1. Introduction
Rare-earth ions are employed in a sweeping range of applications and techniques. A wide range of applications depend upon their catalytic, chemical, electrical, optical, and magnetic properties. REEs are widely utilized in classic sectors, including petroleum, metallurgy, agriculture, and textiles. They also have substantial and unique uses in numerous industries such as compact lights, wind turbines, hybrid cars, mobile phones, screen televisions, defense technologies, and disc drives [
1,
2,
3,
4,
5,
6,
7,
8,
9]. REEs are formed in the earth’s crust during the process of fractional crystallization in molten rock; they are concentrated in residual fluid that crystallizes as pegmatite dikes, and so great number of their minerals occur chiefly in pegmatite dikes associated with igneous rocks and in deposits derived from the weathering of pegmatite [
10].
On the other hand, chemical alteration of the original igneous minerals has produced rare earth minerals such as bastnasite [
11]. In addition, other rare earth resources involve euxenite, gadolinite, apatite, pyrochlore, and non-rare earth mineral resources, especially igneous rocks containing uranium and thorium [
12]. Rare earth elements (REEs) are recovered from ore materials, requiring some hydrometallurgical processes. Amazing efforts have been concentrated upon separating REEs from new materials. Impregnated resins originated by altering the solid support for metal separation from complex matrices. Two processes have embraced to organize solid sets. One is based on the physical modification of a suitable solvent at solid support. The second involves tying the chelating complex to support materials. For the extraction and separation of particular REEs, various solid-extraction techniques have been conceived using distinct styles of solid supports, such as activated carbon, silica, clay, titanium oxide, polymeric resins, Dowex 50 × 8, Dowex X1, and naphthalene [
13].
A resin was proposed for the extraction of lanthanides from acidic wastes. Nonionic amberlite XAD-16 polymeric was impregnated with undiluted TBP to extract Ce
4+ from nitrate solution at room temperature. The cerium loading capacity of the impregnated resin reached 95.6% of the calculated theoretical capacity (173 mg/g) under the conditions of a solution to resin ratio of 10.0 and a contact time of 5.0 min [
14]. A mono aza dibenzo crown ether/amberlite XAD-4 was applied to extract Sm
3+, La
3+, and Nd
3+ from a synthetic solution at pH 4.5 [
15]. Lanthanum and cerium were separated using calix [4]arene-o-vanillinsemicarbazone immobilized on a polymeric matrix—a Merrifield peptide resin at pH 5–8 [
16]. Dowex 50X8 resin was used for REE separation from chloride solution at pH 6 [
17]. La
3+ and Ce
3+ species were extracted using ethylhexyl phosphonic acid mono-2-ethylhexyl ester covered by polyvinyl alcohol that was crosslinked by divinyl sulfone or glutaraldehyde [
18].
Recently, foam flotation methods have become a promising technique of recovering RE elements from leachates of primary and secondary resources. Foam flotation can recover La
3+, Ce
3+, Gd
3+, and Yb
3+ ions individually, as a group, and as a group with gangue ions (Al
3+, Zn
2+, Ca
2+, and Mg
2+). The anionic surfactants sodium dodecyl sulfate (SDS) at basic pH and mono-rhamnolipid at pH 9 were used to separate REEs in the presence of gangue cations with a surfactant; the total cation (excluding Na+) ratio was as low as 1:13 [
19]. Rare earth minerals enriched pre-concentrate (after lab-scale gravity and magnetic separation steps) were separated by hydroxamic acid flotation [
20]. Copper oxide sulfidization flotation was applied after the modification of cuprite by hydrogen peroxide (as an oxidant to improve its consequent sulfidization) [
21]. Moreover, the direct sulfidization of cuprite is ineffective because cuprite is a copper-oxide mineral with strong surface hydrophilicity. The flotation recovery of pre-oxidized cuprite was nearly 25% higher than that of direct sulfidization flotation, which indicates that the cuprite surface activity was enhanced after pre-oxidation by the transformation of Cu
+ species (weak affinity with sulfur ions) to Cu
2+ species (strong affinity with sulfur ions) [
22].
