CN114560483A - Method for comprehensively recycling aluminum ash - Google Patents

Method for comprehensively recycling aluminum ash Download PDF

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Publication number
CN114560483A
CN114560483A CN202210194904.7A CN202210194904A CN114560483A CN 114560483 A CN114560483 A CN 114560483A CN 202210194904 A CN202210194904 A CN 202210194904A CN 114560483 A CN114560483 A CN 114560483A
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aluminum ash
aluminum
water
roasting
washing
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CN202210194904.7A
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Inventor
焦芬
覃文庆
董良民
张又飞
王焕龙
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Central South University
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Central South University
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/02Aluminium oxide; Aluminium hydroxide; Aluminates
    • C01F7/04Preparation of alkali metal aluminates; Aluminium oxide or hydroxide therefrom
    • C01F7/06Preparation of alkali metal aluminates; Aluminium oxide or hydroxide therefrom by treating aluminous minerals or waste-like raw materials with alkali hydroxide, e.g. leaching of bauxite according to the Bayer process
    • C01F7/0693Preparation of alkali metal aluminates; Aluminium oxide or hydroxide therefrom by treating aluminous minerals or waste-like raw materials with alkali hydroxide, e.g. leaching of bauxite according to the Bayer process from waste-like raw materials, e.g. fly ash or Bayer calcination dust
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01CAMMONIA; CYANOGEN; COMPOUNDS THEREOF
    • C01C1/00Ammonia; Compounds thereof
    • C01C1/24Sulfates of ammonium
    • C01C1/242Preparation from ammonia and sulfuric acid or sulfur trioxide
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D3/00Halides of sodium, potassium or alkali metals in general
    • C01D3/04Chlorides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D3/00Halides of sodium, potassium or alkali metals in general
    • C01D3/14Purification
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/02Aluminium oxide; Aluminium hydroxide; Aluminates
    • C01F7/04Preparation of alkali metal aluminates; Aluminium oxide or hydroxide therefrom
    • C01F7/06Preparation of alkali metal aluminates; Aluminium oxide or hydroxide therefrom by treating aluminous minerals or waste-like raw materials with alkali hydroxide, e.g. leaching of bauxite according to the Bayer process
    • C01F7/0613Pretreatment of the minerals, e.g. grinding
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00Hydraulic cements
    • C04B7/24Cements from oil shales, residues or waste other than slag
    • 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
    • C22B21/00Obtaining aluminium
    • C22B21/0015Obtaining aluminium by wet processes
    • C22B21/0023Obtaining aluminium by wet processes 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
    • C22B21/00Obtaining aluminium
    • C22B21/0038Obtaining aluminium by other processes
    • C22B21/0069Obtaining aluminium by other processes from scrap, skimmings or any secondary source aluminium, e.g. recovery of alloy constituents
    • 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)
    • 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
    • C22B7/006Wet 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
    • 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
    • C22B7/04Working-up slag
    • 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
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding

Abstract

The invention discloses a method for comprehensively recycling aluminum ash, which comprises the following steps: washing and desalting the aluminum ash to obtain washed aluminum ash and washing liquid; drying the washed aluminum ash, and performing elemental analysis; then carrying out thermodynamic calculation of calcification alkali fusion according to the contents of aluminum and fluorine, then adding an alkali fusing agent and a calcification agent into the aluminum ash according to the result of the thermodynamic calculation, and uniformly mixing to obtain a roasting raw material; roasting the roasting raw material to obtain a roasted material; soaking the roasted material in water, and then carrying out solid-liquid separation to obtain a water leaching solution and water leaching residues; concentrating and crystallizing the water leaching solution to obtain sodium metaaluminate; and drying the water leaching slag, and then using the water leaching slag in the cement industry. The method of the invention treats the harmful substances in the aluminum ash and recycles the valuable elements in the aluminum ash, and no pollutant is discharged, and simultaneously the valuable metal resources in the aluminum ash are utilized to the maximum extent, thereby realizing the recycling of the aluminum metal resources and the harmless disposal of hazardous wastes.

