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Article

Application of Ion Exchange for Recovery of Noble Metals

1
Łukasiewicz Research Network-Institute of Non-Ferrous Metals, Sowińskiego 5, 44-100 Gliwice, Poland
2
Department of Inorganic Chemistry, Analytical Chemistry and Electrochemistry, Faculty of Chemistry, Silesian University of Technology, B. Krzywoustego 6, 44-100 Gliwice, Poland
*
Author to whom correspondence should be addressed.
Minerals 2021, 11(11), 1188; https://doi.org/10.3390/min11111188
Submission received: 23 September 2021 / Revised: 18 October 2021 / Accepted: 20 October 2021 / Published: 26 October 2021

Abstract

:
The production of noble metals has started to shift towards using different types of wastes. The leaching solutions collected during the processing of waste have low concentrations of noble metals; therefore, it forces the use of sorption methods in recovery technology. This work focused on recovering noble metals with a technological solution, obtained during the processing of waste from refining processes. The research consisted of a set of experiments using a batch method that enabled determination of the parameters of the process and selection of the leading resins. Sorption isotherms were determined and kinetic studies were conducted, along with the preliminary elution tests with the use of different eluents. Cementation experiments were the final part of the research. During the experiments, it was concluded that the leading resins for the sorption of noble metals were Puromet MTS9200, Puromet MTS9850, and Lewatit K 6362. The volume ratio Vr:Vs = 1:10 and the reaction time 15–30 min could be used as basic conditions to conduct the experiments in the column; the solution of thiourea in hydrochloric acid can be used as an eluting agent from which noble metals could be cemented using powder zinc.

1. Introduction

Noble metals, such as platinum, palladium, rhodium, and gold, are some of the most valuable elements due to their exceptional properties, such as high chemical and thermal resistance, which directly leads to their wide applicability in the electrical, jewelry, and automotive industries [1,2,3,4]. Due to their scarcity in the deposits naturally occurring in the Earth′s crust, the current manufacturing tendency is slowly shifting to obtaining them from secondary raw materials, e.g., automotive catalysts, computer parts, and other electronic equipment [5,6,7]. Recovering noble metals from such sources is not an easy task, due to the similarity of their properties and the presence of other metals such as copper, iron, and zinc, which often hinder the recovery process [8,9]. The leaching solutions obtained in the process of dissolution of wastes have low concentrations of noble metals, which makes using traditional methods such as selective precipitation or extraction practically ineffective. Therefore, to be able to recover noble metals from those solutions sorption technologies have to be introduced into the process.
Ion exchange has been researched in noble metal recovery technology for quite some time due to a number of advantages, such as the low cost of exploitation, low energy consumption, the possibility of regenerating the resins, long life span of the resins, price, selectivity, high efficiency, and the simple process apparatus [10]. Over the years, many resins have been researched in terms of noble metal recovery from different types of solutions, mostly synthetic ones [11,12,13,14,15]. Although conducting experiments using a premade synthetic solution provides a large database of information helping to plan further tests, introducing industrial solutions very often results in uncovering another set of problems for the researchers to resolve before being able to use the tested materials in the real processes. Currently, more research is focusing on recovering PGM and gold from industrial-like solutions instead of synthetic ones [16,17]. Nevertheless, many more tests have to be conducted to obtain a knowledgeable database that would be able to quickly and easily transfer laboratory experiments to the industry.
Therefore, the aim of this research is to examine the applicability of the commercial ion exchange resins in the technology of recovery of noble metals, such as platinum, palladium, rhodium, and gold, from a technological solution. The solution used in the experiments came from the leaching of different types of waste obtained from the refining processes of noble metals, hence its complex composition. Many publications concentrate on obtaining elements from one type of waste, e.g., automotive catalysts, WEEE (Waste of Electrical and Electronic Equipment), or computer elements, which is undoubtedly important, although not a lot of attention is paid to obtaining noble metals from the waste produced during the refining process. The technological solution used in the experiments came from leaching of that type of waste.

