Next Article in Journal / Special Issue
Treatment of Aqueous Effluents from Steel Manufacturing with High Thiocyanate Concentration by Reverse Osmosis
Previous Article in Journal
Pervaporative Dehydration of Methanol Using PVA/Nanoclay Mixed Matrix Membranes: Experiments and Modeling
Previous Article in Special Issue
Development of Chitosan/Starch-Based Forward Osmosis Water Filtration Bags for Emergency Water Supply
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Pertraction of Co(II) through Novel Ultrasound Prepared Supported Liquid Membranes Containing D2EHPA. Optimization and Transport Parameters

by
Gerardo León
1,*,
Asunción María Hidalgo
2,
Beatriz Miguel
1 and
María Amelia Guzmán
1
1
Departamento de Ingeniería Química y Ambiental, Universidad Politécnica de Cartagena, Paseo Alfonso XIII, 30203 Cartagena, Spain
2
Departamento de Ingeniería Química, Campus de Espinardo, Universidad de Murcia, 30100 Murcia, Spain
*
Author to whom correspondence should be addressed.
Membranes 2020, 10(12), 436; https://doi.org/10.3390/membranes10120436
Submission received: 30 November 2020 / Revised: 14 December 2020 / Accepted: 15 December 2020 / Published: 17 December 2020
(This article belongs to the Special Issue Membranes for Water and Wastewater Treatment)

Abstract

:
Pertraction of Co(II) through novel supported liquid membranes prepared by ultrasound, using bis-2-ethylhexyl phosphoric acid as carrier, sulfuric acid as stripping agent and a counter-transport mechanism, is studied in this paper. Supported liquid membrane characterization through scanning electron microscopy, energy-dispersive X-ray spectroscopy and Fourier transform infrared spectroscopy shows the impregnation of the microporous polymer support by the membrane phase by the action of ultrasound. The effect on the initial flux of Co(II) of different experimental conditions is analyzed to optimize the transport process. At these optimal experimental conditions (feed phase pH 6, 0.5 M sulfuric acid in product phase, carrier concentration 0.65 M in membrane phase and stirring speed of 300 rpm in both phases) supported liquid membrane shows great stability. From the relation between the inverse of Co(II) initial permeability and the inverse of the square of carrier concentration in the membrane phase, in the optimized experimental conditions, the transport resistance due to diffusion through both the aqueous feed boundary layer (3.7576 × 104 s·m−1) and the membrane phase (1.1434 × 1010 s·m−1), the thickness of the aqueous feed boundary layer (4.0206 × 10−6 m) and the diffusion coefficient of the Co(II)-carrier in the bulk membrane (4.0490 × 10−14 m2·s−1), have been determined.

Graphical Abstract

1. Introduction

Cobalt is associated with many industrial and technological activities such as mining, hydrometallurgy, medicine and the manufacture of batteries, steels, magnetic alloys, catalysts, glass, ceramics, paints, lacquers, etc. [1]. Due to its industrial significance, cobalt production has grown steadily over the last two decades, from 56,635 tonsin 2005 [2] to 124,344 tonsin 2018 [3], leading to both the decrease of primary cobalt resources and the increase in cobaltwaste.
Moreover, the presence of cobalt in the wastewater of the above industries is an important environmental problem because, like other heavy metals, it is not biodegradable and tends to accumulate in living organisms, causing diseases and disorders. The acute effects of cobalt on humans affect cardiovascular, endocrine, hematological, respiratory and nervous systems [4].
All this makes the recovery of cobalt from raw materials and secondary sources very interesting from both environmental and economic reasons.
Different techniques have been described for cobalt removal from aqueous solutions, including flocculation [5], adsorption [6,7,8,9], biosorption [10,11,12], phytoremediation [13], solvent extraction [14,15], ion exchange [16] capacitive deionization [17], electrowinning [18], micellar enhanced ultrafiltration [19], nanofiltration [20], reverse and forward osmosis [21,22], membrane distillation [23], liquid membranes [24,25,26,27] and combined methods [28].
Liquid membranes are receiving great attention as a separation process because they combine the extraction and the recovery processes in a single continuous stage [29]. In a liquid membrane, two miscible phases (feed and product phases) are separated by an immiscible phase (membrane phase). Supported liquid membranes (SLM) are obtained when the pores of a thin microporous solid support are filled with the membrane phase [29].
Traditionally, the filling of these pores has been carried out by impregnation of the microporous support by the liquid membrane solution under pressure or under vacuum. In this paper, we use a novel method based on the effects of ultrasound. The application of ultrasound to a liquid medium causes mechanical vibration and acoustic streaming. As the liquid medium usually contains dissolved gaseous nuclei, ultrasound generates acoustic cavitation (expanding and collapsing them), releasing large amounts of energy that generate, among other effects, shock waves and micro jets [30]. Polyvinylidene fluoride (PVDF) has been selected as the microporous support, due to its greater resistance to the ultrasound mechanical effects [31,32].
Transport in a liquid membrane system is usually improved by adding to the membrane phase a complexing agent (carrier) to carry the diffusing species across the membrane to the product phase [33]. This process can be accompanied by the transport of other chemical species from the product to the feed phase (coupled counter-transport mechanism), which offers the possibility of transporting a component against its own concentration gradient [34].
In this paper we study the Co(II) pertraction from an acetate buffered aqueous feed phase to an aqueous product phase which contains sulfuric acid as stripping agent (protons as counter ions), through an ultrasound prepared supported liquid membrane containing D2EHPA in kerosene, by using a coupled counter-transport mechanism.
To optimize the pertraction process, the effect on Co(II) initial flux of different experimental conditions (pH of the feed phase, carrier concentration in the membrane phase, stripping agent concentration in the product phase and stirring rate in both feed and product phases) is analyzed. From the relation between the inverse of Co(II) initial permeability and the inverse of the square of carrier concentration in the membrane phase, at the optimal experimental conditions, the transport resistance due to diffusion through both the aqueous feed boundary layer and the membrane phase, the thickness of the aqueous feed boundary layer and the diffusion coefficient of the Co(II)-carrier in the bulk membrane phase are determined.