Description

Method for comprehensively recycling aluminum ash
Technical Field
The invention belongs to the technical field of solid hazardous waste treatment, and particularly relates to a method for comprehensively recycling aluminum ash.
Background
In the process of producing aluminum, the aluminum processing industry (electrolytic aluminum, aluminum casting, waste aluminum regeneration and the like) can generate waste materials containing high-content aluminum elements, wherein the content of the aluminum elements is often several times of that of ore resources, and the waste materials have great resource property, meanwhile, aluminum ash is also the forty-eight harmful waste in national hazardous waste records, and heavy metals (the content of the heavy metals is less, and mainly fluoride and soluble salts) cause great harm to human health and environment.
Because the aluminum ash has complex components, difficult disposal and higher economic cost, the aluminum ash is only subjected to simple stockpiling or landfill treatment before. However, since it contains substances harmful to the natural environment and human health, it must be treated, and at present, the treatment methods of aluminum ash are divided into two categories, namely disposal methods and recycling treatment.
Aiming at the treatment method of the aluminum ash, although the harmless treatment method is simple, the utilization value of valuable elements in the aluminum ash is ignored, the resource treatment mode has complex process flow, great treatment difficulty and higher economic cost, so that the aluminum ash is still in the situation that a large amount of aluminum ash is stockpiled and cannot be recycled at present. Although the aluminum ash harmless treatment technology is relatively mature, the current harmless treatment method can cause that a large amount of valuable aluminum elements cannot be continuously recycled. At present, the research of a method for efficiently recycling valuable resources of aluminum ash to the maximum extent while harmlessly treating the aluminum ash is newly reported, so that the research of a simple and effective solid waste recycling method is necessary.
Disclosure of Invention
The invention aims to provide a method for comprehensively recycling aluminum ash, which has the advantages of simple process, environmental friendliness, no pollutant discharge and high-efficiency resource recycling.
The method for comprehensively recycling the aluminum ash comprises the following steps:
1) washing and desalting the aluminum ash to obtain washed aluminum ash and washing liquid;
2) drying the washed aluminum ash in the step 1), and performing element analysis; then carrying out thermodynamic calculation of calcification alkali fusion according to the contents of aluminum and fluorine, then adding an alkali fusing agent and a calcification agent into the aluminum ash according to the result of the thermodynamic calculation, and uniformly mixing to obtain a roasting raw material;
3) roasting the roasting raw material in the step 2) in a muffle furnace to obtain a roasted material after roasting is finished;
4) soaking the roasted material in the step 3) in water, and after the soaking is finished, carrying out solid-liquid separation to obtain a water leaching solution and water leaching slag;
5) concentrating and crystallizing the water extract obtained in the step 4) to obtain sodium metaaluminate; and drying the water leaching slag, and then using the water leaching slag in the cement industry.
And in the step 1), the obtained water washing liquid is further treated by an ion permeable membrane, and sodium chloride and potassium chloride are recovered.
In the step 1), gas can be generated in the washing process, the generated gas is collected and absorbed by dilute sulfuric acid, and the residual gas after absorption can supply energy for the roasting process. In the washing process, a small amount of metal aluminum in the material reacts with water to generate hydrogen, aluminum nitride is hydrolyzed to generate ammonia gas, the aqueous solution becomes alkaline, and the ammonia gas overflows.
In the step 1), washing is carried out according to a liquid-solid ratio of (7-9) mL/1g, and the washing time is 5-7 h.
In the step 2), the alkali fusing agent is sodium hydroxide, and the calcification agent is calcium oxide; according to thermodynamic calculation, the adding amount of sodium hydroxide is added according to the molar ratio of aluminum to sodium of 1: 0.6-1.4, and the adding amount of calcium oxide is added according to the molar ratio of calcium fluoride of 1: 2.0-7.0.
In the step 3), the roasting temperature is 600-1000 ℃, and the roasting time is 0.5-2.5 h.
In the step 4), the liquid-solid ratio of water leaching is (5-7) to 1, and the leaching time is 20-40 min.
The principle of the invention is as follows: the invention takes the aluminum ash as the main roasting raw material, calcium oxide and sodium hydroxide are added as external raw materials, fluorine in the aluminum ash and a calcium source are combined and solidified to generate stable calcium fluoride and calcium fluoroaluminate under the high temperature condition, simultaneously, an aluminum compound in the aluminum ash reacts with the sodium hydroxide to generate sodium metaaluminate, after water immersion, aluminum elements enter an aqueous solution in the form of the sodium metaaluminate, and the calcium fluoride and the calcium fluoroaluminate are stably remained in residues, thereby achieving the aim of harmlessly and efficiently recycling the aluminum elements.
