CN107012328A - A kind of high ferro zinc leaching residue clean utilization method - Google Patents

A kind of high ferro zinc leaching residue clean utilization method Download PDF

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Publication number
CN107012328A
CN107012328A CN201710139793.9A CN201710139793A CN107012328A CN 107012328 A CN107012328 A CN 107012328A CN 201710139793 A CN201710139793 A CN 201710139793A CN 107012328 A CN107012328 A CN 107012328A
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zinc
high ferro
leaching residue
zinc leaching
utilization method
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郑永兴
王�华
文书明
吕晋芳
蓝卓越
杨春曦
赖振宁
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Kunming University of Science and Technology
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Kunming University of Science and Technology
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    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/001Dry processes
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B1/00Preliminary treatment of ores or scrap
    • C22B1/02Roasting processes
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B1/00Preliminary treatment of ores or scrap
    • C22B1/26Cooling of roasted, sintered, or agglomerated ores
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B11/00Obtaining noble metals
    • C22B11/02Obtaining noble metals by dry processes
    • C22B11/021Recovery of noble metals from waste materials
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B13/00Obtaining lead
    • C22B13/02Obtaining lead by dry processes
    • C22B13/025Recovery from waste materials
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B15/00Obtaining copper
    • C22B15/0026Pyrometallurgy
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B19/00Obtaining zinc or zinc oxide
    • C22B19/30Obtaining zinc or zinc oxide from metallic residues or scraps
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B30/00Obtaining antimony, arsenic or bismuth
    • C22B30/06Obtaining bismuth
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B58/00Obtaining gallium or indium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/001Dry processes
    • C22B7/002Dry processes by treating with halogens, sulfur or compounds thereof; by carburising, by treating with hydrogen (hydriding)
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Abstract

The present invention relates to a kind of high ferro zinc leaching residue clean utilization method, belong to selecting and smelting technology field.First by high ferro zinc leaching residue drying and dehydrating; then reducing agent and vulcanizing agent are added simultaneously; carbon sulphur mixed atmosphere, which is carried out, under the conditions of temperature is 400 DEG C ~ 900 DEG C is calcined anti-0.5h ~ 3.5h; after roasting terminates; it is passed through nitrogen or argon gas makees protective gas; Slow cooling is carried out with 150 DEG C/h ~ 300 DEG C/h speed, water quenching obtains Water Quenching Slag after temperature is down to below 200 DEG C;Obtained Water Quenching Slag is carried out to conventional flotation processing, artificial sulphide concentrate and flotation tailing is obtained;Obtained flotation tailing is subjected to conventional magnetic separator and obtains zinc-iron oxides concentrate, zinc-iron oxides concentrate is passed through gaseous reducing agent and is 950 DEG C ~ 1300 DEG C reduction volatilization reaction 1.0h ~ 4.0h in temperature, after reduction volatilization terminates, the zinc product containing indium is obtained after the gas evaporated is reclaimed, iron product is obtained after remaining solid cooling of volatilizing.The valuable metal such as copper of the present invention, lead, zinc, indium and silver element can high efficiente callback and high-valued, cleaning new technology without scum generation.

Description

A kind of high ferro zinc leaching residue clean utilization method
Technical field
The present invention relates to a kind of high ferro zinc leaching residue clean utilization method, belong to selecting and smelting technology field.
Background technology
High ferro zinc leaching residue is that high-iron zinc sulfide concentrate leaches a kind of intermediate obtained after flow for-two sections by fluidized bed roasting Material, it is always the problem that domestic and international metallurgy industry needs to be broken through that high-valued and clean utilization is carried out to it.