2. Theoretical Background

The coupled counter-transport of Co(II) ions through a liquid membrane using D2EHPA as carrier and H+ as counter ion (sulfuric acid as a stripping agent) is illustrated in Figure 1. Dimerized molecules of carrier (HR)2 [35] diffuse from the membrane phase to the feed/membrane interface where they undergo reaction with Co(II). Each Co(II) ion is exchanged for two protons, according to the following equation [36]:
Co2+(aq) + 2(HR)2(org) ⇔ CoR2(HR)2 (org) + 2H+(aq)
The Co(II)-carrier complex, CoR2(HR)2, diffuses through the membrane phase to the membrane/product interface where due to the high acidic conditions of product phase, the described reaction is reversed and protons are exchanged for Co(II) ions, which are released into the product phase, the carrier being regenerated to begin a new separation cycle. A coupled counter-transport mechanism takes place, so that Co(II) and H+ travel in opposite directions.
The equilibrium constant of the described reversible reaction (Ke) can be expressed by Equation (1).
K e = [ CoR 2 ( HR ) 2 ] org × [ H + ] aq 2 [ Co 2 + ] aq × [ ( HR ) 2 ] org 2
It can be considered that chemical reactions that take place at the feed/membrane and membrane/product interfaces occur faster than the diffusion processes [37] and the Co(II) transport rate is determined by the rate of diffusion of Co(II) through the feed diffusion layer and the rate of diffusion of the Co(II)-carrier complex through the membrane. The Co(II) flux across the membrane can be obtained by applying Fick’s first diffusion law to the diffusion layer on the feed side (Jfbl) and to the membrane (Jm) through the following equations [38]:
J f b l = [ Co 2 + ] f [ Co 2 + ] i , f / m Δ f b l
J m = [ CoR 2 ( HR ) 2 ] i , f / m [ CoR 2 ( HR ) 2 ] i , m / p Δ m
where Δfbl is the transport resistance due to diffusion through the aqueous feed boundary layer (δfbl/Daq) (s·m−1), Δm is the transport resistance due to diffusion through the membrane phase(δm/Dps(s·m−1), [Co2+]f is the cobalt concentration in the feed phase, [Co2+]i,f/m is the cobalt concentration in the feed/membrane interface, [CoR2(HR)2]i,f/m is the complex concentration in the feed/membrane interface, [CoR2(HR)2]i,m/p is the complex concentration in the membrane/product interface, δfbl is the thickness of the aqueous feed boundary layer (m), Daq is the average aqueous diffusion coefficient of the Co(II) (m2·s−1), δm is the thickness of the membrane phase (m) and Dps is the diffusion coefficient of the Co(II)-carrier in the polymeric support.
Due to the different pH values of the feed and the product phases, the distribution coefficient of Co(II) between the membrane phase and the product phase is much lower than that between the feed phase and the membrane phase. Consequently, the concentration of the Co(II)-carrier complex at the membrane/product interface may be considered negligible compared to that at the feed/membrane interface and Equation (3) can be rewritten as
J m = [ CoR 2 ( HR ) 2 ] i , f / m Δ m
If, as assumed above, chemical reactions are fast compared with the diffusion rate, local equilibrium is reached at the interface, where concentrations are related through Equation (1). Thus, in the steady state, Jfbl = Jm= J, and by combining Equations (1), (2) and (4), the following flux expression can be obtained:
J = K e [ ( HR ) 2 ] 2 [ Co 2 + ] f Δ m [ H + ] 2 + Δ f b l K e [ ( HR ) 2 ] 2
Thus, the permeability coefficient, P = J/[Co(II)]f, can be written as [38]
P = K e [ ( HR ) 2 ] 2 Δ m [ H + ] 2 + Δ f b l K e [ ( HR ) 2 ] 2
From Equation (6), the following expression for 1/P is obtained
1 P = Δ f b l + Δ m [ H + ] 2 K e [ ( HR ) 2 ] 2
By plotting 1/P as a function of 1/[(HR)2]2, at constant pH, a straight line should be obtained with slope (∆m·[H+]2)/Ke and ordinate ∆fbl. Knowing Ke and the pH of the feed solution, ∆m can be obtained from the slope.
Since ∆fbl = δfbl/Daq, the value of the thickness of the aqueous feed boundary layer can be calculated if the average aqueous diffusion coefficient is known.
Similarly, since ∆m = δm/Dps, knowing the thickness of the supported liquid membrane, Dps can be calculated, while the diffusion coefficient of the Co(II)-carrier in the bulk membrane phase (Dbm) can be obtained by the following equation [39]:
D b m = D p s τ 2 ε
The porosity of the membrane (ε) is usually given by the membrane supplier and the tortuosity of the membrane (τ) can be calculated according to the relationship [40]:
τ = 1 + V p 1 V p
where the volume fraction of polymeric support (Vp) is 1 − ε [41].

