Characteristics of Precipitation of Rare Earth Elements with Various Precipitants

Abstract

The effective and selective leaching of rare earth elements (REEs) from various sources is frequently possible in practice by adopting a carefully coordinated strategy incorporating a selective precipitation of these elements from undesired ones in solution. In this study, the behavior of chemical precipitation of REEs with commonly used precipitants such as sulfate, carbonate, fluoride, phosphate, and oxalate was examined using thermodynamic principles and calculations. It was found that the pH of the system has a profound effect on determining particular chemical species of precipitants, which are subsequently responsible for the precipitation of REEs. The role of various anions such as Cl⁻, NO₃⁻, and SO₄²⁻ derived from the acid used in the leaching process on the precipitation behavior of REEs was examined. These anions form complexes with REEs and display a very positive effect on the precipitation behavior. The nitrate environment exhibits most conducive to precipitation followed by sulfate and then chloride.

1. Introduction

Rare earth elements (REEs) are becoming very important in modern society. REEs are essential ingredients in the transition to green technology and there have been numerous recent articles describing their extraction processes from various sources [1,2].

Most rare earth bearing minerals are refractory in nature and therefore, a pretreatment or strong acid treatment of ores bearing these minerals is usually necessary [3,4,5,6] before leaching is affected. Such pretreated ores are then subjected to the leaching process of REEs. The leach liquor is frequently subjected to the removal of impurities such as iron, calcium, uranium, and thorium by going through stage-wise precipitation using various compounds such as hydroxide, carbonate, sulfate, and oxalate [7,8,9,10,11,12,13]. After the removal of these impurities by chemical precipitation, REEs in solution are then subjected to precipitation using various precipitants, which in general takes place at pH above 3−4, since most of these impurities are precipitated at around these pHs. However, during the precipitation of impurities, some REEs are also removed from the solution by coprecipitation or adsorption. Therefore, it is desirable to precipitate REEs before removal of the impurities. It is the hope of this study to identify the precipitants and chemical conditions to achieve this objective.

The chemical complexity of the aqueous medium introduced by various chemical treatment of leach liquor has introduced a complex nature to the system making the analysis of the subsequent chemical precipitation a challenge. In addition to metal ions in the leach liquor extracted from ores, many anions such as Cl⁻, NO₃⁻, and SO₄²⁻ mostly derived from acids used in the leaching operation also play an important role in leaching as well as precipitation.

The effect of various anions on the leaching behavior has been discussed in earlier studies [14,15]. For example, the leaching of Re-phosphate in the presence of sulfuric acid can be simply described by Equation (1). (It is noted that Re is the elemental symbol for rhenium. However, Re(III) refers to only REE(III) in this paper.)

<RePO₄> + {H₂SO₄} = {Re³⁺} + {PO₄³⁻} + {SO₄²⁻} + 2 {H⁺}

(1)

Here the symbols, < > and { } stand for solid and liquid form, respectively. The oxidation state of REEs in solution and solids is assumed to be Re(III) throughout this presentation. It should be noted however, that some REEs can be oxidized to Re(IV) or reduced to Re(II) in aqueous media in very rare cases [16]. The concentration of the free REEs at equilibrium can be estimated if the concentration of all species involved in Equation (1) is known. However, such calculated values are far from real values since the chemicals produced from the leaching process undergo hydrolysis and complexation [14,15]. As a result, the correct evaluation of the product concentration requires a very complicated process involving calculations of equilibrium equations simultaneously in some cases.

The chemical precipitation of REEs is similarly complicated. For example, a simple chemical precipitation of a free Re-ion, Re³⁺ with phosphate ion, PO₄³⁻ can be given by Equation (2).

