This patent application claims priority from Australian Provisional Patent Application No. 2010905533 titled “Extraction of Metals” and filed 17 Dec. 2010, the entire contents of which are hereby incorporated by reference.
The present invention relates to processes for extracting target metal ions from aqueous solutions using liquid-liquid extraction.
Liquid-liquid extraction, also known as solvent extraction (SX), is a process for separating a specific component from a mixture that is widely used in manufacturing, synthetic chemistry, analytical chemistry, waste treatment, and nuclear waste processing (Bernardis, Grant et al. 2005). In mineral processing, SX plays an important role in recovery and refining of valuable metals from mineral ores including copper, precious metals, uranium and lanthanides, etc (Billard, Ouadi et al.; Kumar, Sahu et al. 2010).
SX offers a number of advantages of other separation processes, such as continuous operation, simple equipment, high throughput, as well as diversity of the extraction chemistry. Thus, SX is a separation technique of major industrial significance (Bond, Dietz et al. 1999; Gmehling 2004). In traditional SX, the two immiscible phases are an organic solvent and an aqueous solution. However, many common organic solvents are volatile, flammable and toxic, and therefore are hazardous and are becoming less acceptable from an environmental viewpoint. Disposal of spent extractants and diluents also attracts increasing costs through the impact of environmental protection regulations.
In recent times, room temperature ionic liquids (RTILs) have gained interest in solvent extraction processes as they are potentially environmentally benign alternatives to the use of volatile organic compounds (VOCs). RTILs possess a number of potential advantages over traditional VOCs, such as a wide liquid range of up to 200° C., good thermal stability up to 300° C., extremely low vapour pressure, non-flammability and the properties of the RTILs can be fine-tuned by varying the anion and cation. RTILs are known to be polar but non-coordinating media, and have been shown to dissolve different organic, inorganic, organometallic and biomolecules. For example, RTILs have been used as a liquid-liquid extraction media to separate organic solutes, such as aromatic solutes, from aqueous solutions (Huddleston, Wilauer et al. 1998; Gmehlig, 2004).
To date, a limited range of RTILs have been used in solvent extraction processes to extract metal ions from aqueous solutions. Dai et al. (1999) describes a process for extracting strontium from aqueous solutions of strontium nitrate using an RTIL containing a crown ether. Dietz et al. (2006) describes processes for extracting various metal ions using ionic liquids containing organic extractants such as 1-(2-pyridylazo)-2-naphthol (PAN), 1-(2-thiazolyl)-2-naphthol (TAN), crown ethers and calixarenes. Visser and Rogers (2003) describe processes for extracting actinide metals from aqueous solutions using RTILs containing crown ethers. In each of the aforementioned processes, the RTILs are used as a solvent and an organic extractant is added to the organic phase. In the absence of an extractant, the distribution ratios in [C4mim][PF6]/aqueous phases at pH 1 to 13 of the metal ions studied (including Hg2+, Cd2+, Co2+, Ni2+, Fe3+) were all relatively low, indicating retention in the aqueous phase. In the presence of extractants, the partitioning of the extracted organic moieties or metal ions in the RTIL/water systems is similar to the partitioning that is achieved in traditional organic solvent-water systems.
A problem with the use of RTILs on a large scale is the cost of the solvent and the higher viscosity of the RTILs relative to VOCs. This is further compounded by the fact that extractants need to be added to the RTILs to assist in the efficient extraction of metals from aqueous solutions.
There is a need for a better understanding of the kinetics of extraction of metal ions from aqueous solutions using RTILs and also any relationship between the structure of the RTIL (the cation and/or the anion) and the extraction efficiency. Alternatively and/or in addition, there is a need for improved extraction processes using RTILs.
The present invention arises from research into the extraction of precious metals and base metals from aqueous phases into different types of RTILs, and in particular, our finding that RTILs can be used in liquid-liquid extraction of metal ions not only as solvents but also extractants. We have shown that RTILs can be used as effective anion exchange extractants and that the extraction process is fast and highly efficient with extraordinarily high loading capacity. For example, some metals can be extracted quantitatively in one cycle.
In a first aspect, the present invention provides a process for extracting a target metal ion from an aqueous feedstock containing the target metal ion, the process comprising:
wherein the RTIL is substantially free of an extraneous organic extractant.
In some embodiments, the target metal ion is chosen from one or more of the group consisting of: Pt, Pd, Fe, Co, Cu, Sn, Bi, Zn, and Mn.
In some embodiments, the process further comprises recovering the target metal ions or metal from the RTIL.
In some embodiments, the process further comprises treating the aqueous feedstock to increase the concentration of inorganic anions in the feedstock prior to contact with the RTIL. In some embodiments, the inorganic anion is selected from the group consisting of: halide ion, thiocyanate ion, thiosulfate ion, nitrate ion, and perchlorate ion. In some embodiments, the halide ion is selected from iodide, bromide, chloride, and fluoride. In some specific embodiments, the halide ion is chloride.