3. Materials and Methods

3.1. Materials

Cobalt(II) chloride (98%), sodium acetate (99%), acetic acid (95%) and sulfuric acid (95–98%) were purchased from Panreac. Bis-2-ethylhexyl phosphoric acid (97%) was obtained from Sigma-Aldrich, Madrid, Spain. Kerosene (99%) was supplied by BDH Middle East, Dubai, UAE. A microporous hydrophobic PVDF ultrafiltration membrane (Millipore Durapore GVHP 10, Merck, Madrid, Spain), was utilized as support for the liquid membrane (geometrical area 20 cm2, porosity of 75%, pore size of 0.22 μm and thickness of 125 μm).

3.2. Methods

3.2.1. Preparation of Supported Liquid Membrane

The liquid membrane phase was constituted by kerosene solutions of D2EHPA at concentrations between 0.2 and 0.8 M. The pores of the microporous support were filled with the membrane solution by applying ultrasound, using Labsonic M (Sartorius SA, Madrid, Spain) ultrasound equipment (titanium probe 10 mm diameter, sound rating density 130 W/cm2), at 30 KHz, 150 μm, for 30 min (three times for 10 min, with 5 min intervals between them), and the active layer of the polymeric support at a distance of 16 mm from the ultrasound probe [24] (Figure 2a).

3.2.2. Supported Liquid Membrane Characterization

Scanning electron microscopy (SEM), energy-dispersive X-ray spectroscopy (EDX) and infrared spectrometry (IR) were used to study the impregnation of the pristine PVDF porous polymeric support with the liquid membrane phase by the effect of ultrasound (PVDF-USLM).
The outer surface and elemental composition of both PVDF and PVDF-USLM were analyzed by SEM using a HITACHI S-3500N apparatus, containing secondary and backscattered electron detectors (Hitachi High-Technologies Corporation, Tokyo, Japan), equipped with an EDX XFlash 5010 analysis system (Brukers AXS, Karlsruyhe, Germany). 15 kV, 10 mm work distance, samples sputtered with a thin layer of platinum during 90 s by a sputter coater Polaron SC 7640 (Quorum Technologies, Newhaven, UK) and 5000× magnification were used in SEM study, while 15 kV and 15 mm work distance were used in EDX analysis.
The outer surface chemical functional groups of both PVDF and PVDF-USLM were analyzed by using a NICOLET 5700 FTIR equipment (ThermoFischer Scientific, Waltham, MA, USA), in transmittance mode from 400 cm−1 to 4000 cm−1.

3.2.3. Transport Experiments

Transport studies were carried out using a permeation cell consisting of two identical compartments, containing 250 cm3 (V) of feed or product phase, separated by the supported liquid membrane with an effective area (A) of 15 cm2 [24] (Figure 2b). As feed phase, aqueous solutions of Co(II) between 0.010 M to 0.200 M (10 mol/m3 to 200 mol/m3) in 0.2 M acetate buffer, with pH ranging from 3 to 7, were used, and aqueous sulfuric acid solutions between 0.005 and 1 M were used as product phase. Both phases were mechanically stirred at speeds ranging from 50 to 400 rpm, at room temperature.

3.2.4. Analytical Methods and Calculations

Samples from the product phase compartment were taken every 30 min and Co(II) concentrations were determined by flame atomic absorption spectrophotometry at 240.7 nm usinga Shimadzu AA-2600 apparatus (Duisburg, Germany). The experiments were carried out in duplicate and the results obtained showed less than 3% deviation.
Initial Co(II) fluxes were determined, according to Equation (10) [42], from the slope of the straight line obtained when plotting the Co(II) concentration in the product phase ([Co+2]pt) as a function of time during the first four hours of the experiment, because of the linear relationship observed during that time.
J = V A d Co 2 + pt dt
Initial Co(II) permeability values (P) were determined, according to Equation (11) [43], from the straight line obtained when plotting ln[C0/(C0Cpt)] versus time during the first four hours of the experiment, when a linear relationship was observed
ln Co 2 + f 0 Co 2 + f 0 Co 2 + pt = A V P t
where [Co2+]f0 is the initial Co(II) concentration in the feed phase.
The instability of the supported liquid membrane was determined from the decrease in Co(II) flux through the membrane in four successive experiments using the same membrane at the optimal experimental conditions.