{Re³⁺} + {PO₄³⁻} = <RePO₄>

(2)

It should be noted that REEs precipitate with the phosphate ion as a free Re-ion, Re³⁺ at relatively high pHs such as 4 and 6. However, when the pH of the solution changes to a lower value, for example 1 or 2, by adding acids of HCl, HNO₃, or H₂SO₄, the anions such as Cl⁻, NO₃⁻, and SO₄²⁻ will form various complexes with REEs [3,14,15], and then these complexes are subjected to precipitation. For example, in the presence of sulfate ions, there will be at least Re³⁺, Re(SO₄)⁺, Re(SO₄)₂⁻, and Re₂(SO₄)₃, present in solution, and for most of the sulfate concentration, Re(SO₄)₂⁻ is the predominant species when the concentration of sulfate ions is especially more than 0.1 M [14,15]. As a result, in such cases, Re(SO₄)₂⁻ should be used instead of the free ion and the resulting concentration of rare earth elements after precipitation is an order of magnitude different from when the free ion is used.

In addition, the phosphate ion also may not exist depending upon the pH of the system. It should be noted that the values of pKa are 2.0 for H₃PO₄/H₂PO₄⁻, 7.2 for H₂PO₄⁻/HPO₄²⁻, and 12.0 for HPO₄²⁻/PO₄³⁻ (see

Table 1. The pKa values for various precipitants [17].

Precipitants	pKa
H3PO4/H2PO4−	2.1
H2PO4−/HPO42−	7.2
HPO42−/PO43−	12.0
H2CO3/HCO3−	6.38
HCO3−/CO32−	10.34
HF/F−	3.0
H2C2O4/HC2O4−	1.0
HC2O4−/C2O42−	4.2
HSO4−/SO42−	2.0

) [17]. This means that H₃PO₄ should be used instead of the phosphate ion in Equation (2) for the system whose pH lies below 2 and likewise, H₂PO₄⁻ for pH between 2 and 7.2 and so on.

In this paper, factors such as pH, complexation, and hydration of precipitants affecting the chemical precipitation with various precipitants will be examined and their practical implication in the analysis of such precipitation processes will be discussed. The precipitation behavior of REEs with carbonate, fluoride, phosphate, sulfate, and oxalate was considered in this study, since these precipitants are most widely used in precipitation of REEs in practice.

2. Acquisition of Thermodynamic Information

Table 1 presents the values of pKa for the precipitants considered in this study. It should be noted that there are some variations in the numerical values of pKa based on various literature sources. For example, the values for oxalic acid given by Pourbaix [17] and Dean [18] are different from those by HSC [19] and Wagman [20]. However, the effect of such differences on the final outcome of the behavior of chemical precipitation is not very significant.

The thermodynamic data used in this study are listed in

Table 2. The Gibbs standard free energy formation of various compounds in kCal/mol. Information taken from [14,15] with some modifications.

	Carbonate	Phosphate	Sulfate	Fluoride	Oxalate	Oct-Sulfate
La	−768.5	−455.3	−892.6	−399.8	−872.2	−1399.9
Ce	−761.4	−455.2	−884.7	−396.8	−868.3	−1340.2
Pr	−764.5	−451.0	−879.4	−394.2	−860.6	−1343.5
Nd	−761.6	−448.7	−877.2	−391.5	−861.8	−1335.0
Sm	−759.6	−447.6	−878.8	−392.3	−860.1	−1330.5
Eu	−759.4	−446.7	−875.3	−391.0	−859.1	−1275.3
Gd	−758.6	−445.5	−874.2	−390.5	−857.7	−1328.1
Tb	−757.0	−444.7	−873.7	−388.7	−856.9	−1313.2
Dy	−750.6	−442.2	−868.9	−385.9	−856.0	−1323.3
Ho	−744.2	−440.4	−861.3	−383.0	−849.6	−1314.3
Er	−743.9	−439.1	−855.9	−380.9	−842.0	−1309.5
Tm	−736.9	−438.2	−862.9	−379.6	−846.6	−1308.1
Yb	−735.5	−437.6	−861.5	−378.4	−839.5	−1293.4
Lu	−734.5	−435.7	−860.1	−376.8	−841.3	−1319.1
Y	−749.9	−443.0	−866.8	−389.4	−851.5	−1320.6
Sc	−714.9	−418.2	−845.1	−361.5	−828.4	−1300.0

Oct-sulfate: Re₂(SO₄)₃·8H₂O (here Re represents REEs).