2. Materials and Methods

2.1. Materials

Puromet MTS9200, Purolite MTS9850, and Puromet MTS9100 were supplied by Purolite (King of Prussia, PA, USA); Lewatit MonoPlus TP 214 and Lewatit K 6362 were provided by Lanxess Energizing Chemistry (Cologne, Germany). Depending on the functional group, they are strong or weak basic ion exchangers and are supplied in a form of spherical beads. Their main characteristics are reported in Table 1.
Noble metal concentrates and wastes (e.g., filters and precipitates) were supplied by the Łukasiewicz Research Network-Institute of Non-Ferrous Metals (Łukasiewicz-IMN, Gliwice, Poland) and used as the sources of metals for the technological solution. Nitric acid (65%, AR, Avantor, Gliwice, Poland) and hydrogen peroxide (30%, AR, Avantor, Gliwice, Poland) were applied for leaching of the waste materials and concentrates. Hydrochloric acid (35–38%, AR, Avantor, Gliwice, Poland) was used for the leaching, conditioning, and elution experiments. Ammonium thiocyanate and thiourea (AR, Avantor, Gliwice, Poland) were applied for the elution experiments. Zinc powder was supplied by the Łukasiewicz-IMN (Gliwice, Poland) and used for the cementing of noble metals from eluates. Distilled water (<2 μS/cm) was used in the experiments. A rotary shaker (330 rpm; CERTOMAT MO II, Sartorius, Göttingen, Germany) was used to mix the solutions and resins.
The technological solution used in the research (belonging to the Łukasiewicz-IMN) was obtained from the concentrates and precipitates produced during the refining process of noble metals, containing low percentages of them. Below we present a simplified scheme of the noble metal refining process developed by the Łukasiewicz Research Network-Institute of Non-Ferrous Metals, the Centre of Hydroelectrometallurgy (Figure 1).
The refining steps, such as filtration, precipitation, concentration, or reduction, generate a large amount of waste, including waste solutions, filters, precipitates, or concentrates, all of which contain low concentrations of noble metals. Such materials were leached with a mixture of hydrochloric acid, nitric acid, and hydrogen peroxide, and the solution obtained during this process was used in the following experiments.
Table 2 and Table 3 show the composition of the solution obtained by the semiquantitative analysis and quantitative analysis.
Aside from the noble metals (such as platinum, palladium, rhodium, and gold), the solution also contained significant amounts of copper and zinc, which are often found in the industrial solutions [8].
The results from Table 3 were used as the basic parameters of the technological solution.

2.2. Methods

2.2.1. Conditioning of the Resins

The resins were conditioned with 10% (w/w) HCl. This stage was conducted to ensure that all the functional groups were activated and, therefore, were able to exchange ions.
The measured by volume amounts of chosen resins were submerged in distilled water and stirred for about 20 min, to remove any physical contamination. The resins were filtered and 10% HCl was added in a 1:1 volume ratio (Vresin:VHCl). The mixture was stirred at room temperature for about 1 h and then filtered. The resins were then washed with distilled water, until the pH of the washing water was around 5. Resins prepared this way were used in the further experiments.

2.2.2. Batch Experiments

First, from a larger group of ion exchangers, a smaller number of resins was selected to be used in the further research. In this stage, 5 resins were bought, and 3 were selected for the following experiments based on the noble metal recovery of the initial tests.
The yields were calculated according to the formula:
SY = C i C f C i × 100 %
SY—sorption yield (recovery), %; Ci = initial concentration of the metal in the solution, mg/dm3; and Cf—final concentration of the metal in the solution, mg/dm3.
In total, 50 cm3 of technological solution was added to 10 cm3 of resin and the mixture was stirred for an hour at room temperature (Vr:Vs = 1:5, Vr—volume of the resin, vs.—volume of the solution). At the end of the process, the resin was filtered and the solution analyzed. The same experiment was conducted for every resin. The selected resins were then used in the next stage of research.
For each resin, the sorption isotherm was plotted. For this purpose, the sorption of platinum, palladium, gold, and rhodium was studied under more detailed batch experiment conditions; different volumes of resins (10–60 cm3) were mixed with different volumes of technological solution (30–100 cm3) to conduct experiments with different Vr:Vs ratios. The mixtures were stirred in the rotary shaker for 1 h. These sorption processes were repeated for each selected resin.
Kinetic studies were also conducted during which the resins were mixed with the technological solution for various durations (5–60 min), using Vr:Vs = 1:2 ratio.
The samples of resins were then used to check how many steps were needed to obtain technological solution with the concentrations of noble metals < 5 mg/dm3, which could be treated as a waste. The resins were mixed with the technological solution in the volume ratio of Vr:Vs = 1:10 for 30 min. After the designated time the mixture was filtered, part of the solution was analyzed, and the rest was mixed with a fresh batch of conditioned resin, still in the same conditions. The process was repeated six more times.

