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Article

Solvent-Impregnated Resins Based on the Mixture of (2-Diphenylphosphoryl)-4-ethylphenoxy)methyl) diphenylphosphine Oxide and Ionic Liquid for Nd(III) Recovery from Nitric Acid Media

1
A. N. Frumkin Institute of Physical Chemistry and Electrochemistry, Russian Academy of Sciences, Leninsky Prospect 31, Building 4, 119071 Moscow, Russia
2
Institute of Physiologically Active Substances, Russian Academy of Sciences, Severnyi Proezd 1, Chernogolovka, 142432 Moscow Region, Russia
*
Author to whom correspondence should be addressed.
Molecules 2021, 26(9), 2440; https://doi.org/10.3390/molecules26092440
Submission received: 27 February 2021 / Revised: 19 April 2021 / Accepted: 20 April 2021 / Published: 22 April 2021

Abstract

:
Novel solvent-impregnated resins (SIRs) were prepared by treatment of styrene–divinylbenzene copolymer (LPS-500) with mixtures of the promising polydentante extractant (2-diphenylphosphoryl)-4-ethylphenoxy)methyl)diphenylphosphine oxide (L) and an ionic liquid [C4mim]+[Tf2N]for the extraction chromatography recovery of Nd(III) from nitric acid solutions. It was shown that introduction of the ionic liquid into the SIR composition results in considerable enhancement of the Nd(III) recovery efficiency compared with resin impregnated only by L in slightly acidic media. The influence of the L: ionic liquid molar ratio in the SIRs composition, their percentages, concentration of metal and HNO3 in the eluent, and acid type on the value of synergistic effect and adsorption efficiency of Nd(III) recovery was studied. The SIR containing 40% of mixture of L and [C4mim]+[Tf2N] with molar ratio 2:1 turned out to be the most efficient. The selectivity of Nd(III) separation from light and heavy rare-earth elements was studied and the optimal conditions of Nd(III) adsorption recovery and stripping by this SIR were chosen. It was found that in recovery efficiency of Nd(III) developed SIR exceeded the SIR containing Cyanex 923 (a mixture of monodentate trialkylphosphine oxides) and [C4mim]+[Tf2N].

Graphical Abstract

1. Introduction

Applications of rare-earth elements (REEs) in various high technology industries are conditioned by their unique physical properties. Satisfying the needs of various industries, such as metallurgy, nuclear energy, manufacture of optical, magnetic, luminescent, and laser materials, and petrochemicals most often requires high purity individual REEs. Among the rare earth elements neodymium is important for doping alloys [1] and manufacturing permanent magnets [2], laser production [3], and preparing catalysts [4,5]. Due to their similar physical and chemical properties the recovery of individual rare earth metals is a complex and yet partially unresolved problem [6]. The most important REEs minerals processed in industrial scale are monazite, bastnesite, and xenotime [7]. However, due to the growing global demand for REEs their recovery from alternative secondary resources such as phosphate ores [8], coal combustion products [9], permanent magnets [10], mine tailings [11], etc. has become more relevant. At the same time, the need to extract REE from secondary resources gives rise to new scientific challenges for the development of new effective approaches to the extraction of REE due to the complex multicomponent composition of these resources and the extremely low content of REE in them [12].
Currently, extraction chromatography methods based on the use of highly selective solvent-impregnated resins (SIRs) are becoming increasingly important for solving problems of concentration, recovery, and separation of elements with similar properties [13]. Extraction chromatography combines the efficiency of liquid-liquid extraction with the simplicity and convenience of performing adsorption methods [14]. However, for the successful implementation of the extraction chromatography process, it is necessary to develop new extraction chromatographic materials.
Synthetically available SIRs in which a selective organic ligand (extractant) is non-covalently fixed on the surface of an inert support are most widely used in extraction chromatography [15]. An important aspect of the development of effective SIRs is the optimization of their stationary phase composition, which includes both the choice of a selective organic extractant and a suitable diluent. The latter can affect both the efficiency of metal recovery (values of distribution coefficients and resin capacity), and the selectivity of metal separation (values of metal separation factors) [16,17]. The choice of organic extractants and diluents for preparation of SIRs is commonly performed by using the results of preliminary experiments of liquid–liquid extraction.
For REEs liquid-liquid extraction and separation alkyl-substituted phosphorus acids are used such as di-(2-ethylhexyl)phosphoric acid (DEHPA) [18], 2-ethylhexylphosphonic acid mono-2-ethylhexyl ester (PC88A) [19], bis-(2,4,4-trimethylpentyl)phosphinic acid (Cyanex 272) [20], as well as neutral organophosphorus extractants, for example, tributylphosphate (TBP) [21], trialkylphosphine oxides (Cyanex 923) [22], dicarboxylic acid amides such as N,N-dioctyldiglycolamic acid (DODGAA) [23], and N,N,N′,N′-tetraoctyldiglycolamide (TODGA) [8],. However, these extractants do not always allow solving the problem of selective separation of individual REEs.
The development of organic synthesis has led to the creation of new synthetically available polydentate extractants such as phosphorylpodands of neutral [24,25,26,27], and acidic type [28,29,30]. They possess high extraction ability and selectivity in relation to a wide range of chemical elements. Varying of substituents at the phosphoryl group and the design of polyether chain are effective approaches toward obtaining of phosphorylpodands with suitable extraction properties in relation to various metals, REEs inclusively. In a review [31] the applications of series of phosphorylpodands as extractants in impregnated resins for processing radioactive waste are reported.
Short-chain phosphorylpodand (2-diphenylphosphoryl-4-ethylphenoxy)-methyl)diphenylphosphine oxide (L) (Figure 1) is a promissing extractant for REEs recovery from nitric acid solution.
In our previous report, we studied the effect of substituents at phosphoryl groups of compound L on the efficiency of liquid-liquid extraction of REEs [32]. Additionally, extraction of REEs, U(VI), and Th(IV) from perchlorate solutions into dichloroethane was investigated. The stoichiometry of the extractable complexes was determined, and the influence of the aqueous phase composition on the efficiency and selectivity of the extraction of U(VI), Th(IV), and REEs into the organic phase was explored [33]. The solution of L in 1,1,7-trihydrododecafluoroheptanol have also been investigated for rare earth element extraction from nitric acid media. It was shown that the values of distribution coefficients of REEs are negligible at nitric acid concentration lower 1 mol/L. Distribution coefficient sharply increases with nitric acid concentration from 1 mol/L and reaches 5.5 for the yttrium subgroup elements at HNO3 concentration of 6 mol/L. The rare earth elements of the yttrium subgroup were found to be extracted much better than the rare earth elements of the cerium one under the same conditions. Additionally, the values of distribution coefficients in both subgroups smoothly rise with atomic number of element. It was established using the method of extraction equilibrium shift that the metal: L ratio in extracted complexes is 1:2 irrespective of the nature of the rare earth element. The structure of the complex of Yb with L was determined by an X-ray diffraction study [34]. The complex of L with neodymium was studied by X-ray structural analysis and IR spectroscopy [35].
Recently increasing attention is focused on using of ionic liquids as promising dilutents both in liquid–liquid extraction [36,37,38], and as components of SIRs [39,40,41,42]. In both cases, the using of ionic liquids leads to a significant improvement of REEs recovery efficiency. Unlike traditional organic solvents, ionic liquids are not flammable or toxic, and have low pressure of vapor and high electric conductivity [43]. In the composition of SIRs ionic liquids may be used both independently [42,44] and as mixture with different extractants [41,45,46,47]. In the present report we are interested in the second case, that’s why first we consider extraction of REEs by such systems.
Numerous reports on the liquid–liquid extraction of REEs with different neutral extractants in the presence of variously structured ionic liquids have shown that the higher the hydrophilicity of the cation and the hydrophobicity of the anion in ionic liquids, the greater is the extraction of REEs [38,48,49,50]. Varying cations and anions of various structures yields ionic liquids with suitable properties necessary for certain application [43,51,52]. An important feature of ionic liquids is that their components can serve as hydrophobic counterions in the extracted metal complexes during their recovery from aqueous phase by various extractants -[36]. The most pronounced improvement in the efficiency of REE recovery in liquid-liquid extraction was achieved in the presence of ionic liquids of bis [(trifluoromethyl) sulfonyl] imide-1-alkyl-3-methylimidazolium derivatives ([Cnmim]+[Tf2N] (where n = 4, 6, 8))].
Recently, we have found that liquid-liquid extraction of REEs with solutions of some neutral phosphorylpodands in dichloroethane from nitric acid media significantly increases in the presence of [C4mim]+[Tf2N] [53,54,55].
In this report, novel SIRs containing (2-diphenylphosphoryl)-4-ethylphenoxy)methyl) diphenylphosphine oxide and ionic liquid [C4mim]+[Tf2N] were obtained and the features of the chromatographic extraction of Nd (III) from nitric acid solutions were studied as well. The selectivity of Nd(III) recovery at the presence of La(III), Dy(III), and Tm(III) was examined. The comparison of recovery efficiency of Nd(III) by novel SIR and resin based on the mixture of Cyanex 923 (a mixture of monodentate trialkylphosphine oxides) and [C4mim]+[Tf2N] was performed.

