Next Article in Journal
Assessing the Risk of Total and Available Potentially Toxic Elements in Agricultural Soil in Typical Mining Areas in Xiangjiang River Basin, Hunan Province
Next Article in Special Issue
Effect of Basicity on the Sulfur Precipitation and Occurrence State in Kambara Reactor Desulfurization Slag
Previous Article in Journal
Editorial for Special Issue “Geology of Uranium Deposits”
Previous Article in Special Issue
An Investigation of the Adsorption of Xanthate on Bornite in Aqueous Solutions Using an Atomic Force Microscope
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Maintenance of the Metastable State and Induced Precipitation of Dissolved Neodymium (III) in an Na2CO3 Solution

1
Faculty of Materials Metallurgy and Chemistry, Jiangxi University of Science and Technology, Ganzhou 341000, China
2
Institute of Engineering Research, Jiangxi University of Science and Technology, Ganzhou 341000, China
3
College of Vanadium and Titanium, Panzhihua University, Panzhihua 617000, China
*
Author to whom correspondence should be addressed.
Minerals 2021, 11(9), 952; https://doi.org/10.3390/min11090952
Submission received: 19 July 2021 / Revised: 24 August 2021 / Accepted: 27 August 2021 / Published: 31 August 2021

Abstract

:
Rare earths dissolved in carbonate solutions exhibit a metastable state. During the period of metastability, rare earths dissolve stably without precipitation. In this paper, neodymium was chosen as a representative rare earth element. The effects of additional NaCl and CO2 on the metastable state were investigated. The metastable state can be controlled by adding NaCl to the Na2CO3 solution. Molecular dynamics studies indicated that the Cl provided by the additional NaCl partially occupied the coordination layer of Nd3+, causing the delayed formation of neodymium carbonate precipitation. In addition, the additional NaCl decreased the concentration of free carbonate in the solution, thereby reducing the behavior of free contact between carbonate and Nd, as well as resulting in the delay of Nd precipitate formation. Consequently, the period of the metastable state was prolonged in the case of introduction of NaCl. However, changing the solution environment by introducing CO2 can destroy the metastable state rapidly. Introduction of CO2 gas significantly decreased the CO32− content in the solution and increased its activity, resulting in an increase of the free CO32− concentration of the solution in the opposite direction. As a result, the precipitation process was accelerated and the metastable state was destroyed. It was possible to obtain a large amount of rare earth carbonate precipitation in a short term by introducing CO2 into the solution with dissolved rare earths in the metastable state to achieve rapid separation of rare earths without introducing other precipitants during the process.

1. Introduction

Rare earths are strategic metal resources that are used in a wide range of industries. For example, they can be found in the development of high-tech advanced materials for permanent magnets, luminescence, catalysis and hydrogen storage, as well as in basic industries such as metallurgy, machinery and petrochemicals in general [1,2,3,4,5].
Rare earth carbonate is a barely soluble substance, with a solubility in water of only 10−5–10−7 mol·L−1 [6,7]. However, when rare earth ions are added to a higher concentration of alkali metal carbonate solution, there occurs the phenomenon of rare earth dissolution in the carbonate solution. The amount of rare earth dissolution increases with increased carbonate concentration. As early as 1963, Taketatsu [8,9] found that when a certain amount of rare earth chloride solution was gradually added to a concentrated K2CO3 solution, sediment of the rare earth carbonate was generated first and then dissolved again with the passage of reaction time. The dissolution amount of rare earth increased with the increase of CO32− concentration and the atomic number of the rare earth (except for Ce and Y). Restricted by the situation of the industry at that time, rare earth resources were not as scarce as nowadays, but comparatively abundant. Therefore, the discovery of the regularity of dissolution of rare earths in carbonate solution did not attract the attention of the rare earth separation industry.
Vasconcellos et al. [10] carried out a feasibility study on selective dissolution, separation and enrichment of a rare earth in carbonate solution based on Taketatsu’s regularity [8,9]. Low-Ce rare earth carbonate concentrates were selectively dissolved and successfully enriched with yttrium by using NH4HCO3/(NH4)2CO3 solution as a carrier. The grade of yttrium increased from 2.4% to 81.0%. In addition, it was also found that the concentration of NH4+ influenced the dissolution behavior of rare earth in the solution system in that a higher concentration of NH4+ could enhance the solubility of rare earths. Reference to research on the equilibrium hydrochemical behavior of neodymium in a Na+-Cl-CO32−-HCO3 solution system [11], shows that there is a relationship between the solubility of rare earth in a carbonate solution and the concentration of the NaCl salt as an impurity, and the dissolved amount of rare earth increases with increasing concentration of NaCl in the solution. High concentration of NaCl results in high ionic strength of the solution. In addition, according to research data on rare earth adsorption in a water-bearing sand layer [12], at higher ionic strength of the solution, the more significant was the rare earth adsorption in the sand layer. In other words, a greater amount of rare earth loss was caused by dissolution. Thus, when the concentration of NH4+ in the solution increased, this resulted in a greater amount of dissolved rare earths, as observed by Vasconcellos [10], which can be attributed to the influence of the ionic strength of the solution [13].
Nowadays, a number of techniques have been developed for the separation of rare earths, such as solvent extraction [14], ion exchange, membrane separation and ionic liquids [15], as well as other methods. Among them, the most widely used is the traditional solvent extraction technique. The other methods are less used because of high cost. The core component of solvent extraction is the extractant. Currently, a number of high-performance extractants have been developed [16], but toxicity and loss of extractants are always the key weaknesses limiting the development of the technology. In addition, due to the increasingly stringent requirements of environmental protection, the high salt wastewater generated during the separation of rare earths remains a problem [17], and is also a bottleneck in the solvent extraction separation process [18]. For the healthy development of the rare earth industry, it is necessary and urgent to develop a new type of highly efficient and environmentally friendly separation technology.
A good and feasible green method to separate rare earths is by using the metastable state of the carbonate solution which dissolves them. In our previous study [19], a series of experiments on metastable states was carried out by choosing neodymium as an example of rare earth elements. Our results indicated that neodymium dissolved in a sodium carbonate solution exhibited some metastable properties. Among them, the most important one was that there is a limit to the dissolution of neodymium in a certain concentration of sodium carbonate solution, after which there is instantaneous saturated solubility. When the dissolved neodymium in the solution does not exceed its solubility, it is stable in the solution for a period (metastable period) without precipitating neodymium carbonate. Our previous study was not very comprehensive and limited by the length of the paper, so a follow-up study of metastable solution-induced precipitation was not carried out.
Now, combined with the idea of the solid-liquid separation of rare earths, we are continuing to consider the potential value of the metastable state. Rare earths are dissolved and enriched in the metastable period and precipitated and separated after exceeding this period. No other impurities are introduced in this process. In addition, the carbonate solution can be recycled. Therefore, this may be a potential method for green separation of rare earths. Hence, how to manually control the metastable state and the precipitation of rare earth carbonate is the core content of the present study.
In this study, the artificial control of metastable states is discussed in detail. Neodymium was chosen as a representative of rare earth elements. The effect of changing the solution environment, such as ion concentration, on the metastable state was studied, and the effective conditions for maintaining and destroying the metastable state were discovered.