4. Results

4.1. Membrane Characterization

Figure 3 shows SEM, EDX and FTIR of both PVDF and PVDF-USLM.
SEM shows that the surface microstructure, in terms of the surface morphology and porous structure, was not significantly changed after sonification/impregnation process, though the surface roughness of the impregnated support slightly decreased, which must be a consequence of filling the pores with the liquid membrane phase.
EDX characterization results of the shell surface shows the absence of phosphorus in the original PVDF support but its presence in the PVDF-USLM membrane. This confirms that the polymeric porous support has been adequately impregnated with the liquid membrane phase through the application of ultrasound.
The analysis of the FTIR of PVDF-USLM film shows the presence of several significant bands which are not present in PVDF film. The bands between 2958 and 2859 cm−1 (corresponding to C-H stretching) show the presence of methyl and ethyl groups and the band at 1027 cm−1 (corresponding to P–O–C stretching) shows the presence of P–O–CH2– groups. This supports the incorporation of the liquid membrane phase (D2EHPA in kerosene) into the PVDF microporous support during the sonification process with the liquid membrane phase.

4.2. Optimization of Co(II) Transport Process

The influence on the Co(II) pertraction (expressed in terms of flux) of different parameters such as feed phase Co(II) concentration and pH, sulfuric acid concentration in the product phase, carrier concentration in the membrane phase and stirring speed in both feed and product phases, is shown in Figure 4a–f.
Figure 4a shows the effect of Co(II) concentration in the feed phase on Co(II) flux. The flux increased as the Co(II) concentration in the feed phase increased from 10 mol/m3 to 100 mol/m3 due to the presence of a higher number of Co(II) ions in the feed/membrane interface, which facilitated the formation of Co(II)-carrier complex leading to a higher transport. A further increase in Co(II) concentration has no significant effect on flux due to saturation of the feed/membrane interface by the Co(II) ions. A Co(II) concentration of 0.025 M (25 mol/m3) was selected for subsequent experiments as it is the lowest concentration at which significant flux variations were observed with the other parameters studied.
As shown in Figure 4b, the flux increased when feed pH increased between pH 3 and pH 6 and then remained constant. At low feed pH (high [H+]), the equilibrium of the extraction reaction was highly displaced to the left, and no Co(II)-carrier complex was formed. Moreover, the low proton gradient between product and feed phases generated a low driving force. As the feed pH increased ([H+] decrease), both the equilibrium of the extraction reaction shifted towards the right (more Co(II) carrier complex is formed) and the proton gradient between the product and the feed phases increased. Consequently, Co(II) transport from the feed to the permeate phase increased. Above pH 6, the OH- competes with the carrier to form a Co(II) complex and so its transport decreases. Thus, a pH of 6 in the feed phase was maintained throughout the study.
The pertraction of Co(II) from aqueous feed phase across the membrane phase is dependent on the concentration of the stripping agent (H2SO4) present in the product phase (Figure 4c). The results show that the Co(II) flux increased sharply as the sulfuric acid concentrations raised from 0.005 to 0.100 M, and then more slowly up to 0.5 M. At higher sulfuric acid concentrations, the Co(II) flux remained practically constant. These results confirm that the presence of a proton gradient between the product and the feed phases is essential for a high mass transfer. Therefore, a sulfuric acid concentration of 0.5 M in the permeate phase was chosen for further experiments.
The effect of the carrier concentration in the membrane phase on Co(II) flux is shown in Figure 4d. As can be seen, Co(II) flux increased as the carrier concentration increased from 0.2 to 0.65 M, but further increases in carrier concentration had no significant effect on Co(II) flux. According to the equilibrium of the extraction reaction (reaction 1), the higher the carrier concentration in the membrane phase, the more Co(II)-carrier complex is formed. Above 0.65 M, both the saturation of the feed/membrane interface by the carrier and the higher viscosity of the membrane phase led to the Co(II) flux remaining constant. Therefore, a carrier concentration of 0.65 M was used in subsequent experiments.
The effect of stirring rate on Co(II) flux is shown in Figure 4e. The flux increased as the stirring rate increased from 50 to 300 rpm, above which no appreciable variation was observed. This indicates that the boundary layers thickness diminished continuously as the stirring rate increased and that minimum values of these boundary layers (minimal diffusion resistance due to the boundary layers) are reached at 300 rpm and above. Therefore, further experiments were carried out at 300 rpm.
The instability of the supported liquid membrane, measured as the decrease in Co(II) flux in four successive runs, is shown in Figure 4f, where the variation of Co(II) concentration with time in those four successive experiments with the same membraneis also shown. The flux in runs 2, 3 and 4, expressed as percentage with respect to the flux in run 1, were 94%, 83% and 71%, respectively. These flux decreases are lower than those found by other authors using similar supported liquid membranes, but prepared by immersion of the polymeric support in the liquid membrane phase [44].