. Most data given in the table were taken from the literature information [21,22,23,24,25,26] and those unavailable were estimated using the parallel plot method as described earlier [14].

Some of the standard Gibbs free energy formation values, such as Y- and Sc-oxalates were not available in the literature and, therefore, were estimated using the parallel method as described by earlier studies [14,15]. It should be noted that there were typographical errors in the values for Re-octa-hydrated sulfates in earlier publications [14,15]. It should also be noted that subsequent relevant calculations in the same articles were carried out using correct values, however.

3. Carbonate System

It is well known that rare earth elements are readily precipitated with carbonate at high pHs. Rare earth elements are readily subjected to precipitation with carbonate [27,28] especially at high pHs. Re-carbonates are ideal precipitates, since carbonates are readily available, relatively less expensive than other precipitants, and precipitates can be easily dissolved in a mild acid for further treatments of REEs in subsequent processes of purification. However, it is not easily precipitated in acidic media. As a result, the leach liquor is usually subjected to a neutralization step before the precipitation of REEs with carbonate is affected. During the neutralization process, however, impurities such as Fe³⁺, Ca²⁺ are precipitated first resulting in loss of REEs due to adsorption and coprecipitation of REEs with oxides or sulfates of impurities.

A simple stoichiometric equation describing the precipitation of REEs with carbonate can be written in Equation (3), which is analogous to Equation (2).

2 {Re³⁺} + 3 {CO₃²⁻} = <Re₂(CO₃)₃>

(3)

As discussed earlier, the concentration of CO₃²⁻ at pH 1−6 that was considered in this study, which is consistent with the range of pH practiced in industry, is practically zero, since the pK value for HCO₃⁻/CO₃²⁻ is 10.34. The stable species at pH less than 6, is H₂CO₃, which is the dominant species as seen in Table 1 and, therefore, H₂CO₃ should be used in Equation (3). Furthermore, when pH of the solution is less than 6, Re³⁺ is subjected to complexation to become either ReCl²⁺, Re(NO₃)²⁺, or Re(SO₄)₂⁻ depending upon the kind of acid used [14,15]. Therefore, for the working pH range (pH 1−6) in this study, Equations (4)–(6) should be used for chloride, nitrate, and sulfate systems instead of Equation (3).

2 {ReCl²⁺} + 3 {H₂CO₃} = <Re₂(CO₃)₃> + 2 {Cl⁻} +6 {H⁺}

(4)

2 {Re(NO₃)²⁺} + 3 {H₂CO₃} = < Re₂(CO₃)₃> + 2 {NO₃⁻} +6 {H⁺}

(5)

2 {Re(SO₄)₂⁻} + 3 {H₂CO₃} = < Re₂(CO₃)₃> + 4 {SO₄²⁻} +6 {H⁺}

(6)

In order to illustrate the steps involved in calculating the equilibrium concentration of REEs in solution, let us take Equation (4) as an example. The equilibrium constant for Equation (4), K_eq can be found knowing the Gibbs standard free energy formation of each component involved in the reaction. Such found equilibrium constant is given in Equation (7) below:

$${\mathrm{K}}_{\mathrm{eq}}=\frac{{\left\{C{l}^{-}\right\}}^2{\left\{H^{+}\right\}}^6}{{\left\{ReC{l}^{2+}\right\}}^2{\left\{H_{2}C{O}_3\right\}}^3}$$

(7)

Here {H⁺} is known if the pH of the system is known, {Cl⁻} is known since the pH of the system is adjusted by HCl in this reaction, (see

Table 3. Concentrations of various anions used in the study at different pH’s [17].