The heavy rare-earth elements were adsorbed by hexyl-ethyl-octyl-isopropylphosphonic acid anchored resin from 0.2 M hydrochloric acid [
23]. Bis(2-ethylhexyl)phosphoric acid/polyethersulfone polymer was prepared and tested for its suitability for separating rare-earth ions from chloride media at 0.5 M containing La
3+, Sm
3+, and Y
3+ [
24]. The chromatographic separation of the impurities Ce
3+, Pr
3+, Nd
3+, Sm
3+, Zn
2+, Al
3+, Ca
2+, and Fe
3+ from La
3+ was examined using bis(2-ethylhexyl)phosphoric acid impregnated Amberlite™ XAD-7 HP from HCl solution [
25]. La
2O
3 was extracted from monazite that was treated in three steps; (a) lanthanum hydroxide extraction by using NaOH, (b) digestion with HNO
3, (c) precipitation with NH
4OH, and calcination to La
2O
3 [
26]. Tributyl phosphate (TBP) was used to extract lanthanum, cerium, yttrium, and neodymium from an aqueous solution produced by nitric acid leaching of apatite concentrate by solvent extraction at 3.65 mol/L TBP in kerosene, 5 min, 25 °C, and a 1:1 organic/aqueous ratio [
27].
TLPE was utilized as the group extraction of multi-component approaches owing to its unique extraction of three-liquid-phases via several physiochemical effects [
28,
29,
30]. A straightforward TLPE strategy was applied to attain group separation of the light, middle, and heavy rare-earth ions by liquid–liquid–liquid three-phase systems. The heavy rare-earth ion Yb
3+ was selectively extracted in the top organic phase. In contrast, the middle rare-earth ion Eu
3+ and the light rare-earth ion La
3+ can be enriched, respectively, in the PEG-rich middle phase and the (NH
4)
2SO
4-rich bottom aqueous phase of the Cyanex 272/PEG/(NH
4)
2SO
4–H
2O three-liquid-phase system. Moreover, the three-liquid-phase employed the recovery of REEs from liquid liquor [
31,
32].
Herein, hydrochloric acid was used to liquefy rare earth ions from Abu Rashied Lamprophyre dykes in the southeastern desert of Egypt. The prepared sodium diethyldithiocarbamate trihydrate/polyvinyl chloride (DdTC/PVC) was utilized to adsorb REEs from hydrochloride solution. Various influences of aqueous pH, (NH4)2SO4 concentrations, complexing agents, polymers, and added amounts on the three-liquid-phase separation of light, middle, and heavy rare-earth ions were examined. Furthermore, a possible partitioning mechanism for three rare-earth ions was analyzed. The optimum sorption conditions and three-liquid phase of REEs were also found. A three-liquid extraction phase was explored to isolate light, middle, and heavy rare-earth as different groups.
2. Materials and Methods
2.1. Materials and Instrumentations
All materials utilized in all different sections were of analytical grade and they were used without further purification. The polyvinyl chloride was impregnated with sodium diethyldithiocarbamate (DdTC) in the laboratory. REEs (1000 mg/L) were obtained from Loba Chemie, Mumbai, India. Diethylenetriamine penta-acetic acid (DTPA), ammonium hydroxide, hydrochloric acid, ammonium sulfate, and phosphoric acid were obtained from BDH, Poole, UK. Cyanex 272 and three kinds of polyethylene glycols (600, 2000, 6000 molecular weight of PEG) were obtained from Sigma-Aldrich, St. Louis, MO, USA.
A double beam spectrophotometer (Unicam, Cambridge, UK) with 1 cm quartz cells covering the UV-visible range of 200–1100 nm was employed for the determination of REEs and other major oxides in all aqueous samples. In addition, Na+ and K+ were determined by flame photometer (Model 410, Sherwood, Cambridge, UK). Atomic absorption and inductively coupled plasma-optical emission spectrometer (Agilent, Santa Clara, CA, USA) techniques were utilized to analyze the trace metal ions. The X-ray diffraction approach (XRD) (Malvern Panalytical, Almelo, The Netherlands) was also used to categorize the materials’ constituents. The material groups were explored via a Fourier transform infrared (FTIR) spectrophotometer (Shimadzu, Kyoto, Japan). The specific surface area and total pore volume of prepared materials were assessed using nitrogen sorption at 77 K (USA).
2.2. Preparation of Sodium Diethyldithiocarbamate Trihydrate/Polyvinyl Chloride
The dry technique was used to prepare sodium diethyldithiocarbamate trihydrate/polyvinyl chloride (DdTC/PVC). Five grams of polyvinyl chloride were suspended in 70 mL double-distilled H2O. Then, it was mixed well with 0.5 g of sodium diethyl-dithiocarbamate, which was dissolved in 70 mL ethyl alcohol. The mixture was stirred under reflux for 3 h at 22 °C until complete homogenization and then left to evaporate on a hotplate. The modified polyvinyl chloride was dried at 65 °C.