In some embodiments, the RTIL is selected from the group consisting of: ethyl-3-methylimidazolium bis(trifluoromethanesulfonypimide (emim.NTf2); 1-hexyl-3-methylimidazolium bis(trifluoromethanesulfonypimide (hmim.NTf2); 1-hexyl-3-methylimidazolium hexafluorophosphate (hmim.PF6); 1-dodecyl-3-methylimidazoliumbis(trifluoromethylsulfonypimide (dmim.NTf2); 1-methyl-1-propylpiperidinium bis(trifluoromethylsulfonypimide (mppip.NTf2); 1-methyl-1-propylpyrrolidinium bis(trifluoromethylsulfonyl)imide (mpPyr.NTf2); tradecyl(trihexyl)phosphonium bis(trifluoromethanesulfonyl)imide P14,6,6,6.NTf2); tetradecyl(trihexyl)phosphonium chloride (P14,6,6,6. Cl); methyltrioctylammonium bis(trifluoromethylsulfonyl)imide (N8,8,8,1.NTf2); and butyltrimethylammonium bis(trifluoromethylsulfonyl)imide (N4,1,1,1.NTf2).
In some specific embodiments, the RTIL is tetradecyl(trihexyl)phosphonium chloride (P14,6,6,6.Cl). In these embodiments, the target metal ion may be selected from the group consisting of: Pt, Pd, Cu, Fe, Co, Mn, Zn, Bi, and Sn ions.
In some specific embodiments, the RTIL is 1-hexyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (hmim.NTf2). In these embodiments, the target metal ion may be selected from the group consisting of: Pt, Bi, and Sn ions.
In some specific embodiments, the RTIL is 1-dodecyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (dmim.NTf2). In these embodiments, the target metal ion may be Pt ions.
In some specific embodiments, the RTIL is methyltrioctylammonium bis(trifluoromethylsulfonyl)imide (N8,8,8,1.NTf2). In these embodiments, the target metal ions may be selected from the group consisting of: Pt, Pd, Bi, and Sn ions.
In some specific embodiments, the RTIL is 1-hexyl-3-methylimidazolium hexafluorophosphate (hmim.PF6). In these embodiments, the target metal ion may be selected from the group consisting of: Pt and Pd ions.
Surprisingly, we have found that Sn, Bi, Cu, Zn, Mn, Fe and/or Co ions can be selectively extracted from an aqueous feedstock that also contains Mg, Ca, Al, Cr, and/or Ni ions at 3M HCl concentration using tetradecyl(trihexyl)phosphonium chloride as the RTIL.
We have also found that Sn, Bi, and/or Fe ions can be selectively extracted from an aqueous feedstock containing Mg, Ca, Al, Cu, Zn, Cr, Mn, Co, and/or Ni ions at 3M HCl concentration using 1-hexyl-3-methylimidazolium hexafluorophosphate as the RTIL.
We have further found that Sn, Bi, and/or Fe ions can be selectively extracted from aqueous feedstock containing Mg, Ca, Al, Cu, Zn, Cr, Mn, Co, and/or Ni ions at 3M HCl concentration using methyltrioctylammonium bis(trifluoromethylsulfonyl)imide as the RTIL.
The present invention provides a process for extracting a target metal ion from an aqueous feedstock containing the target metal ion. The process Comprises providing said feedstock. The feedstock may be any aqueous solution, suspension, emulsion, etc containing the target metal ion. Examples of feedstocks include leachates, leach solutions, waste water, nuclear waste, reaction mixtures, etc.
The feedstock is contacted with a room temperature ionic liquid (RTIL) under liquid-liquid extraction conditions for a time sufficient to allow transfer of at least some of the target metal from the feedstock to the RTIL. As used herein, the terms “room temperature ionic liquid”, “RTIL”, and similar terms, mean a salt that is in the liquid state at room temperature. Room temperature ionic liquids consist of a bulky, asymmetric organic cation and a smaller anion and they are liquids at relatively low temperatures (eg below about 100° C.). A range of RTILs are available commercially or can be synthesised using known methods. Specific RTILs that are suitable for use in processes of the present invention have imidazolium, piperidinium, pyrrolidiunium, ammonium or phosphonium cations. The anion of the RTIL may be bis(trifluoromethanesulfonyl)imide, chloride or hexafluorophosphate.