The invention has the beneficial effects that: firstly, processing raw materials, knowing the basic physical and chemical properties of the raw materials, then carrying out thermodynamic calculation on known substances in the materials, mixing a calcification agent and an alkali flux with aluminum ash according to a calculation result, and carrying out roasting reaction, so that harmful fluorine elements in the aluminum ash can be solidified and recovered to utilize fluorine, and meanwhile, high-content aluminum resources are recovered in the form of sodium metaaluminate; the method treats the harmful substances in the aluminum ash and simultaneously recycles the valuable elements in the aluminum ash, discharges no pollutants, simultaneously utilizes the valuable metal resources in the aluminum ash to the maximum extent, realizes the recycling of the aluminum metal resources and the harmless disposal of hazardous wastes, and further has the advantages of simple process, no pollutant discharge in the whole process flow and environmental friendliness.
Drawings
FIG. 1 is a process flow diagram of the present invention;
FIG. 2 is an XRD analysis of the aluminum grey water wash of example 1 after evaporative crystallization;
FIG. 3 is an XRD analysis chart of an aluminum ash calcified alkali fused material in example 1;
FIG. 4 is an XRD analysis of the grey water aluminum dross in example 1;
FIG. 5 is an XRD analysis pattern of the water immersion liquid after evaporation and crystallization in example 1.
Detailed Description
The following description is only exemplary of the present invention, but the scope of the present invention is not limited thereto, and it should be understood by those skilled in the art that any changes or substitutions that can be easily made by those skilled in the art within the technical scope of the present invention are within the scope of the present invention and the disclosure.
Example 1
A harmless and efficient recycling treatment method for aluminum ash comprises the following steps according to the flow shown in figure 1:
(1) 30g of aluminum ash raw material is taken and washed for 6h for desalination pretreatment according to the liquid-solid ratio of 8mL:1g, bubbles can be generated during washing (in view of the fact that only a small amount of treatment is performed in the embodiment, gas is not recovered, and the generated gas needs to be collected during large-scale treatment), after washing, filtration and drying are performed on the washed water, evaporation concentration crystallization is performed on the washed water, and the XRD phase chromatogram after evaporation concentration of the washed water is shown in FIG. 2, which is known from FIG. 2: the main components of the water-soluble salt are soluble salts, mainly sodium chloride and potassium chloride (because the amount of the washing water in the embodiment is less, if the water-soluble salt is treated in a large scale, the water-soluble salt can be further purified through an ion permeable membrane, and the sodium chloride and the potassium chloride are recovered); and drying the washing slag to obtain the washed aluminum ash.
(2) And (3) analyzing the element content of the washed aluminum ash, wherein the aluminum ash as the raw material contains 33.52% of Al, 11% of F and a small amount of oxides of calcium, silicon, iron, magnesium and the like.
(3) And (3) carrying out thermodynamic calculation on the reaction process in the step (2), and mainly calculating the reaction thermodynamics of the aluminum compound and the fluorine compound after the calcium agent and the alkali fusing agent are added.
(4) Taking 20.0g of the aluminum ash washed by the water in the step (1), adding calcium hydroxide and calcium oxide into the aluminum ash to prepare a calcified alkali fusion mixed material; the adding amount of the sodium hydroxide is the ratio of the aluminum to the sodium in a molar ratio of 1:0.6, and the adding amount of the calcium oxide is the ratio of the calcium fluoride in a molar ratio of 1: 6.0.
(5) Adding the calcified alkali-fused mixed material obtained in the step (4) into a 100mL ceramic crucible, sending the mixture into a muffle furnace, adjusting the temperature to 1000 ℃, reacting for 2.0h to obtain a calcified alkali-fused material, and performing XRD (X-ray diffraction) test on the obtained calcified alkali-fused material, wherein the main components of the calcified alkali-fused material are sodium metaaluminate, calcium fluoride and calcium fluoroaluminate, and the result is shown in figure 3.