2.3. REE Sorption Studies
In the current study, various experiments were conducted to determine the relevant parameters affecting the sorption of REEs from either the synthetic solution or leach liquor on sodium diethyl-dithiocarbamate anchored polyvinyl chloride (DdTC/PVC). The studied parameters were aqueous pH, initial RE ion concentration, sorbent dose, contact time, and temperature.
A series of investigations was undertaken using different concentrations of the REE synthetic solution with a constant volume at 200 rpm to determine the optimum parameters. The influence of pH upon REE sorption was investigated with pH 1 to 7. The influences of sorbent dosage (10 to 90 mg) and agitation time (5 to 120 min) were also studied. The initial RE ion concentrations were studied in the 25–400 mg/L range. The effect of temperature was analyzed under various temperatures. These parameters were applied to the DdTC/PVC adsorbent by batch strategy. All the studies were executed in duplicate. The sorption power
qe (mg/g), sorption efficiency (
E, %), and distribution coefficient (
Kd) were summed by Equations (1)–(3) [
33,
34,
35].
Ce and C0 (mg/L) denote the equilibrium and initial REE concentrations, V (L) and v (mL) are solution volumes, and m (g) is a sorbent weight.
2.4. Desorption Studies
The rare earth-loaded DdTC/PVC was used to study desorption characteristics. The desorption processes were performed with 0.5 g of REEs/DdTC/PVC treated with 25 mL of adaptable concentrations of hydrochloric, nitric, and sulfuric acids ranging from 0.1 to 3 M for 60 min contact time and then filtered. The eluting RE ions were determined. The effect of desorption parameters like the desorbent type, the concentration of eluent, contact time, and temperature were investigated. After treating the studied adsorbent with the desorbing agent, it was carefully washed through double-distilled water to be eligible for recycling.
2.5. Precipitation of REEs
After the REEs sorption-desorption procedure, the eluting REEs were precipitated by an excess oxalic acid (20.0%) at pH 1–2. The latter processes are continually used in industrial operations due to the processes’ simplicity and effective recovery. The mixture was left for 24 h to complete precipitation, and the precipitate was filtered.
2.6. Group Separation of REEs by Three-Liquid-Phase Technique
TLPE is a unique technique for convoluted multi-component strategy group extraction due to its superior separation. A sufficiently conceived three-liquid-phase that is an achievable method of enhancing other ingredients to three separate liquid phases. Hence, a one-stage separation of multi-components is achievable. Three-liquid extraction phases were explored to separate light, middle, and heavy rare-earth into groups from REE leachate. TLPE is composed of three phases: Cyanex 272 (top organic phase), polyethylene glycol (middle polymer phase), and NH4)2SO4 (bottom salt phase). The influence of pH, phase concentration, and complexing intermediates on REE partitioning were studied.
4. Conclusions
The present experimental investigations were established to extract RE ions in three groups (LRE, MRE, and HRE ions) by TLPE from rare earth oxalate concentrate obtained from the extraction of RE ions from Lamprophyre dyke leachate using DdTC/PVC sorbent. The latter was prepared by sodium diethyldithiocarbamate and polyvinyl chloride, and it was used for RE ion adsorption. The optimum sorption parameters were pH 5.5, 200 mg/L REEs, 50 mg DdTC/PVC dose, and 60 min sorption time. The maximum uptake was obtained at 156.50 mg/g. Furthermore, kinetic validations were used to fit the results into the first-order nonlinear model. The Langmuir model was also suited for adsorption processes. Thermodynamic changes were explored, showing the negative ∆S° and negative ∆H°, which demonstrated RE ions’ adsorption randomness and exothermic predictability; moreover, the negative ∆G° showed that the adsorption processes were spontaneous. The sorption-desorption cycles were repeated frequently until desorption reduced to 80.0% at eight cycles. Lastly, the LRE, MRE, and HRE ions separated by TLPS were applied to the obtained rare earth oxalate concentrate solution after dissolving in diluted HCl. Finally, this study introduced a new technique that is easy to apply in extracting REEs from their resources, with a good result for RE ion separation in three groups with high purity as rare earth oxides (98%).