CN103449517A - Method for preparing white arsenic from arsenic-containing dust in evaporation-free manner - Google Patents

Method for preparing white arsenic from arsenic-containing dust in evaporation-free manner Download PDF

Info

Publication number
CN103449517A
CN103449517A CN2013103776310A CN201310377631A CN103449517A CN 103449517 A CN103449517 A CN 103449517A CN 2013103776310 A CN2013103776310 A CN 2013103776310A CN 201310377631 A CN201310377631 A CN 201310377631A CN 103449517 A CN103449517 A CN 103449517A
Authority
CN
China
Prior art keywords
arsenic
acid
smoke dust
containing smoke
white
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.)
Granted
Application number
CN2013103776310A
Other languages
Chinese (zh)
Other versions
CN103449517B (en
Inventor
廖亚龙
彭志强
周娟
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.)
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
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 Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CN201310377631.0A priority Critical patent/CN103449517B/en
Publication of CN103449517A publication Critical patent/CN103449517A/en
Application granted granted Critical
Publication of CN103449517B publication Critical patent/CN103449517B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Inorganic Compounds Of Heavy Metals (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

The invention relates to a method for preparing white arsenic from arsenic-containing dust in an evaporation-free manner, which belongs to the field of metallurgical engineering. The method comprises the following steps of: adding an oxidizing agent to oxidize trivalent arsenious acid into pentavalent arsenic acid during a process of leaching by water by virtue of the characteristics that arsenic acid is high in solubility in water and is low in solubility in water; purifying and removing impurities, then charging a reducing agent to reduce the pentavalent arsenic acid into the trivalent arsenious acid, cooling, and then crystallizing the arsenious acid into arsenic trioxide; and returning the filtrate obtained by filtering the cooled and crystallized product, leaching, drying the filter cake, thus obtaining the white arsenic product. According to the method, the characteristic of high solubility of pentavalent arsenic can be adequately utilized, and the high leaching rate of arsenic is realized with low water consumption and at a low reaction temperature, thus reducing water consumption and energy consumption.