2. Results

2.1. The Influence of Various Factors on Adsorption Recovery of Nd(III)

2.1.1. The Influence of HNO3 Concentration

The influence of HNO3 concentration on the adsorption recovery of Nd(III) with SIRs impregnated by phosphorylpodand L alone (SIR 10), [C4mim]+[Tf2N] alone (SIR 11), and their mixture (SIR 4) was studied. The values of distribution coefficient (Kd) of Nd(III) for these SIRs were established at the same conditions with varied values of HNO3 concentration in the eluent while the percentage of extractants in SIRs and the mass of SIRs in column were identical.
SIR 4 extracts Nd(III) much better than SIR 10 and SIR 11 in the range of HNO3 concentrations from 0.001 to 0.1 (Figure 2). This means that introduction of an ionic liquid into the SIR composition results in a synergistic enhancement of the value of Nd(III) Kd when it is extracted by SIR 4 in slightly acidic media, which is likely due to the replacement of NO3- by more hydrophobic Tf2N- in extracted complexes of Nd(III) [50]. It should be noted that the recovery of Nd(III) by SIR 4 is the best in slightly acidic media, which allows to avoid the equipment corrosion. Moreover, in this case there is no need to use the salting-out agents to achieve quantitative recovery of Nd(III) in contrast to SIR 10 [56]. When the concentration of HNO3 is more than 0.01 mol/L the values of Nd(III) Kd decrease, likely due to the decline of concentration of free compound L due to its protonation.
Recently, we have studied the liquid-liquid extraction of REEs by mixture of (2-((diphenylphosphoryl)methoxy)phenyl)diphenylphosphine oxide L1 (a structural analog of L, Figure 1) and ionic liquid [C4mim]+[Tf2N] from nitric acid solutions [33]. It was established that the REE:L1 stoichiometric ratio in the extracted complexes in the presence of [C4mim]+[Tf2N] varied from 1:3 to 1:2 as the HNO3 concentration in the aqueous phase increases, i.e., the system with ionic liquid displays a solvation number growth in extracted complexes as compared with REEs extraction by solutions of phosphorylpodand in dichloroethane. REEs are extracted with L1 as mixture of mono- and disolvates in presence of dichloroethane [33].The mechanism of REEs liquid-liquid extraction with neutral polydentate extractants in the presence of ionic liquids is considered in detail in [37,38]. The extraction of REEs by mixture of neutral organophosphorus extractant (E) and ionic liquid [Cnmim]+Tf2N can be described using Equation (1) [37,54]:
Ln3+(a) + sE(o) + [Cnmim]+[Tf2N](o) = LnEs(Tf2N)3(o) + 3[Cnmim]+(a)
where “s” is the solvation number; (a) and (o) denote components of aqueous and organic phases, respectively. From Equation (1) it is seen that extraction of REEs by organophosphorus extractants in presence of ionic liquid can be achieved via cation exchange mechanism which is accompanied with transfer of [Cnmim]+ to the aqueous phase. Lower concentrations of free L in the organic phase due to its interaction both with HNO3, and HTf2N presented in system are due to an marked transfer of C4mim+ and Tf2N- into the aqueous phase seem to account for lower Kd of Nd(III) with HNO3 concentration over 0.01 mol/L [54].
The dependence of Nd(III) Kd from HNO3 concentration for SIR 4 is substantially different from that observed for SIR 10. For the latter case, the increase of Kd along with the increase of HNO3 concentration is typical for neutral extractants, which was noted in numerous reports [57,58,59]. When the concentration of HNO3 is over 1 mol/L, Nd(III) is recovered by SIR 10 much better than by SIR 4, which should be attributed to the salting-out effect of NO3] [60,61] that provides for rise values of Nd(III) Kd for SIR 10, but hardly influences the Nd(III) recovery by SIR 4. The latter is in accordance with reaction Equation (1), which show that anions NO3- don’t take part in extracted complex formation. The saling-out effect of nitrate ion is the main reason of increasing of Nd(III) Kd values with increasing acidity for SIR 10. The mechanism of Nd(III) recovery by neutral extractant (L) may be presented as:
Nd3+ + 3(NO3) + nL = Nd(NO3)3Ln
Thus, the increasing NO3 concentration shifts the equilibrium of Reaction (2) to the right. However the salting agent is an electrolyte, and may be solvated by extractant, and can compete with extractad metal for the extractant. That’s why the dependency of Nd(III) Kd from HNO3 concentration is non-monotonic. To the contrary SIR 11 does not adsorb Nd(III) within the whole examined range of HNO3 concentrations as demonstrated in [37]. The influence of HNO3 concentration on the value of synergy effect for Nd(III) recovery by SIR 4 is shown in Table 1.
It is noted that values of synergistic effect are much higher in low concentrations of HNO3 than in medium ones. A similar result was previously observed when studying the liquid-liquid extraction of REEs with a mixture of 2-(diphenylphosphoryl) methoxy]-5-ethylphenylphosphonate and an ionic liquid [C4mim]+[Tf2N] [54].

2.1.2. The Influence of Component Relation in SIRs

The influence of the L:[C4mim]+[Tf2N] molar ratio in SIRs on Nd(III) adsorption recovery and values of synergy effect was studied under the same conditions (Table 2). It was found that the capacity of SIRs for Nd(III) rises with an increase of L content in SIRs. The values of Nd(III) Kd have the same trend. At the same time the increase of [C4mim]+[Tf2N] containing in SIRs has the opposite effect, which is probably attributed with fact that excess of ionic liquid in the stationary phase of SIR acts as inert diluent because [C4mim]+[Tf2N] itself does not extract Nd(III) in all examined range of HNO3 concentrations (Figure 2).
The greatest values of capacities and synergy effects were achieved for SIRs 4 and 5 (Table 2). Since the capacities and synergy effects differ for these SIRs very slightly, a molar ratio of L and [C4mim]+[Tf2N] of 2:1 was selected for subsequent preparation of SIRs. It should be noted that relatively small amount of [C4mim]+[Tf2N] needs to be added to L in SIR composition in order to get synergy effect of Nd(III) recovery from slightly acid media (for SIR 6: 0.0291 g [C4mim]+[Tf2N]/1 g SIR (see the experimental section).

2.1.3. The Influence of the Percentage Extractants

The percentage of mixture of L and [C4mim]+[Tf2N] in the SIR influences significantly both the value of Nd(III) distribution coefficient and the synergy effect. The increase of extractant content in SIRs from 20 to 60% was found to raise the value of Kd of Nd(III) from 37.4 to 262.4 mL/g, respectively (Figure 3). When the percentage of extractant increases the equilibrium of reaction (Equation (1)) shifts to the right, that is the reason for the Nd(III) Kd enhancement. On the other hand the growth of values of Nd(III) Kd is limited by the load capacity of SIRs on extractants. Herewith, the maximal value of synergy effect was attained for the SIR containing 60% mixture (L:[C4mim]+[Tf2N] = 2:1) (SIR 4) (Table 3).