In zinc metallurgical process, because zinc concentrate is often associated with 10% or so ferro element, in order to reach in roasting process Zinc amount in zinc ferrite, zinc ferrite accounts for total zinc amount 8% ~ 10% is inevitably generated in preferable desulfurization degree, zinc calcine.When zinc essence Ore deposit is the high iron charge that China is largely present(≥10%)Or during marmatite, ferrous acid Zn content can be higher in calcining.Zinc ferrite category is difficult Zinc species are soaked, neutrality is leached and Weak-acid leaching link is difficult to be leached, and substantial amounts of leached mud can be produced in leaching process.Hot acid Leach successfully solve zinc leaching rate improve and valuable metal lead silver recovery problem, but also generate two it is big new the problem of:Remove Iron is burdensome, complex operation, production cost high;A large amount of iron dross removings are produced, valuable element loses big with scum, and iron resource can not It is utilized effectively, there are a large amount of unstable heavy metal contaminants in scum, the process leaching ability of heavy metal of storing up easily causes secondary dirt Dye etc., country has prohibited the outdoor of heavy scum and stored up.After fire metallurgy process processing the high ferro acid leaching residue quantity of slag is few, scum is dirty Dye is small, is the new direction that zinc cleans smelting technique.However, nowadays rotary kiln technology Jiao amount consumption is up to the 50% of the quantity of slag, cause big Measure CO2 emission and need to increase low concentration SO2Smoke processing system.In addition, iron, rare precious metal and gangue content have been given birth to Into composite solid solution, rare precious metal and iron resource is caused to be difficult to reclaim.
Appoint as the continuous reinforcement of people's environmental consciousness, especially country attach most importance in the formulation energy-saving and emission-reduction of 12 periods Since business, the thinking of development low-carbon green economy, and lead zinc deficiency and excess price is depressed, and Some Enterprises start to stop to such smelting The pyrogenic attack of slag is refined, causes a large amount of zinc smelting slags to have to handle in the way of storing up or direct out sale, causes serious ring Border pollution and the waste of valuable resource.Therefore, exploitation zinc smelting dreg cleaning treatment new technology to alleviate resource supply and demand contradiction with And reduction environmental pollution has great importance.
Selecting smelting combination technology is zinc smelting dreg cleaning treatment research new trend in recent years.Chinese patent The method that reduction roasting is used in CN201110332253.5, CN201110096566.5 and CN201210122328.1, leads to Being precisely controlled for different reducing conditions is crossed, zinc ferrite selectivity zinc oxide and ferroso-ferric oxide is reduced to, then using magnetic Choosing and the method for weak-acid leaching, realize efficiently separating for zinc-iron, but still there is the reduction of crossing of iron, and a large amount of iron enter after zinc leaching Enter to leach the problems such as the recovering effect such as night and other metals such as lead, silver and indium is undesirable.In addition, primarily directed to zinc in patent The zinc calcine that concentrate is obtained after fluidized bed furnace is handled, and the high ferro zinc leaching residue containing copper, silver and lead zinc sulfate is paid close attention to It is less.For the slag charge of leaded zinc sulfate, the research team where applicants is once by introducing reducing atmosphere, by lead The autovulcanization of zinc sulfate selectivity then uses flotation, the certain conversion of acquirement and flotation recovering effect for artificial sulphide ore (CN201310065266.X), but do not proposed for the high-valued and clean utilization of the high ferro zinc leaching residue containing various ingredients The method of effect.
The content of the invention
The environmental pollution brought for a large amount of high ferro zinc leaching residues produced in Zinc Hydrometallurgy Process, wet method or pyrogenic process are recycled into This height, conventional beneficiation method reclaims a series of problems, such as valuable metal difficulty is big, the present invention is intended to provide a kind of high ferro zinc leaching residue High-valued, clean utilization method, material is dehydrated by this method first, after drying process, by slag under carbon-sulphur mixed atmosphere In material lead zinc sulfate selectivity be converted into artificial sulphide ore, while realize copper, bismuth and silver vulcanization and zinc ferrite magnetic Change conversion, artificial sulphide ore and high-purity ferrous acid zinc concentrate are then respectively obtained using floating-magnetic combined process flow, the former can be used as zinc Concentrate sells, and the latter is by obtaining zinc product and high-grade ironmaking material containing indium after reduction volatilization.The present invention is by following Technical scheme is realized.