Description

A kind of method of non-evaporating the white arsenic of preparation of arsenic-containing smoke dust
Technical field
The present invention relates to a kind of method of non-evaporating the white arsenic of preparation of arsenic-containing smoke dust, belong to the metallurgical engineering field.
Background technology
Arsenic and compound thereof are generally all toxic, and its toxicity is notorious, almost widely known.But arsenic and compound thereof are in industrial field and the superior use function of but having a wide range of applications.Be used as alloy addition and produce plumbous bullet processed, type metal, brass (condenser), accumulator grid, wear resistant alloy, High Strength Construction Steel and corrosion-resisting steel etc.Contain a certain amount of arsenic in brass and can prevent dezincify.High purity arsenic is the raw material of producing gaas compound semiconductor, indium arsenide etc., is also the doped element of semiconductor material germanium and silicon.The compound of arsenic is also for the manufacture of agricultural chemicals, sanitas, dyestuff and pharmaceutical preparation etc.
Arsenic is content little in the earth's crust, but it grows on trees at occurring in nature, is mainly that the form with sulfide mineral exists.All contain the sulfide of a certain amount of arsenic in which kind of metallic sulfide ores, heavy metal and the association of gold and silver precious metal ore or the symbiosis such as general and copper, lead, zinc, tin, tungsten, molybdenum, mercury, enter smeltery and chemical plant with the concentrate of metal.Arsenic pollutes mining, the mineral ore dressing processing that is present in nonferrous metallurgy and chemical industry and separates, smelts in the processes such as purification and chemical industry deep processing, and in recent years, environmental pollution becomes the focus of social concerns, and particularly heavy metal and arsenic pollute.The improvement of arsenic has become the bottleneck of restriction metallurgical industry development.
Arsenic-containing smoke dust in metallurgy or chemical industry contains other valuable metals toward contact, after generally taking to extract arsenic wherein, valuable constituent is returned to technical process.The extraction process of arsenic in flue dust, generally have following several method.With acid or water, at the temperature that approaches boiling, leach, after purifying evaporation concentration prepare white arsenic product (Huang Gansheng, Quan Changrong. the wet-extraction for arsenic novel process is explored [J]. non-ferrous metal (Smelting Part), 1994 (3): 3~4).Due to As 2o 3in water, solubleness is little, prepares white arsenic with the method for evaporation concentration and need further to solve the problem that energy consumption is large, cost is high.
Summary of the invention
For overcoming the deficiencies in the prior art, the invention provides a kind of method of non-evaporating the white arsenic of preparation of arsenic-containing smoke dust, can take full advantage of the characteristic that pentavalent arsenic solubleness is high, under low water consumption and low reaction temperatures, realize the high leaching yield of arsenic, reduced water consumption and energy consumption.
Technical scheme of the present invention is: utilize that the solubleness of arsenic acid in water is large, arsenus acid dissolves lowly, in the process leached at water, adds oxygenant the arsenus acid of trivalent to be oxidized to the arsenic acid of pentavalent.Pass into reductive agent after purification and impurity removal and the arsenic acid of pentavalent is reduced to the arsenus acid of trivalent, cooling rear arsenus acid crystallization is white arsenic.Concrete steps comprise as follows:
(1) heat water to 60~90 ℃, under the state stirred, add arsenic-containing smoke dust, hydrogen peroxide and diluted acid successively in water, the pH value that diluted acid is controlled mixing solutions is 1~3, filters after reacting 0.5~3h, obtains the filter cake that contains the valency metal and the solution that contains arsenic acid;
(2) to being 4~7 containing adding the pH value of ammoniacal liquor regulator solution in the solution of arsenic acid, stirring reaction 0.5~2h under the condition that is 40~70 ℃ at solution temperature, after finishing, reaction filters, the filtrate obtained and filter cake, and filter cake is the material (recoverable) that contains the valuable metal such as copper;
(3) in the filtrate prepared to step (2), pass into containing SO 2---gas carry out reduction reaction, filter after being cooled to after completion of the reaction 20~25 ℃, filter cake obtains white arsenic product after 60~80 ℃ of drying 8~24h.
Described arsenic-containing smoke dust is As 2o 3the flue dust of 30 wt%.
In described step (1), the solid-to-liquid ratio of arsenic-containing smoke dust and water is 1:2~8g/ml.
A kind of in the sulfuric acid that described diluted acid is concentration 10~20wt%, hydrochloric acid or nitric acid.
The concentration of described hydrogen peroxide is 25~30wt%, and add-on is 1.8~3.0 times of arsenic weight in arsenic-containing smoke dust.
Described ammoniacal liquor is industrial ammonia, and industrial ammonia is the aqueous solution containing ammonia 25%~28%.
Described containing SO 2---gas in SO 2---volume be greater than 5%, SO in the gas passed into 2weight be arsenic in solution
0.8~1.5 times of weight.
Described passing into containing SO 2---the speed of gas be 150~170L/h.
Principle of the present invention is: utilize that the solubleness of arsenic acid in water is large, arsenus acid dissolves lowly, in the process leached at water, adds oxygenant the arsenus acid of trivalent to be oxidized to the arsenic acid of pentavalent.Pass into reductive agent after purification and impurity removal and the arsenic acid of pentavalent is reduced to the arsenus acid of three, cooling rear arsenus acid crystallization is white arsenic.The filtrate that the product of crystallisation by cooling filters is returned to leaching, obtains white arsenic product after filtration cakes torrefaction.
