA)3 at 373 K.

Run no.Composition/wt.%

Table 5.

The composition of Nd electrodeposits analyzed by EDX.

3.5. Electrodeposition

Considering the above fundamental electrochemical behavior of Nd(III), the electrodeposition of Nd(0) was carried out, and the condition was listed in Table 4. The electrodeposition was smoothly performed on the high anodic current efficiency. The current slowly decreased to the limiting current during electrodeposition. After the electrodeposition, the blackish electrodeposits were obtained on the Cu substrate. The electrodeposits observed by SEM had a granular morphology with a nonuniform size distribution. This morphology is considered to be explained from the fact that the initial stage of nucleation and growth occurred according to the progressive nucleation model [15]. The quantitative analysis using EDX for the electrodeposits obtained from the electrodeposition at −3.20 V versus Fc/Fc+ is summarized in Table 5. The results indicated that the electrodeposits on Cu substrate comprised mainly Nd component. However, a small amount of O component was also included in the electrodeposits, suggesting that the oxidizing Nd metal with O atoms would occur. In order to investigate the chemical bond state of Nd, XPS analysis with Al-Kα was carried out on the electrodeposits. The metallic and oxide components for Nd correspond to the binding energies of Nd3d5/2 at 980.5–981.0 eV and 981.7–982.3 eV, respectively, in the case of monochromated Al-Kα line [41]. The Nd3d5/2 spectra for the middle layer and top surface of electrodeposits are shown in Figure 7. For an in-depth analysis of the middle layer, the oxide layer of the electrodeposits was perfectly removed with an Ar ion beam, that is, (a) 0.42 μm under the electrodeposits. The peak maximum in the Nd3d5/2 spectrum acquired for the layers below 0.42 μm was at 980.77 eV. Hence, the electrodeposits obtained through electrodeposition using [P2225][TFSA] with M(TFSA)3 were identified as Nd metal and partial oxide mixtures. This result indicated that metallic Nd would have been electrodeposited on the Cu substrate and subsequently oxidized by O in the electrolyte, that is, residual water or dissolved oxygen. The XRD profile of the electrodeposits is shown in Figure 8 with the profile from Ref. [42] for Nd metal. The position of 2θof the electrodeposits was nearly identical to that of Nd metal. Therefore, the electrodeposits were identified to be crystalline Nd metal.

Figure 7.

XPS spectra for Nd3d5/2 region of electrodeposits (a) middle layer at 0.42 μm, (b) top surface.

Figure 8.

XRD profile of the Nd electrodeposits obtained from [P2225][TFSA].

3.6. Material flow of VCM recycling

As described earlier, it is worthwhile to evaluate the material flow from a series of processes such as pretreatment, hydrometallurgy, and electrodeposition using [P2225][TFSA] melts. The whole material flow is shown in Figure 9,and the recovery target in this material flow was based on the oxidized Nd-Fe-B wastes after the roasting process. As the first step of hydrometallurgy, the selective leaching of RE components (85.7 ± 5.8% Nd and 5.8 ± 0.1% Fe in 66 h) was performed in the leaching process. Then, the deironization treatment was carried out using precipitation formation of [Fe(OH)x]3−x, and the residual Fe component was perfectly removed in this process. After the deironization process, the M(TFSA)nsalts with high purity were obtained from the evaporation by a spray dryer, and the yield of M(TFSA)nsalts was as high as 91.7%. Scaling up for the vaporization treatment is relatively simple because a large-scale spray dryer can be available through cooperation with an associated company. A series of hydrometallurgy indicates that 78.6% (356.0 g/453.0 g × 100) Nd and 77.9% (10.9 g/14.0 g) Dy can be recovered as purified M(TFSA)nsalts from the initial oxidized Nd-Fe-B powder. After the hydrometallurgical process, M(TFSA)nsalts were available as an electrolytic bath in the electrodeposition process. In terms of material flow, the induced overpotential (E = −3.20 V vs. Fc/Fc+) and the cathodic current efficiency (ε = 74.6%) were determined from the actual electrodeposition results described above. Assuming that the total transported charge is Q = 7618.2 × 102 C (100 times at laboratory scale) under proper conditions based on the scaling-up electrolytic bath, 283.2 g of Nd metal can be recovered during the electrodeposition process, and the recovery yield calculated from the starting material (453.0 g Nd) was estimated to be 62.5%. Therefore, the recovery process based on hydrometallurgy and electrodeposition using [P2225][TFSA] was applicable for practical Nd-Fe-B wastes. From the economic point of view, H[TFSA] is currently slightly expensive compared with mineral acids. However, H[TFSA] can be prepared through an ion-exchange reaction of residual components. Studies to further improve the recovery process are now in progress.

Figure 9.

Material flow of hydrometallurgy and electrodeposition using [P2225][TFSA].


4. Conclusion

Hydrometallurgical process based on leaching, deironization, and purification of rare earth (RE) amide salts were carried out at bench scale. In the leaching process using 1.7 kg of oxidized Nd-Fe-B sample and 14.2 L of an aqueous solution of 1,1,1-trifluoro-N-[(trifluoromethyl) sulfonyl]methanesulfonamide (HN(SO2CF3)2, H[TFSA]), The leaching percentage of Nd and Fe for 66h in the H[TFSA] solution were 85.7±5.8% and 5.8±0.1%, respectively. Moreover, the oxidized Nd-Fe-B sample applied as a precipitation agent in the deironization process, and >99.9% Fe component was successfully separated from RE components. Finally, 3.57 kg of purified amide salts (M(TFSA)3, M = Pr, Nd, Dy, B, Al, and trace elements) were recovered through the evaporation process using an improved spray dryer and the percentage of RE components for amide salts was 96.81%.

The cyclic voltammetry (CV) with electrochemical quartz crystal microbalance (EQCM) was applied at elevated temperatures in this study. CV/EQCM measurements for the investigation of the reduction behavior related to Nd(III) in triethyl-pentyl-phosphonium bis(trifluoromethyl-sulfonyl)amide ([P2225][TFSA]) were conducted at 373 K. At the potential of −2.79 V, the objective electrodeposition, Nd(III)/Nd(0) was confirmed because a clear cathodic peak was observed and the apparent molar mass, Mapp was calculated to be 46.8 g mol−1, and this value was consistent with the theoretical value for Nd(III)/Nd(0), 48.1 g mol−1. At more negative potential than −2.79 V, the mass and ηρincreased with the comparatively low values of Mapp for 0.05 M Nd(III) in [P2225][TFSA]. This behavior indicated that the cathodic decomposition reaction of IL occurred on the electrode surface. Moreover, from the controlled potential electrolysis with EQCM (CPE/EQCM) measurements at −3.20 V versus Fc/Fc+ in the solutions of 0.05 and 0.10 M Nd(III) in [P2225][TFSA] at 373 K, the electrodeposits of Nd(0) metal were confirmed at the initial stage considering the Mapp values (49.1 and 49.6 g mol−1). The electrodeposition of Nd was carried out under potentiostatic conditions of −3.20 V versus Fc/Fc+ at 373 K. The electrodeposits in the middle layer 0.15 μm below the surface were identified to be Nd metal from the analysis of SEM/EDX, XPS, and XRD. Finally, the material flow of whole process allowed us to conclude that the novel recovery process was effective for practical use.



This study was partly supported by the Grant-in-Aid for Scientific Research (No. 15H02848) from the Ministry of Education, Culture, Sports, Science, and Technology, Japan.


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Written By

Masahiko Matsumiya

Submitted: April 6th, 2016 Reviewed: October 12th, 2016 Published: February 22nd, 2017