	HCl	HNO3	H2SO4
pH	Cl− (M)	NO3− (M)	SO42−(M)	HSO4− (M)
6	1.0 × 10−6	1.0 × 10−6	1.0 × 10−6	9.9 × 10−11
5	1.0 × 10−5	1.0 × 10−5	1.0 × 10−5	9.9 × 10−9
4	1.0 × 10−4	1.0 × 10−4	9.9 × 10−5	9.9 × 10−7
3	1.0 × 10−3	1.0 × 10−3	9.1 × 10−4	9.0 × 10−5
2	1.0 × 10−2	1.0 × 10−2	5.0 × 10−3	5.0 × 10−3
1	1.0 × 10−1	1.0 × 10−1	9.0 × 10−3	9.1 × 10−2
0	1.0	1.0	1.0 × 10−2	9.9 × 10−1

) and {H₂CO₃} was set as 10⁻⁴ M. Therefore, {ReCl²⁺} can be determined.

It should be noted that Equation (6) is valid above pH 2 but SO₄²⁻ should be replaced by HSO₄⁻ when the pH of the system is less than 2 (See Table 3). When Equations (4)–(6) are solved to calculate the equilibrium concentrations of REEs in solution, it was assumed that the final concentrations of Cl⁻, NO₃⁻, and SO₄²⁻ are those set by respective acid concentration to adjust the pH of the solution as discussed above. This assumption is reasonable for low pHs but the accurate estimation of the final equilibrium concentrations of REEs at pH 6 should be carried out taking into account all of practical conditions of the system.

It should also be noted that most of precipitants considered here are mostly weak acids and, therefore, they contribute in setting the pH of the solution (see

Table 4. The pH values of some weak acids for various concentrations.

Concentration, M.	H3PO4	HF	H2CO3	H2C2O4
1.0 × 10−6	5.97	6	6.31	6
1.0 × 10−4	4	4.05	5.2	4
1.0 × 10−3	3	3.26	4.69	3
1.0 × 10−2	2.3	2.64	4.18	2.09
1.0 × 10−1	1.63	2.1	3.68	1.31

). This can be a cause of inaccuracy in the final results especially at relatively high pHs, say pH greater than 4. The correction of such effects can be made but no attempt on such corrections was made in this study. This is because the objective of the study is to observe the precipitation behavior at low pHs.

It is important to note that any calculated value exceeding the highest concentration of REEs in practice should be treated with caution. The highest concentration of REEs possible in the aqueous system is based on the grade of REEs in the ore being leached. Assuming the highest grade of REEs of the ore being treated is 50%, the highest concentration of REEs possible in the aqueous media could be about 1.5 M [15]. It is safe to assume that when the calculated value is more than 1−2 M, the precipitation is impossible under the conditions considered. On the other hand, when the calculated value is less than the target value, 1 ppm, then the precipitation could be favorable.

Figure 1 presents the equilibrium concentration of dissolved REEs in solution when REEs are subjected to precipitation with carbonate. In this study, the concentration of the precipitant, was kept constant at 10⁻⁴ M throughout the paper as stated earlier. The choice of the precipitant concentration being 10⁻⁴ M, which is the final concentration after the precipitation is completed, is arbitrary and deemed reasonable in view of practical application. The horizontal dashed line across the figure represents the concentration of REEs in solution being 3 × 10⁻⁶ M, which is about 1 ppm of REEs. This is an arbitrary concentration representing an acceptable target level of precipitation of REEs after subjecting to the carbonate precipitation.

It is a reasonable assumption that the initial concentration of REEs in the leach liquor would be in the range of 3 × 10⁻¹ to 3 × 10⁻³ M [15]. It is a usual practice that the initial concentration of the precipitant is a little more than the stoichiometric amount. It is obvious that carbonate is incapable of precipitating most of REEs, except a few light REEs at pH 6. It is interesting to note that the precipitation of nitrate and sulfate complexes is significantly better than free REE ions. The anomaly behavior by Eu seems to be due to inaccuracy in the standard Gibbs free energy data given in the literature.