2.2.3. Elution Experiments

Resins samples from the tests with different ratios were used in the elution tests with different eluents using a batch method. The eluents were as follows: 10% HCl, 2 mol/dm3 ammonium thiocyanate, 2 mol/dm3 ammonium thiocyanate in 10% HCl, and 1 mol/dm3 thiourea in 2 mol/dm3 HCl.
The samples were washed with distilled water until the water pH was around 5. The resins were then contacted with the eluents for 1 h in the volume ratio of Vr:Vs = 1:5. At the end of the process, the resins were filtered and the solutions analyzed.
The yields were calculated according to the formula:
EY = C f C i × 100 %
EY—elution yield (recovery), %; Ci—initial concentration of the metal in the resin, mg/dm3; and Cf—final concentration of the metal in the solution, mg/dm3.

2.2.4. Cementation Experiments

We mixed together the solutions after the elution experiments using 1 mol/dm3 thiourea in 2 mol/dm3 HCl. These were used for the cementation experiments using Zn powder.
Four different amounts of zinc (0.1 g, 0.5 g, 1.0 g, and 2.0 g) were added separately to 20 cm3 of eluate and then each was stirred for 1 h using a rotary shaker. The residues were then filtered and the solutions analyzed.
The yields were calculated according to the formula:
CY = C i C f C i × 100 %
CY—cementation yield (recovery), %; Ci—initial concentration of the metal in the solution, mg/dm3; and Cf—final concentration of the metal in the solution, mg/dm3.

2.2.5. Analytical Methods

The analyses were carried out by the Łukasiewicz Research Network-Institute of Non-Ferrous Metals, the Department of Analytical Chemistry (Gliwice, Poland). The concentrations of platinum, palladium, rhodium, and gold in the collected solution samples were determined by Inductively Coupled Plasma Mass Spectrometry (ICP-MS; NexION 300D, PerkinElmer, Waltham, MA, USA). Copper and zinc were analyzed via Flame Atomic Absorption Spectroscopy (FAAS; SOLAAR S4, Thermo, Waltham, MA, USA). The semiquantitative analysis was determined using Inductively Coupled Plasma Mass Spectrometry (ICP-MS; NexION 300D, PerkinElmer, Waltham, MA, USA). The average error of the method was between 10% and 20%, depending on the dilution of the samples and the concentration of noble metals.

3. Results and Discussion

3.1. Batch Experiments

3.1.1. Selection of the Ion-Exchange Resins

Sorption yields of the ion exchange resins selection experiments are presented in Table 4.
In addition to platinum, palladium, rhodium, and gold, copper and zinc were taken into account during the selection process, because they are the most common impurities present in industrial solutions directed to the ion-exchange process. Their concentration in the solution was high; therefore, they could influence the sorption process.
According to the data in Table 4, it was possible to recover noble metals with a high yield, oscillating even around 99%. It is common knowledge that platinum, palladium, and gold are the metals that easily undergo ion exchange, while rhodium is the hardest one to sorb on resins [12]. This is visible in the results in Table 4 because the sorption yields of Pt, Pd, and Au were around 99%, whereas rhodium could only be recovered with the yield around 70%.
The main factor eliminating specific resins from further tests was the uptake of copper and zinc in comparison to the rest of noble metals. That is because the resins chosen for specific industrial processes should be selective, even in a complex solution that could be fed into the technology. Heeding this line of thinking, Lewatit MonoPlus TP 214 was immediately excluded from further research (Zn yield = 69.31%, Cu yield = 99.17%). Puromet MTS9100 was also rejected due to the lower intake of Pt (yield = 74.18%) and Rh (yield = 43.26%) in comparison to the other ion-exchange resins. The remaining resins—Puromet MTS9200, Puromet MTS9850, Lewatit K 6362—were then used in the more specific and detailed batch experiments.
It is also worth noting that the concentration of Pd and Au in the post-process solution was <5 mg/dm3. Thus, this type of solution could be used to recover rhodium and platinum and later treated as a waste.

