EP0042702A1 - Process for the recovery of lead and silver from minerals and process residues - Google Patents
Process for the recovery of lead and silver from minerals and process residues Download PDFInfo
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- EP0042702A1 EP0042702A1 EP81302614A EP81302614A EP0042702A1 EP 0042702 A1 EP0042702 A1 EP 0042702A1 EP 81302614 A EP81302614 A EP 81302614A EP 81302614 A EP81302614 A EP 81302614A EP 0042702 A1 EP0042702 A1 EP 0042702A1
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- 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
- C22B11/00—Obtaining noble metals
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- 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
- C22B13/00—Obtaining lead
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- This invention relates to the extraction of metal compounds from metal bearing materials and more particularly to the.extraction and recovery of lead values in. a calcium plumbate and/or oxide product from minerals or lead bearing materials.
- Silver which may be present in association with the lead may be recovered as native silver, silver chloride, sulfide or sulphate, or a silver complex with other metals, or in some other form from which it can be recovered by conventional techniques.
- West German Patent 2,500,453, (1976) describes a method of leaching lead sulphate containing material in sodium chloride solution and after residue separation, precipitating the Pb from solution with milk of lime.
- the lead precipitates contain greater than 10% chloride and 11% sulphate and are not acceptable to conventional lead smelters except in small amount and at depressed prices due to the deleterious effects of chlorides on. acid plant catalysts, baghouses, and refractories.
- Australian Patent 28,957,(1971) describes a method of precipitating lead chloride from brine solution by cooling followed by reacting said lead chloride with water and calcium sulphate to produce a lead sulphate precipitate and calcium chloride solution.
- low chloride levels in the lead sulphate were obtainable with rigorous washing, the product is again suitable to lead smelters in limited quantities and must be treated on a sinter machine to remove sulphur before the blast.
- Capital and operating costs are projected to be high for the process since the brine solution must be heated for high lead solubility and then cooled for lead chloride precipitation.
- Canadian Patent 13918 describes a method of precipitating lead and silver from brine solution by cementation on metallic zinc. Recently other researchers have rediscovered the cementation techique and advocate either zinc or iron as cementation media. High grade metallic lead and silver cementates are produced in these processes which are acceptable to lead smelters at premium prices at high tonnage. Considerable economic penalties are incurred to produce good quality cementates, however, since the cementation reagents are expensive and the zinc or iron in the lean brine resulting from cementation must be recovered in a form acceptable for sale or reuse. This can be accomplished only at considerable cost.
- a process comprising the steps of (1) preparing a solution of lead chloride by dissolving lead sulphate contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride by adding lime.to said solution and separating said lead oxychloride precipitate from the residual lean brine solution; (4) reacting the said oxychloride precipitate with oxygen and lime in a reactor at an elevated temperature to produce a calcine containing most of the lead as calcium plumbates and/or lead oxides; (5) washing said calcine in water and/or dilute chloride brine to dissolve soluble chlorides; (6) separating the resulting residue obtained from the resulting chloride brine; and, (7) washing said residue containing calcium plumbates and/or lead oxides with fresh water to remove residual chlorides.
- a process for gaining lead and silver values comprising the steps of (1) preparing a solution of lead chloride and silver compounds by dissolving lead sulphate and silver compounds contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride and silver compounds by adding lime to said solution and separating said precipitate from the residual lean brine solution; (4) reacting the said oxychloride precipitate with oxygen and lime in a reactor at an elevated temperature to produce a calcine containing most of the lead as calcium plumbates and/or lead oxides and most of the silver as silver or silver compounds; (5) washing said calcine in water and/or dilute chloride brine to dissolve soluble chlorides; (6) separating the resulting residue from the resulting chloride brine; and, (7) washing said residue containing calcium plumbates and/or lead oxides, as well as silver and silver compounds, with fresh water to remove
- a process comprising the step of (1) preparing a solution of lead chloride by dissolving lead sulphate contained in ore or process residues in concentrated chloride brine, thereby also dissolving any silver associated with the lead; (2) separating the solution so formed from the insoluble gangue and other residues; (3) forming a precipitate of lead oxychloride (ana any silver which may be present) by adding lime to the solution and separating the lead oxychloride and silver precipitate from the residual lean brine solution; (4) recycling the lean brine, normally after concentration thereof such as by evaporation or by addition of further chloride and also normally after re-acidification by the addition of further acid, for reuse in the further extraction of lead sulphate as under steps (1) and (2).
- the improvement comprises (5) reacting the said precipitate containing lead oxychloride with oxygen such as by air and with excess lime present in the precipitate, and if desired adding fresh lime, in a reactor at a temperature above 325°C for longer than one half hour to produce a calcine containing most of the lead as calcium plumbates and lead oxides, and containing any silver present as native silver, silver chloride, sulfide or sulphate, and complexes of silver with other materials; (6) repulping said calcine in water and/or dilute chloride brine to remove soluble chlorides;(7) separating the residue obtained in step (6) from the resulting chloride brine; (8) recycling the brine resulting from step (7), with the optional treatment mentioned above, for further extraction of lead sulphate under the previous steps; (9) washing the said residue from step (7) with fresh water to remove residual chlorides; and (10) recycling the chloride brine obtained in step (9) to step (6) and/or recycling the said chloride brine, again with the optional treatment mentioned
- Lead and silver extractions into brine can be accelerated by increasing the acidity by addition of an acid such as hydrochloric or sulfuric acid which will ensure at least'mildly acidic conditions.
- an acid such as hydrochloric or sulfuric acid which will ensure at least'mildly acidic conditions.
- the optimum p H in the brine leach for high lead and silver extraction, efficient residue washing, and low lime consumption appears to be about 1.5.
- Extractions of lead from lead sulphate material into brine are very high and may approach 99% with the proper choice of retention time, temperature, brine composition, and residue washing techniques as long as the solubility limit of the lead is not approached.
- Lead extractions fall from 99% at 75% of lead chloride saturation to 96% at 86% of saturation to 91% at 94% of saturation for brine leaching in 269 gpl NaCl- 33 gpl CaC1 2 - pH 1.5 brine at 35°C and 1.5 hours leaching time.