4. Fluoride System

It has been well understood that fluoride readily complexes with rare earth elements [6,29]. The pKa value of HF/F⁻ is 3 as seen in Table 1 and, therefore, the relevant equations governing the precipitation of REEs with fluoride should be formulated in such a way that HF is the precipitant at pH less than 3 and F⁻ should be used at higher pHs. For example, the precipitation of ReCl₂⁺ with fluoride is described by Equation (8) when the pH of the solution is 6 or 4, while Equation (9) is for pH 2 and 1. Here too, the concentration of the precipitant is assumed to be 10⁻⁴ M. The precipitation of the complexed REEs is remarkable as in the case with the carbonate system. Most of REEs is easily complexed with chloride, nitrate, and sulfate as long as the concentration of these anions is more than 0.1 M, below which they remain as Re³⁺ [14,15].

{Re³⁺} + 3 {F⁻} = <ReF₃>

(8)

{Re³⁺} + 3 {HF} = <ReF₃> + 3 {H⁺}9

(9)

Figure 2a–d present the precipitation of Re³⁺, ReCl₂⁺, Re(NO₃)₂⁻, and Re(SO₄)₂⁻ with fluoride, respectively. With regard to Figure 2a, there appears to be only one line representing pH 6 and 4. This is because when pH is above 3, F⁻ is responsible for the precipitation reaction as seen in Equation (7), in which the precipitation becomes independent of pH. As seen in these figures, fluoride is a more powerful precipitant for REEs than carbonate in the pH range considered in this study.

5. Phosphate System

When phosphoric acid, H₃PO₄ is placed in water, it dissociates into dihydrogen phosphate, H₂(PO₄)⁻, hydrogen phosphate, H(PO₄)²⁻, or phosphate ion, PO₄³⁻ depending upon the pH of the solution. The pKa values of these conjugated species are 2.1 for H₃PO₄/H₂PO₄⁻, 7.2 for H₂PO₄⁻/HPO₄²⁻, and 12.0 for HPO₄²⁻/PO₄³⁻ as noted in Table 1. Therefore, the relevant equilibrium equations for the precipitation of REEs with phosphate should involve phosphoric acid for pH 1 and 2, and dihydrogen phosphate for pH 4 and 6. These are shown in Equations (10) and (11), respectively, for precipitation of ReCl₂⁺.

{ReCl₂⁺} + H₂PO₄⁻ = <RePO₄> + 2{Cl⁻} + 2{H⁺}

(10)

{ReCl₂⁺} + {H₃PO₄} = <RePO₄> + 2{Cl⁻} + 3{H⁺}

(11)

Figure 3 illustrates the precipitation of Re³⁺, ReCl₂⁺, Re(NO₃)₂⁻ and Re(SO₄)₂⁻ with phosphate. Unlike the carbonate but similar to fluoride systems, the phosphate system shows a powerful precipitation behavior even for free REEs. REEs are readily precipitated for all forms of rare earth element ions in solution except Re-chloride complexes. Here again, the unusual behavior shown by europium is most likely due to erratic thermodynamic data given in the literature. It should be noted that industrially important REE-bearing minerals are monazite and xenotime, both of which are phosphate compounds. Chemical interaction between REEs and phosphate has been investigated in numerous studies [30,31].