3.1.2. Sorption Isotherms

Figure 2 shows the correlation between the sorption yields of the individual noble metals and the volume ratio of the process (Vr:Vs).
It is noticeable that platinum, palladium, and gold can be recovered with the yields around 99% in almost every case. The only exception is the behavior of gold while using Puromet MTS9850. In this case, Au behaves like Rh, so the sorption yields raise with the higher resin to solution volume ratio. Rhodium can be recovered with the yield around 90% only using the higher ratios (Vr:Vs = 1:1 or 2:1), which is not a condition that can be used in any industrial technology. This means that the process needs to be refined, possibly with the addition of another step of recovering rhodium. Changing the parameters of the inputted solution is also not excluded. Specific sorption isotherms were determined and are presented in Figure 3.
According to the isotherms shown in Figure 3, not all of them obeyed the laws of typical Langmuir or Freundlich isotherms—two of most popular and known models [17,18,19].
The most exceptional case was gold, where the plot was only moderately similar to the traditional isotherm while using Puromet MTS9850. The reason for that could be the quick way the gold undergoes the ion exchange process, so even in lower volume ratios its concentration in the resin is too high to determine the isotherm. However, it is also possible that the ion exchange of gold transpires not according to Langmuir or Freundlich isotherm laws. Nevertheless, the results confirmed the theory that gold was the first one to undergo the ion exchange process. In every example, it was possible to recover gold with a high yield, leaving only trace amounts in the solution (~0.1 mg/dm3), which is an amount impossible to recover.
The graphs for platinum and palladium were relatively similar, with points of palladium isotherm being closer to lower concentrations of this element in the post-process solution. In every example it was possible to recover palladium with a high yield, leaving only trace amounts in the solution (~0.5 mg/dm3). In the case of platinum, the process became more problematic due to the lessening amount of free space, which could recover the remaining metals from the solution after gold and palladium. It results in slightly lower yields of the platinum sorption and the overall process. Near the lower volume ratios, platinum remained in the solution in concentrations greater than 5 mg/dm3, which means that additional steps of processing and recovery need to be undertaken.
The classic isotherms were visible only in the graphs related to rhodium. It was the last element to undergo the ion-exchange process. Similar to platinum, the process was hindered by the amount of free functional groups, but also the inert character of the element.
Nevertheless, in most cases satisfactory results could be obtained by conducting the ion-exchange process with the ratio of Vr:Vs = 1:10, which is a ratio that can be used on an industrial scale.

3.1.3. Kinetic Studies

Diagrams showing the relation between the time and the sorption yields are presented below. The ratio Vr:Vs = 1:2 was chosen due to the fact it allowed maximization of the recovery of all noble metals in the process, which was conducted for 1 h. After the experiment, neither gold nor palladium were analyzed in the solution.
Figure 4 clearly shows that in terms of platinum, the time does not influence the sorption yields to a high extent [17]. At almost every point of time, the yield was above 98%. However, to obtain the solution with the Pt concentration below 5 mg/dm3, the process needs to be conducted for at least 15 min.
In the case of rhodium, Figure 4 presents mostly upward trends (for Puromet MTS9200 and Lewatit K 6362). In no case was the reaction yield above 90%, although the trend would indicate that obtaining such a result would be possible only after conducting the process for a long enough time, taking into account the possibility of sorbing other elements remaining in the solution. For all three resins, after 15 min the sorption yield was above 80%, which is an optimistic result, one that could be used later in dynamic studies.

3.1.4. Determination of the Sorption Yield Depending on the Number of Process Steps

The possibility of obtaining the post-process solution, by increasing the number of steps, consisting of less than 5 mg/dm3 of each metal was checked. The results are presented in Table 5 and Figure 5.
The results presented in Table 5 show that it is possible to recover platinum after two steps to the level of 5 mg/dm3 remaining in the post-reaction solution. In the case of rhodium, even conducting seven steps with a fresh batch of resin on the same solution did not result in a post-reaction solution with a concentration of Rh below 5 mg/dm3.
The sorption yield of rhodium decreased with the number of steps, and it stabilized at the same value after the fourth step. In both examples, there is a visible sudden increase in the yield in the 5th step, but it may be because steps 5–7 were researched at a later time than the previous ones. This would mean that, in the meantime, new complexes of rhodium formed in the solution, ones that could more easily undergo the ion-exchange process. However, it also could be the results of a measurement error due to a different time of the conducted analysis.
In all experiments, rhodium was the hardest element to be recovered, due to its inert character. In acidic solutions, especially in the aqueous chloride solutions, it forms a series of complexes, such as: [RhCl6]3−, [Rh(H2O)Cl5]2−, [Rh(H2O)2Cl4] or [RhCl6]2− [20]. Even though rhodium can exist in a tetravalent oxidation state, it more often appears in the chloride solutions in a trivalent oxidation state, therefore forming the aforementioned variety of aqua-complexes. The noble metals complexes have a specific tendency to create ion pairs with ion exchangers, according to: [MCl6]2− > [MCl4]2− >> [MCl6]3− > aqua-complexes. In accordance with this series, rhodium is the last one to undergo the ion exchange process, hence its low sorption yields in the experiments [21,22].