The advantage that the present invention possesses and effect:
(1) can take full advantage of the characteristic that pentavalent arsenic solubleness is high, under low water consumption and low reaction temperatures, realize arsenic
High leaching yield, reduced water consumption and energy consumption;
(2) filtrate after the purification of leaching liquor removal of impurities adds smeltery's relieving haperacidity flue gas that the pentavalent arsenic acid is reduced to the trivalent arsenic acid,
Crystallisation by cooling, crystallized product filters, the white arsenic of dry rear preparation.Process, without carrying out the evaporation concentration operation, is saved a large amount of energy consumptions.
(3) harmful material of arsenic-containing smoke dust metallurgical process produced is converted into white arsenic product and has reclaimed having in the flue dust
The valency metal, realize the resource comprehensive recycle, reduced the amount that is discharged into arsenic in environment in the commercial run, is conducive to environment protection.
Embodiment
Below in conjunction with embodiment, the invention will be further described.
Embodiment one: the method for non-evaporating the white arsenic of preparation of the arsenic-containing smoke dust of present embodiment is:
(1) heat water to 85 ℃, add containing As in water successively under the state stirred 2o 339.6wt%, Pb18.6wt%, H 2flue dust, the concentration that the plumbous metallurgical process of O 8wt% produces is 30wt% hydrogen peroxide (add-on is 2.3 times of arsenic weight in arsenic-containing smoke dust) and diluted acid (sulfuric acid of concentration 10wt%), the pH value of controlling mixing solutions is 1.5 reaction 3h, then filter the solution that obtains mainly containing the filter cake of valency metal and contain arsenic acid;
(2) to being 5 containing adding the pH value of ammoniacal liquor regulator solution in the solution of arsenic acid, stirring reaction 2h under the condition that is 70 ℃ at solution temperature, filtration after reaction finishes, the filtrate obtained and filter cake, filter cake is the material (recoverable) that contains the valuable metal such as copper;
(3) in the filtrate prepared to step (2), pass into containing SO 2---gas (SO in gas 2---volume 8%, SO in the gas passed into 21.5 times of the weight weight that is arsenic in solution, pass into containing SO 2---the speed of gas be 160L/h) carry out reduction reaction, filter after being cooled to after completion of the reaction 24 ℃, filter cake obtains white arsenic product, As after 80 ℃ of dry 20h 2o 3content is 99.2%.
Embodiment two: the method for non-evaporating the white arsenic of preparation of the arsenic-containing smoke dust of present embodiment is:
(1) heat water to 90 ℃, under the state stirred, add As successively in water 2o 3the arsenic-containing smoke dust of 38 wt%, concentration are 28wt% hydrogen peroxide (add-on is 1.8 times of arsenic weight in arsenic-containing smoke dust) and diluted acid (concentration 15wt% hydrochloric acid), the pH value of controlling mixing solutions is 1 reaction 2h, then filter the solution that obtains mainly containing the filter cake of valency metal and contain arsenic acid;
(2) to being 4 containing adding the pH value of ammoniacal liquor regulator solution in the solution of arsenic acid, stirring reaction 1h under the condition that is 40 ℃ at solution temperature, filtration after reaction finishes, the filtrate obtained and filter cake, filter cake is the material (recoverable) that contains the valuable metal such as copper;
(3) in the filtrate prepared to step (2), pass into containing SO 2---gas (SO in gas 2---volume 7%, SO in the gas passed into 21 times of the weight weight that is arsenic in solution, pass into containing SO 2---the speed of gas be 150L/h) carry out reduction reaction, filter after being cooled to after completion of the reaction 25 ℃, filter cake obtains white arsenic product, As after 60 ℃ of dry 24h 2o 3content is 99.5%.
Embodiment three: the method for non-evaporating the white arsenic of preparation of the arsenic-containing smoke dust of present embodiment is:
(1) heat water to 60 ℃, under the state stirred, add As successively in water 2o 3the arsenic-containing smoke dust of 41 wt%, concentration are 25wt% hydrogen peroxide (add-on is 3.0 times of arsenic weight in arsenic-containing smoke dust) and diluted acid (nitric acid of concentration 20wt%), the pH value of controlling mixing solutions is 3 reaction 0.5h, then filter the solution that obtains mainly containing the filter cake of valency metal and contain arsenic acid;
(2) to being 7 containing adding the pH value of ammoniacal liquor regulator solution in the solution of arsenic acid, stirring reaction 0.5h under the condition that is 60 ℃ at solution temperature, after finishing, reaction filters, the filtrate obtained and filter cake, and filter cake is the material (recoverable) that contains the valuable metal such as copper;
(3) in the filtrate prepared to step (2), pass into containing SO 2---gas (SO in gas 2---volume 6%, SO in the gas passed into 20.8 times of the weight weight that is arsenic in solution, pass into containing SO 2---the speed of gas be 170L/h) carry out reduction reaction, filter after being cooled to after completion of the reaction 20 ℃, filter cake obtains white arsenic product, As after 70 ℃ of dry 8h 2o 3content is 99.4%.
Above the specific embodiment of the present invention is explained in detail, but the present invention is not limited to above-mentioned embodiment, in the ken possessed those of ordinary skills, can also under the prerequisite that does not break away from aim of the present invention, make various variations.

