CN113174479B - Antimony sulfide concentrate volatilizing roasting process - Google Patents

Antimony sulfide concentrate volatilizing roasting process Download PDF

Info

Publication number
CN113174479B
CN113174479B CN202110466025.0A CN202110466025A CN113174479B CN 113174479 B CN113174479 B CN 113174479B CN 202110466025 A CN202110466025 A CN 202110466025A CN 113174479 B CN113174479 B CN 113174479B
Authority
CN
China
Prior art keywords
antimony
arsenic
oxygen
sulfide concentrate
atmosphere
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN202110466025.0A
Other languages
Chinese (zh)
Other versions
CN113174479A (en
Inventor
唐朝波
刘将
杨建广
陈永明
杨声海
何静
朱强
王嘉慧
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Central South University
Original Assignee
Central South University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Central South University filed Critical Central South University
Priority to CN202110466025.0A priority Critical patent/CN113174479B/en
Publication of CN113174479A publication Critical patent/CN113174479A/en
Application granted granted Critical
Publication of CN113174479B publication Critical patent/CN113174479B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • C22B30/00Obtaining antimony, arsenic or bismuth
    • C22B30/02Obtaining antimony
    • 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

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Mechanical Engineering (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Geology (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

The invention discloses a volatilization roasting process of antimony sulfide concentrate, which comprises the following steps: (1) mixing materials: carrying out ball milling on the antimony sulfide concentrate and the solid arsenic catalyst to obtain a mixture; (2) low-temperature high-oxygen potential arsenic fixation: spreading the mixture into a thin material layer, and reacting at 200-500 ℃ in a high-oxygen atmosphere, wherein the high-oxygen atmosphere is an oxidizing atmosphere with the oxygen content not lower than 10 vol%; (3) high-temperature low-oxygen potential volatile antimony: after the arsenic fixation is finished, placing the obtained product in a low-oxygen atmosphere, and reacting at the temperature of 600-900 ℃ to volatilize antimony, wherein the low-oxygen atmosphere is an oxidizing atmosphere with the oxygen content of 0.5-5 vol.%. Antimony sulfide concentrate is mixed with solid arsenic, arsenic is solidified at low temperature and high oxygen potential in a first-stage reaction, and arsenic is generated into arsenate which is difficult to volatilize and is left in slag; and then in the second-stage reaction, antimony is volatilized at high temperature and low oxygen potential, antimony is volatilized to generate antimony oxide and enters smoke dust, so that the effective separation of arsenic and antimony is realized, and the generation of arsenic alkali slag is reduced from a smelting source.