3.2. Elution

In the elution experiments, four types of eluents were researched: 10% HCl, 2 mol/dm3 ammonium thiocyanate, 2 mol/dm3 ammonium thiocyanate in 10% HCl, and 1 mol/dm3 thiourea in 2 mol/dm3 HCl. The results of the research are presented in Table 6.
The further recovery of noble metals from the resins is not an easy task as is clearly visible in Table 6 [11]. Only the solution of 1 mol/dm3 thiourea in 2 mol/dm3 HCl showed promising results in terms of elution of PGMs and gold. Nevertheless, the recovery depends on the previously used resin. The best results were obtained for Puromet MTS9850 and Puromet MTS9200. The high results of the recovery of rhodium could be caused by its small initial concentration in the resin. Therefore, a small amount of rhodium freed to the solution would give significant results.
The low elution yields could be also the result of conducting the experiments using the batch method, whereas dynamic studies are believed to give better outcomes. Another reason could be the character of the eluting agent. In case of thiourea, which has a high selectivity towards noble metals. according to the theory of hard and soft acids and bases. The metals are released when the negatively charged chlorides in noble metal anionic complexes are fully replaced by neutral thiourea [23]. The process continues until the complexes are positively charged or neutral. It is fully possible that this state was not reached [24]. Another reason is the character of the resins′ functional groups. Both Puromet MTS9200 and Puromet MTS9850 are weak base resins, containing isothiouronium or polyamine functional groups. In comparison, Lewatit K 6362 is a strong base resin, containing quaternary ammonium salt as the functional group. In the case of weak base exchangers, the process of sorption can be reversed by changing the acid concentration (hence, the use of less acidic thiourea). The deprotonation does not happen as easily in strong base resins, from which metals can be eluted using large amounts of eluting agents containing competing agents [20]. Therefore, the elution yield of Lewatit K 6362 could be increased by increasing the amount of eluting solution, although it is not a method that could be used in industry, due to the hazardous character of thiourea. In the case of Puromet MTS9200 and Puromet MTS9850, the elution yields could be increased by lowering the acid concentration.

3.3. Cementation

The cementation experiments were conducted to examine the possibility of obtaining noble metal concentrates. The results are presented in Table 7.
Cementation with zinc powder is a well-known method of metal recovery from acidic solutions [25,26,27,28,29]. Increasing the amount of Zn to the same amount of acidic thiourea solution caused the pH to increase, which is a natural phenomenon. The concentration of dissolved zinc increased to a specific point and further on decreased. Therefore, the amount necessary for cementation has dissolved and the solubility equilibrium has been reached. There is no reason to add more zinc powder.
Figure 6 confirms the theory that the cementation yield increased with the addition of Zn powder. After adding 1g of Zn, the recovery reached 99%. The plot stabilized after reaching a specific point, which was also confirmed by the results visible in Table 6. Cementation with the use of zinc powder from the thiourea acidic solution is a good method of recovering noble metals.

3.4. Comparison with Other Research

It is difficult to compare the results of one’s own work with already published results, as every type of research has a different approach to the experiments and the results. Table 8 shows the results of the experiments conducted in the most similar conditions.
The results presented in this work are promising, as they are similar or in some cases superior in comparison with the results presented in other work.