2.1.4. The Influence of Nd(III) Concentration

Figure 4 illustrates the influence of Nd(III) concentration in eluent on recovery of this metal with SIR impregnated only by L (SIR 10) and SIR 4, which contains the mixture of L and [C4mim]+[Tf2N] from HNO3 of 0.001 mol/L. It was shown that SIR 10 does not adsorb Nd(III) under these conditions. This is due to the fact that phosphorylpodand L is a neutral extractant, and it does not extract metals from slightly acidic media if lacking enough salting-out agent [34]. If the concentration of Nd(III) in the eluent increases from 15 up to 150 mg/L, Kd of Nd(III) drops significantly from 209.6 to 47.6 mL/g for SIR 4, which is reason of decrease of synergy effect values (Equation (5)). The values of synergy effect for experiments A and B are equal to 18.6 and 4.25, respectively.
The decrease of Kd with the rise of metal concentration in aqueous phase (eluent) is typical for various resins used in liquid chromatography and is attributed to a limited number of adsorption centers on the surface of resins [60]. It should be noted that SIR containing only [C4mim]+[Tf2N] (SIR 11) does not recover Nd(III) in these conditions, for this reason frontal loading curves for this SIR are not presented on Figure 4.

2.1.5. The Influence of Acid Type

The adsorption recovery of Nd(III) by SIR 4 in nitric, hydrochloric, and sulfuric media was studied. The concentrations of all the chosen acids in the eluent were maintained the same equaling 0.001 mol/L. It was found that replacement of HNO3 for HCl does not change values of Nd(III) Kd or SIR capacity for the metal (Figure 5). With H2SO4 the adsorption of Nd(III) is somewhat worse, which is likely due to a higher energy of hydration of sulfate ions [62] and their strong interaction with cations of REEs [63].
Since the values of Nd(III) Kd at presence of HNO3, HCl, and H2SO4 differ insignificantly, SIR 4 may be used for REEs recovery from slightly sulfuric medium, which may be important at practical side [64,65,66].

2.2. Selectivity of REEs Recovery by SIR 4

The adsorptive recovery of La(III), Nd(III), Dy(III), and Tm(III), as representatives of light, medium, and heavy REEs, in HNO3 of 0.01 mol/Lby SIR 4 was studied. It is noticed that SIR 10 and SIR 11 containing only L and only [C4mim]+[Tf2N] don’t adsorb these REEs in such conditions (Frontal curves of REEs for these SIRs in Figure 6 are not presented). It means that introduction of [C4mim]+[Tf2N] into the resin composition results in significant enhancement of recovery efficiency of La(III), Dy(III), and Tm(III) in HNO3 of 0.01 mol/L (Figure 6), as in the case of Nd(III). The values of synergy effect of La(III), Nd(III), Dy(III) and Tm(III) recovery by SIR 4 are 15.1, 14.8, 16.7 and 19.4, respectively.
The values of distribution coefficients increase non-monotonously during the transition from La(III) to Tm(III) (Table 4). Probably, this should be attributed to the fact that as the charges of Ln3+ ions get denser because of smaller ionic radii with the increase of Z, the complexes of the REEs with L become more stable] [67]. Therefore heavy REEs are adsorbed by SIR 4 much better then light ones. The values of separation factors increase in the trend βNd/La < βDy/Nd < βTm/Nd, thus Nd(III) are more easily separated from heavy REEs then light ones.
The values of β is higher for Dy(III)/Nd(III) and Tm(III)/Nd(III) than for Nd(III)/La(III). Thus Nd(III) is more easily separated from heavy REEs than light ones. It occurs because in case of heavy REEs extractad complexes are more stable than light ones, which is probably due to the cation exchanged mechanism of its recovery and the increase of charge density at cross from light REEs to heavy ones.

2.3. Extraction Chromatography Recovery of Nd(III)

Based on performed experiments, the following approach to Nd(III) recovery with SIR 4 was suggested. A feed solution of Nd(III) of a precisely defined concentration of 15 mg/L in HNO3 of 0.001 mol/L was continuously put through a column containing SIR 4 until the complete saturation of SIR with Nd(III). Then 45 mL of HNO3 solution of 0.001 mol/L were pumped through the column to remove the remaining Nd(III) from the intergrain space. After that Nd(III) was stripped by distilled water. The breakthrough curves for Nd(III) are given in Figure 7.
The capacity of the SIR 4 for Nd(III) before breakthrough and its full load capacity for the metal are 1.31 and 2.27 mg Nd/1 g SIR, respectively (Figure 7). The reason for the low load capacity of Nd(III) for SIR 4, is probably due to the losses of extractant from SIR 4, which are likely conditioned by the small affinity of extractants to the support (LPS-500). Despite of the fact that Kd of Nd(III) is minimal in the presence of distilled water (Figure 2), the stripping of Nd(III) with distilled water is too slow for its quantitative recovery.
In order to improve the Nd(III) stripping, EDTA solution of 0.1 mol/L was used. It was shown earlier in [48] that EDTA is efficient for back-extraction of REEs from organic phase which consists of the mixture of a neutral organophosphorus extractant and ionic liquid. Preliminary SIR 4 was loaded with Nd(III) by passing the solution of Nd(III) with concentration of 15 mg/L in HNO3 of 0.001 mol/L through the column, packed with 1.0 g of SIR 4, until full saturation of SIR 4 with Nd(III). Thus in these conditions 2.27 mg of Nd(III) was loaded in SIR 4. The stripping of Nd(III) with EDTA of 0.1 mol/L from SIR 4 is given in Figure 8.
It was found that Nd(III) is stripped quantitatively by putting 6.0 mL of EDTA solution with concentration of 0.1 mol/L through SIR 4. The concentration of Nd(III) in eluate was 376.7 mg/L. Thus the extent stripping of Nd(III) is 99.5% in such condition. Thus, the advantage of SIR 4, at contrast to generally used SIRs, is that recovery and stripping of Nd(III) may be performed from practically neutral solutions which allows to avoid the equipment corrosion.

2.4. Comparison of SIRs

The closest analog of SIR 4, which is used for REEs recovery is the SIR impregnated by mixture of Cyanex 923 (a mixture of monodentate trialkylphosphine oxides) and ionic liquids [38,68,69]. We prepared SIR 12 containing 40% of mixture Cyanex 923 and [C4mim]+[Tf2N] in molar ratio of 2:1 and compared efficiency recovery of Nd(III) with SIR 4 in identical conditions (Figure 9).
The results of this experiment clearly show that recovery of Nd(III) is more effectively performed by SIR 4 compared to SIR 12. The values of full load capacity for the metal are 2.27 and 1.39 mg Nd/1 g SIR for SIRs 4 and 12, respectively. SIR 4, containing polydentate extractant L, turned out to be more effective at Nd(III) recovery, than SIR 12 based on monodentante Cyanex 923, probably, because in the case of L Nd(III) is coordinated by two P=O groups. Previously, we have synthesized the complex of Nd(III) with L and determined its structure by X-ray diffraction. The comprehensive tables of the atomic coordinates, bond lengths, and bond angles in structures L, and its complex with Nd(III) have been deposited with the Cambridge Crystallographic Data Centre (nos. 907137–97139; [email protected] (accessed on 20 April 2021) or http://www.ccdc.cam.ac.uk/data_request/cif (accessed on 20 April 2021)). An analysis of the obtained results allowed us to conclude that the binding of the neodymium ion by the extractant L occurs due to the coordination with four phosphoryl groups of two L molecules, which was further confirmed by IR spectroscopy [35].