Description

Antimony sulfide concentrate volatilizing roasting process
Technical Field
The invention relates to a volatilization roasting process of antimony sulfide concentrate, belonging to the field of metallurgy and chemical engineering.
Background
The production of antimony trioxide is an important step of pyrometallurgy of antimony, is a process of oxidation and oxidation enrichment of antimony sulfide concentrate, and is an important link directly influencing the recovery rate of antimony and the grade of crude antimony. At present, the production mode of antimony trioxide in the antimony pyrometallurgy process mainly comprises two modes of volatile roasting and non-volatile roasting. The volatilization roasting is based on that antimony sulfide is heated and oxidized into easily volatilized antimony trioxide under the condition of insufficient air, the antimony trioxide enters a dust collection system, and antimony white is condensed and deposited, so that the separation of antimony and gangue components is realized. It has been widely used in industry.
The chemical properties of arsenic and antimony are very similar, and the antimony is often present in the form of associated ores in nature, is one of the common harmful impurities which are difficult to remove in antimony, and has a very large influence on the application of the antimony. In the current industrial production, the arsenic element is not effectively treated by the two roasting modes. In particular, in the volatilization roasting process, due to the high production temperature, arsenic is oxidized into easily volatilized arsenic trioxide in the roasting process, so that the arsenic trioxide and antimony trioxide enter a dust collecting system together, the quality of antimony white is affected, and the subsequent smelting burden is increased.
The traditional antimony smelting process mainly focuses on the refining link of crude antimony, and the traditional antimony smelting process is mainly operated by adding alkaline substances such as sodium carbonate and the like into the crude antimony to react with arsenic to generate corresponding arsenate, so that the aim of separating arsenic from antimony is fulfilled, and slag generated in the process is called primary arsenic alkali slag. The primary arsenic alkali slag generally contains 20-40% of antimony and 1-5% of arsenic, and because the antimony content is high, smelting enterprises generally need to return the slag to a reverberatory furnace for treatment, so that the flow and energy consumption of smelting are increased undoubtedly, and the slag generated in the process is called secondary arsenic alkali slag, wherein the antimony content is below 10%, and the arsenic content is 4-10%.
The average content of arsenic in the arsenic-alkali residue is 1% -15%, the arsenic exists in the form of soluble sodium arsenate, the arsenic-alkali residue is extremely toxic, and a large amount of residual alkali is also contained in the arsenic-alkali residue, so that the arsenic-alkali residue seriously pollutes the environment and harms the survival safety of human beings. The proper treatment of the arsenic alkali slag is a worldwide problem, large and medium-sized enterprises adopt a special slag storehouse to properly stack the arsenic alkali slag, and the arsenic alkali slag of small-sized smelters is basically stacked in the open air, so that the arsenic alkali slag is extremely harmful. By the end of 2017, the total stacking amount of arsenic-alkali residues in China reaches more than 30 million tons, and the increase amount is about 5000-10000 tons every year. The antimony and arsenic smelting alkaline residue becomes a heavy metal heavy pollution source in China, and a simple and effective treatment way is urgently needed to be found.
Disclosure of Invention
In order to solve the problems that arsenic and antimony can not be separated in the roasting process of the existing antimony sulfide concentrate and arsenic caustic sludge pollutes the environment in the subsequent smelting process, the invention aims to provide a volatilization roasting process of antimony sulfide concentrate, which realizes the preliminary separation of arsenic and antimony in the roasting process of antimony sulfide concentrate and reduces the generation amount of arsenic caustic sludge from the source.
In order to achieve the technical purpose, the invention adopts the following technical scheme:
a volatilization roasting process for antimony sulfide concentrate comprises the following steps:
(1) mixing materials: carrying out ball milling and mixing on the antimony sulfide concentrate and the solid arsenic agent to obtain a mixture;