4.3. Determination of Transport Parameters

The effect of the carrier concentration in the membrane phase on Co(II) initial permeability is shown in Figure 5a. As in the case of initial flux, initial permeability increased as the carrier concentration increased from 200 to 650 mol·m−3, but further increases in carrier concentration had no significant effect on Co(II) permeability.
From data obtained when plotting the inverse of Co(II) initial permeability versus the inverse of the square of carrier concentration in the membrane phase (Figure 5b, R2 = 0.9908), at constant pH (pH = 6), knowing the value of Ke of D2EHPA (Ke = 1.1 × 10−7 [45]) and using Equation (7), the transport resistance due to diffusion through the aqueous feed boundary layer (fbl) and due to diffusion through the membrane (m) were calculated (Table 1). From these values and data for the membrane polymeric support provided by the supplier (δm), the Daq value of 1.07 × 10−10 m2·s−1 [46] and the Equations (8) and (9), the thickness of the aqueous feed boundary layer (δfbl) and the diffusion coefficient of the Co(II)-carrier complex in the bulk membrane phase (Dbm) were obtained (Table 1).

5. Conclusions

This paper has analyzed the optimization and the determination of transport parameters of the Co(II) pertraction through novel ultrasound prepared supported liquid membranes by using a coupled counter-transport mechanism, with D2EHPA as carrier in the membrane phase and sulfuric acid as stripping agent (protons as counter-ions) in the product phase. SEM, EDX and FTIR characterization of the supported liquid membrane show good impregnation of the microporous polymer support by the membrane phase throughthe action of ultrasound. To optimize the pertraction process, the effect of different experimental conditions on Co(II) initial fluxes was studied. The optimal experimental conditions were: feed phase pH 6, 0.5 M sulfuric acid in product phase, carrier concentration 0.65 M in membrane phase and stirring speed of 300 rpm in both phases. Supported liquid membrane shows great stability (71%) after four successive runs (four hours each run). From the relation between the inverse of Co(II) initial permeability and the inverse of the square of carrier concentration in the membrane phase, in the optimized conditions, transport resistance due to diffusion through the aqueous feed boundary layer (fbl) and transport resistance due to diffusion through the membrane (m) were calculated as being 3.7576 × 104 sm−1 and 1.1434 × 1010 sm−1, respectively. The thickness of the aqueous feed boundary layer (δfbl) was 4.0206 × 10−6 m and the membrane diffusion coefficient of the Co(II)-carrier complex through the membrane (Dbm) was 4.0490 × 10−14 m2·s−1.

Author Contributions

G.L., B.M. and M.A.G. conceived, designed and performed the experiments. G.L., A.M.H., M.A.G. and B.M. analyzed the data and contributed to the interpretation of the results. G.L. and A.M.H. wrote the paper. All authors have read and agreed to the published version of the manuscript.

Funding

This research has not received external funding.

Acknowledgments

The authors are grateful for the support provided by the Technological Research Support Service of the Technical University of Cartagena (UPCT).