3. Experimental Section

3.1. Synthesis

The structure and the purity degree of synthesized compound L was ascertained with NMR spectroscopy and elemental analysis data. The content of C, H was established with standard methods using a Carlo Erba CHN analyzer (Erba Group, Brno, Czech Republic). NMR spectra were registered with a CXP-200 or Bruker-DXP-200 (200 MHz) instrument (Bruker, MA, USA) with tetramethylsilane as the internal standard, while for 31P NMR 85% H3PO4 was used as reference. The control of composition of reaction mixture was conducted by the method of thin-layer chromatography on Silufol plates (Merck, NJ, USA). The mixture chloroform:isopropanol = 10:1 was used as eluent. The development of chromatograms was performed by fuming iodine.
((2-Diphenylphosphoryl)-4-ethylphenoxy)methyl)diphenylphosphine oxide (L). A mixture of 5.0 g (15.5 mmoL) (5-ethyl-2-hydroxyphenyl)diphenylphosphine oxide, 6.00 g (15.5 mmoL) diphenylphosphoryl)methylbebzenesulfonate and 5.1 g (15.5 mmoL) anhydrous cesium carbonate in 45 mL dioxane was heated and stirred at 100 °C for 10 h. The reaction mixture was diluted by 50 mL of water, acidified by adding concentrated HCl to pH 1, and extracted by CHCl3 (3 × 25 mL). The organic layer was separated, washed with water, and evaporated under reduced pressure to give 7.25 g (86%) of crude product. After recrystallization from a benzene-hexane mixture (1:1), 6.6 g (79%) of compound L was obtained, mp = 166–168 °C (The melting temperature is established with a short Anschutz thermometer). It was found, %: C 73.63, 73.50; H 5.35, 5.60; P 11.49, 11.39. For C33H30O3P2. It was calculated, %: C 73.87; H 5.64; P 11.55. 1H-NMR δ, ppm (CDCl3): 1.12 t (6H, 3JH_H = 7.02 Hz CH3CH2_Ar), 2.55 q (2H, 3JH-H = 7.58 Hz CH3CH2Ar), 4.49 d (2H, 2JH-P = 5.18 Hz OCH2P(O)Ph2), 7.07 m (1H, Ar-H), 7.30–7.65 m (22H, Ar–H). 31P-NMR, δ, ppm (CDCl3): 28.13, 29.92.
Bis[(trifluoromethyl)sulfonyl]imide-1-buthyl-3-methylimidazolium was provided by Sorbent-Technologies, Ltd. (Moscow, Russia). This compound was “purim” grade and assay an ≥99% (GC). The purity of synthesized compounds was ≥99.0% (according to the NMR data and elemental analysis results).

3.2. Preparation of Solutions and Analysis

Nitric acid solutions of Nd(III) were prepared by dissolving precisely weighed portions of Nd2O3 (purity > 99.9%, Aldrich, Germany)in nitric acid solutions of the corresponding concentrations. Nitric acid solutions were prepared by diluting concentrated HNO3. The concentrations of the obtained diluted solutions of HNO3 were determined by titration with the standard solution of NaOH in the presence of bromothymol blue. Solutions of Arsenazo M (ACS Reagent grade, Acros Organics, Belgium were prepared by dissolving precisely weighed portions of the reagent in distilled water. Solutions of EDTA (“purum” grade, Acros Organics) were prepared similarly. The concentrations of Nd(III) in the eluates were evaluated spectrophotometrically using Arsenazo M] [70]. All reagents used were analytical grade. The measurements of optical density of Nd(III) solutions flowing from the column were performed automatically with a spectrophotometric detector and software. With concentration of HNO3 in eluates exceeding 0.5 mol/L, the concentration of Nd(III) in such solutions was detected spectrophotometrically using specific absorption spectrum of Nd(III) (Figure 10), with the wavelength of 576 nm] [71].

3.3. Preparation of SIRs

The studied SIRs (Table 5) were prepared with method described earlier in [38]. Weighed portions of L and ionic liquid [C4mim]+[Tf2N] (Table 6) were dissolved in 30 mL CHCl3 and mixed with the suspension of copolymer of styrene with divinylbenzene LPS-500 (specific surface area is 570 m2/g, diameter of pores is 3–50 μm, size of particles is 40–70 μm) (provided by RossPolimer, Moscow, Russia) in approx. 20 mL CHCl3. The resulting mixture was stirred in the rotating flask of the rotary evaporator, and then CHCl3 was removed with vacuum at 50 °C. Having collected all the condensate and not seeing bubbles in the suspension, the SIR was stirred in complete vacuum at 40–50 °C for 30 min for full removal of CHCl3.

3.4. Equipment

The recovery of Nd(III) was studied in dynamic mode on an automatic chromatographic device manufactured by Knauer (Germany), consisting of three high pressure pumps, dosing valve, chromatography column, and a spectrophotometric detector. The recovery of Nd(III) was carried out using a plastic column with the length of 100 mm and the internal diameter equaling 4 mm, respectively. The column was packed with resins by the “dry method”, loading dry resin inside the column in small portions and compacting it by a glass rod. The physical constants of the prepared columns are presented in Table 7.

3.5. Batch Uptake of Nd(III)

The chromatographic column stuffed with SIRs (Table 1) was rinsed using a peristaltic pump by HNO3 solution of a chosen concentration with a flow rate of 1 mL/min for 1 h. Then Nd(III) solution of a certain concentration, which was previously determined by titration with standard solution of EDTA] [72], in HNO3 of the same concentration as on the rinsing step was constantly passed through the column until the complete SIR saturation with a flow rate of 0.5 mL/min. The Nd(III) concentrations in eluates which left the column were automatically determined by the spectrophotometric method. The obtained frontal loading curves (Figure 11) were used to calculate the values of distribution coefficients and the capacity of the SIRs.
The dynamic distribution coefficients (Kd, mL/g) were calculated per Equation (3)] [60]:
Kd = V0.5/me,
where V0.5 is the volume of solution until half breakthrough of metal, mL; me is the mass of extractant in the resin, g.
The values of separation factors (β) were calculated per Equation (4):
β = Kd2/Kd1,
where Kd1 and Kd2 are distribution coefficients of separating metals
The values of the synergy effect (SE) were calculated per Equation (4):
SE = Kd(L+IL)/Kd L+Kd IL
where Kd(L+IL), Kd L and Kd IL (mg/L) are values of the distribution coefficient obtained for SIRs impregnated by mixture of phosphorylpodand L with ionic liquid, phosphorylpodand L alone and ionic liquid alone, respectively.

4. Conclusions

Novel solvent impregnated resins (SIRs) containing the mixture of the promising polydentante extractant (2-diphenylphosphoryl)-4-ethylphenoxy)methyl)diphenyl-phosphine oxide (L) and the ionic liquid [C4mim]+[Tf2N] were prepared for adsorptive recovery of Nd(III). The performed study was dealt with investigation of influence of [C4mim]+[Tf2N] on the recovery efficiency of Nd(III) using these resins. It was shown that the addition of even a small amount of ionic liquid (0.0291 g [C4mim]+[Tf2N]/1 g resin) to phosphorylpodand L into the SIR composition results in significant enhancement of Nd(III) recovery from slightly acidic nitric solutions. The values of synergy effect are maximal with the concentration of HNO3 from 0.001 to 0.1 mol/L, are close to 1.0 in the range from 0.5 to 1.0 mol/L, and for the concentrations of HNO3 over 1 mol/L there is no synergy effect. It was established that the synergy effect is proportional to the amount of L in the SIRs and inversely proportional to the amount of [C4mim]+[Tf2N]. The percentage of extractants in SIRs was optimized. The most efficient SIR for Nd(III) recovery is that containing 40% mixture of L with [C4mim]+[Tf2N] in a molar ratio of 2:1 (SIR 4). The optimal conditions for adsorption and stripping of Nd(III) with this SIR were chosen. Nd(III) is most efficiently adsorbed from HNO3 with concentration of 0.01 mol/L. In these conditions 1.31 mg Nd(III)/1 g of SIR 4 can be loaded without breakthrough and then can be stripped quantitatively by putting 6.0 mL of EDTA solution with concentration of 0.1 mol/L through the column. The selectivity of Nd(III) recovery was studied. It was found that Nd(III) is easier to separate from heavy REEs then light ones. It was found that in recovery efficiency of Nd(III) novel SIR exceeded the SIR containing mixture of Cyanex 923 and [C4mim]+[Tf2N]. The results of this work showed that Nd(III) adsorption with SIRs impregnated by L is improved significantly by introducing [C4mim]+[Tf2N] into the SIR composition, and it can be used for the recovery of Nd(III) from slightly acidic media.

Author Contributions

O.K.: Conceptualization, O.K. and V.B.; methodology, A.T. and V.B.; software, D.B.; validation, O.K.; formal analysis, O.K. and A.T.; investigation, O.K. and V.B.; resources, V.B.; data curation A.T. and V.B.; wrighting original draft, O.K.; writing-review and editing, D.B. and V.B.; visualization, O.K. and D.B.; supervision, A.T.; project administrator, V.B.; funding acqusion, V.B. and A.T. All authors have read and agreed to the published version of the manuscript.

Funding

The work was supported by the Ministry of Science and Higher Education of Russia (grant agreement № 075-15-2020-782).

Institutional Review Board Statement

The study did not require ethical approval.

Informed Consent Statement

The study did not require ethical approval.

Data Availability Statement

Not available.

Conflicts of Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

References

  1. Wang, S.; Zhang, X.; Li, J.; Liu, C.; Guan, S. Investigation of Mg–Zn–Y–Nd alloy for potential application of biodegradable esophageal stent material. Bioact. Mater. 2020, 5, 1–8. [Google Scholar] [CrossRef]
  2. Mounkachi, O.; Lamouri, R.; Abraime, B.; Ez-Zahraouy, H.; El Kenz, A.; Hamedoun, M.; Benyoussef, A. Exploring the magnetic and structural properties of Nd-doped Cobalt nano-ferrite for permanent magnet applications. Ceram. Int. 2017, 43, 14401–14404. [Google Scholar] [CrossRef]
  3. Bonnet, L.; Boulesteix, R.; Maître, A.; Belon, R.; Chrétien, L.; Sallé, C. Influence of (Nd+Y)/Al ratio on sintering behavior and optical features of Y3-xNdxAl5O12 ceramics for laser applications. Opt. Mater. 2018, 77, 264–272. [Google Scholar] [CrossRef]
  4. Costa, S.I.; Cauneto, V.D.; Fiorentin-Ferrari, L.D.; Almeida, P.B.; Oliveira, R.C.; Longo, E.; Módenes, A.N.; Slusarski-Santana, V. Synthesis and characterization of Nd(OH)3-ZnO composites for application in photocatalysis and disinfection. Chem. Eng. J. 2020, 392, 123737. [Google Scholar] [CrossRef]
  5. Rather, R.A.; Siddiqui, Z.N. Synthesis, characterization and application of Nd-Salen schiff base complex Immobilized Mesoporous Silica in solvent free synthesis of pyranopyrazoles. J. Organomet. Chem. 2018, 868, 164–174. [Google Scholar] [CrossRef]
  6. Voncken, J. The Rare Earth Elements. In Briefs in Earth Sciences; Springer: Berlin/Heidelberg, Germany, 2016. [Google Scholar] [CrossRef]
  7. Charalampides, G.; Vatalis, K.I.; Apostoplos, B.; Ploutarch-Nikolas, B. Rare Earth Elements: Industrial Applications and Economic Dependency of Europe. Procedia Econ. Financ. 2015, 24, 126–135. [Google Scholar] [CrossRef] [Green Version]
  8. Xu, D.; Shah, Z.; Cui, Y.; Jin, L.; Peng, X.; Zhang, H.; Sun, G. Recovery of rare earths from nitric acid leach solutions of phosphate ores using solvent extraction with a new amide extractant (TODGA). Hydrometallurgy 2018, 180, 132–138. [Google Scholar] [CrossRef]
  9. Huang, C.; Wang, Y.; Huang, B.; Dong, Y.; Sun, X. The recovery of rare earth elements from coal combustion products by ionic liquids. Miner. Eng. 2019, 130, 142–147. [Google Scholar] [CrossRef]
  10. Riaño, S.; Binnemans, K. Extraction and separation of neodymium and dysprosium from used NdFeB magnets: An application of ionic liquids in solvent extraction towards the recycling of magnets. Green Chem. 2015, 17, 2931–2942. [Google Scholar] [CrossRef]
  11. Tunsu, C.; Menard, Y.; Eriksen, D.Ø.; Ekberg, C.; Petranikova, M. Recovery of critical materials from mine tailings: A comparative study of the solvent extraction of rare earths using acidic, solvating and mixed extractant systems. J. Clean. Prod. 2019, 218, 425–437. [Google Scholar] [CrossRef]
  12. Swain, N.; Mishra, S. A review on the recovery and separation of rare earths and transition metals from secondary resources. J. Clean. Prod. 2019, 220, 884–898. [Google Scholar] [CrossRef]
  13. Qi, D. Hydrometallurgy of Rare Earth, 1st ed.; Extraction and Separation; Elsevier: Amsterdam, The Netherlands, 2018; Volume 804. [Google Scholar]
  14. Horwitz, E.P.; McAlister, D.R.; Dietz, M.L. Extraction Chromatography Versus Solvent Extraction: How Similar are They? Sep. Sci. Technol. 2006, 41, 2163–2182. [Google Scholar] [CrossRef]
  15. Aguilar, M.; Cortina, J.L. Solvent Extraction and Liquid Membranes. In Solvent Extraction and Liquid Membranes; Apple Academic Press: Cambridge, MA, USA, 2008; pp. 301–304. [Google Scholar] [CrossRef]
  16. Kabay, N.; Cortina, J.L.; Trochimczuk, A.; Streat, M. Solvent-impregnated resins (SIRs)—Methods of preparation and their applications. React. Funct. Polym. 2010, 70, 484–496. [Google Scholar] [CrossRef]
  17. Ansari, S.A.; Mohapatra, P.K. A review on solid phase extraction of actinides and lanthanides with amide based extractants. J. Chromatogr. A 2017, 1499, 1–20. [Google Scholar] [CrossRef] [PubMed]
  18. Parhi, P.; Park, K.; Nam, C.; Park, J. Liquid-liquid extraction and separation of total rare earth (RE) metals from polymetallic manganese nodule leaching solution. J. Rare Earths 2015, 33, 207–213. [Google Scholar] [CrossRef]
  19. Abdeltawab, A.A.; Nii, S.; Kawaizumi, F.; Takahashi, K. Separation of La and Ce with PC-88A by counter-current mixer-settler extraction column. Sep. Purif. Technol. 2002, 26, 265–272. [Google Scholar] [CrossRef]
  20. Rodrigues, L.E.O.C.; Mansur, M.B. Hydrometallurgical separation of rare earth elements, cobalt and nickel from spent nickel–metal–hydride batteries. J. Power Sources 2010, 195, 3735–3741. [Google Scholar] [CrossRef]
  21. Jorjani, E.; Shahbazi, M. The production of rare earth elements group via tributyl phosphate extraction and precipitation stripping using oxalic acid. Arab. J. Chem. 2016, 9, S1532–S1539. [Google Scholar] [CrossRef]
  22. Aly, M.; Masry, B.; Gasser, M.; Khalifa, N.; Daoud, J. Extraction of Ce (IV), Yb (III) and Y(III) and recovery of some rare earth elements from Egyptian monazite using CYANEX 923 in kerosene. Int. J. Miner. Process. 2016, 153, 71–79. [Google Scholar] [CrossRef]
  23. Shimojo, K.; Fujiwara, I.; Fujisawa, K.; Okamura, H.; Sugita, T.; Oshima, T.; Baba, Y.; Naganawa, H. Extraction Behavior of Rare-earth Elements Using a Mono-alkylated Diglycolamic Acid Extractant. Solvent Extr. Res. Dev. Jpn. 2016, 23, 151–159. [Google Scholar] [CrossRef] [Green Version]
  24. Nazarenko, A.; Baulin, V.; Lamb, J.; Volkova, T.; Varnek, A.; Wipff, G. Solvent extraction of metal picrates by phosphoryl-containing podands. Solvent Extr. Ion Exch. 1999, 17, 495–523. [Google Scholar] [CrossRef]
  25. Turanov, A.; Karandashev, V.; Baulin, V. Extraction of metal species from HNO3 solutions by phosphoryl-containing podands. Solvent Extr. Ion Exch. 1999, 17, 525–552. [Google Scholar] [CrossRef]
  26. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E. Extraction of rare-earth nitrates by phosphoryl podands. Russ. J. Inorg. Chem. 2006, 51, 1829–1835. [Google Scholar] [CrossRef]
  27. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E. Extraction of Lanthanides(III) from Nitric Acid Solutions by Selected Polyfunctional Monoacidic Organophosphorus Compounds. Solvent Extr. Ion Exch. 2007, 25, 165–186. [Google Scholar] [CrossRef]
  28. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E.; Tsivadze, A.Y. Extraction of REEs(III), U(VI), and Th(IV) with acidic phosphoryl-containing podands from nitric acid solutions. Radiochem. 2014, 56, 22–26. [Google Scholar] [CrossRef]
  29. Safiulina, A.M.; Matveeva, A.G.; Ivanets, D.V.; Kudryavtsev, E.M.; Baulin, V.E.; Tsivadze, A.Y. Phosphoryl-containing acidic podands as extractants for recovery of f-elements. Russ. Chem. Bull. 2015, 64, 169–175. [Google Scholar] [CrossRef]
  30. Safiulina, A.M.; Matveeva, A.G.; Ivanets, D.V.; Kudryavtsev, E.M.; Baulin, V.E.; Tsivadze, A.Y. Phosphoryl-containing acidic podands as extractants for recovery of f-elements. Russ. Chem. Bull. 2015, 64, 187–193. [Google Scholar] [CrossRef]
  31. Tsivadze, A.Y.; Baulin, V.; Baulin, D. New Sorbents for Processing Radioactive Waste. In Handbook of Ecomaterials; Springer: Cham, Switzerland, 2019; pp. 3621–3660. [Google Scholar] [CrossRef]
  32. Turanov, A.N.; Karandashev, V.K.; Fedoseev, A.M.; Rodygina, N.I.; Baulin, V.E. Effect of the Structure of o-Methyleneoxyphenyldiphosphine Dioxides on Their Extractive Power and Selectivity in Nitric Acid Solutions. Radiochemistry 2005, 47, 177–180. [Google Scholar] [CrossRef]
  33. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E.; Baulin, D.V. Extraction of REE(III), U(VI), and Th(IV) from Perchlorate Solutions with Tetraphenyl(o-oxyphenylenemethylene)diphosphine Dioxide. Radiochemistry 2019, 61, 156–161. [Google Scholar] [CrossRef]
  34. Demin, S.V.; Zhilov, V.I.; Nefedov, S.E.; Baulin, V.E.; Tsivadze, A.Y. Extraction of rare earth elements with 1-(diphenylphosphorylmethoxy)-2-diphenylphosphoryl-4-ethylbenzene with the use of 1,1,7-trihydrododecafluoroheptanol as a solvent. Russ. J. Inorg. Chem. 2012, 57, 897–902. [Google Scholar] [CrossRef]
  35. Demin, S.V.; E Nefedov, S.; Baulin, V.E.; Demina, L.I.; Tsivadze, A.Y. Structures of the compounds preparatively isolated in the extraction of rare-earth metals with 2-diphenylphosphoryl-1-diphenylphosphorylmethoxy-4-ethylbenzene. Russ. J. Co-ord. Chem. 2013, 39, 333–341. [Google Scholar] [CrossRef]
  36. Liu, Y.; Chen, J.; Li, D. Application and Perspective of Ionic Liquids on Rare Earths Green Separation. Sep. Sci. Technol. 2012, 47, 223–232. [Google Scholar] [CrossRef]
  37. Wang, K.; Adidharma, H.; Radosz, M.; Wan, P.; Xu, X.; Russell, C.K.; Tian, H.; Fan, M.; Yu, J. Recovery of rare earth elements with ionic liquids. Green Chem. 2017, 19, 4469–4493. [Google Scholar] [CrossRef]
  38. Rout, A.; Binnemans, K. Influence of the ionic liquid cation on the solvent extraction of trivalent rare-earth ions by mixtures of Cyanex 923 and ionic liquids. Dalton Trans. 2015, 44, 1379–1387. [Google Scholar] [CrossRef] [Green Version]
  39. Hawkins, C.A.; Momen, A.; Dietz, M.L. Application of ionic liquids in the preparation of extraction chromatographic materials for metal ion separations: Progress and prospects. Sep. Sci. Technol. 2017, 53, 1820–1833. [Google Scholar] [CrossRef]
  40. Sun, X.; Peng, B.; Ji, Y.; Chen, J.; Li, D. The solid–liquid extraction of yttrium from rare earths by solvent (ionic liquid) impreganated resin coupled with complexing method. Sep. Purif. Technol. 2008, 63, 61–68. [Google Scholar] [CrossRef]
  41. Ansari, S.A.; Mohapatra, P.K. Solid phase extraction of trivalent actinides and lanthanides using a novel CMPO-RTIL based chromatographic resin. Radiochim. Acta 2013, 101, 163–168. [Google Scholar] [CrossRef]
  42. Liu, Y.; Zhu, L.; Sun, X.; Chen, J.; Luo, F. Silica Materials Doped with Bifunctional Ionic Liquid Extractant for Yttrium Extraction. Ind. Eng. Chem. Res. 2009, 48, 7308–7313. [Google Scholar] [CrossRef]
  43. Guo, X.; Yao, W.; Chen, Y.; Fan, J.; Zhao, Y.; Wang, J. PEG-functionalized ionic liquids: A class of liquid materials for highly efficient extraction of rare earth metals from aqueous solutions. J. Mol. Liq. 2017, 236, 308–313. [Google Scholar] [CrossRef]
  44. Avdibegović, D.; Yagmurlu, B.; Dittrich, C.; Regadío, M.; Friedrich, B.; Binnemans, K. Combined multi-step precipitation and supported ionic liquid phase chromatography for the recovery of rare earths from leach solutions of bauxite residues. Hydrometallurgy 2018, 180, 229–235. [Google Scholar] [CrossRef]
  45. Liu, Y.; Sun, X.; Luo, F.; Chen, J. The preparation of sol–gel materials doped with ionic liquids and trialkyl phosphine oxides for Yttrium(III) uptake. Anal. Chim. Acta 2007, 604, 107–113. [Google Scholar] [CrossRef]
  46. Yu, B.; Bell, J.R.; Luo, H.; Dai, S. Ionic Liquid and Silica Sol-Gel Composite Materials Doped with N,N,N′,N′-tetra(n-octyl)diglycolamide for Extraction of La3+and Ba2+. Sep. Sci. Technol. 2012, 47, 244–249. [Google Scholar] [CrossRef]
  47. Friend, M.T.; Parker, T.G.; Mastren, T.; Mocko, V.; Brugh, M.; Birnbaum, E.R.; Fassbender, M.E. Extraction chromatography of 225Ac and lanthanides on N,N-dioctyldiglycolamic acid/1-butyl-3-methylimidazolium bis(trifluoromethylsulfonyl)imide solvent impregnated resin. J. Chromatogr. A 2020, 1624, 461219. [Google Scholar] [CrossRef]
  48. Nakashima, K.; Kubota, F.; Maruyama, T.; Goto, M. Feasibility of Ionic Liquids as Alternative Separation Media for Industrial Solvent Extraction Processes. Ind. Eng. Chem. Res. 2005, 44, 4368–4372. [Google Scholar] [CrossRef]