- the saturation limit of lead as lead chloride in this brine is 18.3 gpl.
- Silver extraction by brine is very dependent on the nature and prior history of the lead sulphate containing material. Some materials, usually those which have been very recently produced in a roaster or leach process exhibit silver extractions greater than 80%. Other materials, usually stockpiled, exhibit lower . silver extractions of about 50%. Silver recoveries can be increased from these materials by flotation recovery of a silver concentrate and using the present process on the flotation tailings which contain most of the lead and all the remaining silver. The silver flotation concentrate and the plumbate product can then be combined for sale to conventional lead smelters. Flotation processes such as described by Moriyama,E. and Yamamoto,Y: in AIME World Symposium of Mining and Metallurgy of Lead and Zinc, Vol. II, 1970, page 215 have been shown to yield silver concentrates with high silver assays and recoveries from lead sulphate containing materials.
- Silver can be removed from the brine leach solution by cementation on a suitable metallic medium such as zinc, iron, or lead. With proper stoichiometric conditions, retention time, and pH nearly all the silver can be recovered in a high grade metallic product containing some little lead and copper as contaminants. Lead along with the solubilized cementation agent would then be recovered in the plumbate product as in steps (3) - (9).
- the lead compounds formed will depend on-the pH or the mole ratio of base to lead chloride and the total chloride concentration. Table 1 shows the effect of these variables on the nature of the lead precipitate when lead is precipitated from a brine solution containing 15 gpl lead as lead chloride at 45°C and a retention time of 1.5 hours. Shorter retention times can be employed but chloride levels in the precipitate will increase unless the temperature is increased above 45°C. Silver is coprecipitated with lead. Most of the brine soluble impurities which are present in the lead sulphate containing starting material such as zinc, copper, iron, bismuth, and arsenic also coprecipitate with lead.
- the precipitate is repulped with water or any reasonably unsaturated brine solution produced in the process.
- Lime is added to the pulp to bring the mole ratio of the total lime addition in the process to between 2.5 and 5.5.
- the pulp is subjected to thermal treatment.
- the lead oxychloride precipitate may be blended with lime to increase the total mole ratio to between 2.5 and 5.5, without repulping and the blend subjected to thermal treatment.
- step (3) If the lime addition in step (3) was greater than 2.5 mole ratio to lead, then repulping and/or further lime addition is not necessary before thermal treatment.
- the lead oxychloride-lime blend is heated in a reactor in the presence of oxygen or air.
- the reactor can be a rotary kiln, furnace, roaster, autoclave or any device commonly used for thermal treatment.
- the retention time in the reactor depends upon the desired degree of conversion of oxychloride to plumbate and oxide, the temperature in the reator, the lime to lead mole ratio, and the oxygen partial pressure. The effects of these variables on the nature of the calcine product are shown in Table 2.. At reaction temperatures above 500 C sintering of the product appears and volatilization of lead chloride begins.
- Preferred conditions appear to be a total process lime addition to lead mole ratio of about 3, a reaction temperature of about 400 o C, a retention time of about 1 hour, and an excess of oxygen for lead oxidation. Pressure above atmospheric is not required for the reaction to be complete within 2 hours. Sufficient air or oxygen can be supplied for the reaction by convection, free or forced, or by pressurizing the reactor.
- calcium orthoplumbate (Ca 2 Pb0 4 ) is formed at high yields with such low temperatures and short retention times.
- Calcium orthoplumbate in a pure form (>90%) is a valuable commodity and is used- in the manufacture of primers for steel and galvanized steel, of pigments and of binders for paints. It also has use in the plastics and resin industries.
- the common commercial production method is the reaction of PbO with lime and air or oxygen at temperatures above 700°C. The reaction kinetics are reportedly slow below this temperature and the reaction will not go below 500°C. It has been reported by Denev, D.G.
- the present invention differs from the customary practice in that the reagent for calcination is lead oxychloride and not lead oxide. Also, the oxychloride is contaminated with significant quantities of NaCl and CaCl2. Accordingly, the kinetics and energetics of plumbate formation have been altered significantly from commercial experience.
- Figure 3 is a schematic plant layout for a particular embodiment of the invention relating to example 1.
- Samples of hot sulphuric acid leach residues obtained from the sulphation roasting and leaching of bulk zinc-lead-copper-silver sulphide concentrates assaying 30-32% Zn, 3.5-10% Pb, 0.7% Cu, 4.4 - 8.8 oz/ST (troy ounce per short ton) silver, and 14-23% iron were processed accordingly to the invention.
- a sample (example 10) of a hot acid leach residue from a dead roast zinc plant was also processed. The residues assayed as in Table 3.
- One pregnant brine solution (example #6) was treated with zinc dust at an addition rate of 0.5 gpl producing a cementate containing 99% of the silver, 95% of the copper and 80% of the bismuth in the pregnant brine.
- the remaining pregnant brines and the solution resulting from the zinc dust cementation test were then treated with lime at 1.5 mole ratio to lead in the brine solution.
- the temperature and retention time were 45°C and 1.5 hours respectively.
- Precipitates were allowed to settle and the thickened precipitates filtered.
- the precipitates in all tests were then blended with lime, as required, to bring the total mole ratio of lime added to the process to lead in the precipitate to 1.75-5.5.
- the blends were treated in an oven with a slow purge of fresh air for 1.0 hours at 400 0 C.
- the calcines were repulped to 50% pulp density for 15 minutes in fresh water and filtered and displacement washed with a volume of water equal to the calcine repulp water.
- the assays (dry basis) of the resulting plumbate products are given in Table 6.
- a sample of the hot sulfuric acid leach residue used in example 5 was repulped in water at 10% pulp density, American Cyanamid flotation reagents Aero 404 (trade mark) promoter and Aerofroth 77A (trade mark) (frother) were added at 600 g. and 60 g . per metric ton of residue respectively. After 5 minutes conditioning time, flotation was initiated and a stable froth was maintained for about 7.5 minutes. The concentrate obtained assayed 18% Pb, 24% Fe, 1.8% Zn, and 635 oz/ST silver. Silver recovery from the head material was 70%.