Claims (7)

  1. Non-evaporating of an arsenic-containing smoke dust preparation white arsenic method, it is characterized in that comprising the following steps:
    (1) heat water to 60~90 ℃, under the state stirred, add arsenic-containing smoke dust, hydrogen peroxide and diluted acid successively in water, the pH value that diluted acid is controlled mixing solutions is 1~3, filters after reacting 0.5~3h, obtains the filter cake that contains the valency metal and the solution that contains arsenic acid;
    (2) to being 4~7 containing in the solution of arsenic acid, adding the pH value of ammoniacal liquor regulator solution, stirring reaction 0.5~2h under the condition that is 40~70 ℃ at solution temperature, filter the filtrate obtained and the filter cake that contains copper after reaction finishes;
    (3) in the filtrate prepared to step (2), pass into containing SO 2---gas carry out reduction reaction, filter after being cooled to after completion of the reaction 20~25 ℃, filter cake obtains white arsenic after 60~80 ℃ of drying 8~24h.
  2. Non-evaporating of arsenic-containing smoke dust according to claim 1 the preparation white arsenic method, it is characterized in that: described arsenic-containing smoke dust is As 2o 3the flue dust of 30 wt%.
  3. 3. the method for non-evaporating of the arsenic-containing smoke dust according to claim 1 white arsenic of preparation, it is characterized in that: the solid-to-liquid ratio of arsenic-containing smoke dust and water is 1:2~8g/ml in described step (1).
  4. 4. the method for non-evaporating of the arsenic-containing smoke dust according to claim 1 white arsenic of preparation, is characterized in that: the sulfuric acid that described diluted acid is concentration 10~20wt%, hydrochloric acid or nitric acid.
  5. 5. the method for non-evaporating of the arsenic-containing smoke dust according to claim 1 white arsenic of preparation, it is characterized in that: the concentration of described hydrogen peroxide is 25~30wt%, add-on is 1.8~3.0 times of arsenic weight in arsenic-containing smoke dust.
  6. 6. the method for non-evaporating of the arsenic-containing smoke dust according to claim 1 white arsenic of preparation, is characterized in that: described containing SO 2---gas in SO 2---volume be greater than 5%, SO in the gas passed into 20.8~1.5 times of the weight weight that is arsenic in solution.
  7. 7. the method for non-evaporating of the arsenic-containing smoke dust according to claim 6 white arsenic of preparation, is characterized in that: described passing into containing SO 2---the speed of gas be 150~170L/h.
CN201310377631.0A 2013-08-27 2013-08-27 Method for preparing white arsenic from arsenic-containing dust in evaporation-free manner Expired - Fee Related CN103449517B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310377631.0A CN103449517B (en) 2013-08-27 2013-08-27 Method for preparing white arsenic from arsenic-containing dust in evaporation-free manner

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310377631.0A CN103449517B (en) 2013-08-27 2013-08-27 Method for preparing white arsenic from arsenic-containing dust in evaporation-free manner

Publications (2)

Publication Number Publication Date
CN103449517A true CN103449517A (en) 2013-12-18
CN103449517B CN103449517B (en) 2014-12-31

Family

ID=49732420

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310377631.0A Expired - Fee Related CN103449517B (en) 2013-08-27 2013-08-27 Method for preparing white arsenic from arsenic-containing dust in evaporation-free manner

Country Status (1)

Country Link
CN (1) CN103449517B (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106268179A (en) * 2016-08-25 2017-01-04 长沙有色冶金设计研究院有限公司 The energy saving technique of a kind of synthetical recovery sulfuric acid purification spent acid and system
CN106801151A (en) * 2017-01-22 2017-06-06 中国恩菲工程技术有限公司 The method of flyash reduction melting enriched germanium
CN106834718A (en) * 2016-12-21 2017-06-13 中南大学 A kind of arsenic-containing smoke dust comprehensive utilization and the method for arsenic harmlessness disposing
CN106834707A (en) * 2016-12-21 2017-06-13 中南大学 A kind of method of arsenic-containing material synthetical recovery and arsenic recycling
CN106834676A (en) * 2016-12-21 2017-06-13 中南大学 A kind of method that valuable metal and arsenic resource harmlessness disposing are reclaimed from arsenic-containing smoke dust
CN106834711A (en) * 2016-12-21 2017-06-13 中南大学 A kind of method for reclaiming and preparing high purity tellurium in the flue dust from tellurium containing arsenic
CN107523702A (en) * 2017-08-23 2017-12-29 中南大学 A kind of method that sodium salt system pressure oxidation prepares sodium pyroantimonate

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN85107157A (en) * 1985-09-18 1987-04-01 广西冶金研究所 Wet method is extracted white arsenic from arsenic-containing smoke dust
CN1101010A (en) * 1994-06-10 1995-04-05 大厂矿务局来宾冶炼厂 Wet method for preparation of sodium arsenate from fume containing arsenic