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Cote, G. Hydrometallurgy of strategic materials. Solvent Extr. Ion. Exch. 2000, 18, 703–727. [Google Scholar] [CrossRef]
  2. Kapusca, J.P.T. Cobalt production and markets: A brief overview. Cobalt News 2007, 7, 9–12. [Google Scholar]
  3. Weight, D. Cobalt Production Statistics; Cobalt Development Institute: Surrey, UK, 2018; Available online: https://www.cobaltinstitute.org/statistics.html (accessed on 28 July 2020).
  4. Leyssensa, L.; Vincka, B.; Van Der Straeten, C.; Wuytse, F.; Maesa, L. Cobalt toxicity in humans. A review of the potential sources and systemic health effects. Toxicology 2017, 387, 43–56. [Google Scholar] [CrossRef] [PubMed]
  5. Wang, G.; Zhang, Y.; Jiang, S.; Ma, X.; Wei, B. Removal and recovery of cobalt from Co(II)–Containing water samples by dithiocarboxyl polyethyleneimine. Sep. Purif. Technol. 2020, 251, 117338. [Google Scholar] [CrossRef]
  6. Zhang, X.; Wang, X.; Chen, Z. Radioactive Cobalt(II) Removal from aqueous solutions using a reusable nanocomposite: Kinetic, isotherms, and mechanistic study. Int. J. Environ. Res. Public Health 2017, 14, 1453. [Google Scholar] [CrossRef] [Green Version]
  7. Islam, M.A.; Morton, D.W.; Johnson, B.B.; Pramanik, B.K.; Mainali, B.; Angove, M.J. Opportunities and constraints of using the innovative adsorbents for the removal of cobalt(II) from wastewater: A review. Environ. Nanotechnol. Monit. Manag. 2018, 10, 435–456. [Google Scholar] [CrossRef]
  8. Salmani, M.H.; Ehrampoush, M.H.; Eslami, H.; Eftekhar, B. Synthesis, characterization and application of mesoporous silica in removal of cobalt ions from contaminated water. Groundw. Sustain. Dev. 2020, 11, 100425. [Google Scholar] [CrossRef]
  9. Dehghani, M.H.; Yetilmezsoy, K.; Salari, M.; Heidarinejad, Z.; Yousefi, M.; Sillanpää, M. Adsorptive removal of cobalt(II) from aqueous solutions using multiwalled carbon nanotubes and γ-alumina as novel adsorbents: Modelling and optimization based on response surface methodology and artificial neural network. J. Mol. Liq. 2020, 299, 112154. [Google Scholar]
  10. Vafajoo, L.; Cheraghi, R.; Dabbagh, R.; McKay, G. Removal of cobalt (II) ions from aqueous solutions utilizing the pre-treated 2-Hypnea Valentiae algae: Equilibrium, thermodynamic, and dynamic studies. Chem. Eng. J. 2018, 331, 39–47. [Google Scholar] [CrossRef]
  11. Qian Zhang, Q.; Zhuang, S.; Wang, J. Biosorptive removal of cobalt(II) from aqueous solutions using magnetic cyanoethyl chitosan beads. J. Environ. Chem. Eng. 2020, 8, 104531. [Google Scholar] [CrossRef]
  12. Iáñez-Rodríguez, I.; Calero, M.; Blázquez, G.; Martín-Lara, M.Á. Greenhouse crop residue and its derived biochar: Potential as adsorbent of cobalt from aqueous solutions. Water 2020, 12, 1282. [Google Scholar] [CrossRef]
  13. Mosoarca, G.; Vancea, C.; Popa, S.; Boran, S. Adsorption, bioaccumulation and kinetics parameters of the phytoremediation of cobalt from wastewater using elodea canadensis. Bull. Environ. Contam. Toxicol. 2018, 100, 733–739. [Google Scholar] [CrossRef] [PubMed]
  14. Quintero-Almanza, D.; Gamiño-Arroyo, Z.; Sánchez-Cadena, L.E.; Gómez-Castro, F.I.; Uribe-Ramírez, A.R.; Aguilera-Alvarado, A.F.; Ocampo-Carmona, L.M. Recovery of cobalt from spent lithium-ion mobile phone batteries using liquid–liquid extraction. Batteries 2019, 5, 44. [Google Scholar] [CrossRef] [Green Version]
  15. Wiecka, Z.; Rzelewska-Piekut, M.; Cierpiszewski, R.; Staszak, K.; Regel-Rosocka, M. Hydrometallurgical recovery of Cobalt(II) from spent industrial catalysts. Catalysts 2020, 10, 61. [Google Scholar] [CrossRef] [Green Version]
  16. Jamiu, Z.A.; Saleh, T.A.; Ali, S.A. Biogenic glutamic acid-based resin: Its synthesis and application in the removal of cobalt(II). J. Hazard. Mater. 2017, 327, 44–54. [Google Scholar] [CrossRef]
  17. Liu, X.; Wu, J.; Wang, J. Electro-enhanced removal of cobalt ions from aqueous solution by capacitive deionization. Sci. Total Environ. 2019, 697, 134–144. [Google Scholar] [CrossRef]
  18. Lu, J.; Dreisinger, D.; Glück, T. Cobalt electrowinning. A systematic investigation for high quality electrolytic cobalt production. Hydrometallurgy 2018, 178, 19–29. [Google Scholar] [CrossRef]
  19. Kumar, V.A.; Marathe, K.V. Selective separation of copper (II) and cobalt (II) from wastewater by using continuous cross-flow micellar-enhanced ultrafiltration and surfactant recovery from metal micellar solutions. Can. J. Chem. Eng. 2011, 89, 292–298. [Google Scholar]