  49. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E. Effect of ionic liquids on the extraction of rare-earth elements by bidentate neutral organophosphorus compounds from chloride solutions. Russ. J. Inorg. Chem. 2008, 53, 970–975. [Google Scholar] [CrossRef]
  50. Turanov, A.N.; Karandashev, V.K.; Yarkevich, A.N. Extraction of REE(III), U(VI), and Th(IV) from Nitric Acid Solutions with Carbamoylmethylphosphine Oxides in the Presence of Bis[(trifluoromethyl)sulfonyl]imide Ions. Radiochemistry 2018, 60, 170–176. [Google Scholar] [CrossRef]
  51. Plechkova, N.V.; Seddon, K.R. Applications of ionic liquids in the chemical industry. Chem. Soc. Rev. 2008, 37, 123–150. [Google Scholar] [CrossRef]
  52. Zhou, H.; Wang, Y.; Guo, X.; Dong, Y.; Su, X.; Sun, X. The recovery of rare earth by a novel extraction and precipitation strategy using functional ionic liquids. J. Mol. Liq. 2018, 254, 414–420. [Google Scholar] [CrossRef]
  53. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E. Extraction of Rare-Earth Elements from Nitric Acid Solutions with Bidentate Phosphoryl-containing Compounds and Their Mixtures. Radiochemistry 2001, 43, 72–78. [Google Scholar] [CrossRef]
  54. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E.; Baulin, D.V.; Khvostikov, V.A. Extraction of Rare-Earth Elements(III) from Nitric Acid Solutions with Diethyl 2-[(Diphenylphosphoryl)methoxy]-5-ethylphenylphosphonate. Russ. J. Inorg. Chem. 2019, 64, 1297–1303. [Google Scholar] [CrossRef]
  55. Turanov, A.N.; Karandashev, V.K.; Baulin, D.V.; Baulin, V.E. Extraction of Uranium(VI), Thorium(IV), and Trivalent Rare Earths from Nitric Acid Solutions with {[2-(2-Diphenylphosphoryl)-4-ethylphenoxy]ethyl}diphenylphosphine Oxide. Russ. J. Gen. Chem. 2020, 90, 1012–1019. [Google Scholar] [CrossRef]
  56. Turanov, A.; Karandashev, V.; Baulin, V. Extraction of rare-earth elements from nitric solutions by phosphoryl-containing podands. Solvent Extr. Ion Exch. 1999, 17, 1423–1444. [Google Scholar] [CrossRef]
  57. Turanov, A.N.; Karandashev, V.K.; Baulin, V.E.; Yarkevich, A.N.; Safronova, Z.V. Extraction of Lanthanides(III) from Aqueous Nitrate Media with Tetra-(p-tolyl)[(o-Phenylene)Oxymethylene] Diphosphine Dioxide. Solvent Extr. Ion Exch. 2009, 27, 551–578. [Google Scholar] [CrossRef]
  58. Turanov, A.N.; Karandashev, V.K.; Evseeva, N.K.; Kolesnikov, N.N.; Borisenko, D.N. The sorption properties of carbon nanotubes modified with tetraphenylmethylenediphosphine dioxide in nitric acid media. Russ. J. Phys. Chem. A 2008, 82, 2223–2226. [Google Scholar] [CrossRef]
  59. Gupta, B.; Malik, P.; Deep, A. Solvent Extraction and Separation of Tervalent Lanthanides and Yttrium Using Cyanex 923. Solvent Extr. Ion Exch. 2003, 21, 239–258. [Google Scholar] [CrossRef]
  60. Braun, T.; Ghersini, G. Extraction Chromatography; Akademian Kiado: Budapest, Hungary, 1975; Volume 615. [Google Scholar]
  61. Li, H.; Guo, F.; Zhang, Z.; Li, D.; Wang, Z. A new hydrometallurgical process for extracting rare earths from apatite using solvent extraction with P350. J. Alloy. Compd. 2006, 408–412, 995–998. [Google Scholar] [CrossRef]
  62. Ang, K.L.; Li, D.; Nikoloski, A.N. The effectiveness of ion exchange resins in separating uranium and thorium from rare earth elements in acidic aqueous sulfate media. Part 2. Chelating resins. Miner. Eng. 2018, 123, 8–15. [Google Scholar] [CrossRef]
  63. Naumov, K.; Karimov, K.; Klyushnikov, A. Complex Rare Earth Minerals Sulfate Decomposition Techniques Investigation. Mater. Sci. Forum 2019, 946, 580–584. [Google Scholar] [CrossRef]
  64. Huang, X.; Li, J.; Long, J.; Zhang, Y.; Xue, X.; Zhu, Z. Synergistic extraction of rare earth by mixtures of 2-ethylhexyl phosphoric acid mono 2-ethylhexyl ester and di-(2-ethylhexyl) phosphoric acid from sulfuric acid medium. J. Rare Earths 2008, 26, 410–413. [Google Scholar] [CrossRef]
  65. Borai, E.H.; Abd El-Ghany, M.S.; Ahmed, I.M.; Hamed, M.M.; Shahr El-Din, A.M.; Aly, H.F. Modified acidic leaching for selective separation of thorium, phosphate and rare earth concentrates from Egyptian crude monazite. Int. J. Miner. Process. 2016, 149, 34–41. [Google Scholar] [CrossRef]
  66. Xinju, Z.; Qui, L.; Li, H.; Kangbi, L.; Su, Y. Summar of leaching and extraction for the associated rare-earth elements in the phosphorus ore. Gen. Rev. 2014, 22, 65–69. [Google Scholar]
  67. Huang, C. Rare Earth Coordination Chemistry. Fundamentals and Applications; Markono Print Media Pte, Ltd.: Singapore, 2010; Volume 587. [Google Scholar] [CrossRef]
  68. Sun, X.; Waters, K.E. Synergistic Effect between Bifunctional Ionic Liquids and a Molecular Extractant for Lanthanide Separation. ACS Sustain. Chem. Eng. 2014, 2, 2758–2764. [Google Scholar] [CrossRef]
  69. Regadío, M.; Hoogerstraete, T.V.; Banerjee, D.; Binnemans, K. Split-anion solvent extraction of light rare earths from concentrated chloride aqueous solutions to nitrate organic ionic liquids. RSC Adv. 2018, 8, 34754–34763. [Google Scholar] [CrossRef] [Green Version]
  70. Gladilovich, D.; Kubáň, V.; Sommer, L. Determination of the sum of rare-earth elements by flow-injection analysis with Arsenazo III, 4-(2-pyridylazo)resorcinol, Chrome Azurol S and 5-bromo-2-(2-pyridylazo)-5-diethylaminophenol spectrophotometric reagents. Talanta 1988, 35, 259–265. [Google Scholar] [CrossRef]
  71. Baulin, V.E.; Baulin, D.V.; Usolkin, A.N.; Ivenskaya, N.M.; Vlasova, N.V.; Kozlov, P.V.; Remizov, M.B.; Chuchlanseva, E.V.; Tsivadze, A.Y. The extraction-chromatographic separation of neodymium from solution from nitric acid with application of sorbents impregnated by N,N,N’,N’-tetraoctyldiglicolamide. Sorbts. I Khromat. Prots. 2018, 18, 717–725. [Google Scholar]
  72. Pribil, R.; Veselý, V. A note on successive complexometric determination of thorium and rare earths. Talanta 1972, 19, 1448–1450. [Google Scholar] [CrossRef]
Figure 1. Structural formulas of the studied compounds.
Figure 1. Structural formulas of the studied compounds.
Molecules 26 02440 g001
Figure 2. The influence of HNO3 concentration on the value of distribution coefficient of Nd(III).
Figure 2. The influence of HNO3 concentration on the value of distribution coefficient of Nd(III).
Molecules 26 02440 g002
Figure 3. Influence of the extractant percentage in SIRs on recovery of Nd(III).