2. Experiment

2.1. Raw Materials and Equipment

The rare earth material used in the experiment was a 10 g·L−1 dilute NdCl3 solution obtained by diluting high purity NdCl3 solution with deionized water. The high purity NdCl3 solution was purchased from the rare earth smelting & separating plant in Longnan, Jiangxi Province, and its distribution is shown in Table 1. Solutions of Na2CO3, Na2CO3/NaCl with different concentration gradients and dilute hydrochloric acid for acidification were obtained by dissolving AR-grade Na2CO3, solid NaCl and HCl solution with deionized water.
An experiment in which CO2 gas was used to induce precipitation of a metastable state solution was carried out by using an autoclave with a CO2 high-pressure cylinder, as shown in Figure 1. Other equipment used in experiments is shown in Table 2.

2.2. Maintenance and Mechanism of Metastable State of the Neodymium Dissolved in Na2CO3 Solution

2.2.1. Maintaining Metastable State by NaCl

Following on from our previous research [19], the effect of additional NaCl on the maintenance of the metastable state of a solution of dissolved Nd3+ was investigated. The neodymium concentration in 2 mol·L−1 Na2CO3 solution was controlled at 2.621 g·L−1. The ionic strength of the solution was controlled by adding NaCl to Na2CO3 solution to create a mixed electrolyte NaCl/Na2CO3 solution. The concentration of the additional NaCl ranged from 0 to 0.5 mol·L−1. During the experiment, the volume of the Na2CO3 (or mixed electrolyte NaCl/Na2CO3) solution was fixed at 25 mL, and the NdCl3 solution was added to it drop by drop with oscillation. The time was set from 0 to 480 min. When the experiment finished, the solution containing precipitates was further centrifuged at 6000 rpm for 5 min. After that, the obtained supernatant was split into two parts; one was selected as aqueous sample for the further testing, and the another was completely acidulated by using dilute hydrochloric acid, after which complexometric titration was used to determine the concentration of Nd3+.

2.2.2. Effect of NaCl on Neodymium Coordination and Solid Phase Precipitates

The metastable state solution in each representative stationary period was scanned by ultraviolet-visible light (UV-vis) full-wavelength scanning. In order to provide an experimental comparison, a blank solution (Na2CO3 and NdCl3 solution only addition with water) was also scanned by UV-vis full wavelength. The precipitates were collected as solid samples and detected by Fourier transform infrared spectroscopy (FTIR). Because drying could cause the sample to decompose [20], producing errors in the results, the samples were all stored in deionized water. Before determination, the water was filtered, the samples dried with filter paper, and the analysis carried out immediately.

2.2.3. Mechanism of Maintaining the Metastable State by NaCl

In order to find the maintenance mechanism of the additional NaCl on the metastable state, a molecular dynamics (MD) calculation was carried out using Materials Studio 8.0 [21] software. The solution model was established by using an Amorphous Cell module, and the model was geometry optimized using a Forcite module. Finally, MD calculation and radial distribution function (RDF) analysis [22] were carried out to reveal the relationship between the RDF and the coordination number of each component in the solution. The average coordination number of each component was calculated by Equation (1).
N ( L )   =     0 L g ( r )   ρ   4 π r 2 dr
where N(L) refers to the number of coordination atoms(molecules) in the 0−L spherical shell around the target atom, ρ refers to the number density of coordination atoms (molecules), where the value is the ratio of the number of atoms (molecules) to the volume of space, g(r) refers to the RDF value, and indicates the probability of the occurrence of coordination atoms(molecules) within a certain distance, and r refers to the cutoff radius.