- the process of this invention may be applied to the recovery of metals from a variety of metallurgical products such as ores and concentrates, smelter dusts, metal drosses, middling concentrates from flotation processing, slags and process residues, and other like sources of lead and silver.
Abstract
Description
- This invention relates to the extraction of metal compounds from metal bearing materials and more particularly to the.extraction and recovery of lead values in. a calcium plumbate and/or oxide product from minerals or lead bearing materials. Silver which may be present in association with the lead may be recovered as native silver, silver chloride, sulfide or sulphate, or a silver complex with other metals, or in some other form from which it can be recovered by conventional techniques.
- The recovery of a high grade lead product suitable for treatment for metal recovery from lead bearing minerals has usually been accomplished by flotation concentration of coarse grained lead sulphide deposits into a concentrate containing greater than 50% lead and pyrometallurgical reduction of this concentrate in a blast furnace. The reserves of these coarse grained lead sulphide deposits are rapidly being depleted. The major new reserves of lead are being found in fine grained massive sulphide deposits containing sulphides of zinc, lead, copper, silver, and iron. Recoveries into high grade lead concentrates are typically low from these deposits, necessitating significant reduction in grade to maintain economic recoveries. It will be necessary for some of these deposits to resort to the production of bulk zinc, lead, copper concentrates to insure high recoveries. Several new processes are available for treating these low grade and bulk type concentrates including ferric chloride leach processes, copper chloride leach processes, sulphuric acid-oxygen pressure leach processes and the sulphation roast process. The lead and silver in the latter two processes report in a low grade lead sulphate-hematite leach residue. In the ferric and cupric chloride leach processes, leach filtrates are produced which contain lead and silver as chlorides in a concentrated brine solution. The present process - has application for lead and silver recovery from the leach residues and brine solutions generated in all of these processes. Substantial reserves of lead and silver also exist in leach residues from electrolytic zinc plants. These residues typically assay 15-40% lead as lead sulphate and for the most part are considered as unsuitable as feed for a conventional lead smelter except in small amounts. Another source of low grade materials is slag from lead smelters. Lead is presently recovered from these slags by energy intensive fuming processes. The present process can be employed directly to recover lead and silver from. zinc plant residues and after either sulphuric acid leaching or sulphation roasting to recover lead and silver from slags.
- It is known that lead sulphate and associated silver may be solubilized by means of concentrated brines as proposed in Canadian Patent 19,918, (1883); Canadian Patent 228,518, (1919); and U.S. Bureau of Mines Bulletin 157, (1918). Whilst these methods solve the problem of separating the lead and silver from the residues there has been some economic difficulty in the subsequent recovery of the lead and silver from the solution in a usable form.
- West German Patent 2,500,453, (1976) describes a method of leaching lead sulphate containing material in sodium chloride solution and after residue separation, precipitating the Pb from solution with milk of lime. The lead precipitates contain greater than 10% chloride and 11% sulphate and are not acceptable to conventional lead smelters except in small amount and at depressed prices due to the deleterious effects of chlorides on. acid plant catalysts, baghouses, and refractories.
- Canadian Patent 228,518, (1919); United States Patent 4,063,933, (1977)r and processes currently being developed by the U.S. Bureau of Mines, Minemet Recherche, (France), and Cominco Limited (Canada), advocate lead recovery by the precipitation of lead chloride crystals from solution by evaporation and/or cooling.. The subsequent recovery of lead metal to be accomplished by electrolysis. Capital and operating costs are projected to be much higher for these processes than for conventional smelting.
- Australian Patent 28,957,(1971) describes a method of precipitating lead chloride from brine solution by cooling followed by reacting said lead chloride with water and calcium sulphate to produce a lead sulphate precipitate and calcium chloride solution. Although low chloride levels in the lead sulphate were obtainable with rigorous washing, the product is again suitable to lead smelters in limited quantities and must be treated on a sinter machine to remove sulphur before the blast. Capital and operating costs are projected to be high for the process since the brine solution must be heated for high lead solubility and then cooled for lead chloride precipitation.
- Canadian Patent 228,518,(1919)describes a method of lead recovery from concentrated brine solution by direct precipitation as sulphide or sulphate. These precipitates are difficult to wash and contain significant amounts of entrapped chlorides. Again conventional lead smelters will accept only small quantities.
- Canadian Patent 13918 describes a method of precipitating lead and silver from brine solution by cementation on metallic zinc. Recently other researchers have rediscovered the cementation techique and advocate either zinc or iron as cementation media. High grade metallic lead and silver cementates are produced in these processes which are acceptable to lead smelters at premium prices at high tonnage. Considerable economic penalties are incurred to produce good quality cementates, however, since the cementation reagents are expensive and the zinc or iron in the lean brine resulting from cementation must be recovered in a form acceptable for sale or reuse. This can be accomplished only at considerable cost.
- It is an objective of this invention to provide a process for the extraction and recovery of lead and silver into a product which will be acceptable to conventional lead smelters in large tonnages and at a premium price.
- Further objectives are for the process to consume minimum energy and the reagents used to be recovered and either reused with high efficiency or credited in the sale of the lead product.
- In accordance with a broad aspect of this invention there is provided a process comprising the steps of (1) preparing a solution of lead chloride by dissolving lead sulphate contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride by adding lime.to said solution and separating said lead oxychloride precipitate from the residual lean brine solution; (4) reacting the said oxychloride precipitate with oxygen and lime in a reactor at an elevated temperature to produce a calcine containing most of the lead as calcium plumbates and/or lead oxides; (5) washing said calcine in water and/or dilute chloride brine to dissolve soluble chlorides; (6) separating the resulting residue obtained from the resulting chloride brine; and, (7) washing said residue containing calcium plumbates and/or lead oxides with fresh water to remove residual chlorides.