(2) low-temperature high-oxygen potential arsenic fixation: spreading the mixture into a thin material layer, and reacting at 200-500 ℃ in a high-oxygen atmosphere, wherein the high-oxygen atmosphere is an oxidizing atmosphere with the oxygen content not lower than 10 vol%;
(3) high-temperature low-oxygen potential volatile antimony: after the arsenic fixation is finished, placing the obtained product in a low-oxygen atmosphere, and reacting at the temperature of 600-900 ℃ to volatilize antimony, wherein the low-oxygen atmosphere is an oxidizing atmosphere with the oxygen content of 0.5-5 vol.%.
Preferably, in the step (1), the arsenic fixing agent is one or more of lime, soda ash and caustic soda, and the dosage of the arsenic fixing agent is 1-10% of the weight of the antimony sulfide concentrate.
Preferably, in the step (2), the thickness of the thin material layer is 1-5 mm.
Preferably, in the step (2), the oxidizing atmosphere containing oxygen in an amount of not less than 10 vol.% is a pure oxygen atmosphere or a mixed nitrogen-oxygen atmosphere containing oxygen in an amount of not less than 10 vol.%.
Preferably, in the step (2), the reaction temperature is 400-500 ℃, and the reaction time is 30-120 min.
Preferably, in the step (3), the oxidizing atmosphere containing oxygen of not more than 5 vol.% is a nitrogen-oxygen mixed atmosphere containing oxygen of 0.5 to 5 vol.%.
Preferably, in the step (3), the reaction temperature is 800-.
The invention takes lime as an example of a solid arsenic agent, and the reaction principle is as follows:
(1) conversion between arsenic, antimony and their oxysulfides at low temperatures
Sb2S3(s)+4.5O2(g)=Sb2O3(s)+3SO2(g)
4As(s)+3O2(g)=2As2O3(s)
As2S3(s)+4.5O2(g)=As2O3(s)+3SO2(g)
As2S5(s)+6.5O2(g)=As2O3(s)+5SO2(g)
As2O3(s)+O2(g)=As2O5(s)
As2O3(s)=As2O3(g)
(2) Reaction of arsenic with lime at low temperature
As2O3(s)+2CaO(s)+O2(g)=Ca2As2O7(s)
As2O3(g)+2CaO(s)+O2(g)=Ca2As2O7(s)
As2O5(s)+2CaO(s)=Ca2As2O7(s)
(3) Volatilization of arsenic and antimony at high temperature
Sb2S3(s)+4.5O2(g)=Sb2O3(g)+3SO2(g)
Sb2O3(s)=Sb2O3(g)
As2O5(s)=As2O3(g)+O2(g)
As2O3(s)=As2O3(g)
(4) Fixation of arsenic and antimony by lime at high temperature
As2O3(g)+2CaO(s)+O2(g)=Ca2As2O7(s)
Sb2O3(s)+2CaO(s)+O2(g)=Ca2Sb2O7(s)
Sb2O3(g)+2CaO(s)+O2(g)=Ca2Sb2O7(s)
The invention has the advantages that:
mixing antimony sulfide concentrate with solid arsenic, adopting two-stage heating roasting, strictly controlling two-stage reaction temperature and reaction atmosphere, and in one-stage reaction, fixing arsenic at low temperature and high oxygen potential, wherein arsenic generates arsenate which is difficult to volatilize and is left in slag; and then in the second-stage reaction, antimony is volatilized at high temperature and low oxygen potential, antimony is volatilized to generate antimony oxide, and the antimony oxide enters smoke dust, so that the arsenic and the antimony are effectively separated, and the production of arsenic alkali slag is reduced from a smelting source.
Detailed Description
The substance of the present invention is illustrated by the following examples, but the scope of the present invention is not limited thereto.
Example 1
The main chemical components of the antimony sulfide concentrate are Sb 29.2%, As 0.94%, S30.4%, Fe 18.3%, Ca 0.29% and Zn 0.49%. 10g of antimony sulfide concentrate and 1g of calcium oxide are placed in a ball milling tank, ball milling is carried out for 30min at the rotating speed of 500r/min, and the antimony sulfide concentrate and the calcium oxide concentrate are spread into a thin layer of 2mm and placed in a horizontal tubular furnace. Introducing W into the furnace(O2)60 vol.% nitrogen-oxygen mixed gas (flow rate 500mL/min), heating to 400 ℃, and keeping the temperature for 1 h; after the heat preservation at 400 ℃, W is rapidly introduced(O2)Heating to 800 ℃ at a heating rate of 7 ℃/min and keeping the temperature for 75min, finally cooling to 500 ℃ at a rate of 10 ℃/min, and taking out the material. The calculation shows that the volatilization rate of antimony in the concentrate is 91.21%, the arsenic fixation rate is 64.63%, and the sulfur fixation rate is 17.16%.
Example 2
The main chemical components of the antimony sulfide concentrate are Sb 41.05%, As 0.53%, S26.75%, Fe 10.67%, Ca 0.75% and Zn 0.31%. 10g of antimony sulfide concentrate and 1.5g of calcium oxide are placed in a ball milling tank, ball milling is carried out for 30min at the rotating speed of 500r/min, and the mixture is spread into a thin layer of 2mm and placed in a horizontal tubular furnace. Introducing W into the furnace(O2)20 vol.% nitrogen-oxygen mixed gas (flow rate 500mL/min), heating to 400 ℃, and keeping the temperature for 1 h; after the heat preservation is finished, W is rapidly introduced(O2)Heating the nitrogen-oxygen mixed gas (the flow rate is 2000mL/min) at the temperature rising rate of 7 ℃/min to 800 ℃, keeping the temperature for 75min, finally cooling the nitrogen-oxygen mixed gas at the speed of 10 ℃/min to 500 ℃, and taking out the material. The calculation shows that the volatilization rate of antimony in the concentrate is 93.02%, the arsenic fixation rate is 69.66%, and the sulfur fixation rate is 18.89%.