2.3. Induced Precipitation of Neodymium Carbonates in Metastable State Solution

The precipitation process of neodymium carbonates by introducing CO2 gas into the metastable state solution was studied. The procedure of the dissolution of Nd3+ in the solution was as previously described. Further, the dissolved Nd3+ solution was transferred to an autoclave for introducing CO2 gas. The solution contained a large amount of halogen Cl, so a corrosion-resistant polytetrafluoroethylene tank was selected as the inner tank of the autoclave. During the experiment, the input pressure of CO2 was uniformly controlled at 0.2 Mpa. The time was set from 0–60 min. When the set time was reached, the solution containing precipitate was centrifuged at 6000 r·min−1 for 5 min, then the supernatant obtained after centrifugation was split in two parts. One was acidified, and the concentration of neodymium in the supernatant was determined by inductively coupled plasma emission spectrometer (ICP-OES). The other was analyzed by CO32− and HCO3 acid-base titration to determine the concentration of CO32− and HCO3.

3. Results and Discussion

3.1. Maintenance and Mechanism of the Metastable State of Neodymium Dissolved in Na2CO3 Solution

3.1.1. Maintaining Metastable State by NaCl

The metastable period of the solution with the addition of NaCl was greater than that of the solution without NaCl due to neodymium being dissolved stably in solution for a longer time. As shown in Figure 2a, the metastable period was sustained only for about 120 min without the addition of NaCl. However, the metastable period reached 240 min when the concentration of the additional NaCl was 0.2 mol·L−1. Moreover, the amount of dissolved neodymium in the solution reached 2.578 g·L−1, which was only 1.64% lower than the initial amount of 2.621 g·L−1. Surprisingly, when the additional concentration of sodium chloride in the solution reached 0.5 mol·L−1, the metastable period was extended to 480 min, i.e., twice as long as before.
The molar concentration in the above solution was converted into mass molar concentration according to Equation (2). Then, the ionic strength of each solution was calculated by using Equation (3). The results are shown in Figure 2b which shows that the addition of NaCl effectively improved the ionic strength of the solution.
C = b B · ρ
  I = 1 2 C i b B i 2
bB refers to the molar concentration, ρ refers to the density of the solution, and I refers to the ionic strength of the solution.
In the case of the equivalent concentration of Na2CO3, the addition of NaCl resulted in neodymium dissolving stably in Na2CO3 solution for a longer time. The higher the concentration of NaCl in solution, and the stronger the ionic strength, resulting in a longer metastable period of the solution. Hence, the additional NaCl maintained the metastable state effectively.

3.1.2. Effect of NaCl on Neodymium Coordination and Solid Phase Precipitates

To confirm whether the coordination reaction between Nd3+ and CO32− still occurred in the mixed electrolyte solution of NaCl/Na2CO3, the aqueous samples in each period of the above experiments were collected and scanned by UV-vis with full wavelength. As shown in Figure 3, the characteristic peak of neodymium was not found in the UV-vis spectra of the sample of the blank NaCl/Na2CO3 mixed electrolyte solution with only added water. Characteristic peaks of neodymium at the 340–370 nm and 500–620 nm wavebands [23] were observed in the spectra of the blank NdCl3 solution with added water only.
As shown in Figure 3, characteristic peaks of neodymium were obtained at 349 and 357 nm wavelengths in the spectra of the NaCl/Na2CO3 mixed electrolyte solution with dissolved neodymium. Compared with the blank neodymium solution spectrum, it is worth noting that the characteristic peaks of neodymium obtained from the NaCl/Na2CO3 solutions with dissolved neodymium were slightly red-shifted from the initial 347 and 354 nm wavelengths due to the high alkalinity of the NaCl/Na2CO3 mixed electrolyte solution.
There were also neodymium characteristic peaks at 524 and 575 nm wavelengths in the UV-vis spectrum of the neodymium-dissolving solution, as in our previously results [19]. In addition, a new peak with higher intensity was observed at 583 nm. This indicates that neodymium could still coordinate with CO32− in the Na2CO3 solution with the addition of NaCl. The precipitate sample generated from the solution after 480 min was collected and analyzed by FTIR. The results shown in Figure 4.
Figure 4 shows that the characteristic infrared peak position of the precipitate generated from the NaCl/Na2CO3 solution with dissolved neodymium was consistent with that of the blank sample NaNd(CO3)2 solid phase. This was consistent with results reported in previous studies [11,24]. These reports and our results confirm that in the presence of additional NaCl in a highly concentrated CO32− solution, the insoluble rare earth existed only in the form of an NaNd(CO3)2 double salt, while Nd2(CO3)3 was almost non-existent.