A kind of high ferro zinc leaching residue clean utilization method, it is comprised the following steps that:
(1)First by high ferro zinc leaching residue drying and dehydrating, reducing agent and vulcanizing agent are then added simultaneously, are 400 DEG C ~ 900 in temperature Carbon-sulphur mixed atmosphere is carried out under the conditions of DEG C and is calcined anti-0.5h ~ 3.5h, after roasting terminates, nitrogen is passed through or argon gas makees protective gas, Slow cooling is carried out with 150 DEG C/h ~ 300 DEG C/h speed, water quenching obtains Water Quenching Slag after temperature is down to below 200 DEG C;
Specifically reaction equation is:
PbSO4+ 4C = PbS + 4CO(g) (1)
ZnSO4+ 4C = ZnS + 4CO(g) (2)
PbSO4 + 4CO(g) = PbS + 4CO2(g) (3)
ZnSO4 + 4CO(g) = ZnS + 4CO2(g) (4)
3ZnFe2O4(s) + C(s) = 3ZnO(s) + 2Fe3O4(s) + CO(g) (5)
3ZnFe2O4(s) + CO(g) = 3ZnO(s) + 2Fe3O4(s) + CO2(g) (6)
Fe2O3(s) + C(s) =2Fe3O4(s) + CO(g) (7)
Fe2O3(s) + CO(g) = 2Fe3O4(s) + CO2(g) (8)
FeS2= FeS+1/2S2(g) (9)
S→S2(g) (10)
2CuO+3/2S2(g)=2CuS+SO2(g) (11)
2CuO+ C+S2 (g)=2CuS+CO2 (g) (12)
2BiO+3/2S2(g)=2BiS+SO2(g) (13)
2BiO+ C+S2 (g)=2BiS+CO2 (g) (14)
4Ag2O+5S2(g)=8AgS+2SO2(g) (15)
2Ag2O+ C+2S2 (g)=4AgS+CO2 (g) (16)
Wherein react(1)~(4)The autovulcanization for being lead zinc sulfate under reducing atmosphere reaction,(5)~(8)For zinc ferrite and three Aoxidize the magnetization decomposition reaction of two iron;(9)~(16)For the vulcanization reaction of copper, bismuth and silver oxide;
(2)By step(1)Obtained Water Quenching Slag carries out conventional flotation processing, obtains artificial sulphide concentrate and flotation tailing; Vulcanization ore deposit floating agent system is used, flotation flowsheet is bulk flotation or diffeential floatation, and wherein bulk flotation is obtained Be bulk concentrate, what diffeential floatation was obtained is single copper, lead and zinc concentrate;
(3)By step(2)Obtained flotation tailing carries out conventional magnetic separator and obtains zinc-iron oxides concentrate, zinc-iron oxides Concentrate is passed through gaseous reducing agent and is 950 DEG C ~ 1300 DEG C reduction volatilization reaction 1.0h ~ 4.0h in temperature, after reduction volatilization terminates, The zinc product containing indium is obtained after the gas evaporated is reclaimed(Zinc product containing indium is metal zinc or oxide powder and zinc, metal The composition of zinc powder is:Zn90% ~ 95%, In0.5 ~ 2%, other 3% ~ 9.5%, the composition of oxide powder and zinc for Zn50% ~ 75%, In0.5 ~ 3% other 23% ~ 49.5%), iron product is obtained after remaining solid cooling of volatilizing(Composition is Fe85 ~ 97%, other 3 ~ 15%), wave Sending out reaction equation specific is:
ZnFe2O4(s) + 4H2(g)= Zn(g) + 2Fe(s) + 4H2O(g) (17)
ZnFe2O4(s) + 4CO(g) = Zn(g) + 2Fe(s) + 4CO2(g) (18)
ZnO(s) + H2(g) = Zn(g) + H2O(g) (19)
ZnO(s) + CO(g) = Zn (g) + CO2(g) (20)
In2O3+ 3CO(g) =2In(g) + 3CO2(g) (21)
In2O3 + 3H2(g) = 2In(g) + 3H2O(g) (22)
FeO(s) + H2(g) = Fe(s) + H2O(g) (23)
FeO(s) + CO(g) = Fe(s) + CO2(g) (24).
The high ferro zinc leaching residue includes following mass percent component:Pb2~5%、Zn10~20%、Fe15~25%、Ag200~ 400g/t and In150 ~ 450g/t.
The step(1)Middle reducing agent and vulcanizing agent be in sulphur coal, sulphur coal carbon content be 70wt% ~ 85wt%, sulphur Content 3wt% ~ 6wt%, addition is high ferro zinc leaching residue quality 6% ~ 15%.
The step(1)Middle reducing agent is solid reductant or gaseous reducing agent.
The solid reductant is one or more of arbitrary proportion mixtures in activated carbon, coke, carbon dust, and addition is High ferro zinc leaching residue quality 5% ~ 12%.
The gaseous reducing agent is carbon monoxide, hydrogen, producer gas, one or more of arbitrary proportions of coke-stove gas Mixture;Gaseous reducing agent volumetric concentration containing CO 10% ~ 50%, the H2Volumetric concentration 1% ~ 12%, remaining component is N2
The step(1)Middle vulcanizing agent is vulcanized sodium, pyrite or sulphur, and addition is high ferro zinc leaching residue quality 1% ~ 4%.