Comparative example 1
Antimony sulphide concentrate the same as in example 1. 10g of antimony sulfide concentrate and 1g of calcium oxide are placed in a ball milling tank, ball milling is carried out for 30min at the rotating speed of 500r/min, and the antimony sulfide concentrate and the calcium oxide concentrate are spread into a thin layer of 2mm and placed in a horizontal tubular furnace. Introducing W into the furnace(O2)Heating to 800 ℃ at a heating rate of 7 ℃/min and keeping the temperature for 75min, finally cooling to 500 ℃ at a rate of 10 ℃/min, and taking out the material. The calculation shows that the volatilization rate of antimony in the concentrate is 94.03%, the arsenic fixation rate is 19.23% and the sulfur fixation rate is 16.35%.
Comparative example 2
Antimony sulphide concentrate the same as in example 1. 10g of antimony sulfide concentrate and 1g of calcium oxide are placed in a ball milling tank, ball milling is carried out for 30min at the rotating speed of 500r/min, and the antimony sulfide concentrate and the calcium oxide concentrate are spread into a thin layer of 2mm and placed in a horizontal tubular furnace. Introducing W into the furnace(O2)60 vol.% nitrogen-oxygen mixed gas (flow rate 500mL/min), heating to 800 ℃ at a heating rate of 7 ℃/min, keeping the temperature for 75min, finally cooling to 500 ℃ at a speed of 10 ℃/min, and taking out the material. The calculation shows that the volatilization rate of antimony in the concentrate is 28.45%, the arsenic fixing rate is 69.77%, and the sulfur fixing rate is 18.78%.
Comparative example 3
Antimony sulphide concentrate the same as in example 1. 10g of antimony sulfide concentrate and 1g of calcium oxide are placed in a ball milling tank, ball milling is carried out for 30min at the rotating speed of 500r/min, and the mixture is spread into a thin layer of 2mm and placed in a horizontal tubular furnace. Continuously introducing W into the furnace(O2)60 vol.% nitrogen-oxygen mixed gas (flow rate 500mL/min), firstly heating to 400 ℃, and preserving heat for 1 h; then heating to 800 ℃ at the heating rate of 7 ℃/min, preserving the heat for 75min, finally cooling to 500 ℃ at the speed of 10 ℃/min, and taking out the materials. The calculation shows that the volatilization rate of antimony in the concentrate is 25.43%, the arsenic fixing rate is 72.98%, and the sulfur fixing rate is 16.23%.
Comparative example 4
Antimony sulphide concentrate the same as in example 1. Antimony sulphide concentrate the same as in example 1. 10g of antimony sulfide concentrate and 1g of calcium oxide are placed in a ball milling tank, ball milling is carried out for 30min at the rotating speed of 500r/min, and the antimony sulfide concentrate and the calcium oxide concentrate are spread into a thin layer of 2mm and placed in a horizontal tubular furnace. Continuously introducing W into the furnace(O2)1.5 vol.%Heating the nitrogen-oxygen mixed gas (the flow rate is 700mL/min) to 400 ℃ and preserving the heat for 1 h; then heating to 800 ℃ at the heating rate of 7 ℃/min, preserving the heat for 75min, finally cooling to 500 ℃ at the speed of 10 ℃/min, and taking out the materials. The calculation shows that the volatilization rate of antimony in the concentrate is 95.01%, the arsenic fixing rate is 22.45% and the sulfur fixing rate is 17.25%.
Comparative example 5
The main chemical components of the antimony sulfide concentrate are Sb 29.2%, As 0.94%, S30.4%, Fe18.3%, Ca 0.29% and Zn 0.49%. 10g of antimony sulfide concentrate and 1g of calcium oxide are placed in a ball milling tank, ball milling is carried out for 30min at the rotating speed of 500r/min, and the antimony sulfide concentrate and the calcium oxide concentrate are spread into a thin layer of 2mm and placed in a horizontal tubular furnace. Introducing W into the furnace(O2)1.5 vol.% nitrogen-oxygen mixed gas (flow rate 700mL/min), heating to 400 ℃, and keeping the temperature for 1 h; after the heat preservation at 400 ℃, W is rapidly introduced(O2)60 vol.% nitrogen-oxygen mixed gas (flow rate 500mL/min), heating to 800 ℃ at a heating rate of 7 ℃/min, keeping the temperature for 75min, finally cooling to 500 ℃ at a speed of 10 ℃/min, and taking out the material. The calculation shows that the volatilization rate of antimony in the concentrate is 26.45%, the arsenic fixation rate is 70.24% and the sulfur fixation rate is 16.63%.