- In another broad aspect there is provided a process for gaining lead and silver values comprising the steps of (1) preparing a solution of lead chloride and silver compounds by dissolving lead sulphate and silver compounds contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride and silver compounds by adding lime to said solution and separating said precipitate from the residual lean brine solution; (4) reacting the said oxychloride precipitate with oxygen and lime in a reactor at an elevated temperature to produce a calcine containing most of the lead as calcium plumbates and/or lead oxides and most of the silver as silver or silver compounds; (5) washing said calcine in water and/or dilute chloride brine to dissolve soluble chlorides; (6) separating the resulting residue from the resulting chloride brine; and, (7) washing said residue containing calcium plumbates and/or lead oxides, as well as silver and silver compounds, with fresh water to remove residual chlorides.
- In accordance with another aspect of this invention we provide an improvement in a process comprising the step of (1) preparing a solution of lead chloride by dissolving lead sulphate contained in ore or process residues in concentrated chloride brine, thereby also dissolving any silver associated with the lead; (2) separating the solution so formed from the insoluble gangue and other residues; (3) forming a precipitate of lead oxychloride (ana any silver which may be present) by adding lime to the solution and separating the lead oxychloride and silver precipitate from the residual lean brine solution; (4) recycling the lean brine, normally after concentration thereof such as by evaporation or by addition of further chloride and also normally after re-acidification by the addition of further acid, for reuse in the further extraction of lead sulphate as under steps (1) and (2). The improvement comprises (5) reacting the said precipitate containing lead oxychloride with oxygen such as by air and with excess lime present in the precipitate, and if desired adding fresh lime, in a reactor at a temperature above 325°C for longer than one half hour to produce a calcine containing most of the lead as calcium plumbates and lead oxides, and containing any silver present as native silver, silver chloride, sulfide or sulphate, and complexes of silver with other materials; (6) repulping said calcine in water and/or dilute chloride brine to remove soluble chlorides;(7) separating the residue obtained in step (6) from the resulting chloride brine; (8) recycling the brine resulting from step (7), with the optional treatment mentioned above, for further extraction of lead sulphate under the previous steps; (9) washing the said residue from step (7) with fresh water to remove residual chlorides; and (10) recycling the chloride brine obtained in step (9) to step (6) and/or recycling the said chloride brine, again with the optional treatment mentioned above for reuse in the further extraction of lead sulphate under the previous step.
- In the drawings which accompany this invention:
- Figure 1 is a schematic flow sheet showing certain aspects of the present invention;
- Figure 2 is a graph showing the relationship between calcium chloride addition and sulphate in solution;
- Figure 3 is a schematic flow sheet showing a lead-silver recovery plant employing certain aspects of this invention.
- The advantages of producing a calcium plumbate product are as follows:
- i) calcium plumbate is not water or cold brine soluble and will not react with chloride brines under neutral or basic conditions to reform lead oxychlorides.
- ii) .entrained chlorides in the plumbate calcine can be easily removed and reduced to very low levels by washing with water or unsaturated brine solution.
- iii) plumbate repulp solutions filter rapidly, leaving a dry residue.
- iv) plumbate products can be briquetted and fed directly into a lead smelter blast furnaca without prior sintering, increasing smelter throughput for smelters in which the capacity is' limited by the sinter machine.
- v) as reported by Denev, D.G. et al in Dokl. Bolg. Akad. Nauk,. Vol. 26, 11, 1973, page 1485 calcium orthoplumbate is an oxidant for lead sulphide at high temperature resulting in the products PbO, CaO and S02 and hence would make a good dilutant for galena concentrate on a sinter machine.
- vi) CaO is a product of the reduction of calcium plumbate and is also required as a slagging agent in lead blast furnaces, usually at high tonnages. Accordingly, since the use of some calcium plumbate as feed to a lead smelter would reduce the requirement for lime, some credit should be given for the lime in the plumbate product.
- vii) the production of a calcium plumbate product allows for the use of lime for the precipitation of the lead from the brine leach solution and also as a reactant in the high temperature conversion of oxychloride to plumbate. Lime is a relatively inexpensive, easy to handle, environmentally acceptable, and readily available commodity.
- viii) the use of lime results in the formation of calcium chloride after the conversion of the metal chlorides (lead, zinc, copper, iron) to oxides. This calcium chloride is recycled in the brine to the lead sulphate leach and results in the precipitation of most of the sulphate as calcium sulphate into the leach residue. Accordingly the plumbate product is low in sulphate. Also, the low soluble sulphate in the leach enhances . the solubility of lead and silver allowing for leach operation at lower temperatures, resulting in a lower energy consumption and less maintenance due to decreased corrosion. The effect of calcium chloride on sulphate solubility in. sodium chloride brine solution is shown in Figure 2. The solubility of lead as lead sulphate in 269 gpl NaCl brine increases from about 13 gpl at 35°C to about 18 gpl (grams per liter) at 35°C when CaC12 is added to yield a brine containing 34 gpl CaCl2. Lead solubility is directly proportional. to the brine saturation and the sulphate concentration in the brine.
- Since calcium chloride is a more expensive commodity than sodium chloride and since there appears to be a lower limit to the soluble sulphate in the brine leach solution attainable with calcium chloride and since sodium chloride is easier to remove from leach residue by washing, it seems to be preferable but not necessary to use a concentrated sodium chloride brine as the base solution using the lime additions in steps (3) and (5) as the source of calcium chloride for sulphate removal. Small amounts of fresh NaCl and CaC12 will be required to make up for losses in the leach residue and product.
- Lead and silver extractions into brine can be accelerated by increasing the acidity by addition of an acid such as hydrochloric or sulfuric acid which will ensure at least'mildly acidic conditions. The optimum pH in the brine leach for high lead and silver extraction, efficient residue washing, and low lime consumption appears to be about 1.5.
- Extractions of lead from lead sulphate material into brine are very high and may approach 99% with the proper choice of retention time, temperature, brine composition, and residue washing techniques as long as the solubility limit of the lead is not approached. Lead extractions fall from 99% at 75% of lead chloride saturation to 96% at 86% of saturation to 91% at 94% of saturation for brine leaching in 269 gpl NaCl- 33 gpl CaC12 - pH 1.5 brine at 35°C and 1.5 hours leaching time. The saturation limit of lead as lead chloride in this brine is 18.3 gpl.
