CN114988484A - Gypsum tailing treatment method of solid lithium ore neutralization process - Google Patents

Gypsum tailing treatment method of solid lithium ore neutralization process Download PDF

Info

Publication number
CN114988484A
CN114988484A CN202210528492.6A CN202210528492A CN114988484A CN 114988484 A CN114988484 A CN 114988484A CN 202210528492 A CN202210528492 A CN 202210528492A CN 114988484 A CN114988484 A CN 114988484A
Authority
CN
China
Prior art keywords
solution
gypsum
solid
aluminum
lithium ore
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.)
Pending
Application number
CN202210528492.6A
Other languages
Chinese (zh)
Inventor
刘志启
闫东强
李娜
赵鹏程
周自圆
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.)
Green Industry Innovation Research Institute of Anhui University
Original Assignee
Green Industry Innovation Research Institute of Anhui 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 Green Industry Innovation Research Institute of Anhui University filed Critical Green Industry Innovation Research Institute of Anhui University
Priority to CN202210528492.6A priority Critical patent/CN114988484A/en
Publication of CN114988484A publication Critical patent/CN114988484A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G49/00Compounds of iron
    • C01G49/02Oxides; Hydroxides
    • C01G49/06Ferric oxide [Fe2O3]
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/46Sulfates
    • C01F11/468Purification of calcium sulfates
    • 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
    • C01F7/021After-treatment of oxides or hydroxides
    • 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
    • C01F7/44Dehydration of aluminium oxide or hydroxide, i.e. all conversions of one form into another involving a loss of water
    • C01F7/441Dehydration of aluminium oxide or hydroxide, i.e. all conversions of one form into another involving a loss of water by calcination
    • 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
    • C01F7/46Purification of aluminium oxide, aluminium hydroxide or aluminates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity
    • 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

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

The invention discloses a gypsum tailing treatment method of a solid lithium ore neutralization process, which comprises the following steps: step 1, mixing gypsum tailing powder with a strong acid solution and then reacting; step 2, carrying out solid-liquid separation on the product obtained after the reaction in the step 1 to obtain a filtrate and a filter cake; step 3, drying the filter cake obtained in the step 2 to obtain high-strength gypsum; step 4, adding a strong alkali solution into the filtrate obtained in the step 2, adjusting the pH value, and then carrying out solid-liquid separation to obtain an aluminum-containing solution and an iron hydroxide precipitate; step 5, roasting the ferric hydroxide precipitate to obtain ferric oxide solid; step 6, adding a weak alkaline solution into the aluminum-containing solution, carrying out solid-liquid separation after the pH value of the solution is reached, and obtaining aluminum hydroxide filter residues; and 7, roasting the aluminum hydroxide filter residue to obtain the high-purity aluminum oxide. The method can separate high-strength gypsum, aluminum oxide and ferric oxide products with high added values from the gypsum tailings, is environment-friendly, and improves the environmental protection of the solid lithium ore treatment process.

