METHOD FOR THE SEPARATE RECOVERY OF METALS FROM WASTE IN PARTICULAR CHEMICAL WASTE

Abstract: A method for the separate recovery of metals such as chromium, zinc, cadmium and nickel from iron-containing chemical waste, is disclosed. To achieve good separation of these metals from each other and without contamination by lead, and also with effective removal of iron, the method has the following steps: A. treatment of the waste with an acid whereby an aqueous solution (1) and a residue are obtained, B. selective extraction of iron (III) from solution (I) at a pH of 0-1 using an organo-phosphoric acid as an extraction medium (I), C-2 oxidative treatment of the chromium (III) in solution freed from iron at a pH of 2-4 using an oxidising agent, such as sodium hypoclhorite (NaClO), and C-3 selective extraction of the chromium (VI) formed from the solution at a pH of 2.5-4 using a suitable extraction medium (III) and the removal of co-extracted cadmium and zinc from the charged extraction medium (III) by washing with a wash liquor such as a sodium sulphate solution at a pH of 3 before back-extraction of the chromium (VI), zinc, cadmium and nickel can be extracted together from the solution freed from chromium at a pH of 6-7 using a suitable extraction medium (V) and separated by back-­ extraction of the extraction medium (V) at a pH of less than 5 using an aqueous solution which contains about 5 MoL/1 NaCl, fixing of zinc and cadmium from this solution on a strongly basic anion exchanger followed by subsequent elu­ tion of zinc and cadmium with about 0.02 m HCl and water respectively, and extraction of the nickel from the solution which has passed unhindered through the anion exchanger at a pH of 6-7.

Description: METHOD FOR THE SEPARATE RECOVERY OF METALS FROM WASTE IN PARTICULAR CHEMICAL WASTE The applicant names as inventors: Ir. Arend Bolt of Geldrop Dr. Ir. Wilhelmus J. Th. van Gemert of Apeldoorn Ing. Bernhard A. Kamphuis of Baarn Prof. Ir. Martinus Tels of Eindhoven The invention relates to a method for the separate recovery of metals such as chromium, zinc, cadmium, nickel from iron-containing waste, especially chemical waste, in which the waste is treated with an acid, whereby an aqueous solution (1) and a residue are obtained. In this connection, by chemical waste is understood waste materials which are recognized as chemical waste by the laws of any country and for which there are restrictions concerning the disposal of such waste. The invention relates in particular to the disposal of this chemical waste. The invention is not limited to this however. The invention can be also in general applied to the processing of waste (or waste materials), for instance a waste product or by-product of a process, which is not waste within the meaning of the law but which is a metal-containing mixture which in any case contains iron, and from which the separate recovery of metals is rational. In particular the invention relates to waste originating from the electroplating and pickling industries. The method is however also applicable to waste from other origins such as harbour or dock sludge. The method may even be applied to waste in the form of e.g. dust. As a rule the waste undergoes a pre-treatment in which the metals in the waste are concentrated. After the pre-treatment the waste often takes the form of a metal-containing sludge. It is known, as the first step in the recovery of metals, to treat the chemical waste with acid. The aim here is to obtain an aqueous solution containing the ions of the metal, and a residue which is not chemical waste within the meaning of the law and which can be freely disposed of. The preferred acid is the cheap sulphuric acid. Known methods for the separate recovery of metals are liquid-liquid extraction - called extraction in the following - and ion exchange. Mostly, the chemical waste contains significant quantities of iron, and although iron is not chemical waste within the meaning of the law it goes partially into solution during the dissolution treatment. The iron which is dissolved interferes with the separate recovery of other metals and must therefore be removed. It is known to remove iron (III) selectively from an aqueous solution by extraction using MIBK (methylisobutyl ketone) as the extraction medium. This extraction has the following difficulties. Firstly the extraction is only possible from a solution containing much hydrochloric acid. The hydrochloric acid must, after the recovery of other metals from the hydrochloric solution, (1) be recovered by distillation or (2) be neutralised whereby expensive hydrochloric acid is lost and much salt is produced for the disposal of which a levy must be paid; both methods carry large extra costs. Secondly, when MIBK is used much of this extraction medium is lost due to its high solubility in the aqueous solution. If the waste also contains lead, it is necessary to use another acid such as hydrochloric or nitric acid, in place of the sulphuric acid, since the use of sulphuric acid leaves an unacceptable quantity of lead sulphate in the residue as a result of its poor solubility. When hydrochloric acid is chosen there remains the above-mentioned second difficulty, with MIBK, of the loss of this extraction material in the aqueous solution. A further problem with lead is that, during the recovery of other metals in an anion exchanger, this metal diffuses. The metals recovered in an anion exchanger are therefore heavily contaminated with lead. The separate recovery of chromium also poses a problem. When an anion exchanger is employed, chromium (III) passes through the exchanger, while during extraction of chromium (IV) zinc and cadmium are co-extracted. The object of the invention is to provide a solution of the above-mentioned difficulties and hence improve known methods. This is achieved in the invention by selectively extracting the iron (III) from the solution (1) at a pH of 0-1 using an organophosphoric acid as extraction medium (1), and by recovering other metals separately too. The advantage of this is that in this way iron can be extracted selectively from the aqueous solution with a partition coefficient of about 1000, with not more than a very slight loss of extraction medium. It is remarked that it is known from DE 2503398 to extract iron and zinc together froman acid sulphate solution with an organophosphoric acid as extraction medium. What is not known is how to use this extraction medium to extract iron (present as Foe 3+) selectively from an acid solution by controlling the pH accurately to a value between 0 and 1, whereby the aqueous medium is not bound to sulphuric acid. Preferably di-2-ethylhexylphosphoric acid dissolved in a suitable organic solvent is used as extraction medium. The regeneration of this extraction medium with sulphuric acid, as described in DE 2503398 is not efficient, and hence the iron is preferably back-extracted from the extraction medium using a strong, e.g. 6 M, HC1 solution. A further improvement consists in subjecting the chromium (III) in the solution (2) to oxidation treatment using an oxidising agent such as sodium hypochlorite (aC10) at a pH of 2-4, in selectively extracting the chromium (VI) so formed from the solution at a pH of 2.5-4 using a suitable extraction medium (III) and in removing co-extracted cadmium and zinc from the charged extraction medium (III) before back extraction of the chromium (IV) by washing with a wash liquid such as a sodium sulphate solution with a pH of about 3; the advantage of this is that the Cr VI to be recovered is hardly contaminated with cadmium and zinc. In another aspect the object of the invention is achieved by the combination of the following steps: a. treatment of the waste with an acid, whereby an aqueous solution (I) and a residue are obtained; b. selective extraction of the iron (III) from solution (1) at a pH of 0-1 using an organophosphoric acid as extraction medium (I); c-2. oxidative treatment of the chromium (III) in solution (2) at a pH of 2-4 using an oxidising agent, such as sodium hypochlorite (NaC10), and c-3. selective extraction of the chromium (VI) formed from the solution at a pH of 2.5-4 using a suitable extraction medium (III) and the removal of Co- extracted cadmium and zinc from the charged extraction medium (III) by washing it with a wash liquid, such as a sodium sulphate solution at a pH of 3, before back-extraction of the chromium (Vi). A further improvement is achieved by the following step: e. extraction of zinc, cadmium and nickel together from the solution (4) at a pH of 6-7 using a suitable extraction medium (V). The solution (4), when zinc, cadmium and nickel have been removed, can be disposed of. The zinc, cadmium and nickel can finally be recovered separately by the three following steps: f. back-extraction of the extraction medium (V) charged in step e at a pH of less than 5 using an aqueous solution which contains about 5 mol/l of NaCl; g. fixing zinc and cadmium from solution (6) on a strongly basic anion exchanger followed by successive elution of zinc and cadmium with 0.02 M HC1 and water respectively and h. extraction from solution (7) of the nickel which has passed unhindered through the anion exchanger during the fixing at step g by the use of a suitable extraction medium (VI) at a pH of 6-7. Particular embodiments of the method of the invention for the case where the chemical waste also contains cobalt, manganese copper or lead are given in subclaims. The invention will be illustrated non-restrictively with reference to the drawing. Fig. 1 shows a process diagram for the separate recovery of metals from chemical waste in accordance with the invention. Fig. 2 shows in detail the step, indicated in Fig. 1 by a, of selective extraction of iron (III) and shows an embodiment of the extraction process. Fig. 3 shows in detail the step, indicated in Fig 1 by c-3, of selective extraction of chromium (VI) and shows an embodiment of the extraction process. In Fig. 1 reference numeral 1 shows the supply of mixed metal-containing sludges to a solution step a. An acid is introduced by a supply 2. The sludge is dissolved in an acid suitable for the purpose so that the pH of a solution (1) obtained reaches a final value of between 0 and 1. Sulphuric acid is preferably used since it is cheap and since when sulphuric acid is used calcium for the most part does not go into solution. If however there is much lead present in the sludge so that the residue obtained from the solution step 'a' through the discharge 3 would not conform with the legal standards, use is made of hydrochloric or nitric acid. Since in the solution step a the rentals cited in the Chemical Waste Law (Cu, Zn, Ni, Cr, Cd, Co and Pb) go into solution with an efficiency of more than 99% together with a quantity of iron and manganese, a residual sludge is obtained which is not a chemical waste within the meaning of the Chemical Waste Law, together with a solution (1) which contains the metals cited. Since iron will interfere during the separate recovery of the metals from the solution, the iron is first removed from the solution (1) obtained at step a. For this purpose solution (1) is brought to a step b, at which the iron is removed selectively from solution (1). This can be achieved by means of liquid-liquid extraction in which an organo-phosphoric acid is used as extraction medium (I). For example a 20% solution of di-2-ethylhexylphosphoric acid (D2EHPA) in a suitable organic solvent is suitable. The stripping/regeneration of the organic extraction medium charged with iron and zinc by means of sulphuric acid, as described in DE 2503398, is not effective. For an effective regeneration of the charged extraction medium the following method is employed (see Fig. 2). The charged extraction medium is subjected to a subsequent liquid-liquid extraction step, in which the aqueous phase consists of a 6 M HC1 solution. The iron thus goes over into the aqueous phase, from which it can be removed by a known technique, for instance by means of liquid-liquid extraction using a solvating extraction medium (II) such as methylisobutyl ketone (MIBK) or tributyl phosphate (TSP). The iron-free hydrochloric solution is after recuperation re-used for the regeneration of the extraction medium (I). The iron extraction is shown schematically in Fig. 2. In addition, an embodiment is given, in which n = number of equilibrium stages q = organic/water phase ratio by volume D = partition coefficient = concentration of metal in organic phase concentration of metal in aqueous phase The other numbers in Fig. 2 are iron concentrations (g/l) in the relevant flows in the embodiment. The extraction media in the example are: Extraction medium I: 20% D2EHPA in kerosine Extraction medium II: 10% TBP in kerosine. By selecting favourable phase ratios the resultant iron chloride solution can be highly concentrated. (In the example by a factor 25 relative to the original solution). Zinc is extracted only to the extent of 1% in the first step, and the other non-ferrous metals remain below that. The solution (2) obtained at step b is, as shown in Fig. 1, brought to a process step c, in which the Cr (III) present is oxidised to Cr (VI) in an oxidation step c-2 using sodium hypochlorite, in which the pH should lie between 2 and 4. The chromium in its hexavalent form can be removed selectively from the solution. The removal of the chromium is necessary since it will interfere with the subsequent process steps The manganese which may be present (as Nun 2+) in solution (2) is deposited as manganese dioxide (MnO2) as a result of the oxidising treatment in oxidation step c-2 and is then filtered off. If lead is also present in solution (2) it is possible to prevent the insoluble lead chromate (2) from being deposited along with the manganese dioxide by treating the solution (2) at a step c-l with sodium chromate, so that the lead chromate can be filtered off before the oxidisation treatment in step c-2 takes place. The Cr (VI) formed is removed selectively from the solution in step c-3 using liquid-liquid extraction. For this purpose it is possible to use basic extraction media known per se such as primary, secondary and tertiary amines, and also quaternary ammonium salts. A mixture of trioctylamine and tributyl phosphate (TOA/TBP) is especially suitable for this purpose. During the extraction of Cr (VI) at an equilibrium pH of between 2.5 and 4 small quantities of zinc and cadmium are co-extracted. At this point, see Fig. 3, by treating the charged extraction medium (III) in a subsequent extraction step with sodium sulphate solution at pH = 3, the co-extractedd zinc and cadmium are selectively washed from extraction medium (III). The Cr (VI) is back-extracted from the charged extraction medium (III) using an aqueous solution at a pH between 6 and 9. By using this aqueous solution several times for this purpose a highly concentrated sodium chromate solution is obtained. The regenerated extraction medium (III) so obtained is re-used for the extraction of the Cr (VI) without further post-treatment. The Cr (VI) extraction is reproduced schematically in Fig. 3. An embodiment is also given in which n and q have the same significance as in Fig. 2. In the embodiment the extraction medium (III) is TOA/TBP (50/100 g/l) in kerosine. For the conditions indicated in Fig. 3, the following partition in the various flows applies (2) (3) W p Relative volume 1 1 0.25 0.10 CR ('71) 1.00 0.001 - 9.99 Zn 1.00 0.92 0.318 0.006 Cd 1.00 0.88 0.476 0.01 Zinc and cadmium are very strongly co-extracted, but can be washed out effectively using a sulphate solution. By partially recycling the product flow P, it is possible to obtain a reducing concentration of the sodium chromate solution. In a subsequent process step d, Cm2+ is selectively removed from the solution (3) obtained at step c by means of liquid-liquid extraction at a pH between 4 and 5.5. The copper-charged extraction medium (IV) is stripped/regenerated using sulphuric acid to obtain a highly concentrated copper sulphate solution. The solution (4) obtained in step d plus the wash water from step c-3 contains ions of zinc, cadmium, nickel and cobalt. These metal ions are extracted at step e from solution (4) using extraction medium (V) by carrying out the extraction in a number of equilibrium steps at a pH between 6 and 7. The aqueous solution (5) so obtained contains no more heavy metals and can be disposed of. The extraction medium (V) obtained at step e and charged with Sn2+, Cud2+, Ni2+ and Co2+ is stripped/regenerated in step f at a pH of less than 5 using an aqueous solution containing 5 mol/l NaCl. In this, the abovementioned metal ions go over into the aqueous solution (6). By passing this solution (6) over a strongly basic anion exchanger the ions of zinc, cadmium and cobalt are fixed on the anion exchanger at step g, while Ni2+ passes through unhindered. Co2+, Zn2+ and Cd 2+ are washed separately from the anion exchanger by successive elution with about 0.5 M H , about 0.02 M HQ and water. Nickel is finally extracted from the salt solution (7) at step h at a pH of between 6 and 7 using extraction medium (VI). The nickel-charged extraction medium (VI) is stripped with sulphuric acid. The resultant salt solution (8) can afterwards be brought back to strength and used again for stripping the extraction medium (V) charged in step e. A mixture of cyclohexanoxime and an unsaturated fatty acid such as e.g. oleic acid in an arbitrary organic solvent is especially suitable for the extraction media (IV), (V) and (VI).

Claims: CLAIMS: Method for the separate recovery of metals such as chromium, zinc, cadmium, nickel from ironcontaining waste, in particular chemical waste, in which the waste is treated with an acid whereby an aqueous solution (1) and a residue are obtained, characterised in that the iron (III) is extracted selectively from the solution (1) at a pH of 0-1 using organophosphoric acid as extraction medium (I) and that other metals are also separately recovered. 2. Method in accordance with claim 1 characterised in that the chromium (III) in solution (2) is subjected to an oxidation treatment at a pH of 2-4 using an oxidising agent, such as sodium hypochlorite (NaClO), that the chromium (VI) formed is selectively extracted from the solution at a pH of 2.5-4 using a suitable extraction medium (III), and that the charged extraction medium (III) is freed of co-extracted cadmium and zinc by washing with a wash liquor, such as a sodium sulphate solution, at a pH of about 3 before backextraction of the chromium (VI). 3. A method for the separate recovery of metals such as chromium, zinc, cadmium and nickel from ironcontaining waste, in particular chemical waste, characterised in the combination of the following steps: a treatment of the waste with an acid wheriby an aqueous solution (1) and a residue are obtained; b. selective extraction of iron (III) from solution (1) at a pH of 0-1 using an organo-phosphoric acid as an extraction medium (I); c-2. oxidative treatment of the chromium (III) in solution (2) at a pH of 2-4 using an oxidising agent, such as sodium hypochlorite (NaC10), and c-3. selective extraction of the chromium (VI) formed from the solution at a pH of 2.5-4 using a suitable extraction medium (III) and the removal of co-extracted cadmium and zinc from the charged extraction medium (III) by washing with a wash liquor such as a sodium sulphate solution at a pH of 3 before back-extraction of the chromium (VI). 4. Method according to one of the above claims, characterised by a subsequent step: e. extraction of zinc, cadmium and nickel together from the solution (4) at a pH of 6-7 using a suitable extraction medium (V). 5. Method according to claim 4 characterised by the three following steps: f. back-extraction of the extraction medium (V) charged in step e at a pH of less than 5 using an aqueous solution which contains about 5 mol/l Nail; g. fixing of zinc and cadmium from solution (6) on a strongly basic anion exchanger followed by subsequent elution of zinc and cadmium with about 0.02 M HC1 and water respectively and h. extraction from solution (7) of the nickel which has passed unhindered through the anion exchanger during fixing in step g, at a pH of 6-7 using a suitable extraction medium. 6. Method according to claims 4 and 5, wherein the waste also contains cobalt, characterised by extraction of cobalt at step e and fixing of cobalt -on the anion exchanger followed by elution of cobalt with about 0.5 M HC1 at step f. 7. Method according to claims 2 or 3, wherein the waste also contains manganese, characterised in that the manganese dioxide precipitate (MnO,) formed during the oxidation treatment (step c-21 is filtered off. 8. Method according to one of the foregoing claims, wherein the waste also contains copper, characterised by a step: selective extraction of copper from solution (3) at a pH of 4as.5 using a suitable extraction medium (IV). 9. Method according to one of the preceding claims, wherein the waste also contains lead, characterised by a step carried out directly after step b: the selective extraction of iron; c-l treatment of solution (2), which is obtained from solution (1) after the iron extraction of step b, this latter solution being obtained by treatment of the waste with hydrochloric acid (HCl) or nitric acid (HN03), using a chromate e.g. sodium chromate (Na2 Cr04) and filtration of the lead chromate (PbCrO4) formed. 10. Method according to one of the preceding claims characterised in that the extraction medium (I) is di-2-ethylhexylphosphoric acid, this acid being dissolved in a suitable organic solvent. 11. Method according to one of the preceding claims, characterised in that the iron is back-extracted from the extraction medium (I) using a concentrated, e.g. 6 M, HC1 solution.

Inventors: BOLT, AREND, KAMPHUIS, BERNHARD A., TELS, MARTINUS, PROF. IR., VAN GEMERT, WILHELMUS J. TH., DR. IR.
Applicants: ESMIL B.V.
Application year: 1984
Main classification: C22B7
IPC codes: C22B7