6. Sulfate System

6.1. Sulfate (SO₄²⁻)

The precipitation of REEs with sulfate is given in Figure 4. In Figure 4a, the concentration of free REEs in solution in equilibrium with Re-sulfate precipitates is shown. In the construction of this figure, Equations (12) and (13) were used. Equation (12) was used for pH 6 and 4, while Equation (13) was used for pH 2 and 1. As mentioned earlier, the concentration of precipitants was kept constant at 10⁻⁴ M. At pH 6, the concentration of sulfate ion is 10⁻⁴ M plus 10⁻⁶ M, in which the first was added by the rule and the latter was from sulfuric acid to adjust the pH. In addition, at pH 4, on the other hand, the concentration of sulfate ion is 2 × 10⁻⁴ M, because of the added sulfate plus sulfate provided by sulfuric acid to adjust the pH of the solution. The same is also applicable for Figure 4d, in which case, Equations (14) and (15) were used instead of Equations (12) and (13).

It is noted that the precipitation is better at low pHs, namely pH 2 and 1, compared to those at pH 6 and 4. The reason for this is because there is more sulfate present at low pHs due to the supply of sulfate via sulfuric acid to adjust the pH of the solution.

2 {Re³⁺} + 3 {SO₄²⁻} = <Re₂(SO₄)₃>

(12)

2 {Re(SO₄)₂⁻} = <Re₂(SO₄)₃> + {SO₄²⁻}

(13)

2 {Re(SO₄)₂⁻} = <Re₂(SO₄)₃> + {SO₄²⁻}

(14)

2 {Re(SO₄)₂⁻} + {H⁺} = <Re₂(SO₄)₃> + {HSO₄⁻}

(15)

For the precipitation of Re(SO₄)₂⁻ using sulfate, the precipitation calculations were done using Equations (14) and (15). The precipitation of Re(SO₄)₂⁻ with sulfate is unusual in that the species does not need any precipitant but it has to release one sulfate or bisulfate to form the precipitate <Re₂(SO₄)₃> as seen in Equations (14) and (15). Such precipitation can be referred to as a decomposition precipitation.

It should be noted that in practice, REEs are usually precipitated with double salt sulfate [5,32], since the precipitation is more effective with double sodium sulfate. However, in this study, precipitation of REEs with only sulfate was carried out. Although double salt sulfate precipitation is more powerful than simple sulfate precipitation, the precipitation behavior of the two systems is expected to be very similar.

6.2. Octa-Hydrated Sulfate (SO₄·8H₂O)

The chemical precipitation of REEs with sulfate to form octa-hydrated sulfate is very similar to the precipitation behavior of sulfate. The relevant equations used in this analysis are given in Equations (16)–(19).

2 {Re³⁺} + 3 {SO₄^2-} + 8 {H₂O} = <Re₂(SO₄)₃·8H₂O>

(16)

2 {Re³⁺} + 3 {HSO₄⁻}+8 {H₂O} = < Re₂(SO₄)₃·8H₂O> + 3 {H⁺}

(17)

2 {Re(SO₄)₂⁻} + 8{H₂O} = < Re₂(SO₄)₃·8H₂O > + {SO₄²⁻}

(18)

2 {Re(SO₄)₂⁻}+ {H⁺}+8 {H₂O} = < Re₂(SO₄)₃·8H₂O > + {HSO₄⁻}

(19)

As in the case with the sulfate system, the appearance of sulfate or bisulfate is based on the pH of the solution. In other words, when the pH of the system is greater than 2, sulfate is the predominant species and at low pHs, bisulfate should be used as shown in Table 3. It was expected that the octa-hydrated system is favored in the chemical precipitation compared to simple sulfate precipitation [14,15]. However, the results shown in Figure 4; Figure 5 show that the two systems behave very similarly.

7. Oxalic Acid

Oxalic acid is the most commonly used precipitant for REEs from solution and the majority of investigators have used this precipitant to separate REEs in the solution from other dissolved ions. This is because oxalic acid has in general a very favorable affinity with REEs in general [4,6,9,13]. As seen in Table 1, the pKa values are 1 and 4.2 for H₂C₂O₄/HC₂O₄⁻ and HC₂O₄⁻/C₂O₄²⁻, respectively. As a result, the relevant equations to be used to solve the equilibrium concentrations of REEs in solution after precipitation are Equations (20) and (21) for pH 6 and 4, and Equation (22) for pH 2 and 1, respectively.