4. Conclusions

The ion-exchange process was investigated to discover the applicability of commercially available resins in the recovery of noble metals from a technological solution, obtained from the leaching of waste produced during the refining process of noble metals. After the conducted experiments, it can be concluded that:
  • The best resins for the sorption of noble metals are Puromet MTS9200, Puromet MTS9850, and Lewatit K 6362. Among the resins, Puromet MTS9200 and Lewatit K 6362 should be used for solutions with a higher concentration of gold (due to the lower gold sorption yields in the isotherm experiments for Puromet MTS9850), and Puromet MTS9850 and Lewatit K 6362 should be used in processes, which need to be conducted using fewer ion exchange steps (due to the lower recovery of noble metals after one step for Puromet MTS9200);
  • The volume ratio Vr:Vs = 1:10 and reaction time of 15–30 min could be used as the basic conditions for conducting the experiments using a dynamic method;
  • The solution of thiourea in hydrochloric acid could be used as the eluent to recover noble metals;
  • From the acidic thiourea eluates, noble metals can be recovered as concentrates using cementation with zinc powder;
  • In case of Lewatit K 6362, to obtain a concentrate with a high concentration of noble metals, the resin must be burned and then leached.

Author Contributions

Conceptualization, K.G.; methodology, K.G. and G.B.; investigation, K.G., J.M. and K.P.; writing—original draft preparation, K.G.; writing—review and editing, K.G., J.K. and G.B.; visualization, K.G.; supervision, G.B., J.K. and K.L.-S. All authors have read and agreed to the published version of the manuscript.

Funding

The study was funded by the Polish Ministry of Science and Higher Education under the project registration code 0334123000 (report no. 8033/20).

Acknowledgments

The authors would like to thank Purolite and Lanxess for providing the samples for the research.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, and in the decision to publish the results.