(6) And (3) soaking the calcified alkali fusion material obtained in the step (5) in water for 40min according to the liquid-solid ratio of 6mL:1g, filtering to obtain water-soaked slag and water-soaked liquid, and evaporating and crystallizing the water-soaked liquid to obtain a sodium metaaluminate product, wherein the water-soaked slag can be used as a cement production raw material. The XRD phase diagram of the water-immersed slag is shown in figure 4, and the main components of the water-immersed slag are calcium fluoride and calcium fluoroaluminate which can be used as raw materials in the cement preparation process. The XRD phase diagram of the water extract evaporation concentrated crystal is shown in figure 5, and the main component of the water extract evaporation concentrated crystal is sodium metaaluminate.
Example 2
A harmless and efficient recycling treatment method for aluminum ash comprises the following steps according to the flow shown in figure 1:
(2) 500g of aluminum ash raw material is taken to be washed with water for 6h for desalination pretreatment according to the liquid-solid ratio of 8mL to 1g, bubbles can be seen to be generated during washing, gas is collected at the same time, the aluminum ash raw material sequentially passes through a test tube with wet red test paper and a test tube with heated black copper oxide powder, the wet red test paper turns blue, the black copper oxide powder gradually turns to mauve along with the continuous introduction of the gas, and the fact that ammonia gas and hydrogen gas are generated in the washing process is proved (because the gas generation amount is less, the gas is not recovered). After the water washing is finished, filtering and drying, taking a small amount of water washing liquid to evaporate, concentrate and crystallize the water washing liquid, wherein the XRD phase atlas of the water washing liquid after evaporation and concentration is shown in figure 2, and can be known from figure 2: the main components of the water-soluble salt are soluble salts, mainly sodium chloride and potassium chloride (because the amount of the washing water in the embodiment is less, if the water-soluble salt is treated in a large scale, the water-soluble salt can be further purified through an ion permeable membrane, and the sodium chloride and the potassium chloride are recovered); and drying the washing slag to obtain the washed aluminum ash.
(2) And (3) analyzing the element content of the washed aluminum ash, wherein the aluminum ash as the raw material contains 34.45% of Al, 10.7% of F and a small amount of oxides of calcium, silicon, iron, magnesium and the like.
(3) And (3) carrying out thermodynamic calculation on the reaction process in the step (2), and mainly calculating the reaction thermodynamics of the aluminum compound and the fluorine compound after the calcium agent and the alkali fusing agent are added.
(4) Taking 20.0g of the aluminum ash washed by the water in the step (1), adding calcium hydroxide and calcium oxide into the aluminum ash to prepare a calcified alkali fusion mixed material; the adding amount of the sodium hydroxide is 1:1.0 of the molar ratio of the aluminum to the sodium and the adding amount of the calcium oxide is 1:5.0 of the molar ratio of the calcium fluoride.
(5) Adding the calcified alkali-fused mixed material obtained in the step (4) into a 100mL ceramic crucible, sending the mixture into a muffle furnace, adjusting the temperature to 800 ℃, reacting for 2.5 hours to obtain a calcified alkali-fused material, and performing XRD (X-ray diffraction) test on the obtained calcified alkali-fused material, wherein the main components of the calcified alkali-fused material are sodium metaaluminate, calcium fluoride and calcium fluoroaluminate, and the result is shown in figure 3.
(6) And (3) soaking the calcified alkali fusion material obtained in the step (5) in water for 30min according to the liquid-solid ratio of 7mL:1g, and filtering to obtain water-soaked slag and water-soaked liquid, evaporating and crystallizing the water-soaked liquid to obtain a sodium metaaluminate product, wherein the water-soaked slag can be used as a cement production raw material.
The method comprises the steps of mixing a calcification agent and an alkali fusion agent with aluminum ash according to a certain proportion for reaction, wherein the technical key point is pyrogenic treatment, so that valuable elements in the aluminum ash can be recycled while harmful substances in the aluminum ash are treated, no pollutant is discharged, valuable metal resources in the aluminum ash are utilized to the maximum extent, the recovery of the aluminum metal resources and the harmless treatment of hazardous wastes are realized, and the treatment method is simple in process and environment-friendly.
In conclusion, the method firstly needs to process the raw materials, knows the basic physical and chemical properties of the raw materials, then carries out thermodynamic calculation on the known substances in the materials, carries out reaction material proportioning on the materials according to the calculation result, takes the ceramic crucible as a container, and sends the materials into the muffle furnace for high-temperature reaction, so that harmful fluorine elements in the aluminum ash can be solidified and recycled, meanwhile, high-content aluminum resources can be recycled, and meanwhile, the whole process flow has no pollutant emission and is environment-friendly.