The step(3)Middle magnetic separator magnetic field intensity is 0.5 ~ 1T.
The step(3)CO volumetric concentrations are 30% ~ 90%, H in middle gaseous reducing agent2Volumetric concentration is 8% ~ 60%, remaining Component is N2
The beneficial effects of the invention are as follows:
(1)In carbon-sulphur mixed atmosphere, realize in slag charge the oxide curative such as lead zinc sulfate autovulcanization, copper, bismuth and silver and The magnetized height coupling of zinc ferrite, has decreased or even eliminated the problem of environmental pollution brought of sulfur dioxide, simultaneously from source Technique of preparing for low cost, low stain creates condition;
(2)Zinc-iron oxides after magnetization do not need ore grinding, directly carry out the magnetic separation in moderate strength magnetic field, improve the comprehensive of zinc-iron Close grade and the rate of recovery.After the zinc-iron oxides reduction volatilization of purifying, obtained zinc, indium is obtained in the form of zinc powder or secondary zinc oxide To reclaim, residue is high-grade iron granule, directly as iron-smelting raw material;
(3)Lead, zinc, indium and silver-colored comprehensive recovery improve 3 ~ 8%, and copper and bismuth comprehensive recovery improve 10% ~ 40%, and iron is integrated back Yield improves 20 ~ 50%;
(4)The present invention is that one kind is produced without SO 2 tail gas, and the valuable metal element such as copper, lead, zinc, indium and silver can high efficiente callback And high-valued, the cleaning new technology generated without scum.
Brief description of the drawings
Fig. 1 is present invention process flow chart.
Embodiment
With reference to the accompanying drawings and detailed description, the invention will be further described.
Embodiment 1
As shown in figure 1, the high ferro zinc leaching residue clean utilization method, it is comprised the following steps that:
(1)First by high ferro zinc leaching residue(The content of copper and bismuth is very low in the high ferro zinc leaching residue, and its chemical composition is:Pb3.4%、 Zn16.5%, Fe21.5%, Ag272.3g/t, In278.5g/t, the chemical and physical phase of lead is PbSO476%th, PbS8%, other 16%, zinc Chemical and physical phase be:ZnSO438.6%、ZnFe2O458.3%, other 3.1%, silver-colored chemical and physical phase is:Ag2O18.6%、 AgS74.4%, other 7%)Drying and dehydrating, then adds reducing agent simultaneously(Carbon dust, addition is high ferro zinc leaching residue quality 12%)With Vulcanizing agent(Vulcanized sodium, addition is high ferro zinc leaching residue quality 1%), carbon-sulphur mixed atmosphere is carried out under the conditions of temperature is 750 DEG C Anti- 1.5h is calcined, after roasting terminates, nitrogen is passed through or argon gas makees protective gas, Slow cooling is carried out with 150 DEG C/h speed, treated Temperature is down to water quenching after 200 DEG C and obtains Water Quenching Slag;
(2)By step(1)Obtained Water Quenching Slag carries out conventional flotation processing, obtains artificial sulphide concentrate(The concentrate is lead Grade 14.5%, zinc grade 34.5%, silver-colored grade 1000g/t bulk concentrate)And flotation tailing;
(3)By step(2)Obtained flotation tailing carries out conventional magnetic separator(Fixed magnetic field intensity is 0.75T)Obtain zinc-iron Oxide concentrate(Chemical composition is Zn21.5%, Fe44.1%, other 34.4%), zinc-iron oxides concentrate is passed through gaseous reducing agent (CO volumetric concentrations are 50%, H in gaseous reducing agent2Volumetric concentration is 15%, and remaining component is N2)And be 1150 DEG C of reduction in temperature Volatiling reaction 1.0h, after reduction volatilization terminates, the zinc product containing indium is obtained after the gas evaporated is reclaimed(Zinc production containing indium Product are oxide powder and zinc, and the composition of oxide powder and zinc is Zn70.5%, In1.7% other 27.8%), after remaining solid cooling of volatilizing To iron product(Composition is Fe92.3%, other 7.7%).
Lead, zinc recovery are respectively 92% and 95% in whole flow process, and the silver-colored rate of recovery is 80%, and the rate of recovery of iron is 90%.
Embodiment 2
As shown in figure 1, the high ferro zinc leaching residue clean utilization method, it is comprised the following steps that:
(1)First by high ferro zinc leaching residue(Its chemical composition is:Pb2.3%、Zn14.4%、Fe19.8%、Ag389.6g/t、 Cu1.4%, In278.5g/t and Bi0.96%, the chemical and physical phase of lead is PbSO468.9%th, PbS12%, other 9.1%, the chemistry of zinc Thing is mutually:ZnSO442.5%、ZnFe2O453.8%, other 3.7%, silver-colored chemical and physical phase is:Ag2O13.8%, AgS71.2%, it is other 15%, the chemical and physical phase of copper is:CuO84.2%, CuS13.9%, other 1.9%, the chemical and physical phase of bismuth is:BiO76.2%、 BiS21.3%, other 2.5%)Drying and dehydrating, then adds reducing agent and vulcanizing agent simultaneously(Reducing agent and vulcanizing agent are high-sulfur Carbon content is 80wt% in coal, sulphur coal, and sulfur content 5.5wt%, addition is high ferro zinc leaching residue quality 14.5%), it is in temperature Carbon-sulphur mixed atmosphere is carried out under the conditions of 850 DEG C and is calcined anti-2.0h, after roasting terminates, nitrogen is passed through or argon gas makees protective gas, with 300 DEG C/h speed carries out Slow cooling, and water quenching obtains Water Quenching Slag after temperature is down to 180 DEG C;
(2)By step(1)Obtained Water Quenching Slag carries out conventional flotation processing, obtains artificial sulphide concentrate(The concentrate is lead Grade is 10.2%, zinc grade 38.8%, silver-colored grade 1870g/t, copper grade 4.3%, the bulk concentrate of bismuth grade 2.8%)And flotation Mine tailing;
(3)By step(2)Obtained flotation tailing carries out conventional magnetic separator(Fixed magnetic field intensity is 0.8T)Obtain zinc-iron Oxide concentrate(Chemical composition is Zn20.2%, Fe44.1%, other 35.7%), zinc-iron oxides concentrate is passed through gaseous reducing agent (CO volumetric concentrations are 60%, H in gaseous reducing agent2Volumetric concentration is 10%, and remaining component is N2)And be 1200 DEG C of reduction in temperature Volatiling reaction 1.5h, after reduction volatilization terminates, the zinc product containing indium is obtained after the gas evaporated is reclaimed(Zinc production containing indium Product are oxide powder and zinc, and the composition of oxide powder and zinc is Zn68.8%, In2.3%), iron product is obtained after remaining solid cooling of volatilizing (Composition is Fe95.1%).
Lead, zinc recovery are respectively 95% and 95.5% in whole flow process, and the silver-colored rate of recovery is 87%, copper, the bismuth rate of recovery 84.5%, the rate of recovery of iron is 89%.
Embodiment 3
As shown in figure 1, the high ferro zinc leaching residue clean utilization method, it is comprised the following steps that:
(1)First by high ferro zinc leaching residue(Its chemical composition is:Pb3.4%, Zn10%, Fe25%, Ag350g/t, Cu2.4%, In450g/t and Bi1.8%, the chemical and physical phase of lead is PbSO472.5%th, PbS2.5%, other 25%, the chemical and physical phase of zinc is: ZnSO438.5%、ZnFe2O455.2%, other 6.3%, silver-colored chemical and physical phase is:Ag2O21.5%, AgS74.5%, other 4%, copper Chemical and physical phase is:CuO78.5%, CuS14.5%, other 7%, the chemical and physical phase of bismuth is:BiO68.4%, BiS19.6%, other 12%) Drying and dehydrating, then adds reducing agent simultaneously(Reducing agent is that volume ratio is 1:1 carbon monoxide and producer gas mixed gas Reducing agent, reducing agent intake is 2L/min units, gaseous reducing agent volumetric concentration containing CO 50%, the H2Volumetric concentration 12%, its Remaining component is N2)And vulcanizing agent(Vulcanizing agent is pyrite, and addition is high ferro zinc leaching residue quality 4%), it is 400 DEG C of bars in temperature Carbon-sulphur mixed atmosphere is carried out under part and is calcined anti-3.5h, after roasting terminates, nitrogen is passed through or argon gas makees protective gas, with 250 DEG C/h Speed carry out Slow cooling, water quenching obtains Water Quenching Slag after temperature is down to 180 DEG C;
(2)By step(1)Obtained Water Quenching Slag carries out conventional flotation processing, obtains artificial sulphide concentrate(The concentrate is lead Grade is 14.5%, zinc grade 34.2%, silver-colored grade 1950g/t, copper grade 6.2%, the bulk concentrate of bismuth grade 4.2%)And flotation Mine tailing;
(3)By step(2)Obtained flotation tailing carries out conventional magnetic separator(Fixed magnetic field intensity is 0.5T)Obtain zinc-iron Oxide concentrate(Chemical composition is Zn18.5%, Fe42.5%, other 39%), zinc-iron oxides concentrate is passed through gaseous reducing agent(Gas CO volumetric concentrations are 90%, H in body reducing agent2Volumetric concentration is 8%, and remaining component is N2)And be 950 DEG C of reduction volatilizations in temperature 4.0h is reacted, after reduction volatilization terminates, the zinc product containing indium is obtained after the gas evaporated is reclaimed(Zinc product containing indium is Oxide powder and zinc, the composition of oxide powder and zinc is Zn70.5%, In3.5%), iron product is obtained after remaining solid cooling of volatilizing(Composition For Fe94.5%).