3.1.3. Mechanism of Maintaining the Metastable State by NaCl

In order to investigate the mechanism of the maintenance of the metastable state by the additional NaCl, molecular dynamic (MD) calculations were carried out. The construction and optimization of the solution components were consistent with our previous study [19]. The model of the solution with the addition of 0.5 mol·L−1 NaCl (with the better metastable condition), and the corresponding blank solution (Na2CO3/NaCl solution with the only additional water) was also established by using the Amorphous Cell module. After that, geometry optimization and the MD calculation were carried out. The components in the model and calculation parameters are shown in Table 3. The energy changed during the geometry optimization process is presented in Figure 5a.
As shown in Figure 5a, the overall energy decreased gradually with increase in the number of optimization steps without large energy disturbances. At the end of optimization, the energy tended to be relatively minimized and achieved convergence. Change of the temperature is presented in Figure 5b, which shows that the temperature of the models decreased gradually with the increase of simulation time. At the end of the calculation, it was stable at about 298 K ± 10% and there was no significant disturbance. This result is very reliable. The optimized models are presented in Figure 5c, which shows that after the geometry optimization step, the Na+, CO32−, Nd3+, Cl ions in each solution model were randomly and uniformly distributed in the model box, and no agglomeration existed.
The models after the MD calculation are presented in Figure 5d, which shows that the solution was generally homogeneous. However, in the local region, the components of the solution model had different degrees of agglomeration due to the interaction between ions (or molecules). Among them, the CO32− distribution exhibited local agglomeration. A large number of Na+ ions were distributed around the CO32−. This can be attributed to the incomplete dissociation of Na+ and CO32− at the high concentration of the NaCl/Na2CO3 mixed electrolyte solution. We speculate that the concentration of carbonate that could move freely (called free CO32−) in the solution was limited and at a low level.
Moreover, Nd3+ was also almost surrounded by CO32− in that Nd3+ was coordinated with about three CO32−. This shows that Nd3+ can coordinate with carbonate despite the addition of NaCl to Na2CO3 solution. In addition, all kinds of complex ions in the form of Ndn(CO3)m3n−2m (m ≥ 2) existed, but in different proportions. As shown in Figure 6a, there was a specific Cl ion around some Nd3+ ions, indicating that, unlike in previous studies, Cl might also coordinate with Nd3+. Previous studies of steady-state dissolution of rare earths in CO32− solution [11,24], showed that the coordination between Cl and Nd3+ could almost be ignored under the condition of steady-state solution equilibrium because of weak Cl coordination ability, which does not agree with our study. The difference could be ascribed to the difference between metastable and steady states. Besides, it is reasonable to speculate that Cl occupied the coordination layer of Nd3+, delaying the formation of carbonate precipitation. Therefore, the addition of NaCl maintained the metastable state.
In order to further quantify the interaction from the microscopic level, the main ion pairs of Nd3+-CO32−, Na+-CO32− and Nd3+-Cl in the solution were analyzed by radial distribution function (RDF), and their coordination numbers were calculated. Figure 6b shows that the RDF peak position of Nd3+ and CO32− in the NaCl/Na2CO3 mixed electrolyte solution was almost the same as that in the single Na2CO3 solution in the chemical bond range (r < 2.6 Å) [25]. This directly proves that Nd3+ can coordinate with CO32− even in the presence of NaCl. At the same time, the RDF peak intensity of Nd3+-CO32− in the presence of NaCl was slightly lower than that in the single Na2CO3 solution. The difference of RDF peak intensity indicated that the additional NaCl had an influence on the interaction between Nd3+ and CO32−. From the point of view of coordination number, with the presence of the additional NaCl the average coordination number around Nd3+ was about 1.83 CO32−, which was lower than the average coordination number of 2.50 in the single Na2CO3 solution. The reason for the decrease of coordination number may be that part of Cl occupied the coordination layer of Nd3+ in the metastable period, causing the decrease in the average coordination number between Nd3+ and CO32−. This is consistent with Figure 6a.
To quantitatively explain the coordination between Nd3+ and Cl in the mixed electrolyte, the RDF and the coordination number were further analyzed and calculated. Figure 6c shows that the RDF peak at 2.275 Å within the range of chemical bond (<2.6 Å) was clearly observed from the spectrum of the Nd3+-Cl ion pair in the mixed electrolyte solution of NaCl/Na2CO3. One Nd3+ was coordinated with about one Cl. In contrast to the single Na2CO3 solution, there was insignificant evidence of an interaction existing between Cl and Nd3+. Hence, it was proved that that Cl could coordinate with Nd3+ in the presence of NaCl during the metastable period.
It is worth noting that the RDF peak position of Nd3+-CO32− was earlier than that of Nd3+-Cl. The result indicates that CO32− tends to occupy the coordination layer of Nd3+ and reacted with it first, then Cl entered the coordination layer of Nd3+, although, previous studies [11,24] showed that in an environment of high concentration of CO32− solution, Cl did not coordinate with Nd3+ in a steady state. However, our result does not conflict with these previous studies because of the difference between metastable and steady states. In addition, when the placement time exceeded the metastable period, the precipitate was still consistent with that obtained in the steady state. Therefore, there is sufficient reason to speculate that in the metastable state, Cl participated in the coordination reaction and temporarily occupied the coordination layer of Nd3+, and then was re-released into the solution with the passage of time. When the metastable period ended, the Cl in the coordination layer of Nd3+ had been exhausted. A diagram of Nd3+, Cl and CO32− coordination in the metastable state is shown in Figure 7.
The concentration of free CO32− in solution was another key factor affecting the existence of metastable states. To explore the interaction between Na+ and CO32− in the solution in the presence of additional NaCl, the RDF of the Na+-CO32− ion pair and its average coordination number were also analyzed and calculated. The results in Figure 6d show that there was interaction between Na+ and CO32− in the mixed electrolyte solution, and the position of the RDF peak was basically the same as that in single Na2CO3 solution. The average coordination number was about 1.14 CO32− around a Na+ ion in the solution with additional NaCl, which was not much different from the corresponding blank solution number of 1.17. However, the value was lower than the value of 1.30 in a single Na2CO3 solution.
The existence of this difference does not mean that the degree of dissociation of Na+-CO32− ion pairs in the mixed electrolyte solution was higher because of the introduction of Na+ via the addition of NaCl. The introduced Na+ would also tend to interact with CO32−, reducing the average coordination number. In this regard, the conversion calculation of the number of Na+ ions around the CO32− is a better illustration of the problem, as listed in Table 4.
Table 4 shows that the distribution of Na+ around CO32− in mixed electrolyte and single Na2CO3 solutions was the same at a cutoff distance of 2.575 Å (within chemical bond range), which was 2.57 Na+ around CO32−. The total number of Na+ was 630 in the mixed electrolyte, higher than that of 580 in a single Na2CO3 solution, due to the existence of additional NaCl. Even so, the distribution of Na+ around CO32− was almost the same. This means that the dissociation degree of the Na+-CO32− ion pairs with the additional NaCl should be much lower than that in the single Na2CO3 solution. Therefore, the additional NaCl could also affect the interaction of Na+-CO32− ion pairs, further reducing the concentration of free CO32−. Thus, the delayed the formation of neodymium carbonates was delayed and the metastable period was extended.