  20. Gherasim, C.V.; Hancková, K.; Palarčík, J.; Mikulášek, P. Investigation of cobalt (II) retention from aqueous solutions by a polyamide nanofiltration membrane. J. Membr. Sci. 2015, 490, 46–56. [Google Scholar] [CrossRef]
  21. Kryvoruchko, A.P.; Yurlova, L.Y. Influence of some organic and inorganic additives on pressure-driven purification of waters containing cobalt. J. Water Chem. Technol. 2015, 37, 271–276. [Google Scholar]
  22. Liu, X.; Wu, J.; Liu, C.; Wang, J. Removal of cobalt ions from aqueous solution by forward osmosis. Sep. Purif. Technol. 2017, 177, 8–20. [Google Scholar] [CrossRef]
  23. Jia, F.; Yin, Y.; Wang, J. Removal of cobalt ions from simulated radioactive wastewater by vacuum membrane distillation. Prog. Nucl. Energy 2018, 103, 20–27. [Google Scholar] [CrossRef]
  24. León, G.; Martínez, G.; Guzmán, M.A.; Moreno, J.I.; Miguel, B.; Fernández-López, J.A. Increasing stability and transport efficiency of supported liquid membranas through a novel ultrsound-assisted preparation method: Its application to cobalt(II) removal. Ultrason. Sonochem. 2013, 20, 650–654. [Google Scholar] [CrossRef] [PubMed]
  25. Hachemaoui, A.; Belhamel, K. Simultaneous extraction and separation of cobalt and nickel from chloride solution through emulsion liquid membrane using Cyanex 301 as extractant. Int. J. Min. Process. 2017, 161, 7–12. [Google Scholar] [CrossRef]
  26. Vafaei, F.; Torkaman, R.; Moosavian, M.A.; Zaheri, P. Optimization of extraction conditions using centralcomposite design for the removal of Co(II) from chloride solution by supported liquid membrane. Chem. Eng. Res. Des. 2018, 133, 126–136. [Google Scholar] [CrossRef]
  27. Parbat, S.A.; Bhanvase, B.A.; Sonawane, S.H. Investigation on liquid emulsion membrane (LEM) prepared with hydrodynamic cavitation process for cobalt (II) extraction from wastewater. Sep. Purif. Technol. 2020, 237, 116385. [Google Scholar] [CrossRef]
  28. Sadyrbaeva, T.Z. Recovery of cobalt(II) by the hybrid liquid membrane—Electrodialysis—Electrolysis process. Electrochim. Acta 2014, 133, 161–168. [Google Scholar] [CrossRef]
  29. Sastre, A.M.; Kumar, A.; Shukla, J.P.; Singh, R.K. Improved techniques in liquid membrane separations: An overview. Sep. Purif. Meth. 1998, 27, 213–298. [Google Scholar] [CrossRef]
  30. Ashokkumar, M. The characterization of acoustic cavitation bubbles—An overview. Ultrason. Sonochem. 2011, 18, 864–872. [Google Scholar] [CrossRef]
  31. Masselin, I.; Chasseray, X.; Durand-Bourlier, L.; Lainé, J.M.; Syzaret, P.I.; Lemordant, D. Effect of sonication on polymeric membranes. J. Membr. Sci. 2001, 181, 213–220. [Google Scholar] [CrossRef]
  32. Kallioinen, M.; Mänttäri, M. Influence of ultrasonic treatment on various membrane materials: A Review. Sep. Sci. Technol. 2011, 46, 1388–1395. [Google Scholar] [CrossRef]
  33. León, G. Facilitated transport. In Encyclopedia of Membranes, 1st ed.; Drioli, E., Giorno, L., Eds.; Springer: Berlin/Heidelberg, Germany, 2016; pp. 763–764. ISBN 978-3-642-40872-4. [Google Scholar]
  34. De Gyves, J.; Rodríguez, E. Metal ion separations by supported liquid membranes. Ind. Eng. Chem. Res. 1999, 38, 2182–2202. [Google Scholar] [CrossRef]
  35. Biswas, R.K.; Habib, M.A.; Islam, M.N. Some Physicochemical Properties of (D2EHPA). 1. Distribution, dimerization, and acid dissociation constants of D2EHPA in a Kerosene/0.10 kmol m−3 (Na+,H+)Cl system and the extraction of Mn(II). Ind. Eng. Chem. Res. 2000, 39, 155–160. [Google Scholar] [CrossRef]
  36. Juang, R.S.; Su, J.Y. Thermodynamic equilibria of the extraction of cobalt (II) from sulfate solutions with bis(2-ethylhexyl)phosphoric acid. Ind. Eng. Chem. Res. 1992, 31, 2395–2400. [Google Scholar] [CrossRef]
  37. Miyake, Y.; Matsuyama, H.; Nishida, M.; Nakai, M.; Nagase, M.; Teramoto, M. Kinetics and mechanism of metal extraction with acidic organophosphorus extractants (I): Extraction rate limited by diffusion process. Hydrometallurgy 1990, 24, 19–35. [Google Scholar] [CrossRef]
  38. Sastre, A.M.; Madi, A.; Alguacil, F.J. Facilitated supported liquid-membrane transport of gold(I) using LIX 79 in cumene. J. Membr. Sci. 2000, 166, 213–219. [Google Scholar] [CrossRef]
  39. Huang, T.C.; Juang, R.S. Rate and mechanism of divalent metal transport through supported liquid membrane containing di(2-ethylhexyl)phosphoric acid as mobile carrier. J. Chem. Technol. Biotechnol. 1988, 42, 1–17. [Google Scholar] [CrossRef]
  40. Alguacil, F.J.; Coedo, A.G.; Dorado, M.T. Transport of chromium(VI) through a Cyanex 923-xylene flat-sheet supported liquid membrane. Hydrometallurgy 2000, 57, 51–56. [Google Scholar] [CrossRef]