Lead, zinc recovery are respectively 96% and 94.2% in whole flow process, and the silver-colored rate of recovery is 85.5%, copper, the bismuth rate of recovery 84.5%, the rate of recovery of iron is 90%.
Embodiment 4
As shown in figure 1, the high ferro zinc leaching residue clean utilization method, it is comprised the following steps that:
(1)First by high ferro zinc leaching residue(Its chemical composition is:Pb5%, Zn19.4%, Fe15%, Ag200g/t, Cu2.4%, In150g/t and Bi1.5%, the chemical and physical phase of lead is PbSO475.4%th, PbS3.5%, other 21.1%, the chemical and physical phase of zinc is: ZnSO441.5%、ZnFe2O457.5%, other 1%, silver-colored chemical and physical phase is:Ag2O20.4%, AgS75.6%, other 4%, the change of copper Learning thing is mutually:CuO46.8%, CuS51.4%, other 1.8%, the chemical and physical phase of bismuth is:BiO38.2%, BiS56.8%, other 5%) Drying and dehydrating, then adds reducing agent simultaneously(Reducing agent is coke, and addition is high ferro zinc leaching residue quality 5%)And vulcanizing agent(Sulphur Agent is sulphur, and addition is high ferro zinc leaching residue quality 3%), carbon-sulphur mixed atmosphere roasting is carried out under the conditions of temperature is 600 DEG C Anti- 0.5h, after roasting terminates, is passed through nitrogen or argon gas makees protective gas, carries out Slow cooling with 200 DEG C/h speed, treats temperature It is down to water quenching after 180 DEG C and obtains Water Quenching Slag;
(2)By step(1)Obtained Water Quenching Slag carries out conventional flotation processing, obtains artificial sulphide concentrate(The concentrate is lead Grade is 11.6%, zinc grade 28.9%, silver-colored grade 1785g/t, copper grade 5%, the bulk concentrate of bismuth grade 3%)And flotation tailing;
(3)By step(2)Obtained flotation tailing carries out conventional magnetic separator(Fixed magnetic field intensity is 1.0T)Obtain zinc-iron Oxide concentrate(Chemical composition is Zn19.2%, Fe46.4%, other 35.4%), zinc-iron oxides concentrate is passed through gaseous reducing agent (CO volumetric concentrations are 30%, H in gaseous reducing agent2Volumetric concentration is 60%, and remaining component is N2)And be 1300 DEG C of reduction in temperature Volatiling reaction 2.0h, after reduction volatilization terminates, the zinc product containing indium is obtained after the gas evaporated is reclaimed(Zinc production containing indium Product are oxide powder and zinc, and the composition of oxide powder and zinc is Zn65.6%, In2.8%), iron product is obtained after remaining solid cooling of volatilizing (Composition is Fe 90.8%).
Lead, zinc recovery are respectively 92.5% and 95.2% in whole flow process, and the silver-colored rate of recovery is 81.5%, copper, the bismuth rate of recovery 82.5%, the rate of recovery of iron is 88%.
Above in association with accompanying drawing to the present invention embodiment be explained in detail, but the present invention be not limited to it is above-mentioned Embodiment, can also be before present inventive concept not be departed from the knowledge that those of ordinary skill in the art possess Put that various changes can be made.