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Figure 1. Simplified scheme of the noble metal refining process conducted in the Łukasiewicz Research Network-Institute of Non-Ferrous Metals.
Figure 1. Simplified scheme of the noble metal refining process conducted in the Łukasiewicz Research Network-Institute of Non-Ferrous Metals.
Minerals 11 01188 g001
Figure 2. Sorption yields of the individual noble metals in relation to the volume ratio of the phases used in the experiments (Vr:Vs): (a) Puromet MTS9200, (b) Puromet MTS9850, and (c) Lewatit K 6362.
Figure 2. Sorption yields of the individual noble metals in relation to the volume ratio of the phases used in the experiments (Vr:Vs): (a) Puromet MTS9200, (b) Puromet MTS9850, and (c) Lewatit K 6362.
Minerals 11 01188 g002
Figure 3. Sorption isotherms (T = 20 °C); for (a) platinum, (b) palladium, (c) rhodium, and (d) gold; Ce—concentration of the metal in the solution in equilibrium, Re—concentration of the metal in the resin in equilibrium.
Figure 3. Sorption isotherms (T = 20 °C); for (a) platinum, (b) palladium, (c) rhodium, and (d) gold; Ce—concentration of the metal in the solution in equilibrium, Re—concentration of the metal in the resin in equilibrium.
Minerals 11 01188 g003
Figure 4. The dependence of the sorption yields on the process time for platinum and rhodium (Vr:Vs = 1:2, RT) for (a) Puromet MTS9200, (b) Puromet MTS9850, and (c) Lewatit K 6362.
Figure 4. The dependence of the sorption yields on the process time for platinum and rhodium (Vr:Vs = 1:2, RT) for (a) Puromet MTS9200, (b) Puromet MTS9850, and (c) Lewatit K 6362.
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Figure 5. The dependence of the sorption yields of rhodium on the number of ion-exchange process steps for (a) Puromet MTS9200, (b) Puromet MTS9850.
Figure 5. The dependence of the sorption yields of rhodium on the number of ion-exchange process steps for (a) Puromet MTS9200, (b) Puromet MTS9850.
Minerals 11 01188 g005
Figure 6. The dependence of noble metal cementation yields [%] on the amount of zinc added to the solution [g].
Figure 6. The dependence of noble metal cementation yields [%] on the amount of zinc added to the solution [g].
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Table 1. Resins used in the research.
Table 1. Resins used in the research.
NameTypeFunctional GroupIonic FormMatrixCompany
Puromet MTS9200weak baseisothiouroniumH+ formpolystyrenic crosslinked with divinylbenzenePurolite
Puromet MTS9850polyamineFB formpolyacrylic crosslinked with divinylbenzene
Puromet MTS9100-amidoxime
Lewatit MonoPlus TP 214weak basethiourea-polystyrenicLanxess
Lewatit K 6362strong basequaternary ammonium salt, type ICl form
Table 2. Composition of the technological solution obtained by the semiquantitative analysis.
Table 2. Composition of the technological solution obtained by the semiquantitative analysis.
Composition [mg/dm3]
PtPdRhAuMgAlP
14218277120.4<5<25
KCaScTiVCrMn
9811<0.5<0.5413<0.5
FeCoNiCuZnGaGe
252.5<2.5693630.1
AsSeBrRbSrYZr
16<5<50<0.5<0.5<0.05<0.5
NbMoRuBBeAgCd
<0.05<0.50.22<0.53.13.9
InSnSbTeICsBa
2.55.6<0.050.1<50<0.5<0.5
LaCePrNdSmEuGd
<0.05<0.05<0.05<0.05<0.05<0.05<0.05
TbDyHoErTmYbLu
<0.05<0.05<0.05<0.05<0.05<0.05<0.05
HfTaWReOsIrLi
<0.05<0.050.11.5<0.5<0.05<0.5
NaHgTlPbBiThU
20<0.5<0.055.74.2<0.05<0.05
Table 3. Composition of the technological solution obtained by the quantitative analysis.
Table 3. Composition of the technological solution obtained by the quantitative analysis.
Concentration [mg/dm3]
PtPdRhAuAsZn
6746012154433159
CuKNaVCaFe
241<0.549<0.564
Table 4. Sorption yields of the individual elements after the preliminary sorption studies.
Table 4. Sorption yields of the individual elements after the preliminary sorption studies.
Puromet MTS9200Puromet MTS9850Puromet MTS9100Lewatit MonoPlus TP 214Lewatit K 6362
Sorption yield [%]Pt99.0899.0474.1899.8699.55
Pd99.9899.9897.9599.9799.80
Rh80.1980.2843.2674.6070.79
Au92.7391.8296.3699.7799.77
Cu8.718.3027.8899.177.68
Zn20.7519.5023.4069.3181.13
Table 5. Concentration of Rh and Pt in the post-process solution depending on the number of sorption steps.
Table 5. Concentration of Rh and Pt in the post-process solution depending on the number of sorption steps.
Number of Steps
1234567