- Silver extraction by brine is very dependent on the nature and prior history of the lead sulphate containing material. Some materials, usually those which have been very recently produced in a roaster or leach process exhibit silver extractions greater than 80%. Other materials, usually stockpiled, exhibit lower . silver extractions of about 50%. Silver recoveries can be increased from these materials by flotation recovery of a silver concentrate and using the present process on the flotation tailings which contain most of the lead and all the remaining silver. The silver flotation concentrate and the plumbate product can then be combined for sale to conventional lead smelters. Flotation processes such as described by Moriyama,E. and Yamamoto,Y: in AIME World Symposium of Mining and Metallurgy of Lead and Zinc, Vol. II, 1970, page 215 have been shown to yield silver concentrates with high silver assays and recoveries from lead sulphate containing materials.
- Another option in the present process is the production of sepa at silver and lead products. Silver can be removed from the brine leach solution by cementation on a suitable metallic medium such as zinc, iron, or lead. With proper stoichiometric conditions, retention time, and pH nearly all the silver can be recovered in a high grade metallic product containing some little lead and copper as contaminants. Lead along with the solubilized cementation agent would then be recovered in the plumbate product as in steps (3) - (9).
- When lead is precipitated from brine solution by the addition of a base as in step (3) of the process, the lead compounds formed will depend on-the pH or the mole ratio of base to lead chloride and the total chloride concentration. Table 1 shows the effect of these variables on the nature of the lead precipitate when lead is precipitated from a brine solution containing 15 gpl lead as lead chloride at 45°C and a retention time of 1.5 hours. Shorter retention times can be employed but chloride levels in the precipitate will increase unless the temperature is increased above 45°C. Silver is coprecipitated with lead. Most of the brine soluble impurities which are present in the lead sulphate containing starting material such as zinc, copper, iron, bismuth, and arsenic also coprecipitate with lead. The best process economics are obtained with lime as the precipitation agent at an addition rate between 1.0 and 5.5 mole ratio of lime to lead chloride. The excess lime also acts as a flocculating agent for oxychloride precipitate,
- Although it is desirable to produce a precipitate containing as little chloride as possible, very low chloride-oxychlorides cannot be precipitated from concentrated brine unless uneconomic quantities of sodium hydroxide are used. Since they are very soluble, all excess sodium hydroxide. and/or sodium carbonate must be neutralized with hydrochloric acid before the lean brine resulting from precipitate separation can be recycled to the brine leach step (1). The use of sodium hydroxide precipitating agent also results in excessive reagent calcium chloride makeup requirements.
- Ermilov, V.V. and Aitenov, S.A..in Trudy Institut Metallurgi Obogashcheniia, Vol. 30, 1969, page 47 proposed a method for producing a lead (iv) oxide precipitate from concentrated brine by adding equal. molar quantities of calcium oxide and calcium hypochlorite to lead chloride. Although the reaction is irreversible and regenerates calcium chloride into solution, and the product can easily be washed to less than 0.5% chloride, the economics are unfavourable due to the value of hypochlorite in comparison to lead metal and lime.
- If the lime addition in the precipitation step (3) was less than 2.5 mole ratio to lead, then after separation of the lead oxychloride precipitate from the lean brine solution, the precipitate is repulped with water or any reasonably unsaturated brine solution produced in the process. Lime is added to the pulp to bring the mole ratio of the total lime addition in the process to between 2.5 and 5.5. After solid/liquid separation the pulp is subjected to thermal treatment. Alternatively the lead oxychloride precipitate may be blended with lime to increase the total mole ratio to between 2.5 and 5.5, without repulping and the blend subjected to thermal treatment.
- If the lime addition in step (3) was greater than 2.5 mole ratio to lead, then repulping and/or further lime addition is not necessary before thermal treatment.
- The lead oxychloride-lime blend is heated in a reactor in the presence of oxygen or air. The reactor can be a rotary kiln, furnace, roaster, autoclave or any device commonly used for thermal treatment. The retention time in the reactor depends upon the desired degree of conversion of oxychloride to plumbate and oxide, the temperature in the reator, the lime to lead mole ratio, and the oxygen partial pressure. The effects of these variables on the nature of the calcine product are shown in Table 2.. At reaction temperatures above 500 C sintering of the product appears and volatilization of lead chloride begins. Preferred conditions appear to be a total process lime addition to lead mole ratio of about 3, a reaction temperature of about 400oC, a retention time of about 1 hour, and an excess of oxygen for lead oxidation. Pressure above atmospheric is not required for the reaction to be complete within 2 hours. Sufficient air or oxygen can be supplied for the reaction by convection, free or forced, or by pressurizing the reactor.
- It issurprising that calcium orthoplumbate (Ca2Pb04) is formed at high yields with such low temperatures and short retention times. Calcium orthoplumbate in a pure form (>90%) is a valuable commodity and is used- in the manufacture of primers for steel and galvanized steel, of pigments and of binders for paints. It also has use in the plastics and resin industries. The common commercial production method is the reaction of PbO with lime and air or oxygen at temperatures above 700°C. The reaction kinetics are reportedly slow below this temperature and the reaction will not go below 500°C. It has been reported by Denev, D.G. et al in Dokl.Bolg.Akad.Nauk, Vol.26 11,1973,.page 1485, however, that additions of small quantities of NaCl to the reaction mixture speed the kinetics. The present invention differs from the customary practice in that the reagent for calcination is lead oxychloride and not lead oxide. Also, the oxychloride is contaminated with significant quantities of NaCl and CaCl2. Accordingly, the kinetics and energetics of plumbate formation have been altered significantly from commercial experience.
- Figure 3 is a schematic plant layout for a particular embodiment of the invention relating to example 1.
- The following examples illustrate the practice of our invention but should not be construed as limiting.