Claims (9)

1. a kind of high ferro zinc leaching residue clean utilization method, it is characterised in that comprise the following steps that:
(1)First by high ferro zinc leaching residue drying and dehydrating, reducing agent and vulcanizing agent are then added simultaneously, are 400 DEG C ~ 900 in temperature Carbon-sulphur mixed atmosphere is carried out under the conditions of DEG C and is calcined anti-0.5h ~ 3.5h, after roasting terminates, nitrogen is passed through or argon gas makees protective gas, Slow cooling is carried out with 150 DEG C/h ~ 300 DEG C/h speed, water quenching obtains Water Quenching Slag after temperature is down to below 200 DEG C;
(2)By step(1)Obtained Water Quenching Slag carries out conventional flotation processing, obtains artificial sulphide concentrate and flotation tailing;
(3)By step(2)Obtained flotation tailing carries out conventional magnetic separator and obtains zinc-iron oxides concentrate, zinc-iron oxides Concentrate is passed through gaseous reducing agent and is 950 DEG C ~ 1300 DEG C reduction volatilization reaction 1.0h ~ 4.0h in temperature, after reduction volatilization terminates, The zinc product containing indium is obtained after the gas evaporated is reclaimed, iron product is obtained after remaining solid cooling of volatilizing.
2. high ferro zinc leaching residue clean utilization method according to claim 1, it is characterised in that:The high ferro zinc leaching residue includes Following mass percent component:Pb2 ~ 5%, Zn10 ~ 20%, Fe15 ~ 25%, Ag200 ~ 400g/t and In150 ~ 450g/t.
3. high ferro zinc leaching residue clean utilization method according to claim 1, it is characterised in that:The step(1)Middle reduction Agent and vulcanizing agent be in sulphur coal, sulphur coal carbon content be 70wt% ~ 85wt%, sulfur content 3wt% ~ 6wt%, addition is high ferro Zinc leaching residue quality 6% ~ 15%.
4. high ferro zinc leaching residue clean utilization method according to claim 1, it is characterised in that:The step(1)Middle reduction Agent is solid reductant or gaseous reducing agent.
5. high ferro zinc leaching residue clean utilization method according to claim 4, it is characterised in that:The solid reductant is work Property charcoal, coke, one or more of arbitrary proportion mixtures in carbon dust, addition is high ferro zinc leaching residue quality 5% ~ 12%.
6. high ferro zinc leaching residue clean utilization method according to claim 4, it is characterised in that:The gaseous reducing agent is one Carbonoxide, hydrogen, producer gas, one or more of arbitrary proportion mixtures of coke-stove gas;The gaseous reducing agent body containing CO Product concentration 10% ~ 50%, H2Volumetric concentration 1% ~ 12%, remaining component is N2
7. high ferro zinc leaching residue clean utilization method according to claim 1, it is characterised in that:The step(1)Middle vulcanization Agent is vulcanized sodium, pyrite or sulphur, and addition is high ferro zinc leaching residue quality 1% ~ 4%.
8. high ferro zinc leaching residue clean utilization method according to claim 1, it is characterised in that:The step(3)In strong magnetic Magnetic separation magnetic field intensity is 0.5 ~ 1T.