In some embodiments, the RUC, is selected from the group consisting of: ethyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (emim.NTf2); 1-hexyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (hmim.NTf2); 1-hexyl-3-methylimidazolium hexafluorophosphate (hmim.PF6); 1-dodecyl-3-methylimidazoliumbis(trifluoromethylsulfonyl)imide (dmim.NTf2); 1-methyl-1-propylpiperidinhun bis(trifluoromethylsulfonyl)imide (mppip.NTf2); 1-methyl-1-propylpyrrolidinium bis(trifluoromethylsulfonyl)imide (mpPyr.NTf2); tradecyl(trihexyl)phosphonium bis(trifluoromethanesulfonyl)imide P14,6,6,6.NTf2); tetradecyl(trihexyl)phosphonium chloride (P14,6,6,6.Cl); methyltrioctylammonium bis(trifluoromethylsulfonyl)imide (N8,8,8,1.NTf2); and butyltrimethylammonium bis(trifluoromethylsulfonyl)imide (N4,1,1,1.NTf2).
Specific RTILs that we have found to be particularly suitable for use in the processes of the present invention include tetradecyl(trihexyl)phosphonium chloride (P14,6,6,6.Cl), 1-hexyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (hmim.NTf2), 1-dodecyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (dmim.NTf2), methyltrioctylammonium bis(trifluoromethylsulfonypimide (N8,8,8,1.NTf2), and 1-hexyl-3-methylimidazolium hexafluorophosphate (hmim.PF6).
The RTIL may be a pure or semi-pure RTIL or it could be part of a mixture containing, for example, another water immiscible solvent. The RTIL is substantially free of an extraneous organic extractant, the significance, of which will be described in more detail later.
The feedstock can be contacted with the RTIL using any apparatus or technique suitable for liquid-liquid extraction. For example, the feedstock may be contacted with the RTIL by combining the two phases in a suitable vessel and mixing to at least partially disperse the phases in one another. The time taken for mixing will vary depending on the nature of the ion to be extracted, the feedstock, the particular RTIL used, the temperature, etc. Processes for bulk phase solvent extraction are known in the art.
Alternatively, the feedstock and the RTIL may be mixed in a microfluidic liquid-liquid extraction device. The microfluidic liquid-liquid extraction device may be as described herein and/or as described in our co-pending published application WO 2010/022441 titled “Extraction Processes” (the disclosure of which is incorporated herein in its entirety) and/or our co-pending unpublished Australian provisional patent application 2010905349 titled “High Throughput Microfluidic Device” and/or using any of the microfluidic separation techniques known in the art. Briefly, the microfluidic device may comprise a microchip containing an aqueous phase microchannel and an extractant phase microchannel. A pressure driven, co-current laminar flow technique may be applied during the process of solvent extraction in the microchannel, where the aqueous phase and the extractant phase converge at a Y-junction and flow together without mixing along the channel length, before separating at another Y-junction downstream. The residence time for extraction can be manipulated by altering the flow rate of the two phases using syringe pumps.
After the feedstock and the RTIL have been in contact with one another for a time sufficient to allow transfer of at least some of the target metal ion from the feedstock to the RTIL, the RTIL is separated from the feedstock. In most cases, the two phases are physically separated from one another using any of the techniques known for that purpose in the art. For example, in a bulk extraction vessel, the aqueous feedstock may be removed from the bottom of the vessel using a suitable valve located toward the bottom of the vessel.
After separating the RTIL from the feedstock, the target metal ion can be recovered from the RTIL either as ions or as the metal. Methods for recovering metal ions or metals from solvents or solution are known in the art and can be used in the processes of the present invention. For example, the RTILs can be used as electrolytes and, therefore, many of the metals extracted into RTILs, including Pd, Pt, Sn, Bi, Cu and Zn, can be recovered by electro-deposition from the RTILs. The stripping stage that is typically used in conventional solvent extraction is therefore not needed in the processes of the present invention. By way of further example, the RTIL containing the target metal ion can be treated with a reducing agent to reduce metal ions to metals which are then able to be separated from the RTIL.
It will be appreciated from the foregoing description that in the processes of the present invention the RTIL is substantially free of any extraneous organic extractant. This is in contrast to prior art processes described previously which use an organic extractant in the RTIL.
The process may further comprise treating the aqueous feedstock to increase the concentration of inorganic anions in the feedstock prior to contact with the RTIL. In some embodiments, the “inorganic anion” is selected from the group consisting of: halide ion, thiocyanate ion, thiosulfate ion, nitrate ion, and perchlorate ion. In some embodiments, the halide ion is selected from iodide, bromide, chloride, and fluoride. In some specific embodiments, the halide ion is chloride.
The concentration of inorganic anions in the aqueous feedstock can be increased by adding a salt containing the inorganic anion to the feedstock. For example, the concentration of halide ion in the aqueous feedstock can be increased by adding a halide salt to the feedstock. In the case of chloride, suitable halide salts include HCl, KCl, NaCl, NH4Cl, etc. Equivalent iodide, bromide, fluoride, thicyanate, nitrate or perchlorate salts could be used.
