The present invention relates to a process of non-ferrous metal recovery, especially a process for producing basic lead carbonate.
The term “yellow lead” is commonly referred to as lead oxide of formula PbO;
The term “low impurity basic lead carbonate” is basic lead carbonate with impurity elements being controlled as (mass fraction): Bi: <0.3%; Cu: <0.05%; Ag: <0.008%; Zn: <0.5%; and Cl: <1%;
The term “economical ammonium bicarbonate” means that a relatively cheap ammonium bicarbonate is used in place of the commonly used ammonium carbonate during the transformation of basic lead chloride into basic lead carbonate in the present invention;
The term “neutralization slag” is a smelting slag produced during the neutralization of the crude bismuth that has been chlorinated, it is composed of sodium hydroxide, sodium chloride, and bismuth metal, etc.;
The term “lead chloride slag” is a smelting slag produced during the removal of lead by chlorinating crude bismuth with chlorine, it is composed of lead chloride, and bismuth metal, etc.;
The term “refined bismuth” is a bismuth product of No. Bi9999 in accordance with GB/T 915-1984;
The term “crude bismuth” is a crude metal produced by reduction of the later slag from the treatment of the lead anode slime inside a silver-smelting furnace;
The term “lean lead” means that lead ions are below a minimum value of 50 g/L that is required for maintenance of normal electrolysis in a circulating system of lead-bismuth alloy electrolysis;
The term “redundant slag” is a collection of lead chloride slag and neutralization slag produced in a large amount during refining of the crude bismuth, which is inexpensive and unmanageable; and
The term “supernatant liquor” is the supernatant sodium hydroxide solution after the immersion and clarification of the neutralization slags.
At present, waste lead slags are produced during the development and production of many mineral resources, which will cause resource-wasting and economic losses as well as significant environmental pollution if not reasonably utilized.
In a process of bismuth smelting, a large amount of lead-containing waste slags is leached out. The slags contain valuable metals such as lead, copper, silver and bismuth, and the lead content is generally from 60% to 70% (mass fraction). Therefore, the use of waste lead slags for producing lead-salt series of chemical products such as basic lead carbonate, tribasic lead sulfate and lead sulfate has attracted great attention.
The object of this invention is to provide a process for producing basic lead carbonate with low impurity content.
The process according to the present invention uses “redundant slags” from fire refining of bismuth to produce basic lead carbonate with low impurity content. The process comprises the following steps: (1) immersing neutralization slags to obtain sodium hydroxide solution; (2) leaching lead chloride slags and filtering; (3) alkali neutralizing, filtering and washing, and (4) carbonate converting, crystallizing, filtering and washing.
In the step of immersing neutralization slags to obtain sodium hydroxide solution, crushed neutralization slags are stirred in an immersing pool, immersed for 1-2 h and clarified. The supernatant liquor is a sodium hydroxide solution which can be used directly. Preferably, the crushed neutralization slags are immersed with addition of clean water in the immersing pool for 1.5 h.
In the step of leaching lead chloride slags and filtering, the crushed lead chloride slags are charged into a reaction tank containing an aqueous solution of sodium chloride with a concentration of 300-400 Kg/m3, stirred for 1-1.5 h and heated to 85-95° C., adjusted to a pH value of 1-4 with hydrochloric acid; reacted for 1-1.5 h, followed by addition of a sulfide salt, such as Na2S, K2S and (NH4)2S. Purification measures are employed, such as filtration and clarification. The amount of sulfide salt added in this step is 1-2 times of the theoretical value of sodium sulfide required for precipitating copper ions in the solution. Copper is removed by 0.5 h of sulfidation. The final pH value for leaching lead chloride is controlled at 3.5-5.5, and filtration is carried out at a temperature of 70-95° C. Preferably, the crushed lead chloride slags are added to an aqueous solution of sodium chloride with a concentration of 380 Kg/m3, adjusted to pH 2 with hydrochloric acid, heated to 90° C. and stirred for 1.5 h. Preferably, the amount of sulfide salt added is 1.2 times of the theoretical value of sodium sulfide required for precipitating copper ions in the solution. Preferably, the final pH for leaching lead chloride is 4, and the temperature therefor is 90° C. The main reactions are as follows:
PbCl2+2NaCl═Na2[PbCl4] (1)
Cu2++S2−═CuS↓ (2)
BiCl3+3H2O═Bi(OH)3↓+3HCl (3)
2Ag++S2−═Ag2S↓ (4)
In the step of alkali neutralizing, filtering and washing, the filtrate obtained in step (2) is back heated to 70-95° C. while stirring, such that the precipitated crystals are dissolved, then the sodium hydroxide solution prepared in step (1) is added slowly until the pH of the solution is 6-8 which means completion of the neutralization, clarified, then filtered through a multi-layer filter cloth, and washed 3-6 times. Preferably, the filtrate obtained is back heated to 85° C. while stirring. Preferably, the sodium hydroxide solution prepared in step (1) is added slowly until the pH of the solution is 7. Preferably, after neutralization is completed, clarification is carried out, followed by filtrating through a multi-layer filter cloth and washing up to four times. The main reactions are as follows:
Na2[PbCl4]+NaOH═[Pb(OH)Cl]↓+3NaCl (1)
NaOH+HCl=NaCl+H2O (2)
In the step of carbonate convering, crystallizing, filtering and washing, the filter slags (filter residue) obtained in step (3) are charged into a reaction tank containing clean water and stirred. The amount of ammonium bicarbonate added is 2-3 times of the theoretical value of ammonium bicarbonate required by the filter slags. At the same time, a small amount of sodium hydroxide solution obtained in step (1) is used to adjust pH which is to be 8-11, and procedures of stirring for 1-2 h, crystallizing & precipitating, filtering, and washing up to 3-6 times are performed. Preferably, an economical carbonate, i.e. ammonium bicarbonate, is used for carbonate conversion in this step. Preferably, the amount of ammonium bicarbonate added is 2.7 times of the theoretical value of ammonium bicarbonate required by the filter slags. Preferably, a small amount of sodium hydroxide solution obtained in step (1) is used to adjust pH which is to be 9, and procedures of stirring for 1.5 h, crystallizing & precipitating, filtering, and washing for 5 times are performed. The main reactions are as follows:
3[Pb(OH)Cl]+2NH4HCO3═2PbCO3.Pb(OH)2↓+2NH4Cl+HCl+H2O (1)
NaOH+HCl═NaCl+H2O (2)
The basic lead carbonate product, as a substitute for yellow lead, can be added directly to a circulating electrolyte of lead-bismuth alloy electrolysis without drying, thus the problem of “lean lead” can be solved, and the process can be optimized. The basic lead carbonate with low impurity content can also be calcined at high temperature to produce yellow lead, and the yellow lead produced can meet the national first class standard.
The process of the present invention uses “redundant slags” from fire refining of bismuth as raw material, the leaching of lead chloride slags and the enriching of impurities such as copper and bismuth are carried out simultaneously. The leached slags containing impurities such as copper and bismuth are returned directly to fire smelting; the mother liquor of alkali neutralization is mainly a sodium chloride solution close to saturation which is to be returned to the step of leaching lead chloride slags. The smelting process of “blast furnace smelting, then lead-bismuth alloy electrolysis, then fire refining” is optimized in the present invention, such that bismuth smelting slags are better processed and utilized, so as to save resource. In the process of the present invention, the circulation of lead is performed in a closed system, so as to reduce environmental pollution.
A process for producing basic lead carbonate comprising the following steps: (1) immersing slag to obtain sodium hydroxide solution; (2) leaching lead chloride slag and filtering; (3) alkali neutralizing, filtering and washing; and (4) carbonate converting, crystallizing, filtering and washing. The process of the present invention uses “redundant slag” from fire refining of bismuth as raw materials. The conventional smelting process of “blast furnace smelting, then lead-bismuth alloy electrolysis, and then fire refining” is improved, such that bismuth smelting slag are better processed and utilized, so as to save resource. In the process of the present invention, the circulation of lead is performed in a closed system, which reduces environmental pollution.
As shown in
(1) Immersing Neutralization Slags to Obtain Sodium Hydroxide Solution:
As shown in
(2) Leaching Lead Chloride Slags and Filtering:
As shown in
(3) Alkali Neutralizing, Filtering and Washing:
As shown in
(4) Carbonate Converting, Crystallizing, Filtering and Washing:
As shown in
As a substitute for yellow lead, the basic lead carbonate product can be added directly to a circulating electrolyte of lead-bismuth alloy electrolysis without drying, thus solving the problem of “lean lead”.
As shown in
(1) Immersing Neutralization Slags to Obtain Sodium Hydroxide Solution:
As shown in
(2) Leaching Lead Chloride Slags and Filtering:
As shown in
(3) Alkali Neutralizing, Filtering and Washing:
As shown in
(4) Carbonate Converting, Crystallizing, Filtering and Washing:
As shown in
The basic lead carbonate product, as a substitute for yellow lead, can be added directly to a circulating electrolyte of lead-bismuth alloy electrolysis without drying, thus the problem of “lean lead” can be solved, and the process can be optimized.
Number | Date | Country | Kind |
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2009 1 0241419 | Dec 2009 | CN | national |
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/CN2009/076289 | 12/30/2009 | WO | 00 | 6/18/2012 |
Publishing Document | Publishing Date | Country | Kind |
---|---|---|---|
WO2011/069311 | 6/16/2011 | WO | A |
Number | Name | Date | Kind |
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2109755 | Sessions | Mar 1938 | A |
3459573 | Morita et al. | Aug 1969 | A |
3511599 | Suriani | May 1970 | A |
4153451 | Crasto et al. | May 1979 | A |
Number | Date | Country |
---|---|---|
1920065 | Feb 2007 | CN |
311986 | May 1929 | GB |
426778 | Apr 1935 | GB |
Number | Date | Country | |
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20130043139 A1 | Feb 2013 | US |