2 {Re(SO₄)₂} + 3 {C₂O₄²⁻} = <Re₂(C₂O₄)₃> + 4 {(SO₄)²⁻}

(20)

2 {Re(SO₄)₂⁻} + 3 {HC₂O₄⁻} = <Re₂(C₂O₄)₃> + 4 {(SO₄)²⁻} + 3 {H⁺}

(21)

2 {Re(SO₄)₂⁻ } + 3 (HC₂O₄⁻) + {H⁺} = <Re₂(C₂O₄)₃> + 4 {(HSO₄)⁻}

(22)

The concentrations of (a) Re³⁺, (b) ReCl₂⁺, (c) Re(NO₃)₂⁺, and (d) Re(SO₄)₂⁻ in equilibrium with oxalate precipitate with 10⁻⁴ M of total concentration of oxalate in solution at pH 6, 4, 2, and 1 is plotted in Figure 6.

As seen in this figure, oxalic acid is proven to be the most effective precipitant for REEs in solution. The degree of precipitation is very favorable for all pH ranges.

8. Comparison Among Precipitants

As expected, all of the precipitants considered in this study have shown good precipitation characteristics. In general, the most effective precipitant is oxalate, which has shown an outstanding precipitation behavior for REEs even at low pHs. On the other hand, most of precipitants are not effective unless the pH of the system is relatively high. As seen in Figure 7, the precipitation of free Re-ions, Re³⁺ is relatively poor even at pH 6 with the exception of oxalate and phosphate. When the pH of the system is low, such as pH 1 (Figure 7b), even oxalate loses its effectiveness. As seen in Figure 7, it is in general that the order of precipitation power follows: oxalate > phosphate > fluoride > sulfate > carbonate.

However, when REEs complex with the anions such as Cl⁻, NO₃⁻, and SO₄²⁻ or HSO₄⁻, which almost always exist, especially at low pHs, since acids frequently used in dissolving Re-bearing minerals in the leaching operation are either HCl, HNO₃, or H₂SO₄. As discussed in the earlier studies [8,9], when such acids are present in the aqueous system, REEs immediately form complexes with these anions. In the presence of chloride, ReCl₂⁺ is the most dominating species, Re(NO₃)₂⁺ for the nitrate system and Re(SO₄)₂⁻ is for the sulfate system. As a result, the calculations involved to find the equilibrium concentrations of REEs should be carried out using these chemical moieties in place of Re³⁺. Consequently, the precipitation behavior of REEs will also change and therefore, Figure 8 will be the relevant figure in place of Figure 7 for the nitric system as an example.

It is very notable in the case of the nitrate system, the precipitation power of carbonate has overtaken that of fluoride and sulfate. Similar plots were made for the chloride system as well as the sulfate system and the results were quite similar but the intensity of precipitation was not as strong as the nitric system.

9. Conclusions

The chemical precipitation of REEs with precipitants including carbonate, fluoride, phosphate, sulfate, and oxalate was studied over a wide range of pH such as 1, 2, 4, and 6. The concentration of precipitants was fixed at 10⁻⁴ M chosen as the standard concentration for comparison. Such precipitation occurs in practice after primary leaching as a part of the purification process.

With all of the five precipitants studied, Ligjt REEs tend to precipitate much easier than Heavy REEs. The effect of anions associated with acids used in the leaching process was found to have had a significant impact on the overall precipitation process. In general, the complexed REEs with these anions tend to provide a conducive environment in precipitation resulting in an order of magnitude difference in the precipitation extent. The nitrate system was found to be most effective followed by sulfate and chloride systems. The pH of the system has another significant factor in determining the precipitation in that the difference in pKa values of the precipitants introduces precipitant moiety of the precipitants, which has a pronounced effect on the overall precipitation.