In some specific embodiments, the process comprises treating the aqueous feedstock with HCl to increase the chloride concentration in the feedstock prior to contact with the RTIL. The amount of HCl added to the feedstock may depend on the target metal and/or the RTIL used. In some embodiments, the aqueous feedstock is from about 0.01M to about 10M HCl. In some specific embodiments, the aqueous feedstock is from about 0.01M to about 0.090M HCl. In some other specific embodiments, the aqueous feedstock is from about 1M to about 9M HCl. In some other specific embodiments, the aqueous feedstock is from about 2M to about 4M HCl. In some other specific embodiments, the aqueous feedstock is from about 6M to about 9M HCl. In some other specific embodiments, the aqueous feedstock is about 0.02M HCl. In some other specific embodiments, the aqueous feedstock is about 3M HCl. In some other specific embodiments, the aqueous feedstock is about 7M HCl.
In some specific embodiments, the process comprises treating the aqueous feedstock with KCl to increase the chloride concentration in the feedstock prior to contact with the RTIL. The amount of KCl added to the feedstock may depend on the target metal and/or the RTIL used. In some embodiments, the aqueous feedstock is from about 1M to about 9M HCl. In some specific embodiments, the aqueous feedstock is about 3M KCl.
In some embodiments, the process also comprises treating the aqueous feedstock to decrease the pH of the feedstock prior to contact with the RTIL.
The target metal ion may be chosen from one or more of the group consisting of: Pt, Pd, Fe, Co, Cu, Sn, Bi, Zn, and Mn. We have found that certain RTILs show selectivity for some of these metal ions over other metal ions. This means that the processes described herein may be used to selectively extract a target metal ion from an aqueous feedstock solution containing other non-target metal ions.
In some embodiments, the RTIL is tetradecyl(trihexyl)phosphonium chloride (P14,6,6,6.Cl). In these embodiments, the target metal may be selected from the group consisting of: Pt, Pd, Cu, Fe, Co, Mn, Zn, Bi, and Sn.
In some embodiments, the RTIL is 1-hexyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (hmim.NTf2). In these embodiments, the target metal may be selected from the group consisting of: Pt, Bi, and Sn.
In some embodiments, the RTIL is 1-dodecyl-3-methylimidazolium bis(trifluoromethanesulfonyl)imide (dmim.NTf2). In these embodiments, the target metal may be Pt.
In some embodiments, the RTIL is methyltrioctylammonium bis(trifluoromethylsulfonyl)imide (N8,8,8,1.NTf2). In these embodiments, the target metal may be selected from the group consisting of: Pt, Pd, Bi, and Sn.
In some embodiments, the RTIL is 1-hexyl-3-methylimidazolium hexafluorophosphate (unim.PF6). In these embodiments, the target metal may be selected from the group consisting of: Pt and Pd.
Surprisingly, we have found that Sn, Bi, Cu, Zn, Mn, Fe and/or Co ions can be selectively extracted from aqueous feedstock that also contains Mg, Ca, Al, Cr, and/or Ni ions at 3M HCl concentration using tetradecyl(trihexyl)phosphonium chloride as the RTIL.
We have also found that Sn, Bi, and/or Fe ions can be selectively extracted from aqueous feedstock containing Mg, Ca, Al, Cu, Zn, Cr, Mn, Co, and/or Ni ions at 3M HCl concentration using 1-hexyl-3-methylimidazolium hexafluorophosphate as the RTIL.
We have further found that Sn, Bi, and/or Fe ions can be selectively extracted from aqueous feedstock containing Mg, Ca, Al, Cu, Zn, Cr, Mn, Co, and/or Ni ions at 3M HCl concentration using methyltrioctylammonium bis(trifluoromethylsulfonyl)imide as the RTIL.
The performance of specific ionic liquids on the extraction of Pt and Pd from 0.02 and 3 M HCl solutions is shown in
The invention is hereinafter described by way of the following non-limiting examples.
All RTILs used in this investigation (listed below) were purchased from IoLiTec, Germany, except for tetradecyl(trihexyl)phosphonium bis(trifluoromethanesulfonyl)imide, which was purchased from Strem Chemicals, USA. Five types of cations were studied: imidazolium (Im), piperidinium (Pip), pyrrolidinium (Pyr), ammonium (N) and phosphonium (P). In all cases the anion was bis(trifluoromethanesulfonyl) imide (NTf2). The anions hexafluorophosphate (PF6) and chloride (Cl) were further chosen for hmim and phosphonium cations, respectively. Imidazolium and ammonium cations with different chain lengths were also used.
Fifteen metals were tested. Precious metal salts of AR grade, PdCl2, and H2PtCl6.×H2O, were purchased from Sigma-Aldrich. AR grade CuCl2.2H2O, MgCl2.6H2O, AlCl3.6H2O and CaCl2 were purchased from Chem-Supply. AR grade BiOCl, SnCl2.2H2O, MnCl2.4H2O, FeCl3.NiSO4.×H2O and CrCl3.6H2O were obtained from BDH. AR grade CoCl2.6H2O was purchased from Merck.