Claims (7)

1. A volatilization roasting process of antimony sulfide concentrate is characterized by comprising the following steps:
(1) mixing materials: carrying out ball milling and mixing on the antimony sulfide concentrate and the solid arsenic agent to obtain a mixture;
(2) low-temperature high-oxygen potential arsenic fixation: spreading the mixture into a thin material layer, and reacting at 200-500 ℃ in a high-oxygen atmosphere, wherein the high-oxygen atmosphere is an oxidizing atmosphere with the oxygen content not lower than 10 vol%;
(3) high-temperature low-oxygen potential volatile antimony: after the arsenic fixation is finished, placing the obtained product in a low-oxygen atmosphere, and reacting at the temperature of 600-900 ℃ to volatilize antimony, wherein the low-oxygen atmosphere is an oxidizing atmosphere with the oxygen content of 0.5-5 vol.%.
2. The antimony sulfide concentrate volatilizing and roasting process of claim 1, characterized in that: in the step (1), the arsenic fixing agent is one or more of lime, soda ash and caustic soda, and the dosage of the arsenic fixing agent is 1-10% of the weight of the antimony sulfide concentrate.
3. The antimony sulfide concentrate volatilizing and roasting process of claim 1, characterized in that: in the step (1), the thickness of the thin material layer is 1-5 mm.
4. The antimony sulfide concentrate volatilizing and roasting process of claim 1, characterized in that: in the step (2), the oxidizing atmosphere having an oxygen content of not less than 10 vol.% is a pure oxygen atmosphere or a mixed nitrogen-oxygen atmosphere having an oxygen content of not less than 10 vol.%.
5. The antimony sulfide concentrate volatilizing and roasting process of claim 1, characterized in that: in the step (2), the reaction temperature is 400-500 ℃, and the reaction time is 30-120 min.
6. The antimony sulfide concentrate volatilizing and roasting process of claim 1, characterized in that: in the step (3), the oxidizing atmosphere having an oxygen content of not higher than 5 vol.% is a nitrogen-oxygen mixed atmosphere having an oxygen content of 0.5 to 5 vol.%.
7. The volatilizing and roasting process of antimony sulfide concentrate according to claim 1, characterized by comprising the following steps: in the step (3), the reaction temperature is 800-900 ℃, and the reaction time is 30-120 min.
CN202110466025.0A 2021-04-28 2021-04-28 Antimony sulfide concentrate volatilizing roasting process Expired - Fee Related CN113174479B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202110466025.0A CN113174479B (en) 2021-04-28 2021-04-28 Antimony sulfide concentrate volatilizing roasting process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202110466025.0A CN113174479B (en) 2021-04-28 2021-04-28 Antimony sulfide concentrate volatilizing roasting process