3.2. Induced Precipitation of Neodymium Carbonates in Metastable State Solution

In theory, if the system dominated by CO32− in the solution could be rapidly transformed into the coexistence of HCO3 and CO32−, a rapid destruction of metastable state could be achieved and most of the dissolved neodymium could be separated from the solution via a self-precipitation. Theoretically, introduction of acidic CO2 gas into the solution, as shown in Equation (4), would neutralize the original alkaline Na2CO3 solution so that the induction of neodymium carbonate from the metastable solution might be more quickly achieved.
Na 2 CO 3 ( aq )   +   CO 2 ( g )   +   H 2 O ( l )   =   2 NaHCO 3 ( aq )
The specific experimental results in Figure 8a show that the metastable state was rapidly terminated after the introduction of CO2 gas. The concentration of dissolved Nd3+ in the solution fell rapidly, and neodymium carbonate precipitate were generated and separated from the solution. After gassing with CO2 for only 5 min, the Nd3+ concentration in the solution decreased from 2.621 to 1.793 g·L−1, and the precipitation rate reached 31.60%. When the ventilation time was extended to 30 min, only 0.239 g·L−1 was left in the solution, and the precipitation rate of Nd3+ reached 90.87%. When the ventilation time reached 60 min, the neodymium concentration in the solution further decreased from 0.239 g·L−1 at 30 min to 0.138 g·L−1, and the precipitation rate slowly increased from 90.78% to almost 95%. The results indicate that Nd3+ in the solution entered the insoluble solid phase and was separated from the solution via self-precipitation.
Acid-base titration analysis was carried out to determine the concentration of CO32− and HCO3 in the solution after CO2 was injected. Figure 8b shows that the concentration of CO32− in the solution decreased with increasing CO2 introduction time. The concentration of HCO3 showed an upward trend during the introduction of CO2, and the system gradually changed from a single CO32−-dominated to a CO32− and HCO3-dominated system.
When the CO2 introduction time reached 5 min, the concentration of HCO3 in the solution approached 0.286 mol·L−1 and the corresponding concentration of CO32− was 1.331 mol·L−1, which was much lower than the initial value of 2 mol·L−1. After 60 min, the concentration of HCO3 in the solution increased than several times and reached about 0.816 mol·L−1. Besides, the corresponding concentration of CO32− was reduced to 1.018 mol·L−1, and the solution system could no longer be considered to be dominated by single CO32−, but both CO32− and HCO3. The reason was that the solution of NaCl/Na2CO3 mixed electrolyte with higher basicity spontaneously absorbed acidic CO2 gas, resulting in the conversion of CO32− to HCO3 in a short time.
After introducing CO2, the concentration of CO32− in the solution decreased, but the solution volume was almost unchanged. In other words, it was equivalent to diluting the solution. It is well known that ion pairs dissociate more completely in dilute solution. Thus, there is no doubt that the concentration of free CO32− in the solution was increased, and it is important that CO2 could induce the precipitation of neodymium carbonate in the metastable state solution. In addition, the concentration of CO32− decreased as CO2 introduction time and the precipitation rate of neodymium carbonate increased. Therefore, the introduction of carbon dioxide into metastable solutions is a new potential method for the separation of rare earths. This is because carbon dioxide is nonpolluting and does not introduce other ion impurities as with the use of precipitants (e.g., ammonium carbon, which is commonly used in industry, introduces ammonium ions). In addition, the separation is achieved by the rapid production of rare earth precipitation in a short time after its entry into the solution.