All metal salts were dissolved in pure water with different HCl concentrations (typically 0.02, 3 and 7 M HCl). Stock solutions of the precious metals were prepared: 500 ppm PdCl2 and 1000 ppm H2PtCl6. The concentrations of copper and nickel were 5 and 15 g/L, respectively. For all other metals, the concentration of metal salt was 10 g/L.
0.5 ml RTIL and 2 ml aqueous solution containing metal ions were added into a small glass vial. They were mixed vigorously with a magnetic stirrer for 30 min to achieve equilibrium distribution. When extraction was completed, the solution was left overnight to phase separate. After that, the aqueous phase was carefully removed and used for UV or ICP measurement.
SiO2 nanoparticles (R816) were purchased from Degussa. The primary particle size is 12 nm and the water contact angle is 30-40°. 5 g/L of copper solution was prepared in 0.02 and 3 M HCl, as well as in 3 M KCl solution. SiO2 nanoparticles (5 g/L) were then added, in the above solution and sonicated for 30 min before extraction. The copper solution loaded with SiO2 nanoparticles was extracted with P14,6,6,6.Cl under the same conditions as described above.
Extraction percentage is defined as the amount of solute in the ionic liquid phase (after extraction) divided by the amount in aqueous phase (before extraction). UV-vis and ICP techniques were used to determine the concentration of metal ions in the aqueous solutions before and after extraction. For precious metals and Cu, Ni, Fe, and Co, the UV-vis absorption spectra in the aqueous phase were recorded. The absorbance at a given wavelength (HAuCl4 at 310 nm, PdCl2 at 429 nm, H2PtCl6 at 375 nm CuCl2 at 807 nm NiCl2 at 393 nm, FeCl2 at 337 nm and CoCl2 at 510 nm) was used to calculate the extraction percentage as:
E %=[(A0−A*)/A0]×100
For all other metals, the ICP technique was used to measure the concentration of metal ions in aqueous solution after extraction. The extraction percentage was calculated as:
E %=[(C0−C*)/C0]×100
The distribution ratio is defined as the concentration of the solute in the ionic liquid divided by its concentration in the aqueous phase:
D=[M]
IL
/[M]
aq
The relationship between extraction percentage and distribution ratio is:
E=100D/[D+(Vaq/VIL)]
In our study, the volume ratio of ionic liquid and aqueous phase is not equal to 1. The distribution ratio is therefore calculated as:
D=[(C0−C*)/C0]×Vaq/VIL
RTILs can also be used to extract base metals. Cu extraction was carried out under the same conditions as those used for the precious metals. The results for Cu extraction with different RTILs from 0.02 M and 3 M HCl solutions are shown in
In order to understand the extraction mechanism of base metals, the extraction of Fe, Co and Cu using P14,6,6,6.Cl was conducted under different conditions. The extraction results along with the corresponding distribution ratios are shown in
Iron can be extracted (E ˜70%) even from neutral water. The extraction percentage reached nearly 100% in 3 and 7 M HCl solutions (the distribution ratio was above 3000 in 7 M HCl). Cobalt is not extracted efficiently from neutral water. With increasing HCl concentration, the extraction percentage increases significantly. For copper, no extraction was observed from neutral water. This indicates that, for example, Fe can be selectively extracted from an aqueous feedstock containing Fe, Co and/or Cu ions at neutral pH. However, the extraction percentage of Cu increased dramatically in 3 and 7 M HCl solution. The extraction percentage in 3 M KCl solution was comparable to that in 3 M HCl. Under these conditions, added SiO2 nanoparticles did not have a significant influence on the extraction percentage. When compared with SiO2 loaded-organic solvent/aqueous system where particle-stabilized emulsions are formed, RTIL/aqueous system did not show the same phenomena. As the aqueous phase was clear and no apparent UV absorption was observed, SiO2 particles were likely transferred to the RTILs (which were opaque, though clear when free of SiO2 particles).
The phenomena observed showed that it is possible to extract base metals effectively when using RTILs including hmim.PF6, N8,8,8,1.NTf2 and P14,6,6,6.Cl under high chloride concentrations. Based on these observations, the extraction of other metals, including Mg, Ca, Al, Sn, Bi, Zn, Cr, Mn and Ni, from 3 M HCl was carried out. The results are shown in
It was observed that phase separation can be completed in one to two minutes in most cases. Phase separation time increased with an increase of hydrocarbon chain length. It can take several hours for RTILs with longer chain lengths (≧12 CH2 units) at low HCl concentrations to complete phase separation. However, it was improved dramatically at high HCl or salt concentrations, where phase separation took only a few minutes.