- Samples of hot sulphuric acid leach residues obtained from the sulphation roasting and leaching of bulk zinc-lead-copper-silver sulphide concentrates assaying 30-32% Zn, 3.5-10% Pb, 0.7% Cu, 4.4 - 8.8 oz/ST (troy ounce per short ton) silver, and 14-23% iron were processed accordingly to the invention. A sample (example 10) of a hot acid leach residue from a dead roast zinc plant was also processed. The residues assayed as in Table 3.
- The residues were leached in brines of composition given in Table 4. Residue was added at a ratio of 15 gm of contained lead per litre of brine. The leaches were conducted at 35-40°C for 1.5 hours. Leach residues were allowed to settle and the thickened residues-filtered and washed with fresh brine. Extractions of lead and silver are given in Table 5. All of the zinc, iron and copper as sulphates in the hot sulphuric acid leach residues leached along with the lead and silver. Copper and bismuth assays in the brine were 40 and 45 mgpl respectively.
- One pregnant brine solution (example #6) was treated with zinc dust at an addition rate of 0.5 gpl producing a cementate containing 99% of the silver, 95% of the copper and 80% of the bismuth in the pregnant brine.
- The remaining pregnant brines and the solution resulting from the zinc dust cementation test were then treated with lime at 1.5 mole ratio to lead in the brine solution. The temperature and retention time were 45°C and 1.5 hours respectively.
- Precipitates were allowed to settle and the thickened precipitates filtered.
- The precipitates in all tests were then blended with lime, as required, to bring the total mole ratio of lime added to the process to lead in the precipitate to 1.75-5.5. The blends were
- A sample of the hot sulfuric acid leach residue used in example 5 was repulped in water at 10% pulp density, American Cyanamid flotation reagents Aero 404 (trade mark) promoter and Aerofroth 77A (trade mark) (frother) were added at 600 g. and 60 g. per metric ton of residue respectively. After 5 minutes conditioning time, flotation was initiated and a stable froth was maintained for about 7.5 minutes. The concentrate obtained assayed 18% Pb, 24% Fe, 1.8% Zn, and 635 oz/ST silver. Silver recovery from the head material was 70%.
- The tailings from the flotation were treated in the process exactly similar to example 4. Silver recovery from the tailings was 35%, resulting in an overall silver recovery of 81%.
- As will be apparent to those skilled in this art, the process of this invention may be applied to the recovery of metals from a variety of metallurgical products such as ores and concentrates, smelter dusts, metal drosses, middling concentrates from flotation processing, slags and process residues, and other like sources of lead and silver.
- The embodiments of the inventionwhich are of particular interest to the applicants are listed below in number order for convenience.
- 1. In a process comprising the steps of (1) preparing a solution of lead chloride by dissolving lead sulphate contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride by adding lime to said solution and separating said lead oxychloride precipitate from the residual lean brine solution; (4) recycling said lean brine for reuse in the further extraction of lead sulphate as under steps (1) and (2.); the improvement which comprises (5) reacting the said oxychloride precipitate with oxygen and lime in a reactor at a temperature above 325°C. for longer than 0.5 hours to produce a calcine containing most of the lead as calcium plumbates and/or lead oxides; (6) repulping said calcine in water and/or dilute chloride brine to dissolve soluble chlorides; (7) separating the residue obtained in step (6) from the resulting chloride brine; (8) recycling the brine resulting from (7) for reuse in the further extraction of lead sulphate as under steps (1) and (2); (9) washing said residue containing calcium plumbates and/or lead oxides resulting, from step (7) with fresh water to remove residual chlorides; and (10) recycling the chloride brine obtained in step (9) to step (6) and/or recycling the said chloride brine for reuse in the further extraction of lead sulphate as under steps (1) and (2).
- 2. In a process for gaining lead and silver values comprising the steps of (1) preparing a solution of lead chloride and silver compounds by dissolving lead sulphate and silver compounds contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride and silver compounds by adding lime to said solution and separating said precipitate from the residual lean brine solution for recycling said lean brine for reuse in the further extraction of lead sulphate as under steps (1) and (2); the improvement which comprises (5) reacting the said oxychloride precipitate-with oxygen and lime in a reactor at a temperature above 325°C for longer than one- half hour to produce a calcine-containing most of the lead as calcium plumbates and/or lead oxides and most of the silver as silver or silver compounds; (6) repulping said calcine in water and/or dilute chloride- brine to dissolve soluble chlorides; (7) separating the residue obtained in step (6) from the resulting chloride brine; (8) recycling the brine resulting from (7) for reuse in the further extraction of lead sulphate as under steps (1) and (2); (9) washing said residue containing calcium plumbates and/or lead oxides, as well as silver and silver compounds resulting from step (7) with fresh water to remove residual chlorides; and (10) recycling the chloride brine obtained in step (9) to step (6) and/or recycling the said chloride brine for reuse in the further extraction of lead sulphate as under steps (1) and (2).
- 3. The process of embodiment 1 wherein the lime in step (5) is excess lime present in the precipitate from step (3).
- 4. The process of embodiment 3 wherein fresh lime is added to supplement the excess lime present in the precipitate.
- 5. The process of embodiment 2 wherein the lime in step (5) is excess lime present in the precipitate from step (3).
- 6. The process of embodiment 2 wherein the fresh lime is added to supplement the excess lime present in the precipitate.
- 7. The process of embodiment 1 wherein the concentrated chloride brine comprises a saturated or nearly saturated solution at room temperature of one or more inorganic chlorides in water.
- 8. The process of embodiments 1 or 2, wherein one component of the chloride brine is calcium chloride.
- 9. The process of embodiments 1 or 2 wherein the chloride brine comprises an aqueous solution of calcium chloride and one or both of sodium and magnesium chloride.
- 10. The process of embodiments 1 or 2 wherein the chloride brine includes calcium chloride, and wherein the mole ratio of calcium chloride to lead sulphate is greater than 4.
- 11.. The process of embodiment 1- wherein step (1) is performed at a temperature in the
range 30°C to the boiling point of the chloride brine, at a pH between 1.5 and 4.5, and a retention time of 0.5 - 2.5 hours. - 12. The process of embodiment 11 wherein the temperature is ambient.
- 13. - The process of embodiment 11 wherein the pH is controlled at 1.5.