Claims (7)

1. A method for comprehensively recycling aluminum ash comprises the following steps:
1) washing and desalting the aluminum ash to obtain washed aluminum ash and washing liquid;
2) drying the washed aluminum ash in the step 1), and performing element analysis; then carrying out thermodynamic calculation of calcification alkali fusion according to the contents of aluminum and fluorine, then adding an alkali fusing agent and a calcification agent into the aluminum ash according to the result of the thermodynamic calculation, and uniformly mixing to obtain a roasting raw material;
3) roasting the roasting raw material in the step 2) in a muffle furnace to obtain a roasted material after roasting is finished;
4) soaking the roasted material in the step 3) in water, and after the soaking is finished, carrying out solid-liquid separation to obtain a water leaching solution and water leaching slag;
5) concentrating and crystallizing the water extract obtained in the step 4) to obtain sodium metaaluminate; and drying the water leaching slag, and then using the water leaching slag in the cement industry.
2. The method for comprehensively recycling aluminum ash as claimed in claim 1, wherein the water washing liquid obtained in step 1) is further treated by an ion permeable membrane to recover sodium chloride and potassium chloride.
3. The method for comprehensively recycling the aluminum ash according to claim 1, wherein in the step 1), gas is generated in the washing process, the generated gas is collected and absorbed by dilute sulfuric acid, and the residual gas after absorption can supply energy for the roasting process.
4. The method for comprehensively recycling the aluminum ash as claimed in claim 1, wherein in the step 1), the washing is carried out according to a liquid-solid ratio of (7-9) mL/1g, and the washing time is 5-7 h.
5. The method for comprehensively recycling aluminum ash according to claim 1, wherein in the step 2), the alkali fusing agent is sodium hydroxide, and the calcification agent is calcium oxide; according to thermodynamic calculation, the adding amount of sodium hydroxide is added according to the molar ratio of aluminum to sodium of 1: 0.6-1.4, and the adding amount of calcium oxide is added according to the molar ratio of calcium fluoride of 1: 2.0-7.0.
6. The method for comprehensively recycling the aluminum ash according to claim 1, wherein in the step 3), the roasting temperature is 600-1000 ℃ and the roasting time is 0.5-2.5 h.
7. The method for comprehensively recycling the aluminum ash according to claim 1, wherein in the step 4), the liquid-solid ratio of water leaching is 5-7 mL:1g, and the leaching time is 20-40 min.
CN202210194904.7A 2022-03-01 2022-03-01 Method for comprehensively recycling aluminum ash Pending CN114560483A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115536050A (en) * 2022-11-02 2022-12-30 中南大学 Process method for preparing cryolite by aluminum ash recombination

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WO2021097912A1 (en) * 2019-11-21 2021-05-27 江苏省沙钢钢铁研究院有限公司 Resource recovery method and resource recovery system for desulfurization ash
CN113149034A (en) * 2021-05-17 2021-07-23 北京科技大学 Method for treating secondary aluminum ash by dry-method ternary roasting
CN113479920A (en) * 2021-07-06 2021-10-08 内蒙古日盛可再生资源有限公司 Aluminum ash resource utilization method
CN113912097A (en) * 2021-09-16 2022-01-11 佛山市吉力达铝材科技有限公司 Harmless treatment method for aluminum ash

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115536050A (en) * 2022-11-02 2022-12-30 中南大学 Process method for preparing cryolite by aluminum ash recombination

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