Anion exchange extraction is a process where metal complex anions move from an aqueous phase to an organic phase, while anions in the organic phase transfer from the organic phase to the aqueous phase. Metal complex anions are surrounded by water molecules and interact with cations in the aqueous phase. When they leave the aqueous phase, they absorb the hydration energy, ΔEhy, as well as the ion association energy, ΔEas-w, releasing cavitation energy in the aqueous phase, −ΔEw-w. During transfer, they absorb cavitation energy, ΔE0-0, to enter into organic phase, meanwhile releasing solvation energy with organic molecules, −ΔEsol, as well as ion association energy with cations in organic phase, −ΔEas-o. Ignoring any entropy change, the free energy change during transfer of metal complex anions can be described by equation 1 (Al-bazi and Chow 1984; Zhang 1984; Yu 2004):
ΔEA-W=(ΔEhy−ΔEsol)A-W+ΔEw-w+ΔE0-0)A-W−(ΔEas-w−ΔEas-o)A-W (1)
Three types of energy are thus involved during this process, which are solvation energy, cavitation energy and ion association energy. Solvation or Hydration energy is proportional to the charge density of ions, while cavitation energy is inversely proportional to charge density. Ion association energy can be expressed by the ion-pair formation constant, which follows Bjerrum's equation for purely Coulombic attraction (Morrison and Freiser 1957):
where N is Avogadro's number, e is the unit of charge, E is the dielectric constant of the medium, k is the Boltzmann constant, T is the absolute temperature,
is a calculable function, and α is an empirical parameter which represents the distance between charge centres of the paired ions when in contact. If the temperature is constant, it is evident that ion association depends on the values of α and ∈, decreasing with increasing α and ∈ values. However, if specific interactions between the paired ions occur, greatly increased stability would result. In most cases, it is expected that ΔEhy>>ΔEsol, ΔEw-w>>ΔE0-0 and ΔEas-w<<ΔEas-o, therefore, ΔEMA can be simply described by equation 2:
ΔEA-W=(ΔEhy)A-W−(ΔEw-w)A-W−(ΔEas-o)A-W (2)
When anions in the organic phase transfer to the aqueous phase, the free energy change follows the equation 3:
ΔEA-O=−(ΔEhy)A-O+(ΔEw-w)A-O+(ΔEas-o)A-O (3)
Therefore, the total free energy change of anion exchange extraction follows the equation 4(Al-bazi and Chow 1984; Mooiman 1993; Yu 2004):
It is evident that when the charge density of metal complex anion in aqueous phase is small, where (ΔEhy)A-W is small and (ΔEw-w)A-W is large, metal complex anions have a high probability of transferring to the organic phase. Vice versa, when the charge density of anion in organic phase is big, where (ΔEhy)A-O is large and (ΔEw-w)A-O is small, the tendency for anions transfer to aqueous phase is enhanced. However, the contribution of the ion association energy depends on the volume of anions when specific interaction can be neglected. A smaller sized metal complex anion and larger sized anion in organic phase tend to improve anion exchange. In most cases, the contribution from hydration energy is generally higher than those from cavitation and solvation energies, when any specific interaction is neglected.
The phenomena observed in this study can be well explained by anion exchange extraction. As there are not enough data in the literature to obtain the actual value of charge density, the estimated value is calculated using charge of an ion divided by the number of atoms forming the ion. The charge density of anions of Cl−, PF6− and NTf2− is thus calculated and the corresponding values are 1, 0.143 and 0.067, respectively. Precious metals Pt and Pd, in HCl solution present in the form of chloride complex as PtCl6− and PdCl42−. The corresponding charge density is 0.286 and 0.4, respectively. Therefore, the extraction percentage decreased in the order of PtCl6− >PdCl42− for metal chloride complex and in the order of Cl−>PF6−>>NTf2− for anion in RTIL phase as shown in
The charge density of bare base metal ions, Mn+, is n, indicating that bare metal ions have high hydration energy and tend to stay in aqueous phase. In order to lower charge density, complexation needs occur to reduce charge and enlarge the volume of metal ions. Bare metal ions are highly hydrated in aqueous solution. In order to form complex, ligands need to replace water molecules associated with metal ions. When the charge density is low enough for anion exchange, extraction occurs. Therefore, the process of extraction of base metal ions involves two steps: complexation and transfer. During complexation, it is expected that higher concentration of ligands present in the solution, more metal complex is formed, and thus higher extraction percentage is observed as shown in