9. high ferro zinc leaching residue clean utilization method according to claim 1, it is characterised in that:The step(3)Middle gas CO volumetric concentrations are 30% ~ 90%, H in reducing agent2Volumetric concentration is 8% ~ 60%, and remaining component is N2
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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109576497A (en) * 2019-01-15 2019-04-05 河套学院 A kind of method that the closed cycle of zinc smelting factory waste residue utilizes
CN110904339A (en) * 2019-12-05 2020-03-24 西南科技大学 Method for recovering zinc by sulfuration, solidification and flotation of steel mill electric furnace smoke dust
CN110983029A (en) * 2019-11-18 2020-04-10 中南大学 Method for carrying out synergistic vulcanization roasting on lead-zinc smelting slag and gypsum slag
CN111167598A (en) * 2020-01-06 2020-05-19 长沙有色冶金设计研究院有限公司 Low-grade lead-zinc oxide ore dressing and smelting treatment method
CN111850305A (en) * 2020-07-28 2020-10-30 昆明理工大学 Method for leaching cobalt and manganese from manganese-rich cobalt slag
CN112813277A (en) * 2020-12-28 2021-05-18 中南大学 Method for separating and recovering valuable metals from copper smelting slag through chlorination roasting
CN113522518A (en) * 2021-06-30 2021-10-22 韶关市青绿环保科技有限公司 Water quenching kiln slag treatment method
CN114606400A (en) * 2022-01-28 2022-06-10 云锡文山锌铟冶炼有限公司 Method for treating arsenic-zinc-containing leaching residues of high-iron
CN114752781A (en) * 2022-03-25 2022-07-15 桂林理工大学 Method for roasting and leaching zinc concentrate by adding carbon and oxidizing

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101824543A (en) * 2010-05-27 2010-09-08 中南大学 Method for sulfidizing heavy metal waste and recovering valuable metals in heavy metal waste
CN103088209A (en) * 2013-03-01 2013-05-08 中南大学 Floating and smelting combined method for air-granulating lead smelting slag and utilizing waste heat
CN103103344A (en) * 2013-03-01 2013-05-15 中南大学 Dressing-smelting combined treatment method for sulfate-containing lead-zinc smelting slags
CN103614572A (en) * 2013-09-12 2014-03-05 昆明理工大学 Method for sulfuration volatilization of tin-containing materials by utilization of high-sulfur coal dust
CN106222397A (en) * 2016-08-04 2016-12-14 中南大学 A kind of utilize pyrite sulfidation roasting smithsonite and the method for Zn accumulation galvanized iron

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101824543A (en) * 2010-05-27 2010-09-08 中南大学 Method for sulfidizing heavy metal waste and recovering valuable metals in heavy metal waste
CN103088209A (en) * 2013-03-01 2013-05-08 中南大学 Floating and smelting combined method for air-granulating lead smelting slag and utilizing waste heat
CN103103344A (en) * 2013-03-01 2013-05-15 中南大学 Dressing-smelting combined treatment method for sulfate-containing lead-zinc smelting slags
CN103614572A (en) * 2013-09-12 2014-03-05 昆明理工大学 Method for sulfuration volatilization of tin-containing materials by utilization of high-sulfur coal dust
CN106222397A (en) * 2016-08-04 2016-12-14 中南大学 A kind of utilize pyrite sulfidation roasting smithsonite and the method for Zn accumulation galvanized iron

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
ZHENG, YONG-XING等: "AN INNOVATIVE TECHNOLOGY FOR RECOVERY OF ZINC, LEAD AND SILVER FROM ZINC LEACHING RESIDUE", 《PHYSICOCHEMICAL PROBLEMS OF MINERAL PROCESSING》 *
胡晓军等: "铁酸锌气体还原的热力学分析", 《工程科学学报》 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109576497A (en) * 2019-01-15 2019-04-05 河套学院 A kind of method that the closed cycle of zinc smelting factory waste residue utilizes
CN110983029A (en) * 2019-11-18 2020-04-10 中南大学 Method for carrying out synergistic vulcanization roasting on lead-zinc smelting slag and gypsum slag
CN110904339A (en) * 2019-12-05 2020-03-24 西南科技大学 Method for recovering zinc by sulfuration, solidification and flotation of steel mill electric furnace smoke dust
CN111167598A (en) * 2020-01-06 2020-05-19 长沙有色冶金设计研究院有限公司 Low-grade lead-zinc oxide ore dressing and smelting treatment method
CN111850305A (en) * 2020-07-28 2020-10-30 昆明理工大学 Method for leaching cobalt and manganese from manganese-rich cobalt slag
CN112813277A (en) * 2020-12-28 2021-05-18 中南大学 Method for separating and recovering valuable metals from copper smelting slag through chlorination roasting
CN113522518A (en) * 2021-06-30 2021-10-22 韶关市青绿环保科技有限公司 Water quenching kiln slag treatment method
CN113522518B (en) * 2021-06-30 2023-10-31 韶关市青绿环保科技有限公司 Water quenching kiln slag treatment method
CN114606400A (en) * 2022-01-28 2022-06-10 云锡文山锌铟冶炼有限公司 Method for treating arsenic-zinc-containing leaching residues of high-iron
CN114606400B (en) * 2022-01-28 2023-09-22 云锡文山锌铟冶炼有限公司 Treatment method of high-iron arsenic-zinc-containing leaching residues
CN114752781A (en) * 2022-03-25 2022-07-15 桂林理工大学 Method for roasting and leaching zinc concentrate by adding carbon and oxidizing

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