4. Conclusions

We chose neodymium as an example of a rare earth element and studied the maintenance of the metamorphic state of Na2CO3 solution with dissolved Nd3+. The results show that the metastable state can be successfully prolonged by adding sodium chloride. In addition, the introduction of carbon dioxide is an effective way to terminate the metastable state and generate neodymium carbonate.
The main conclusions are as follows. (1) The higher the additional NaCl concentration, the longer the metastable period, because the additional NaCl affects the interaction of Na+-CO32−-ion pairs and influences the concentration of free CO32− in the solution. (2) The Cl introduced by the high concentration of NaCl can occupy the coordination layer of Nd3+ temporarily and delay the formation of rare earth carbonate precipitation. (3) After introduction of CO2 gas, the existing environment of the solution directly changes in a short time from a single CO32−-dominated system to a predominantly CO32− and HCO3−-dominated system. As a result, the metamorphic state of the solution is quickly terminated and the precipitation of Nd carbonate is advanced.

Author Contributions

Conceptualization, K.L.; data curation, X.Z.; formal analysis, Y.M.; funding acquisition, Y.Y.; investigation, K.L.; methodology, K.L.; project administration, Y.Y.; validation, F.N.; visualization, K.L.; writing—original draft, K.L.; writing—review & editing, L.W. and D.L. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by National Natural Science Foundation of China, grant number 51774155, and The APC was funded by 51774155.

Data Availability Statement

Not Applicable.

Acknowledgments

The authors gratefully acknowledge the financial supports of the Program of National Natural Science Foundation of China (51774155).