  41. Stolwijk, T.B.; Sudhoelter, E.J.R.; Reinhoudt, D.N. Crown ether mediated transport: A kinetic study of potassium perchlorate transport through a supported liquid membrane containing dibenzo-18-crown-6. J. Am. Chem. Soc. 1987, 109, 7042–7047. [Google Scholar] [CrossRef]
  42. Zaghbani, A.; Tayeb, R.; Dhahbi, M. Studies on the transport of chromium(III) through a supported liquid membrane containing D2EHPA as carrier. Desal. Water Treat. 2009, 12, 247–255. [Google Scholar] [CrossRef] [Green Version]
  43. Ochromowicz, K.; Apostoluk, W. Modelling of carrier mediated transport of chromium(III) in the supported liquid membrane system with D2EHPA. Sep. Purif. Technol. 2010, 72, 112–117. [Google Scholar] [CrossRef]
  44. Alguacil, F.J.; Alonso, M. Separation of zinc(II) from cobalt(II) solutions using supported liquid membranes with DP-8R (di(2-ethylhexyl) phosphoric acid) as carrier. Sep. Purif. Technol. 2005, 41, 179–184. [Google Scholar] [CrossRef]
  45. Van de Voorde, I.; Pinoy, L.; Courtijn, E.; Verpoort, F. Equilibrium Studies of Nickel(II), Copper(II), and Cobalt(II) Extraction with Aloxime 800, D2EHPA, and Cyanex Reagents. Solvent Extr. Ion. Exch. 2006, 24, 893–914. [Google Scholar] [CrossRef]
  46. Rubcumintara, T.; Han, K.N. The effect of concentration and temperature on diffusivity of metal compounds. Metall. Trans. B 1990, 21, 429–438. [Google Scholar] [CrossRef]
Figure 1. Diagram of the coupled counter-transport of Co(II) ions using D2EHPA as carrier and H+ as counter-ion.
Figure 1. Diagram of the coupled counter-transport of Co(II) ions using D2EHPA as carrier and H+ as counter-ion.
Membranes 10 00436 g001
Figure 2. Schematic representations of: (a) sonication system; (b) experimental transport cell.
Figure 2. Schematic representations of: (a) sonication system; (b) experimental transport cell.
Membranes 10 00436 g002
Figure 3. Membrane characterization of PVDF and PVDF-USLM by (a1,a2) SEM; (b1,b2) EDX; (c) FTIR.
Figure 3. Membrane characterization of PVDF and PVDF-USLM by (a1,a2) SEM; (b1,b2) EDX; (c) FTIR.
Membranes 10 00436 g003
Figure 4. Influence on Co(II) flux of: (a) initial feed pH; (b) sulfuric acid concentration in product phase; (c) carrier concentration in membrane phase; (d) stirring rate in both aqueous and product phases; (e) initial Co(II) concentration in feed phase; (f) successive runs with the same membrane.
Figure 4. Influence on Co(II) flux of: (a) initial feed pH; (b) sulfuric acid concentration in product phase; (c) carrier concentration in membrane phase; (d) stirring rate in both aqueous and product phases; (e) initial Co(II) concentration in feed phase; (f) successive runs with the same membrane.
Membranes 10 00436 g004
Figure 5. (a) Effect of the carrier concentration in the membrane phase on Co(II) initial permeability; (b) inverse of Co(II) initial permeability versus the inverse of the square of carrier concentration in the membrane phase.
Figure 5. (a) Effect of the carrier concentration in the membrane phase on Co(II) initial permeability; (b) inverse of Co(II) initial permeability versus the inverse of the square of carrier concentration in the membrane phase.
Membranes 10 00436 g005
Table 1. Transport parameters of Co(II) pertraction through ultrasound prepared supported liquid membranes containing D2EHPA as carrier.
Table 1. Transport parameters of Co(II) pertraction through ultrasound prepared supported liquid membranes containing D2EHPA as carrier.
fbl (sm−1)m (sm−1)δfbl (m)Dbm (m2·s−1)
3.7576 × 1041.1434 × 10104.0206 × 10−64.0490 × 10−14
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

León, G.; Hidalgo, A.M.; Miguel, B.; Guzmán, M.A. Pertraction of Co(II) through Novel Ultrasound Prepared Supported Liquid Membranes Containing D2EHPA. Optimization and Transport Parameters. Membranes 2020, 10, 436. https://doi.org/10.3390/membranes10120436

AMA Style

León G, Hidalgo AM, Miguel B, Guzmán MA. Pertraction of Co(II) through Novel Ultrasound Prepared Supported Liquid Membranes Containing D2EHPA. Optimization and Transport Parameters. Membranes. 2020; 10(12):436. https://doi.org/10.3390/membranes10120436

Chicago/Turabian Style

León, Gerardo, Asunción María Hidalgo, Beatriz Miguel, and María Amelia Guzmán. 2020. "Pertraction of Co(II) through Novel Ultrasound Prepared Supported Liquid Membranes Containing D2EHPA. Optimization and Transport Parameters" Membranes 10, no. 12: 436. https://doi.org/10.3390/membranes10120436

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop