WO2007045055A2 - Method for electroextaction of zinc - Google Patents
Method for electroextaction of zinc Download PDFInfo
- Publication number
- WO2007045055A2 WO2007045055A2 PCT/BG2006/000019 BG2006000019W WO2007045055A2 WO 2007045055 A2 WO2007045055 A2 WO 2007045055A2 BG 2006000019 W BG2006000019 W BG 2006000019W WO 2007045055 A2 WO2007045055 A2 WO 2007045055A2
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- zinc
- solution
- sulphite
- bisulphite
- electroextraction
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Ceased
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
- C25C—PROCESSES FOR THE ELECTROLYTIC PRODUCTION, RECOVERY OR REFINING OF METALS; APPARATUS THEREFOR
- C25C1/00—Electrolytic production, recovery or refining of metals by electrolysis of solutions
- C25C1/16—Electrolytic production, recovery or refining of metals by electrolysis of solutions of zinc, cadmium or mercury
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B19/00—Obtaining zinc or zinc oxide
- C22B19/20—Obtaining zinc otherwise than by distilling
- C22B19/22—Obtaining zinc otherwise than by distilling with leaching with acids
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/04—Extraction of metal compounds from ores or concentrates by wet processes by leaching
- C22B3/06—Extraction of metal compounds from ores or concentrates by wet processes by leaching in inorganic acid solutions, e.g. with acids generated in situ; in inorganic salt solutions other than ammonium salt solutions
- C22B3/08—Sulfuric acid, other sulfurated acids or salts thereof
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Definitions
- the present invention relates to a method for electroextraction of zinc from zinc sulphate solutions obtained in sulphuric acid leaching of zinc calcine.
- a method of zinc electroextraction from sulphuric acid solutions of zinc sulphate is known, in which zinc sulphate solutions, purified from impurities (iron, arsenic, antimony, copper, cadmium, nickel, cobalt, etc.) are subjected to electrolysis with current density of 400-600 A/m 2 and electrolyte acidity of 110-180 g/dm 3 .
- impurities iron, arsenic, antimony, copper, cadmium, nickel, cobalt, etc.
- a disadvantage of the method is that when in the sulphate solutions there are impurities of metals with variable valency such as cobalt, antimony, arsenic, germanium, iron the cathode zinc yield is decreased, because of reverse dissolving, and the electricity consumption is increased.
- the present invention provides a method for electroextraction of zinc by which a higher current efficiency and lower energy consumption is achieved in the electrolysis of solutions with higher content of metal impurities with a variable valency such as iron, cobalt, antimony, arsenic, germanium.
- the present method for electroextraction of zinc from zinc sulphate solutions obtained in sulphuric acid leaching of zinc calcine consists in that to the purified zinc sulphate solution fed for electrolysis a sulphite reagent is added continuously to provide a concentration of SO 3 "2 in the solution between 300 and 1500 mg/1 and said zinc sulphate solution is subjected to electroextraction, where the zinc is plated on the cathode and a part of the spent electrolyte is fed for dissolving new portions of calcine.
- Sulphurous acid or water solution of its salt such as alkali sulphite or alkali bisulphite or ammonium sulphite or ammonium bisulphite or zinc sulphite are used as a sulphite reagent.
- a preferred sulphite reagent of the present invention is a solution of sodium bisulphite NaHSO 3 .
- the sodium bisulphite NaHSO 3 is obtained through absorption of sulphur dioxide contained in waste gases with solutions of sodium carbonate.
- concentrations OfNaHSO 3 in the solution are achieved in the absorption of SO 2 from poor waste gases of metallurgic and chemical productions (0.2 - 2.0 % by volume SO 2 ) compared to the requirements for the trade product (33 - 36 % NaHSO 3 ).
- a relatively large amount OfNaHSO 3 is oxidized to Na 2 SO 4 .
- the advantages of the method according to the present invention are that it provides a higher quality of the cathode zinc as well as improvement of the electrochemical process performance - a higher current efficiency ( ⁇ c , %) and a lower energy consumption (W, kWh/t Zinc) under equal other conditions of electrolysis.
- the method according to the present invention also has a substantial ecological advantage because it allows full extraction of sulphuric dioxide from waste metallurgic gases. Furthermore, the liberation of sulphuric dioxide upon mixing the neutral zinc solution with the working electrolyte is reduced to minimum and deterioration of the sanitary conditions in the electrolysis area is avoided.
- FIG. 1 represents a flowsheet of sulphuric acid leaching of zinc calcine, in which the jarosite process is used, and electroextraction of zinc with addition of sodium bisulphite.
- the method according to the present invention can be broadly described with reference to the flowsheet of FIG. 1.
- the method includes the following consecutively executed operations: Obtaining sodium bisulphite: Spent gases, containing sulphuric dioxide (for example monocatalytic systems for sulphuric acid, dust purified agglomeration gases or gases from the shaft furnace of lead production, etc.) are subjected, in a cyclic or continuous regime, to absorption with a water solution of soda (sodium carbonate Na 2 CO 3 ) in a scrubber type absorber or a Venturi tube, obtaining sodium bisulphite with a concentration of 10-20 % NaHSO 3 . Partial oxidizing of the bisulphite to sulphate occurs (8-10 % Na 2 SO 4 ).
- the NaHSO 3 solution obtained is fed continuously from a collecting tank with a doser (a slide gate or a valve) and is mixed with the purified zinc sulphate solution flow fed for electrolysis.
- the bisulphite solution rate is controlled in accordance with the production load in the leaching scheme (m 3 /h of produced zinc sulphate solution) as well as in accordance with the NaHSO 3 concentration in the fed reagent so that the neutral zinc solution flow dispatched for electroextraction will maintain a concentration of SO 3 "2 not lower than 300 mg/1 and not higher than 1500 mg/1.
- the high reduction potential of the sulphite and bisulphite ions provides even in small concentrations a reduction of polyvalent metal impurities (Fe 3+ , Fe 2+ , Co 3+ , Co 2+ , As 5+ , As 3+ , Sb 5+ , Sb 3+ , Ge 4+ , Ge 2+ , etc.) to their low valency forms according to the following chemical reaction equations:
- H 3 SbO 4 + 2NaHSO 3 2H 3 SbO 3 + Na 2 SO 4 + H 2 SO 4 ;
- H 2 GeO 3 + 2NaHSO 3 2H 2 GeO 2 + Na 2 SO 4 + H 2 SO 4 .
- the main part of the fed NaHSO 3 is oxidized to a sulphate (Na 2 SO 4 ) by the Mn 7+ and Mn + available in the spent electrolyte (as MnO 4 " ions or fine particles of MnO 2 — slurry, respectively) already during mixing of the neutral zinc sulphate solution and the spent electrolyte, according to the following reactions:
- the concentration of sulphite ions in the neutral zinc solution for electrolysis not to exceed 1500 mg/dm 3 SO 3 "2 .
- the obtained sodium sulphate with the spent electrolyte goes as a reagent to the jarosite process stage.
- the full oxidizing of the bisulphite (NaHSO 3 ) to sulphate (Na 2 SO 4 ) is necessary because the presence of a reducer in the solutions, fed in the jarosite process stage is undesirable.
- the sodium bisulphite is fed and mixed up with a rate of about 0.15 m 3 /h (about 6 m 3 per twenty-four hours respectively), which at a rate of 30 mVh of the neutral ZnSO 4 solution corresponds to a concentration of about 480 mg/dm 3 of SO 3 "2 ions in the solution.
- the tank is equipped with a steam heater for maintaining a temperature not lower than 3O 0 C in order to prevent crystallization of the solution. After feeding the lot Of NaHSO 3 solution (for 96 hours approximately), the tank is filled again.
- the cellhouse comprises 222 electrolytic cells connected in a series (each cell of capacity 1.8 m 3 , with 20 cathodes and 21 anodes).
- the series of electrolytic cells works under current load of 10 000 A, which corresponds to a cathode current density D c of about 400 A/m 2 .
- the industrial test is carried out in the course of 360 hours (15 days and nights) with 150 - 160 g/1 Zn and 140 - 150 g/1 H 2 SO 4 in the neutral ZnSO 4 solution and variable valency impurities content: 0.01 - 0.02 mg/1 of antimony (as Sb 5+ ), 0.5 - 1.5 mg/1.of arsenic (as As 5+ ), 0.3 - 0.5 mg/1 of cobalt (as Co 3+ ), 0.003 - 0.007 mg/1 of germanium (as Ge 4+ ), 10 - 20 mg/1 of iron (as Fe 3+ ).
- the calculated average values over a twenty-four-hour period for the current efficiency ( ⁇ c , %) and specific energy consumption (W, kWh/t Zinc) are between 87.7 - 89.0 % (88.4% average) and 3121 - 3103 kWh/t (3112 kWh/t average) respectively.
- the obtained cathode zinc has a very good outer surface of the sheet without black dots on its inner surface. The removing of zinc residues from the cathodes is carried out without difficulty (the so-called "stripping" of the zinc is good).
- the spent electrolyte which contains sodium sulphate obtained from the introduced sulphite reagent is led to the sulphuric acid leaching cycle and the jarosite process (FIG.l) where sodium ions are used in the formation of jarosite.
- Example 1 an industrial test is performed in the course of 6 weeks.
- the addition of sodium bisulphite (with concentrations within 125 - 130 g ⁇ Of NaHSO 3 and 90 - 95 g/1 of Na 2 SO 4 ) is changed as follows: 0.20 m 3 /h - the first week; 0.40 m 3 /h - the second week; 0.60 m 3 /h - the third week; 0.50 m 3 /h - the fourth week; 0.30 m /h - the fifth week; and 0.10 m /h - the sixth week, which corresponds to SO 3 "2 ion concentrations between about 1980 mg/1 (when the addition is 0.60 m 3 /h) and about 300 mg/1 (when the addition is 0.10 m 3 /h).
- Example 2 The obtained results are similar to those in Example 1.
- the calculated average values of the current efficiency ( ⁇ c , %) and specific energy consumption (W, kWh/t Zinc) are 87.5 - 89.8 % (88.6 % average) and 3190 - 3015 kWh/t (3103 kWh/t average) respectively.
- the cathode current density Dc, the concentration of zinc and sulphuric acid in the neutral ZnSO 4 solution, as well as the content of impurities with variable valency are the same as in Example 1: 0.01 - 0.02 mg/1 of antimony (as Sb 5+ ), 0.5 - 1.5 mg/1 of arsenic (as As 5+ ), 0.3 - 0.5 mg/1 of cobalt (as Co 3+ ), 0.003 - 0.007 mg/1 of germanium (as Ge 4+ ), 10 - 20 mg/1 of iron (as Fe 3+ ).
- the calculated average values over a twenty-four-hour period of the current efficiency ( ⁇ c , %) and specific energy consumption (W, kWh/t Zinc) are 85.8 - 87.2 % (86.5 % average) and 3228 - 3194 kWh/t (3211 kWh/t average) respectively.
- the obtained cathode zinc is with good outer surface, but with black dots on the inner surface of many of the cathode sheets, which is an indication of, even though limited, reverse dissolving of zinc.
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- Manufacturing & Machinery (AREA)
- Life Sciences & Earth Sciences (AREA)
- Inorganic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geochemistry & Mineralogy (AREA)
- Geology (AREA)
- Electrochemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrolytic Production Of Metals (AREA)
Abstract
A method for electroextraction of zinc from zinc sulphate solution obtained by leaching of zinc calcine in which a sulphite reagent is added continuously to a purified from impurities zinc sulphate solution to provide a concentration of SO3-2 in the solution of 300 to 1500 mg/1 and said zinc sulphate solution is subjected to electroextraction where the zinc is plated on the cathode and a part of the spent electrolyte is fed for dissolving new portions of calcine. Sulphurous acid or water solution of its salt is used as sulphite reagent. Preferably a solution of sodium bisulphite NaHSO3 is used.
Description
METHOD FOR ELECTROEXTRACTION OF ZINC TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method for electroextraction of zinc from zinc sulphate solutions obtained in sulphuric acid leaching of zinc calcine. BACKGROUND OF THE INVENTION
A method of zinc electroextraction from sulphuric acid solutions of zinc sulphate is known, in which zinc sulphate solutions, purified from impurities (iron, arsenic, antimony, copper, cadmium, nickel, cobalt, etc.) are subjected to electrolysis with current density of 400-600 A/m2 and electrolyte acidity of 110-180 g/dm3. As a result, the zinc is plated on the cathode and a part of the spent electrolyte is fed for dissolving new portions of calcine.
A disadvantage of the method is that when in the sulphate solutions there are impurities of metals with variable valency such as cobalt, antimony, arsenic, germanium, iron the cathode zinc yield is decreased, because of reverse dissolving, and the electricity consumption is increased.
It is found that when there are metal impurities in the sulphuric acid solution the reverse dissolving of zinc is prevented to a certain degree by using additives such as gum arabic, glue, molybdate, 2-butyne-l,4-diol, tetrabutyl- or tetraethylammonim chloride; a mixture of ethoxyacetylenic alcohol, triethylbenzylammonium chloride and polyethylene glycol and other surface-active organic compounds (US 5,194,125). Some of these additives are expensive or scarce and they are accumulated in the electrolyte. They do not affect the valency state of the electrolyte.
In the background art there is also a known method of high temperature extraction of zinc by dissolving of zinc ferrites, followed by precipitation in the presence of ammonium or alkali ions and taking the iron out of the hydrometallurgic cycle as jarosite cake (EP 451456; US 4274931; WO 98/06879). Usually sodium sulphate Na2SO4 is used as a reagent for the formation of the jarosites. The ZnSO4 solution obtained after removing the impurities is subjected to electroextraction and as a result the zinc is plated on the cathode and a part of the spent electrolyte is fed for
dissolving new portions of calcine. A disadvantage of the method is that the sodium sulphate, used for precipitation of jarosites, is expensive and scarce.
DISCLOSURE OF THE INVENTION
The present invention provides a method for electroextraction of zinc by which a higher current efficiency and lower energy consumption is achieved in the electrolysis of solutions with higher content of metal impurities with a variable valency such as iron, cobalt, antimony, arsenic, germanium.
The present method for electroextraction of zinc from zinc sulphate solutions obtained in sulphuric acid leaching of zinc calcine consists in that to the purified zinc sulphate solution fed for electrolysis a sulphite reagent is added continuously to provide a concentration of SO3 "2 in the solution between 300 and 1500 mg/1 and said zinc sulphate solution is subjected to electroextraction, where the zinc is plated on the cathode and a part of the spent electrolyte is fed for dissolving new portions of calcine.
Sulphurous acid or water solution of its salt such as alkali sulphite or alkali bisulphite or ammonium sulphite or ammonium bisulphite or zinc sulphite are used as a sulphite reagent.
A preferred sulphite reagent of the present invention is a solution of sodium bisulphite NaHSO3.
In a preferred embodiment of the present invention, the sodium bisulphite NaHSO3 is obtained through absorption of sulphur dioxide contained in waste gases with solutions of sodium carbonate. Considerably lower concentrations OfNaHSO3 in the solution are achieved in the absorption of SO2 from poor waste gases of metallurgic and chemical productions (0.2 - 2.0 % by volume SO2) compared to the requirements for the trade product (33 - 36 % NaHSO3). Along with that, a relatively large amount OfNaHSO3 is oxidized to Na2SO4.
The advantages of the method according to the present invention are that it provides a higher quality of the cathode zinc as well as improvement of the electrochemical process performance - a higher current efficiency (ηc, %) and a lower energy consumption (W, kWh/t Zinc) under equal other conditions of electrolysis. During the jarosite process in the sulphuric acid extraction stage the necessary amount of sodium ions for the jarosite precipitation is delivered by the spent electrolyte which
W
is led to the cycle of the jarosite process. Thereby the use of the expensive and scarce sodium sulphate is avoided. The method according to the present invention also has a substantial ecological advantage because it allows full extraction of sulphuric dioxide from waste metallurgic gases. Furthermore, the liberation of sulphuric dioxide upon mixing the neutral zinc solution with the working electrolyte is reduced to minimum and deterioration of the sanitary conditions in the electrolysis area is avoided.
BRIEF DESCRIPTION OF THE DRAWING
FIG. 1 represents a flowsheet of sulphuric acid leaching of zinc calcine, in which the jarosite process is used, and electroextraction of zinc with addition of sodium bisulphite.
DETAILED DESCRIPTION OF THE INVENTION
The method according to the present invention can be broadly described with reference to the flowsheet of FIG. 1. The method includes the following consecutively executed operations: Obtaining sodium bisulphite: Spent gases, containing sulphuric dioxide (for example monocatalytic systems for sulphuric acid, dust purified agglomeration gases or gases from the shaft furnace of lead production, etc.) are subjected, in a cyclic or continuous regime, to absorption with a water solution of soda (sodium carbonate Na2CO3) in a scrubber type absorber or a Venturi tube, obtaining sodium bisulphite with a concentration of 10-20 % NaHSO3. Partial oxidizing of the bisulphite to sulphate occurs (8-10 % Na2SO4).
Dosing of the sodium bisulphite: The NaHSO3 solution obtained is fed continuously from a collecting tank with a doser (a slide gate or a valve) and is mixed with the purified zinc sulphate solution flow fed for electrolysis. The bisulphite solution rate is controlled in accordance with the production load in the leaching scheme (m3/h of produced zinc sulphate solution) as well as in accordance with the NaHSO3 concentration in the fed reagent so that the neutral zinc solution flow dispatched for electroextraction will maintain a concentration of SO3 "2 not lower than 300 mg/1 and not higher than 1500 mg/1. The high reduction potential of the sulphite and bisulphite ions provides even in small concentrations a reduction of polyvalent
metal impurities (Fe3+, Fe2+, Co3+, Co2+, As5+, As3+, Sb5+, Sb3+, Ge4+, Ge2+, etc.) to their low valency forms according to the following chemical reaction equations:
2Fe2(SO4)3 + 2NaHSO3 + 2H2O = 4FeSO4 + Na2SO4 + 3H2SO4;
2Co2(SO4)3 + 2NaHSO3 + 2H2O = 4CoSO4 + Na2SO4 + 3H2SO4; H3AsO4 + 2NaHSO3 = 2H3AsO3 + Na2SO4 + H2SO4;
H3SbO4 + 2NaHSO3 = 2H3SbO3 + Na2SO4 + H2SO4;
H2GeO3 + 2NaHSO3 = 2H2GeO2 + Na2SO4 + H2SO4.
It is supposed that the restriction of the relative part of the high valency forms of the said deleterious impurities in the electrolysis cell is a prerequisite for improved quality of the cathode zinc (appearance of the cathode residue), for a higher current efficiency (ηc, %) and also lower energy consumption (W, kWh/t Zinc) during zinc electroextraction. The introduction of a reducer influences favourably the cathode polarization during the electrolytic process.
The main part of the fed NaHSO3 is oxidized to a sulphate (Na2SO4) by the Mn7+ and Mn + available in the spent electrolyte (as MnO4 " ions or fine particles of MnO2 — slurry, respectively) already during mixing of the neutral zinc sulphate solution and the spent electrolyte, according to the following reactions:
10NaHSO3 + 4HMnO4 = 5Na2SO4 + 4MnSO4 + H2SO4 + 6H2O;
2NaHSO3 + 2MnO2 + H2SO4 = Na2SO4 + 2MnSO4 + 2H2O. The small amounts of NaHSO3 which could remain, are oxidized fully in the electrolytic cell where because of the high concentration of the oxygen emitted by the anodes and the large quantity of finely dispersing anode slurry (MnO2 - slurry) a very high oxidizing potential is maintained. In this mechanism of the ongoing oxidization and reduction processes, the emitting of sulphuric dioxide during mixing the neutral zinc solution with the spent electrolyte is reduced to minimum and deterioration of the sanitary conditions in the electrolysis workshop is avoided. In this connection, it is preferred the concentration of sulphite ions in the neutral zinc solution for electrolysis not to exceed 1500 mg/dm3 SO3 "2. The obtained sodium sulphate with the spent electrolyte goes as a reagent to the jarosite process stage. The full oxidizing of the bisulphite (NaHSO3) to sulphate (Na2SO4) is necessary because the presence of a reducer in the solutions, fed in the jarosite process stage is undesirable.
EXAMPLES
The following examples illustrate the present invention without limiting it. EXAMPLE 1.
In a tank with a capacity of 15 m a lot of about 12 m solution of sodium bisulphite with a content of about 125 g/1 OfNaHSO3 and 90 g/1 OfNa2SO4 is fed. The solution of sodium bisulphite is obtained through absorption of sulphuric dioxide from waste gases containing 0.15 - 0.20 % by volume SO2 after a monocatalytic system for sulphuric acid production, with soda solution. The tank is placed over a collector with a capacity of 40 m3 intended for the purified solution of zinc sulphate. In the ZnSO4 solution collector the sodium bisulphite is fed and mixed up with a rate of about 0.15 m3/h (about 6 m3 per twenty-four hours respectively), which at a rate of 30 mVh of the neutral ZnSO4 solution corresponds to a concentration of about 480 mg/dm3 of SO3 "2 ions in the solution. The tank is equipped with a steam heater for maintaining a temperature not lower than 3O0C in order to prevent crystallization of the solution. After feeding the lot Of NaHSO3 solution (for 96 hours approximately), the tank is filled again.
The neutral ZnSO4 solution with the added NaHSO3 is led to the cellhouse according to the flowsheet in Fig.1.
The cellhouse comprises 222 electrolytic cells connected in a series (each cell of capacity 1.8 m3, with 20 cathodes and 21 anodes). The series of electrolytic cells works under current load of 10 000 A, which corresponds to a cathode current density Dc of about 400 A/m2. The industrial test is carried out in the course of 360 hours (15 days and nights) with 150 - 160 g/1 Zn and 140 - 150 g/1 H2SO4 in the neutral ZnSO4 solution and variable valency impurities content: 0.01 - 0.02 mg/1 of antimony (as Sb5+), 0.5 - 1.5 mg/1.of arsenic (as As5+), 0.3 - 0.5 mg/1 of cobalt (as Co3+), 0.003 - 0.007 mg/1 of germanium (as Ge4+), 10 - 20 mg/1 of iron (as Fe3+). The calculated average values over a twenty-four-hour period for the current efficiency (ηc, %) and specific energy consumption (W, kWh/t Zinc) are between 87.7 - 89.0 % (88.4% average) and 3121 - 3103 kWh/t (3112 kWh/t average) respectively.
The obtained cathode zinc has a very good outer surface of the sheet without black dots on its inner surface. The removing of zinc residues from the cathodes is carried out without difficulty (the so-called "stripping" of the zinc is good).
The spent electrolyte which contains sodium sulphate obtained from the introduced sulphite reagent is led to the sulphuric acid leaching cycle and the jarosite process (FIG.l) where sodium ions are used in the formation of jarosite.
EXAMPLE 2.
Using the method described in Example 1 , an industrial test is performed in the course of 6 weeks. The addition of sodium bisulphite (with concentrations within 125 - 130 gΛ Of NaHSO3 and 90 - 95 g/1 of Na2SO4) is changed as follows: 0.20 m3/h - the first week; 0.40 m3/h - the second week; 0.60 m3/h - the third week; 0.50 m3/h - the fourth week; 0.30 m /h - the fifth week; and 0.10 m /h - the sixth week, which corresponds to SO3 "2 ion concentrations between about 1980 mg/1 (when the addition is 0.60 m3/h) and about 300 mg/1 (when the addition is 0.10 m3/h). The obtained results are similar to those in Example 1. The calculated average values of the current efficiency (ηc, %) and specific energy consumption (W, kWh/t Zinc) are 87.5 - 89.8 % (88.6 % average) and 3190 - 3015 kWh/t (3103 kWh/t average) respectively.
When the addition is larger than 0.5 m /h and the SO3 ' ion concentration in the neutral ZnSO4 solution exceeds 1500 mg/1 of SO3 "2, a certain gas emission with a sulphuric dioxide smell is observed when mixing the neutral solution with the electrolyte flow in a recycle, an indication of which is the complete decolorization of the solution at the entry of the electrolytic cells. When leaving the cells the solution regains its pink-violet color, which indicates a full oxidation of SO3 "2 ions to SO4 "2 ions, i.e. of sodium sulphite to sodium sulphate. The obtained cathode zinc is dense, with a good outer surface of the sheet, without black dots on its inner surface. No substantial differences are observed in the so-called "stripping of the cathode zinc", nor differences in the quality of the cathode zinc in the different amounts of additions - from 0.10 to 0.60 m3/h of NaHSO3 solution, respectively concentrations of SO3 "2 ions between 300 mg/1 and 1980 mg/1 in the purified solution of zinc sulphate subjected to electrolysis.
COMPARATIVE EXAMPLE
As a basis for comparison, the so-called "passive industrial experiment" of the electrolysis process was carried out with the whole series of cells with similar parameters of electroextraction as in Example 1, but without addition of sodium bisulphite to the neutral ZnSO4 solution.
The addition of sodium bisulphite is stopped and in the course of 15 days and nights a standard electroextraction is carried out through the set technological mode of production. The cathode current density Dc, the concentration of zinc and sulphuric acid in the neutral ZnSO4 solution, as well as the content of impurities with variable valency are the same as in Example 1: 0.01 - 0.02 mg/1 of antimony (as Sb5+), 0.5 - 1.5 mg/1 of arsenic (as As5+), 0.3 - 0.5 mg/1 of cobalt (as Co3+), 0.003 - 0.007 mg/1 of germanium (as Ge4+), 10 - 20 mg/1 of iron (as Fe3+).
The calculated average values over a twenty-four-hour period of the current efficiency (ηc, %) and specific energy consumption (W, kWh/t Zinc) are 85.8 - 87.2 % (86.5 % average) and 3228 - 3194 kWh/t (3211 kWh/t average) respectively. The obtained cathode zinc is with good outer surface, but with black dots on the inner surface of many of the cathode sheets, which is an indication of, even though limited, reverse dissolving of zinc.
Comparison of the results from the given examples shows that through the addition of sodium bisulphite an average of 100 - 110 kWli/t Zn, respectively 3 to 3.5 %, lower consumption of electricity is achieved compared to electrolysis without additions of sodium bisulphate, with visibly better appearance of the cathode residues.
Claims
1. A method for electroextraction of zinc from zinc sulphate solutions obtained in sulphuric acid leaching of zinc calcine, characterized in that to the purified zinc sulphate solution fed for electrolysis a sulphite reagent is added continuously to provide a concentration of SO3 "2 in the solution between 300 and 1500 mg/1 and said zinc sulphate solution is subjected to electroextraction, where the zinc is plated on the cathode and a part of the spent electrolyte is fed for dissolving new portions of calcine.
2. A method according to claim 1, characterized in that sulphurous acid or water solution of its salt such as alkali sulphite or alcali bisulphite or ammonium sulphite or ammonium bisulphite or zinc sulphite is used as sulphite reagent.
3. A method according to claims 1 and 2, characterized in that sodium bisulphite NaHSO3 solution is used as sulphite reagent.
4. A method according to claim 3, characterized in that the sodium bisulphite NaHSO3 is obtained by absorption of sulphuric dioxide, contained in waste gases, with sodium carbonate solutions.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| BG109329A BG109329A (en) | 2005-10-20 | 2005-10-20 | Method for electroextraction of zinc |
| BG109329 | 2005-10-20 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| WO2007045055A2 true WO2007045055A2 (en) | 2007-04-26 |
| WO2007045055A3 WO2007045055A3 (en) | 2007-11-15 |
Family
ID=37872467
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/BG2006/000019 Ceased WO2007045055A2 (en) | 2005-10-20 | 2006-10-19 | Method for electroextaction of zinc |
Country Status (2)
| Country | Link |
|---|---|
| BG (1) | BG109329A (en) |
| WO (1) | WO2007045055A2 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101824549A (en) * | 2010-04-15 | 2010-09-08 | 赤峰中色库博红烨锌业有限公司 | Method for improving purity of zinc ingot by filtering waste electrolyte |
| CN103774185A (en) * | 2014-01-24 | 2014-05-07 | 中国环境科学研究院 | Device for removing and collecting zinc sulfate crystals on electrolytic zinc negative plate by using dry process |
| CN113249592A (en) * | 2021-05-13 | 2021-08-13 | 西南科技大学 | Method for selectively leaching zinc from zinc ferrite-containing waste residue by mechanical activation and directional reduction |
| CN117926346A (en) * | 2024-03-22 | 2024-04-26 | 清华大学 | Process for producing electrodeposited zinc by leaching zinc-containing paint slag in ammonium chloride solution |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4053552A (en) * | 1976-03-15 | 1977-10-11 | General Mills Chemicals Co. | Solvent extraction of zinc from sulfite-bisulfite solution |