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Takagi, K.; Hirayama, Y.; Okada, S.; Yamaguchi, W.; Ozaki, K. Novel powder processing technologies for production of rare-earth permanent magnets. Sci. Technol. Adv. Mater. 2021, 22, 150–159. [Google Scholar] [CrossRef] [PubMed]
  2. Prokofev, P.A.; Kolchugina, N.B.; Skotnicova, K.; Burkhanov, G.S.; Kursa, M.; Zheleznyi, M.V.; Dormidontov, N.A.; Cegan, T.; Bakulina, A.S.; Koshkidko, Y.S.; et al. Blending Powder Process for Recycling Sintered Nd-Fe-B Magnets. Materials 2020, 13, 3049. [Google Scholar] [CrossRef] [PubMed]
  3. Nelson, J.J.M.; Schelter, E.J. Sustainable Inorganic Chemistry: Metal Separations for Recycling. Inorg. Chem. 2019, 58, 979–990. [Google Scholar] [CrossRef] [PubMed]
  4. Lixandru, A.; Venkatesan, P.; Jönsson, C.; Poenaru, I.; Hall, B.; Yang, Y.; Walton, A.; Güth, K.; Gauß, R.; Gutfleisch, O. Identification and recovery of rare-earth permanent magnets from waste electrical and electronic equipment. Waste Manag. 2017, 68, 482–489. [Google Scholar] [CrossRef] [PubMed]
  5. Kuz’Min, M.D.; Skokov, K.; Jian, H.; Radulov, I.; Gutfleisch, O. Towards high-performance permanent magnets without rare earths. J. Phys. Condens. Matter 2014, 26, 64205. [Google Scholar] [CrossRef] [PubMed]
  6. Bingqian, W. Rare Earth Metallurgy; Central South University of Technology Press: Changsha, China, 1997. [Google Scholar]
  7. Firsching, F.H.; Mohammadzadei, J. Solubility products of the rare-earth carbonates. J. Chem. Eng. Data 1986, 31, 40–42. [Google Scholar] [CrossRef]
  8. Taketatsu, T. The solubilities and anion-exchange behavior of rare earth elements in potassium carbonate solutions. Anal. Chim. Acta 1965, 32, 40–45. [Google Scholar] [CrossRef]
  9. Taketatsu, T. The Dissolution and Anion Exchange Behavior of Rare Earth and Other Metallic Elements in Potassium Bicar-bonate, Potassium Carbonate and Ammonium Carbonate Solutions. Bull. Chem. Soc. Jpn. 1963, 36, 549–553. [Google Scholar] [CrossRef] [Green Version]
  10. de Vasconcellos, M.E.; da Rocha, S.; Pedreira, W.; Queiroz, C.A.D.S.; Abrão, A. Solubility behavior of rare earths with ammonium carbonate and ammonium carbonate plus ammonium hydroxide: Precipitation of their peroxicarbonates. J. Alloy. Compd. 2008, 451, 426–428. [Google Scholar] [CrossRef]
  11. Rao, L.; Rai, D.; Felmy, A.R.; Novak, C.F. Solubility of NaNd(CO3) 6H2O (c) in Mixed Electrolyte (Na-Cl-CO3-HCO3) and Synthetic Brine Solutions. In Actinide Speciation in High Ionic Strength Media; Springer: Berlin/Heidelberg, Germany, 1999; pp. 153–169. [Google Scholar]
  12. Tang, J.; Johannesson, K.H. Rare earth elements adsorption onto Carrizo sand: Influence of strong solution complexation. Chem. Geol. 2010, 279, 120–133. [Google Scholar] [CrossRef]
  13. Thakur, P.; Xiong, Y.; Borkowski, M. An improved thermodynamic model for the complexation of trivalent actinides and lanthanide with oxalic acid valid to high ionic strength. Chem. Geol. 2015, 413, 7–17. [Google Scholar] [CrossRef] [Green Version]
  14. Jing, Y.; Chen, J.; Chen, L.; Su, W.; Liu, Y.; Li, D. Extraction Behaviors of Heavy Rare Earths with Organophosphoric Extractants: The Contribution of Extractant Dimer Dissociation, Acid Ionization, and Complexation. A Quantum Chemistry Study. J. Phys. Chem. A 2017, 121, 2531–2543. [Google Scholar] [CrossRef] [PubMed]
  15. Pavón, S.; Fortuny, A.; Coll, M.; Sastre, A.M. Rare earths separation from fluorescent lamp wastes using ionic liquids as extractant agents. Waste Manag. 2018, 82, 241–248. [Google Scholar] [CrossRef] [PubMed]
  16. Qiu, L.; Pan, Y.; Zhang, W.; Gong, A. Application of a functionalized ionic liquid extractant tributylmethylammonium dibutyldiglycolamate ([A336][BDGA]) in light rare earth extraction and separation. PLoS ONE 2018, 13, e0201405. [Google Scholar] [CrossRef]
  17. Sun, P.; Huang, K.; Liu, H. The nature of salt effect in enhancing the extraction of rare earths by non-functional ionic liquids: Synergism of salt anion complexation and Hofmeister bias. J. Colloid Interface Sci. 2019, 539, 214–222. [Google Scholar] [CrossRef]
  18. Li, C.; Zhuang, Z.; Huang, F.; Wu, Z.; Hong, Y.; Lin, Z. Recycling Rare Earth Elements from Industrial Wastewater with Flowerlike Nano-Mg(OH)2. ACS Appl. Mater. Interfaces 2013, 5, 9719–9725. [Google Scholar] [CrossRef] [PubMed]
  19. Yang, Y.; Zhang, X.; Li, L.; Wei, T.; Li, K. Metastable Dissolution Regularity of Nd3+ in Na2CO3 Solution and Mechanism. ACS Omega 2019, 4, 9160–9168. [Google Scholar] [CrossRef]
  20. Fannin, C.; Edwards, R.; Pearce, J.; Kelly, E. A Study on the Effects of Drying Conditions on the Stability of NaNd (CO3)2·6H2O and NaEu (CO3)2·6H2O. Appl. Geochem. 2002, 17, 1305–1312. [Google Scholar] [CrossRef]
  21. Biovia, D.S. Materials Studio 8.0; Dassault Systèmes: San Diego, CA, USA, 2014. [Google Scholar]
  22. Allen, M.P.; Tildesley, D.J. Computer Simulation of Liquids; Oxford University Press: Oxford, UK, 2017; ISBN 0192524704. [Google Scholar]
  23. Anggraeni, A.; Arianto, F.; Mutalib, A.; Pratomo, U.; Bahti, H.H. Fast and simultaneously determination of light and heavy rare earth elements in monazite using combination of ultraviolet-visible spectrophotometry and multivariate analysis. In AIP Conference Proceedings; AIP Publishing LLC: Bandung, Indonesia, 2017; Volume 1848, p. 30004. [Google Scholar] [CrossRef] [Green Version]
  24. Rao, L.; Rai, D.; Felmy, A.R.; Fulton, R.W.; Novak, C.F. Solubility of NaNd (CO3)2 6 H2O (c) in Concentrated Na2CO3 and NaHCO3 Solutions. Radiochim. Acta 1996, 75, 141–148. [Google Scholar]
  25. Jianfeng, Z. Dynamics Simulation of Interaction between Impurity Inhibitors and Aluminum Impurities. In Ionic Rare Earth Ores No Title; Jiangxi University of Science and Technology: Jiangxi, China, 2015. [Google Scholar]