- 14. The process of embodiment 11 wherein the retention time is 1.5 hours.
- 15. The process of embodiment 1 wherein step (3) is performed by adding lime at a mole ratio of between 0.75 and 5.5 to dissolved lead.
- 16. ' The process of embodiment 15 wherein lime is added at a mole ratio of 1.5 to dissolved lead.
- 17. The process of embodiment 15 wherein the retention time is between 0.5 and 2.5 hours and the temperature in the
range 30°C to the boiling point of the chloride brine. - 18. The process of embodiment 17 wherein the retention time is 1.5 hours and the temperature is ambient.
- 19. The process of embodiment 1 wherein step (5) is performed by adding lime to the said oxychloride precipitate to increase the total of the lime additions in step (3) and step (5) to between 1.75 and 5.5 mole ratio to lead.
- 20. The process of embodiment 19wherein the total lime addition is 3.0 mole ratio to lead.
- 21. The process of embodiment 1 wherein step (5) is performed at a temperature above 350°C for longer than 0.5 hours.
- 22. The process of embodiment 21 wherein the temperature is 400°C for 1.0 hour.
- 23. The process of embodiment 1 wherein step (5) is performed with a mole ratio of oxygen to lead in excess of 0.5
- 24. The process of embodiment 23 wherein the oxygen is in the form of air.
- 25. The process of embodiment 2 wherein lead and silver are recovered in the residue from calcine washing step (9).
- 26. The process of embodiment 1 wherein lead is recovered in- the residue from calcine washing step (9).
- 27. The process of embodiment 2 wherein silver is recovered by cementation on one of metallic zinc, iron, or lead between step (2) and step (3).
- 28. The process of embodiment 2 wherein a portion of the silver is recovered from the lead sulphate containing material by flotation prior to step (1).
- 29. The process of embodiment 1,steps (3) , (5) , (6) , (7), and (9) inclusive,wherein the solution from which lead oxychloride is precipitated is any chloride brine solution containing lead chloride.
- 30. The process of embodiment 29 wherein the chloride brines lean in lead resulting from any or all of steps (3), (7), and (9) are recycled to dissolve fresh lead chloride.. 1 or 2
- 31. The process of embodiment/wherein the brine is concentrated before recycling.
- 32. The process of embodiment 1 or 2 wherein the brine is concentrated by evaporating or by adding further chloride before recycling.
- 1 or 2 33. The process of-embodiment wherein the brine is re-acidified before recycling.
- 34. The process of embodiment 1or 2 wherein the acidic concentrated chloride brine has a pH of about 1.5.
- 35. The process of embodiment 2 wherein step (1) is performed at a temperature in the
range 30°C to the boiling point of the chloride brine, at a pH between 1.5 and 4.5, and a retention time of 0.5 - 2..5 hours. - 36. The-process of embodiment 35 wherein the temperature is ambient.
- 37. The process of embodiment 35 wherein the pH is controlled at 1.5.
- 38. The process of embodiment 35 wherein the retention time is 1.5 hours.
- 39. A process comprising the steps of (1) preparing a solution of lead chloride by dissolving lead sulphate contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride by adding lime to said solution and separating said lead oxychloride precipitate from the residual lean brine solution; (4) reacting the said oxychloride precipitate with oxygen and lime in a reactor in an elevated temperature to produce a calcine-containing most of the lead as calcium plumbates and/or lead oxides; (5) washing said calcine in water and/or dilute chloride brine to dissolve soluble chlorides; (6) separating the resulting residue obtained from the resulting chloride brine; and, (7) washing said residue containing calcium plumbates and/or lead oxides with fresh water to remove residual chlorides.
- 40. The process -of embodiment 39 wherein the chloride brines resulting from the steps are recycled for reuse in the process.
- 41. A process for gaining lead and silver values comprising the steps of (1) preparing a solution of lead chloride and silver compounds by dissolving lead sulphate and silver compounds contained in an ore or process residue in an acidic concentrated chloride brine; (2) separating the solution so formed from insoluble gangue or other residue; (3) forming a precipitate of lead oxychloride and silver compounds by adding lime to said solution and separating said precipitate from the residual lean brine solution; (4) reacting the said oxychloride precipitate with oxygen or a gas containing molecular oxygen and lime in a reactor at an elevated temperature to produce a calcine containing most of the lead as calcium plumbates and/or oxides and most of the silver as silver or silver compounds; (5) washing said calcine in water and/or dilute chloride brine to dissolve sol uble - chlorides; (6) separating the resulting residue from the resulting chloride brine; and, optionally (7) washing said residue containing calcium plumbates and/or lead oxides, as well as silver and silver compounds, with fresh water to remove residual chlorides.
- 42. The process of embodiment 41 wherein the chloride brines resulting from the steps are recycled for..reuse in the process.
- 43. A process for recovering lead from lead chloride solution which comprises reacting the solution with lime to form a precipitate of lead oxychloride, reacting said precipitate with lime and a gas comprising or consisting of molecular oxygen to form residue comprising calcium plumbate and/or lead oxide, and separating said residue (being recovered lead) from'the product mixture, the residue then optionally being treated in a furnace to recover elemental lead.