| US4439288A (en) * | 1983-07-11 | 1984-03-27 | Exxon Research & Engineering Company | Process for reducing Zn consumption in zinc electrolyte purification |
| US4488942A (en) * | 1983-08-05 | 1984-12-18 | Omi International Corporation | Zinc and zinc alloy electroplating bath and process |
| CA1231137A (en) * | 1985-09-12 | 1988-01-05 | Ian H. Warren | Method for monitoring the quality of znso.sub.4 electrolyte containing sb (v) |
-
2005
- 2005-10-20 BG BG109329A patent/BG109329A/en unknown
-
2006
- 2006-10-19 WO PCT/BG2006/000019 patent/WO2007045055A2/en not_active Ceased
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101824549A (en) * | 2010-04-15 | 2010-09-08 | 赤峰中色库博红烨锌业有限公司 | Method for improving purity of zinc ingot by filtering waste electrolyte |
| CN103774185A (en) * | 2014-01-24 | 2014-05-07 | 中国环境科学研究院 | Device for removing and collecting zinc sulfate crystals on electrolytic zinc negative plate by using dry process |
| CN113249592A (en) * | 2021-05-13 | 2021-08-13 | 西南科技大学 | Method for selectively leaching zinc from zinc ferrite-containing waste residue by mechanical activation and directional reduction |
| CN117926346A (en) * | 2024-03-22 | 2024-04-26 | 清华大学 | Process for producing electrodeposited zinc by leaching zinc-containing paint slag in ammonium chloride solution |
Also Published As
| Publication number | Publication date |
|---|---|
| WO2007045055A3 (en) | 2007-11-15 |
| BG109329A (en) | 2007-04-30 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| KR101160752B1 (en) | Method for treatment of arsenic-containing nonferrous smelting intermediate product | |
| CN110669932B (en) | A method for comprehensive utilization of copper electrolyte purification resources | |
| KR20100049593A (en) | Method of treating arsenical matter with alkali | |
| CA2396839C (en) | Lead, zinc and manganese recovery from aqueous solutions | |
| EP4225697B9 (en) | Method for recovering metals from black mass | |
| KR20100043231A (en) | Method of treating nonferrous smelting intermediary product containing arsenic | |
| CN101649396A (en) | Methods of removing F and Cl in secondary zinc oxide dust effectively and producing electrolytic zinc | |
| KR101423860B1 (en) | Method for recovering valuable metals | |
| US7951282B2 (en) | Hydrometallurgical processing of manganese containing materials | |
| JP6550582B1 (en) | Lead manufacturing method and manufacturing equipment | |
| US4030990A (en) | Process for recovering electrolytic copper of high purity by means of reduction electrolysis | |
| JP4203076B2 (en) | Method for producing cadmium | |
| AU2004320078B2 (en) | Method of obtaining electrolytic manganese from ferroalloy production waste | |
| WO2007045055A2 (en) | Method for electroextaction of zinc | |
| CN110358936A (en) | A method of electrolytic manganese dioxide is prepared using pyrolusite | |
| CN102660756B (en) | High-purity manganese metal and preparation method thereof | |
| CN1058056C (en) | Process of chlorine complexing oxidation method for slective leaching nickel cobalt copper sulfurized ore | |
| CN116623001B (en) | Method for efficiently leaching chalcopyrite by reduction-oxidation two-stage method | |
| CN105347544A (en) | Method for precipitating and separating arsenic from waste acid wastewater | |
| DE60225893T2 (en) | Pyro-hydrometallurgical process for the recovery of zinc, lead and other valuable metals from dusts of iron and steel smelters | |
| CN1147027A (en) | Process for producing electrolytic metal manganese using SOx from waste flue gas | |
| CA2245018A1 (en) | Production of electrolytic copper from dilute solutions contaminated by other metals | |
| EP4441258B1 (en) | A method for iron and copper removal from solution using metallic reagents | |
| CN114480856B (en) | Method for recycling high-cadmium smoke and dust cadmium | |
| CN114481165B (en) | Method for producing electrolytic manganese dioxide based on manganese dioxide ore half oxide |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| 121 | Ep: the epo has been informed by wipo that ep was designated in this application | ||
| NENP | Non-entry into the national phase |
Ref country code: DE |
|
| 122 | Ep: pct application non-entry in european phase |
Ref document number: 06804579 Country of ref document: EP Kind code of ref document: A2 |