In HCl solution, different metal ions, however, have different affinity to water molecules and chloride ions. According to the Hard Soft Acid Base (HSAB) principle, both water molecule and chloride ion are hard bases, but the former is harder than the latter. For group A metals, group I and II A metals belong to hard acid. When the order of group A metals move from IA to VA, the hardness decreases, vice versa, the softness increases. The well-accepted empirical rule is that ‘hard likes hard and soft likes soft’, indicating group I and II A metals have higher affinity to water molecules, so they are highly hydrated and tend to stay in water. Therefore, even phCl can only extract group I or II A metals to a very low extent. The aluminium ions, Al3+, in group IIIA belongs to hard acid because of high charge and small ion radii, so it showed the same trend as group I and II A metals. However, group N and V A metals are less hard, which would show high affinity to chloride ions. Group N and V A metal ions thus interact with chloride ions to form chloride complex, facilitating the anion exchange and high extraction percentage was observed as shown in
As for group B transition metals, Cr3+ and Mn2+ belong to hard acids, while Zn2+ and Cu2+ are borderline acids. The hardness follows the order of Cr3+>Mn2+>Zn2+≅Cu2+, resulting in the order of extraction percentage as Cr3+<Mn2+<Zn2+≅Cu2+. However, HSAB principle cannot explain the extraction behaviour of group HIV B metals. Fe3+ is a hard acid, while Co2+ and Ni2+ are borderline acids. The order of hardness is Fe3+>Co2+>Ni2+, so is the extraction percentage. This phenomenon might be attributed to the different tendency of metal′ions to form a chloride complex, which plays a vital role in the anion exchange extraction. From the UV spectra of metal ions presented in different HCl concentrations, it was found that FeCl3 presented in chloride complex form even in neutral water, and CoCl2 existed in hydrated form in neutral water and changed to chloride complex in high HCl concentrations, while NiCl2 only presented in hydrated form in all HCl concentrations. Therefore, Fe3+ can be extracted efficiently in all HCl concentrations, Co2+ can be extracted well in high HCl concentrations, but Ni2+ cannot be extracted in all HCl concentrations as seen in
For conventional organic solvent/water systems, when hydrophobic SiO2 nanoparticles are present in aqueous solution, SiO2 nanoparticles tend to transfer to organic solvent/water interface and form particle-stabilized emulsion during mixing. However, this phenomenon was not observed at RTIL/water systems in most cases, which might be attributed to the different interfacial tensions between these two systems. For the latter, SiO2 nanoparticles cannot attach to the RTIL/water interface and, therefore, particle-stabilized emulsion cannot form. RTILs with longer hydrocarbon chain length tend to form micelle in aqueous phase, a prolonged phase separation time was observed. However, the formation of micelles can be prevented in high salt concentrations and rapid phase separation was achieved.
In summary, we have shown that extractions of metals including Pt, Pd, Mg, Ca, Al, Sn, Bi, Cu, Zn, Cr, Mn, Fe, Co and Ni using pure RTILs can be carried out in HCl solutions. The extraction efficiency increased dramatically for group A metals moving from IIA to VA, while it decreased significantly for group B metals moving from IB to IIVB. The extraction percentage decreased in the order of Fe>Co>>Ni for group IIIVB metals.
The influence of anion on extraction percentage showed in the order of Cl>PF6>>TFSI. The increase of hydrocarbon chain length can enhance the extraction. Cations did not show much influence on extraction except for ammonium cation. The extraction behaviour of metal ions using RTILs can be well described by anion exchange mechanism. RTILs can be used not only as solvent medium, but also novel effective liquid anion exchange extractants. Phase separation can be completed in a few minutes for RTILs with shorter chain length. RTILs containing long hydrocarbon chain showed slow phase separation, however, it can be improved effectively at high chloride concentrations. It was observed that SiO2 nanoparticles did not show much influence on Cu extraction. For RTIL/Water system, no particle-stabilized emulsion was observed for copper extraction containing hydrophobic SiO2 nanoparticles in the solution.
All RTILs used in this investigation (listed below) were purchased from IoLiTec, Germany, except for tetradecyl(trihexyl)phosphonium bis(trifluoromethanesulfonyl)imide, which was purchased from Strem Chemicals, USA. Five types of cations were studied: imidazolium (Im), piperidinium (Pip), pyrrolidinium (Pyr), ammonium (N) and phosphonium (P). In all cases the anion was bis(trifluoromethanesulfonyl) imide (NTf2). The anions hexafluorophosphate (PF6) and chloride (Cl) were further chosen for hmim and phosphonium cations, respectively. Imidazolium and ammonium cations with different chain lengths were also used.
Precious metal salts of AR grade, HAuCl4.3H2O PdCl2, and H2PtCl6.×H2O, were purchased from Sigma-Aldrich.
All metal salts were dissolved in MilliQ water of different HCl concentrations (typically 0.02, 0.1 and 2 M HCl, respectively). The concentration of Au, Pt and Pd in the mixture was measured using ICP.
0.5 ml RTIL and 2 ml aqueous solutions containing metal ions were added into a small glass vial. They were mixed vigorously with a magnetic stirrer for 30 min to achieve equilibrium distribution. When extraction was completed, the solution was left overnight to phase separate. After that, the aqueous phase was carefully removed and used for ICP measurement.