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN85107157A (en) * 1985-09-18 1987-04-01 广西冶金研究所 Wet method is extracted white arsenic from arsenic-containing smoke dust
CN1101010A (en) * 1994-06-10 1995-04-05 大厂矿务局来宾冶炼厂 Wet method for preparation of sodium arsenate from fume containing arsenic

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
赵思佳: "有色冶金工业含砷烟尘处理及利用研究进展", 《湖南有色金属》 *

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106268179A (en) * 2016-08-25 2017-01-04 长沙有色冶金设计研究院有限公司 The energy saving technique of a kind of synthetical recovery sulfuric acid purification spent acid and system
CN106268179B (en) * 2016-08-25 2018-09-07 长沙有色冶金设计研究院有限公司 A kind of energy saving technique and system of synthetical recovery sulfuric acid purification spent acid
CN106834718A (en) * 2016-12-21 2017-06-13 中南大学 A kind of arsenic-containing smoke dust comprehensive utilization and the method for arsenic harmlessness disposing
CN106834707A (en) * 2016-12-21 2017-06-13 中南大学 A kind of method of arsenic-containing material synthetical recovery and arsenic recycling
CN106834676A (en) * 2016-12-21 2017-06-13 中南大学 A kind of method that valuable metal and arsenic resource harmlessness disposing are reclaimed from arsenic-containing smoke dust
CN106834711A (en) * 2016-12-21 2017-06-13 中南大学 A kind of method for reclaiming and preparing high purity tellurium in the flue dust from tellurium containing arsenic
CN106834707B (en) * 2016-12-21 2019-03-26 中南大学 A kind of method that arsenic-containing material synthetical recovery and arsenic resource utilize
CN106801151A (en) * 2017-01-22 2017-06-06 中国恩菲工程技术有限公司 The method of flyash reduction melting enriched germanium
CN106801151B (en) * 2017-01-22 2019-05-07 中国恩菲工程技术有限公司 The method of flyash reduction melting enriched germanium
CN107523702A (en) * 2017-08-23 2017-12-29 中南大学 A kind of method that sodium salt system pressure oxidation prepares sodium pyroantimonate

Also Published As

Publication number Publication date
CN103449517B (en) 2014-12-31

Similar Documents

Publication Publication Date Title
CN103449517B (en) Method for preparing white arsenic from arsenic-containing dust in evaporation-free manner
CN102534228B (en) Method for comprehensively recovering valuable elements from high-arsenic-containing copper smelting soot
CN108002408B (en) Method for preparing nickel sulfate, manganese, lithium, cobalt and cobaltosic oxide from battery waste
CN102747226B (en) Method for treating zinc hydrometallurgy waste residue by using alkali ammonium sulfur coupling method
CN103789550B (en) The recovery method of vanadium potassium silicon in spent vanadium catalyst
CN104178642B (en) A kind of method of zinc and iron in separation of Zinc leached mud
CN102491287B (en) Process for separating and recovering selenium from selenium-containing material
CN101660054B (en) Method for extracting metal indium from waste residues generated from lead and zinc smelting
CN103551025B (en) Harmless treatment method of arsenic-containing flue dust
CN109666789B (en) Method for preparing vanadium pentoxide by using vanadium-chromium slag and manganese carbonate
CN102234721A (en) Treatment method of nickel-cobalt material
CN102390819B (en) Method for preparing tellurium dioxide from tellurium slag
CN103771526B (en) A kind of take industrial manganic sulfate as the method that high purity manganese sulfate prepared by raw material
CN103482680B (en) A kind of technique of being produced nano zine oxide by secondary zinc oxide
CN102701263B (en) Method for preparing copper sulfate in mode that stanniferous copper slag is leached in selective mode and free of evaporation
CN103014357A (en) Method for recovering arsenic from arsenic soot
CN102634668B (en) Roasting-free evaporation-free method for producing cupric sulfate from zinc hydrometallurgy acid-wash copper dross
CN104073650A (en) Process for recovering zinc from tin-smelting electric furnace smoke
CN101817563B (en) Process for preparing high-purity ferrous sulfate by adopting pyrite smelting slag
CN102660690A (en) Method for recovering valuable metal from zinc hydrometallurgy high acid leach residue
CN104032131A (en) Method for processing high-tin anode slurry
CN102583268A (en) Method for extracting selenium from low-grade complex material
CN101525696B (en) Method for leaching indium from leaching residue containing indium
CN104060095A (en) Method of recovering palladium from palladium-loading aluminum oxide waste catalyst
CN113186399A (en) Method for extracting tantalum and niobium

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20141231

Termination date: 20160827

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