Claims (20)
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CA354083 | 1980-06-16 | ||
CA000354083A CA1156048A (en) | 1980-06-16 | 1980-06-16 | Process for the recovery of lead and silver from minerals and process residues |
Publications (2)
Publication Number | Publication Date |
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EP0042702A1 true EP0042702A1 (en) | 1981-12-30 |
EP0042702B1 EP0042702B1 (en) | 1984-09-26 |
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ID=4117190
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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EP81302614A Expired EP0042702B1 (en) | 1980-06-16 | 1981-06-12 | Process for the recovery of lead and silver from minerals and process residues |
Country Status (10)
Country | Link |
---|---|
EP (1) | EP0042702B1 (en) |
JP (1) | JPS5729541A (en) |
AU (1) | AU549357B2 (en) |
CA (1) | CA1156048A (en) |
DE (1) | DE3166293D1 (en) |
ES (1) | ES8301284A1 (en) |
FI (1) | FI71342C (en) |
IE (1) | IE52179B1 (en) |
PT (1) | PT73185B (en) |
ZA (1) | ZA813982B (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101994007B (en) * | 2009-08-28 | 2012-08-15 | 沈阳有色金属研究院 | Method for removing sulfur from waste lead-acid storage battery gypsum mud by using magnesium chloride |
CN104789790A (en) * | 2015-04-08 | 2015-07-22 | 吉林吉恩镍业股份有限公司 | Lead-free smelting process for leaded gold concentrate obtained through Knelson concentration |
RU2670117C2 (en) * | 2013-09-27 | 2018-10-18 | Текникас Реунидас, С.А. | Process for the selective recovery of lead and silver and carbonate lead and silver concentrate, obtained by the method above |
CN112442602A (en) * | 2020-10-09 | 2021-03-05 | 超威电源集团有限公司 | Waste lead plaster recovery method |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
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JP5046263B2 (en) * | 2005-06-24 | 2012-10-10 | 株式会社吉野工業所 | Cap for liquid dispensing container |
JP4781794B2 (en) * | 2005-11-28 | 2011-09-28 | キユーピー株式会社 | Dispensing container |
CN109022817A (en) * | 2018-07-27 | 2018-12-18 | 郴州雄风环保科技有限公司 | The new process of high chlorine lead smelting gas dechlorination |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US1434085A (en) * | 1920-01-02 | 1922-10-31 | Niels C Christensen | Process of treating ores with chloride solutions |
US1745945A (en) * | 1924-01-08 | 1930-02-04 | Us Smelting Refining & Mining | Process of treating ores or analogous materials |
GB365964A (en) * | 1930-06-17 | 1932-01-28 | Paul Gamichon | Process for converting into soluble salts lead and other metals contained in lead bearing ores |
US3477928A (en) * | 1966-03-28 | 1969-11-11 | Cerro Corp | Process for the recovery of metals |
FR2297253A1 (en) * | 1975-01-08 | 1976-08-06 | Duisburger Kupferhuette | Work-lead obtd. from sulphate residues - leached with chloride soln., then lead oxychloroide is pptd. and roasted with redn. agent |
FR2459292A1 (en) * | 1980-03-24 | 1981-01-09 | Asua Ind Quim | Physico:chemical treatment of silver:lead residues - obtd. in winning zinc, and which are treated with sodium chloride or acid solns. to obtain filter cake used for winning silver and lead |
-
1980
- 1980-06-16 CA CA000354083A patent/CA1156048A/en not_active Expired
-
1981
- 1981-06-11 ES ES502948A patent/ES8301284A1/en not_active Expired
- 1981-06-12 IE IE1310/81A patent/IE52179B1/en not_active IP Right Cessation
- 1981-06-12 ZA ZA813982A patent/ZA813982B/en unknown
- 1981-06-12 DE DE8181302614T patent/DE3166293D1/en not_active Expired
- 1981-06-12 PT PT73185A patent/PT73185B/en unknown
- 1981-06-12 FI FI811847A patent/FI71342C/en not_active IP Right Cessation
- 1981-06-12 EP EP81302614A patent/EP0042702B1/en not_active Expired
- 1981-06-15 AU AU71846/81A patent/AU549357B2/en not_active Ceased
- 1981-06-16 JP JP9294681A patent/JPS5729541A/en active Granted
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US1434085A (en) * | 1920-01-02 | 1922-10-31 | Niels C Christensen | Process of treating ores with chloride solutions |
US1745945A (en) * | 1924-01-08 | 1930-02-04 | Us Smelting Refining & Mining | Process of treating ores or analogous materials |
GB365964A (en) * | 1930-06-17 | 1932-01-28 | Paul Gamichon | Process for converting into soluble salts lead and other metals contained in lead bearing ores |
US3477928A (en) * | 1966-03-28 | 1969-11-11 | Cerro Corp | Process for the recovery of metals |
FR2297253A1 (en) * | 1975-01-08 | 1976-08-06 | Duisburger Kupferhuette | Work-lead obtd. from sulphate residues - leached with chloride soln., then lead oxychloroide is pptd. and roasted with redn. agent |
FR2459292A1 (en) * | 1980-03-24 | 1981-01-09 | Asua Ind Quim | Physico:chemical treatment of silver:lead residues - obtd. in winning zinc, and which are treated with sodium chloride or acid solns. to obtain filter cake used for winning silver and lead |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101994007B (en) * | 2009-08-28 | 2012-08-15 | 沈阳有色金属研究院 | Method for removing sulfur from waste lead-acid storage battery gypsum mud by using magnesium chloride |
RU2670117C2 (en) * | 2013-09-27 | 2018-10-18 | Текникас Реунидас, С.А. | Process for the selective recovery of lead and silver and carbonate lead and silver concentrate, obtained by the method above |
CN104789790A (en) * | 2015-04-08 | 2015-07-22 | 吉林吉恩镍业股份有限公司 | Lead-free smelting process for leaded gold concentrate obtained through Knelson concentration |
CN112442602A (en) * | 2020-10-09 | 2021-03-05 | 超威电源集团有限公司 | Waste lead plaster recovery method |
Also Published As
Publication number | Publication date |
---|---|
IE52179B1 (en) | 1987-08-05 |
JPS6352094B2 (en) | 1988-10-18 |
AU7184681A (en) | 1981-12-24 |
DE3166293D1 (en) | 1984-10-31 |
EP0042702B1 (en) | 1984-09-26 |
FI71342B (en) | 1986-09-09 |
ZA813982B (en) | 1982-08-25 |
PT73185A (en) | 1981-07-01 |
AU549357B2 (en) | 1986-01-23 |
IE811310L (en) | 1981-12-16 |
FI71342C (en) | 1986-12-19 |
CA1156048A (en) | 1983-11-01 |
ES502948A0 (en) | 1982-11-16 |
ES8301284A1 (en) | 1982-11-16 |
PT73185B (en) | 1982-07-16 |
FI811847L (en) | 1981-12-17 |
JPS5729541A (en) | 1982-02-17 |
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