Figure 1. Schematic diagram of autoclave ventilation experiment: 1—CO2 pressure reducing valve; 2—high pressure cylinder; 3—rotating motor; 4—air inlet; 5—safety valve; 6—air outlet; 7—controller; 8—polytetrafluoroethylene tank; 9—agitator.
Figure 1. Schematic diagram of autoclave ventilation experiment: 1—CO2 pressure reducing valve; 2—high pressure cylinder; 3—rotating motor; 4—air inlet; 5—safety valve; 6—air outlet; 7—controller; 8—polytetrafluoroethylene tank; 9—agitator.
Minerals 11 00952 g001
Figure 2. The effect of the concentration of the additional NaCl in (a) and Ionic strength of solution in (b).
Figure 2. The effect of the concentration of the additional NaCl in (a) and Ionic strength of solution in (b).
Minerals 11 00952 g002
Figure 3. UV-vis spectrum of NdCl3/Na2CO3 solution with the addition of 0.5M NaCl, wavelength in 340 to 370 nm in (a), and 510 to 600 nm in (b).
Figure 3. UV-vis spectrum of NdCl3/Na2CO3 solution with the addition of 0.5M NaCl, wavelength in 340 to 370 nm in (a), and 510 to 600 nm in (b).
Minerals 11 00952 g003
Figure 4. FTIR pattern of the neodymium precipitate, red line refers to the precipitate obtained in the presence of 0.5 mol NaCl, and blue line refers to the Comparison sample.
Figure 4. FTIR pattern of the neodymium precipitate, red line refers to the precipitate obtained in the presence of 0.5 mol NaCl, and blue line refers to the Comparison sample.
Minerals 11 00952 g004
Figure 5. Geometry optimization process of the solution model (a). Temperature change during the MD calculation in (b). Geometry optimization and after MD calculation of the solution model (c,d). In the figures, (i) refers to the metastable state solution and (ii) is the corresponding blank solution.
Figure 5. Geometry optimization process of the solution model (a). Temperature change during the MD calculation in (b). Geometry optimization and after MD calculation of the solution model (c,d). In the figures, (i) refers to the metastable state solution and (ii) is the corresponding blank solution.
Minerals 11 00952 g005
Figure 6. Coordination between Nd3+, Cl & CO32− (a). RDF of the ion pairs Nd3+-CO32−, Nd3+-Cl & Na+-CO32− and their coordination number (bd), respectively.
Figure 6. Coordination between Nd3+, Cl & CO32− (a). RDF of the ion pairs Nd3+-CO32−, Nd3+-Cl & Na+-CO32− and their coordination number (bd), respectively.
Minerals 11 00952 g006
Figure 7. Coordination process of Nd3+ in the NaCl/Na2CO3 mixed electrolyte solution.
Figure 7. Coordination process of Nd3+ in the NaCl/Na2CO3 mixed electrolyte solution.
Minerals 11 00952 g007
Figure 8. The concentration of dissolved Nd3+ in the solution and the precipitation rate with the ventilation time of CO2 (a), and the concentration of CO32−/HCO3 with the ventilation time of CO2 (b).
Figure 8. The concentration of dissolved Nd3+ in the solution and the precipitation rate with the ventilation time of CO2 (a), and the concentration of CO32−/HCO3 with the ventilation time of CO2 (b).
Minerals 11 00952 g008
Table 1. Content of the high purity solution of NdCl3.
Table 1. Content of the high purity solution of NdCl3.
Concentration of Nd3+ (mol·L−1)Concentration of H+ (mol·L−1)Specific Gravity (g·mL−1)
1.3568<0.101.326
Non-rare earths impurities (µg·mL−1)
Fe2O3SiO2CaO
<0.502.497.3
Rare Earth Impurities/REO (μg·mL−1)
La2O3CeO2Pr6O11Sm2O3Eu2O3Gd2O3Tb2O3
<100<100500<100<100<100<100
Dy2O3Ho2O3Er2O3Tm2O3Yb2O3Lu2O3Y2O3
<100<100<100<100<100<100<100
Table 2. Information of equipment.
Table 2. Information of equipment.
EquipmentModelManufacturers
High-speed centrifugeTGL16MSYancheng Anxin Experimental Instrument Co., Ltd. (Yancheng, China)
Computing serverIBM System X3850 X5International Business Machines Corporation (Armonk, NY, USA)
UV-Visible Spectrophotometer (UV-vis)UV-5500PCShanghai yoke instrument Co., Ltd. (Shanghai, China)
Fourier transform infrared spectrometer (FTIR)ALPHABruker Corporation (Billerica, MA, USA)
inductively coupled plasma-optical emission spectroscopy (ICP-OES)ULTIMA2HORIBA Jobin Yvon (Newark, NJ, USA)
Kang’s oscillatorKSChangzhou Putian Instrument Manufacturing Company (Changzhou, China)
Table 3. Modeling parameters of the solutions.
Table 3. Modeling parameters of the solutions.
ComponentsThe Metastable State SolutionCorresponding Blank Solution
ρ: 1.164 g·L−1ρ: 1.148 g·L−1
NumberMass Fraction (%)NumberMass Fraction (%)
H2O10,59084.710,59085.0
Na+6306.46306.5
CO 3 2 - 2807.52807.5
Nd3+30.200.0
Cl791.2701.1
Table 4. Distribution of Na+ around CO32− in the solution.
Table 4. Distribution of Na+ around CO32− in the solution.
r (Å)Average Coordination Number (Cn)
NaCl/Na2CO3 Mixed Electrolyte SolutionSingle Na2CO3 Solution
2.2251.291.28
2.2751.511.50
2.3251.641.67
2.3751.791.82
2.4251.992.02
2.4752.242.26
2.5252.442.46
2.5752.572.57
2.6252.632.63
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Yang, Y.; Zhang, X.; Li, K.; Wang, L.; Niu, F.; Liu, D.; Meng, Y. Maintenance of the Metastable State and Induced Precipitation of Dissolved Neodymium (III) in an Na2CO3 Solution. Minerals 2021, 11, 952. https://doi.org/10.3390/min11090952

AMA Style

Yang Y, Zhang X, Li K, Wang L, Niu F, Liu D, Meng Y. Maintenance of the Metastable State and Induced Precipitation of Dissolved Neodymium (III) in an Na2CO3 Solution. Minerals. 2021; 11(9):952. https://doi.org/10.3390/min11090952

Chicago/Turabian Style

Yang, Youming, Xiaolin Zhang, Kaizhong Li, Li Wang, Fei Niu, Donghui Liu, and Yuning Meng. 2021. "Maintenance of the Metastable State and Induced Precipitation of Dissolved Neodymium (III) in an Na2CO3 Solution" Minerals 11, no. 9: 952. https://doi.org/10.3390/min11090952

APA Style

Yang, Y., Zhang, X., Li, K., Wang, L., Niu, F., Liu, D., & Meng, Y. (2021). Maintenance of the Metastable State and Induced Precipitation of Dissolved Neodymium (III) in an Na2CO3 Solution. Minerals, 11(9), 952. https://doi.org/10.3390/min11090952

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