Publications (2)

Publication Number Publication Date
CN113174479A CN113174479A (en) 2021-07-27
CN113174479B true CN113174479B (en) 2022-06-07

Family

ID=76926831

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202110466025.0A Expired - Fee Related CN113174479B (en) 2021-04-28 2021-04-28 Antimony sulfide concentrate volatilizing roasting process

Country Status (1)

Country Link
CN (1) CN113174479B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116103505B (en) * 2022-10-18 2024-09-10 东北大学 Gold extraction method by sectional sulfur and arsenic fixation decarburization pretreatment of refractory gold ore

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101423252A (en) * 2008-11-17 2009-05-06 河南豫光金铅股份有限公司 Oxygen-enriched production process of diantimony trioxide
CN105648226A (en) * 2014-11-15 2016-06-08 中国科学院过程工程研究所 Method for separating antimony from arsenic in antimony-arsenic soot

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7524792B2 (en) * 2003-06-04 2009-04-28 Basf Aktiengesellschaft Preparation of catalytically active multielement oxide materials which contain at least one of the elements Nb and W and the elements Mo, V and Cu

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101423252A (en) * 2008-11-17 2009-05-06 河南豫光金铅股份有限公司 Oxygen-enriched production process of diantimony trioxide
CN105648226A (en) * 2014-11-15 2016-06-08 中国科学院过程工程研究所 Method for separating antimony from arsenic in antimony-arsenic soot

Also Published As

Publication number Publication date
CN113174479A (en) 2021-07-27

Similar Documents

Publication Publication Date Title
CN111926175B (en) Method for extracting molybdenum trioxide by using molybdenum concentrate sulfur dioxide to assist calcification roasting
CN100595297C (en) Gold extraction process with low pollution and high recovery for refractory gold concentrate
DE69225993T2 (en) Process for treating ore with recoverable metal materials, including arsenic-containing components
CN111394582B (en) Copper-nickel sludge resource recycling process
CN109355508B (en) Comprehensive recovery method of high-arsenic multi-metal indium-containing material
US11196107B2 (en) Method for recycling lead paste in spent lead-acid battery
CN109368693B (en) Cleaning treatment method for high-arsenic fluorine-containing chlorine material
CN113088708A (en) Method for recycling polymetallic through resource synergistic treatment of copper smelting white smoke and dirty acid
CN113174479B (en) Antimony sulfide concentrate volatilizing roasting process
CN111996383A (en) Method for separating arsenic from copper slag by matching high-arsenic materials
CN106756038B (en) A method of detaching selenium mercury from copper-lead-zinc smelting sulfate system acid mud
CN106834711B (en) A kind of method for reclaiming in the flue dust from tellurium containing arsenic and preparing high purity tellurium
CN114231754A (en) Copper flash smelting process
CN113025821A (en) Comprehensive treatment method for resource utilization of cyanidation tailings
CN110453079B (en) Method for efficiently recovering silver in lead-silver slag by melting-fuming method
CN112176202A (en) Antimony smelting method adopting oxygen-enriched side-blown column smelting
CN110016575B (en) Antimony sulfide concentrate smelting process
CN115011804B (en) Air and water vapor synergistic roasting dearsenification method for high-arsenic antimony lead anode slime
DE69322198T2 (en) Extraction of volatile metals, e.g. Zinc, lead and cadmium, from sulfidic ores
CN101343696A (en) Desulfurization method for molybdenum sulfide
CN112080648B (en) Method for treating indium-containing high-iron zinc sulfide concentrate
CA1162056A (en) Process and apparatus for the separation of lead from a sulfidic concentrate
CN114438323A (en) Environment-friendly harmless treatment method for iron slag, cobalt slag, lead slag and sulfur tailings
CN111172401A (en) Method for treating high-arsenic white smoke
WO2015079116A1 (en) Method and arrangement of separating arsenic from starting materials

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20220607

CF01 Termination of patent right due to non-payment of annual fee