Metal concentration [mg/dm3]Puromet MTS9200Rh109.067.853.444.429.424.019.5
Pt36.52.2-----
Puromet MTS9850Rh58.434.925.723.213.810.78.4
Pt14.14.0-----
Lewatit K 6362Rh91.553.535.225.8--9.2
Pt4.92.4-----
Table 6. Elution yields (AT—ammonium thiocyanate, TU—thiourea).
Table 6. Elution yields (AT—ammonium thiocyanate, TU—thiourea).
Metal10% HCl2 mol/dm3 AT2 mol/dm3 AT in 10% HCl1 mol/dm3 TU in 2 mol/dm3 HCl
Elution yields [%]Puromet MTS9200Pt0.150.151.8441.28
Pd0.170.340.6963.11
Rh1.040.524.187.31
Au2.352.354.7147.08
Puromet MTS9850Pt0.160.472.9161.20
Pd5.941.402.3381.79
Rh0.510.510.680.51
Au2.392.393.1974.15
Lewatit K 6363Pt0.544.861.6935.66
Pd2.420.150.3237.97
Rh19.8822.0810.1211.93
Au2.072.074.3120.70
Table 7. Cementation experiment results with the use of zinc powder; m0Zn—initial mass of zinc powder, mfZn—final mass of zinc powder.
Table 7. Cementation experiment results with the use of zinc powder; m0Zn—initial mass of zinc powder, mfZn—final mass of zinc powder.
1234
m0Zn [g]0.09960.50641.00002.0000
mfZn [g]0.01350.03020.15380.8865
Concentrate composition [%]Pt 0.444
Pd 0.960
Rh 0.187
Au 0.225
Zn 98.184
Pt 0.987
Pd 0.879
Rh 0.083
Au 0.101
Zn 97.950
Pt 0.367
Pd 0.477
Rh 0.016
Au 0.020
Zn 99.120
Pt 0.065
Pd 0.084
Rh 0.003
Au 0.003
Zn 99.845
pH0.000.125.826.00
Table 8. Comparison of this study’s results with other published results [10,13,14].
Table 8. Comparison of this study’s results with other published results [10,13,14].
This Study’s ResultsComparison [13,16,17]
Puromet MTS9200
Type of solutionTechnological solutionSynthetic solution [13]
Sorption studiesPt 97.0%
pH = 0.24, Vr = 10 mL, vs. = 100 mL, t = 1.0 h, T = 20 °C
Pt ~ 91.0%
pH = 0.50, m = 0.05 g, V = 50 mL, t = 1.5 h, T = 25 °C
Kinetic studiesEquilibrium time = 5 min
pH = 0.24, Vr = 10 mL, vs. = 20 mL, T = 20 °C
Equilibrium time = 10 min
pH = 1, m = 0.05 g, V = 50 mL, T = 25 °C
Elution studiesPt 41.0%
CTU = 1 mol/dm3 in 2 mol/dm3 HCl, Vr = 10 mL, vs. = 50 mL, t = 1 h, T = 20 °C
Pt ~ 41.0%
CTU = 0.6 mol/dm3, m = 0.05 g, V = 50 mL, t = 1 h, T = 25 °C
Puromet MTS9850
Type of solutionTechnological solutionSynthetic solution [16]Process leach solution [16]
Sorption studiesPt 98.0%
Pd 99.9%
Rh 74.4%
Vr = 10 mL, vs. = 100 mL, t = 1 h
Pt 75.6%
Pd 52.3%
Rh 94.8%
Pt 81.6%
Pd 58.8%
Rh 87.8%
Vr = 5 mL, vs. = 200 mL, t = 24 h
Kinetic studiesEquilibrium time = 15–30 min
Vr = 10 mL, vs. = 20 ml
Equilibrium time = 30 min
Vr = 5 mL, vs. = 200 ml
Elution studiesPt 61.0%
Pd 81.0%
Rh 0.5%
CTU = 1 mol/dm3 in 2 mol/dm3 HCl, Vr = 10 mL, vs. = 50 mL, t = 1 h
Pt 70.0%
Pd 93.0%
Rh 7.0%
CTU = 1 mol/dm3 in 2 mol/dm3 HCl, Vr = 5 mL, vs. = 50 mL, t = 5 h
Puromet MTS9850
Type of solutionTechnological solutionSynthetic solution [17]
Sorption studiesPt 98.0%
Rh 74.0%
CHCl ~ 1 mol/dm3, Vr = 10 mL, Vs = 100 mL, t = 1 h, T = 20 °C
Pt 89.0%
Rh 94.0%
CHCl = 1 mol/dm3, mr = 0.1–0.2 g, vs. = 10.0–20.0 mL, t = 24 h, T = 20 °C
Kinetic studiesEquilibrium time = 15–30 min
Vr = 10 mL, vs. = 20 ml
Equilibrium time = 30 min
mr = 0.1 g, vs. = 10 ml
Elution studiesPt 61.0%
Rh 0.5%
CTU = 1 mol/dm3 in 2 mol/dm3 HCl, Vr = 10 mL, vs. = 50 mL, t = 1h
Pt 94.0%
Rh 94.8%
CTU = 1 mol/dm3 in 2 mol/dm3 H2SO4
Pt 63.1%
Rh 97.4%
CTU = 1 mol/dm3 in 2 mol/dm3 KOH
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Goc, K.; Kluczka, J.; Benke, G.; Malarz, J.; Pianowska, K.; Leszczyńska-Sejda, K. Application of Ion Exchange for Recovery of Noble Metals. Minerals 2021, 11, 1188. https://doi.org/10.3390/min11111188

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Goc K, Kluczka J, Benke G, Malarz J, Pianowska K, Leszczyńska-Sejda K. Application of Ion Exchange for Recovery of Noble Metals. Minerals. 2021; 11(11):1188. https://doi.org/10.3390/min11111188

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Goc, Karolina, Joanna Kluczka, Grzegorz Benke, Joanna Malarz, Karolina Pianowska, and Katarzyna Leszczyńska-Sejda. 2021. "Application of Ion Exchange for Recovery of Noble Metals" Minerals 11, no. 11: 1188. https://doi.org/10.3390/min11111188

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Goc, K., Kluczka, J., Benke, G., Malarz, J., Pianowska, K., & Leszczyńska-Sejda, K. (2021). Application of Ion Exchange for Recovery of Noble Metals. Minerals, 11(11), 1188. https://doi.org/10.3390/min11111188

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