Glass microfluidic chips (IMT, Japan) containing two microchannels (100 μm×40 μm), that merge temporarily to form a liquid-liquid interface between the flowing aqueous and organic phases, were used for the microfluidic solvent extractions and details of these are shown in
Liquids were introduced into the microchip using precision syringe pumps (KD Scientific) with glass syringes (Hamilton, 1 mL and 2.5 mL) that were fitted with PEEK adaptors and tubing (Upchurch Scientific, 150 μm inner diameter). The microchip experiments were monitored optically (Olympus microscope, BH2-UMA, with a Moticam 2000 digital camera). Different flow rates (up to ˜10 ml/h) and two different liquid-liquid contact lengths, L (80 or 240 mm) were used to access a wide range of extraction times (Priest, Zhou et al. 2011).
Extraction percentage is defined as the amount of solute in the ionic liquid phase (after extraction) divided by the amount in aqueous phase (before extraction). ICP techniques were used to determine the concentration of metal ions in the aqueous solutions before and after extraction. The extraction percentage was calculated as:
E %=[(C0−C*)/C0]×100
Distribution ratio (DR) is defined as the concentration of solute in the ionic liquid phase divided by its concentration in aqueous phase after extraction. It was calculated as:
DR=[M]IL/[M]Aq.
Separation factor (SF) of A to B from A and B mixed solution is calculated as:
SF=DRA/DRB
The selective extraction of Au versus Pt and Pd from HCl solutions using pure RTILs was carried out in conventional batch solvent extraction. The influence of different ionic liquids on the extraction of Au, Pt and Pd from Au, Pt and Pd mixtures dissolved in 0.02, 0.1 and 2 M HCl solutions is shown in
The distribution ratio describes how well a substance can be extracted, while the separation factor describes how well two substances can be separated from their mixture. The distribution ratios of Au, Pt and Pd in 2 M HCl concentration, as well as the separation factors of Au/Pt, Au/Pd and Pt/Pd are listed in Table 1. It can be seen that Au can be extracted very well by all RTILs selected with extraction percentages above 90% in most cases. Except for P14,6,6,6.Cl, which can extract effectively all metals, hmim.PF6 can extract Pt and Pd to a moderate extent. For all other RTILs selected, Pt and Pd cannot be extracted efficiently. Good selectivity for Au extraction can be found using RTILs including emim.NTf2, mppip.NTf2, mppyr.NTf2, N4,1,1,1.NTf2 and P14,6,6,6.NTf2. It was found that above 85% of gold was extracted using the five RTILs mentioned above, while less than 5% of Pt and Pd were extracted. To separate Pt from Pd, dmim.NTf2, hmim.NTf2 and hmim.PF6 are effective from 2 M HCl solution. Continuous separation of Au, Pt and Pd from their mixture can be achieved by first choosing one of the RTILs such as emim.NTf2, mppip.NTf2, mppyr.NTf2, N4,1,1,1.NTf2 and P14,6,6,6.NTf2 to extract Au, then using hmim.PF6 to extract Pt, whilst Pd will be left in the feed solution.
The extraction of Au, Pt and Pd from their mixtures at 0.1 M HCl solution was carried out in a microchannel. ICP was used to measure the concentration of metals in the solution before and after extraction. The extraction percentage of Au, Pt and Pd as a function of residence time using hmimNTf2 is shown in
In summary, the extraction of precious metals including Pt and Pd from their mixtures in HCl solutions using pure RTILs was carried out in both bulk and microchannels. The influence of anion on extraction percentage showed in the order of Cl>PF6>>TFSI. The increase of hydrocarbon chain length can enhance the extraction. Highly selective extraction and continuous separation of Au, Pt and Pd can be achieved by choosing suitable RTILs and adjusting the HCl concentration.
It will be appreciated by persons skilled in the art that numerous variations and/or modifications may be made to the invention as shown in the specific embodiments without departing from the spirit or scope of the invention as broadly described. The present embodiments are, therefore, to be considered in all respects as illustrative and not restrictive.
Throughout this specification the word “comprise”, or variations such as “comprises” or “comprising”, will be understood to imply the inclusion of a stated element, integer or step, or group of elements, integers or steps, but not the exclusion of any other element, integer or step, or group of elements, integers or steps.
All publications mentioned in this specification are herein incorporated by reference. Any discussion of documents, acts, materials, devices, articles or the like which has been included in the present specification is solely for the purpose of providing a context for the present invention. It is not to be taken as an admission that any or all of these matters form part of the prior art base or were common general knowledge in the field relevant to the present invention as it existed in Australia or elsewhere before the priority date of each claim of this application.
Number | Date | Country | Kind |
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2010905533 | Dec 2010 | AU | national |
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/AU2011/001633 | 12/16/2011 | WO | 00 | 6/20/2014 |