Figure 3. Influence of the extractant percentage in SIRs on recovery of Nd(III).
Molecules 26 02440 g003
Figure 4. Influence of Nd(III) concentration in the eluent on its adsorption and the values of synergy effect. 1–SIR 10; 2–SIR 4. The values of Nd(III) concentration are equal 15 and 150 mg/L for experiments (A,B), respectively.
Figure 4. Influence of Nd(III) concentration in the eluent on its adsorption and the values of synergy effect. 1–SIR 10; 2–SIR 4. The values of Nd(III) concentration are equal 15 and 150 mg/L for experiments (A,B), respectively.
Molecules 26 02440 g004
Figure 5. The influence of acid nature on Nd(III) adsorption recovery.
Figure 5. The influence of acid nature on Nd(III) adsorption recovery.
Molecules 26 02440 g005
Figure 6. Frontal loading curves of La(III), Nd(III), Dy(III) and Tm(III) in HNO3 of 0.01 mol/L.
Figure 6. Frontal loading curves of La(III), Nd(III), Dy(III) and Tm(III) in HNO3 of 0.01 mol/L.
Molecules 26 02440 g006
Figure 7. Extraction chromatography recovery of Nd(III) with SIR 4. 1: adsorption of Nd(III) from HNO3 of 0.001 mol/L; 2: rinse of the column by HNO3 with concentration of 0.01 mol/L; 3: stripping of Nd(III) with distilled water.
Figure 7. Extraction chromatography recovery of Nd(III) with SIR 4. 1: adsorption of Nd(III) from HNO3 of 0.001 mol/L; 2: rinse of the column by HNO3 with concentration of 0.01 mol/L; 3: stripping of Nd(III) with distilled water.
Molecules 26 02440 g007
Figure 8. Stripping of Nd(III) with EDTA solution.
Figure 8. Stripping of Nd(III) with EDTA solution.
Molecules 26 02440 g008
Figure 9. Frontal loading curves of Nd(III) for SIR 4 and SIR 12 in HNO3 of 0.001 mol/L.
Figure 9. Frontal loading curves of Nd(III) for SIR 4 and SIR 12 in HNO3 of 0.001 mol/L.
Molecules 26 02440 g009
Figure 10. Specific absorption spectrum of Nd(III) solution in HNO3 of 1 mol/L.
Figure 10. Specific absorption spectrum of Nd(III) solution in HNO3 of 1 mol/L.
Molecules 26 02440 g010
Figure 11. The approach of values calculation of metal distribution coefficients using frontal loading curves.
Figure 11. The approach of values calculation of metal distribution coefficients using frontal loading curves.
Molecules 26 02440 g011
Table 1. The values of synergy effect (SE) of Nd(III) recovery by SIR 4 for various concentrations of HNO3.
Table 1. The values of synergy effect (SE) of Nd(III) recovery by SIR 4 for various concentrations of HNO3.
Concentration of HNO3, mol/LSE = Kd(L+IL)/Kd L+Kd IL
01.60
0.00115.1
0.0116.5
0.13.2
0.51.23
1.00.79
3.00.39
Table 2. The values of distribution coefficient (Kd), capacity and synergy effect (SE) obtained for SIRs of different composition in Nd(III) recovery from HNO3 of 0.001 mol/L.
Table 2. The values of distribution coefficient (Kd), capacity and synergy effect (SE) obtained for SIRs of different composition in Nd(III) recovery from HNO3 of 0.001 mol/L.
SIR *Molar Ratio L:[C4mim]+[Tf2N]Kd, mL/gCapacity, mg Nd/1 g ResinSE
11:12221.5212.7
21:21841.1910.6
31:41310.987.53
42:12602.014.9
55:12742.0415.7
610:12262.6213.0
* All SIRs contain 40% extractants.
Table 3. The values of synergy effect (SE) for recovery of Nd(III) from HNO3 of 0.001 mol/L by SIRs containing the mixture (L:[C4mim]+[Tf2N] = 2:1).
Table 3. The values of synergy effect (SE) for recovery of Nd(III) from HNO3 of 0.001 mol/L by SIRs containing the mixture (L:[C4mim]+[Tf2N] = 2:1).
Content of Extractants, %SE
201.08
4012.9
6015.1
Table 4. The values of distribution coefficients (Kd) and separation factors (βREE/Nd) for La(III), Nd(III), Dy(III), and Tm(III).
Table 4. The values of distribution coefficients (Kd) and separation factors (βREE/Nd) for La(III), Nd(III), Dy(III), and Tm(III).
Rare Earth ElementKd, mL/gβREE/Nd
La(III)242.81.03
Nd(III)250.5_
Dy(III)289.21.15
Tm(III)325.41.30
Table 5. Composition of prepared SIRs.
Table 5. Composition of prepared SIRs.
SIRComposition of Stationary Phase (Mole Ratio of L and [C4mim]+[Tf2N]Extractant Content, %
11:140
21:240
31:440
42:140
55:140
610:140
72:120
82:160
92:175
10L40
11[C4mim]+[Tf2N]40
12Cyanex 923:[C4mim]+[Tf2N] = 2:140
Table 6. Weighed portions of substances used to prepare SIRs *.
Table 6. Weighed portions of substances used to prepare SIRs *.
SIR *Weight of Portion, g
L[C4mim]+[Tf2N]LPS-500
10.22410.17550.6001
20.15560.24440.6000
30.09650.30330.6002
40.28700.11280.6002
50.34550.05340.6003
60.37070.02910.6000
70.14360.05640.8001
80.43110.16910.4003
90.53870.21150.2502
100.4001-0.6002
11-0.40030.6001
* Per 1 g of SIR. For preparing 1 g of SIR 12 we need 0.2590 g of Cyanex 923 and 0.1411 g [C4mim]+[Tf2N].
Table 7. Physical constants of columns packed with developed SIRs.
Table 7. Physical constants of columns packed with developed SIRs.
SIRExtractant Density, (g/mL)Bed Density (g/mL)Vs, mLVm, mLVs/Vm
11.401.180.271.140.24
21.391.170.271.120.24
31.411.190.271.140.24
41.421.180.271.180.23
51.441.200.281.550.18
61.461.230.281.430.20
71.421.210.410.800.51
81.421.220.510.252.04
91.401.180.270.840.32
101.461.240.281.580.18
111.381.160.670.591.13
121.401.180.650.631.03
Vs is the volume of extractant, which is held by SIR; Vm is the volume of eluent, which is located inside column packed with SIR.
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Kovalenko, O.; Baulin, V.; Baulin, D.; Tsivadze, A. Solvent-Impregnated Resins Based on the Mixture of (2-Diphenylphosphoryl)-4-ethylphenoxy)methyl) diphenylphosphine Oxide and Ionic Liquid for Nd(III) Recovery from Nitric Acid Media. Molecules 2021, 26, 2440. https://doi.org/10.3390/molecules26092440

AMA Style

Kovalenko O, Baulin V, Baulin D, Tsivadze A. Solvent-Impregnated Resins Based on the Mixture of (2-Diphenylphosphoryl)-4-ethylphenoxy)methyl) diphenylphosphine Oxide and Ionic Liquid for Nd(III) Recovery from Nitric Acid Media. Molecules. 2021; 26(9):2440. https://doi.org/10.3390/molecules26092440

Chicago/Turabian Style

Kovalenko, Olga, Vladimir Baulin, Dmitriy Baulin, and Aslan Tsivadze. 2021. "Solvent-Impregnated Resins Based on the Mixture of (2-Diphenylphosphoryl)-4-ethylphenoxy)methyl) diphenylphosphine Oxide and Ionic Liquid for Nd(III) Recovery from Nitric Acid Media" Molecules 26, no. 9: 2440. https://doi.org/10.3390/molecules26092440

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