Description

Gypsum tailing treatment method of solid lithium ore neutralization process
Technical Field
The invention relates to the field of tailing treatment methods of lithium ore neutralization processes, in particular to a gypsum tailing treatment method of a solid lithium ore neutralization process.
Background
With the development of social economy, the contradiction between supply and demand of global petroleum resources is increasingly prominent, and the demand of global lithium carbonate is greatly increased by the pulling of lithium battery markets of hybrid power and electric automobiles when main economic entities popularize and popularize electric automobiles. The external dependency degree of 2011-2015 in China, which belongs to the import country of lithium resources at present, reaches 80 percent, the search for new lithium resources becomes the urgent affairs of China, the dependence of the lithium resources of China on the outside can be fundamentally solved, and the energy safety of China is ensured. Also, solid lithium minerals should be used more efficiently and economically as an auxiliary resource to meet the growing demand for lithium and lithium salts.
The main occurrence modes of the global lithium ore resource resources comprise salt lake brine, spodumene and lepidolite, the yield of the world lithium salt pair in 2017 is 60 percent by extracting lithium from 23.54 million tons of brine and 40 percent by extracting lithium from ores in terms of equivalent of lithium carbonate. Many domestic enterprises, such as the southern group, the nine-ridge new energy and other enterprises, are focused on the process of producing lithium carbonate from ores, but acid tailing waste residues generated in the process of producing lithium carbonate are difficult to treat, and the problem of limiting large-scale mass production is solved. Especially for lepidolite ore and lithium-containing bauxite, the impurities are more, and if the acid tailing waste residue of the lepidolite ore and the lithium-containing bauxite cannot be properly and cost-effectively treated, the normal operation and further production expansion of the lithium extraction process can be restricted, so that the comprehensive utilization of the tailing waste residue becomes one of the important problems in the lithium salt industry.
At present, after solid lithium ore is treated by a neutralization process, more gypsum filter residues exist, the storage space is large, if the solid lithium ore is directly discharged, environmental pollution and resource waste can be caused, so that the neutralization filter residues need to be subjected to advanced treatment, and the utilization efficiency of resources is improved. However, in the prior art, no suitable method is available for high-value utilization, so that a method with high efficiency, environmental protection and low cost is needed for further processing the solid lithium ore neutralization tailings so as to realize comprehensive utilization of the solid lithium ore neutralization tailings.
Disclosure of Invention
The invention aims to provide a gypsum tailing treatment method for a solid lithium ore neutralization process, which aims to solve the problem that the prior art does not have an effective treatment method for gypsum tailings obtained by neutralizing solid lithium ores, and realize the recovery of high-strength gypsum, aluminum and iron after the gypsum tailings are treated.
In order to achieve the purpose, the technical scheme adopted by the invention is as follows:
the gypsum tailing treatment method of the solid lithium ore neutralization process comprises the following steps:
step 1, crushing and drying gypsum tailings obtained after the solid lithium ores are subjected to neutralization process treatment to obtain gypsum tailing powder.
One or more of sulfuric acid, hydrochloric acid, nitric acid and perchloric acid are selected and mixed according to any proportion to obtain a strong acid solution, wherein the mass fraction of the strong acid solution is required to be 30-80%.
After mixing the gypsum tailing powder and the strong acid solution according to the solid-liquid mass mixing ratio of 1: 1-1: 5, reacting for 30-90 minutes at the temperature of 30-80 ℃.
And 2, carrying out solid-liquid separation on the product obtained after the reaction in the step 1 to respectively obtain a filtrate and a filter cake.
And 3, drying the filter cake obtained in the step 2 for 3-5 hours at the temperature of 50-100 ℃ to obtain the high-strength gypsum. Through the step, the high-strength gypsum can be recovered from the gypsum tailings.
And 4, optionally selecting one from ammonia water solution, sodium hydroxide solution, potassium hydroxide solution, sodium carbonate solution and ammonium carbonate solution or optionally mixing several solutions according to any proportion to obtain strong alkali solution, wherein the required concentration of the strong alkali solution is 2-5 mol/L.
And (3) adding the strong alkali solution into the filtrate obtained in the step (2) at a dropping speed of 5-20 rpm until the pH value of the filtrate is adjusted to 3.0-4.0, and then carrying out solid-liquid separation to obtain an aluminum-containing solution and ferric hydroxide precipitates.
And 5, roasting the ferric hydroxide precipitate obtained in the step 4 at the temperature of 400-800 ℃ for 3-6 h to obtain ferric oxide solid. Iron can be recovered from the gypsum tailings by this step and is recovered as ferric oxide solids.
And 6, optionally selecting one of ammonia water, sodium carbonate and potassium carbonate or optionally mixing several of the ammonia water, the sodium carbonate and the potassium carbonate according to any proportion to obtain a weak alkaline solution, wherein the required concentration of the weak alkaline solution is 0.5-3.5 mol/L.
And (4) adding a weak alkaline solution into the aluminum-containing solution obtained in the step (4) until the pH value of the aluminum-containing solution is adjusted to 4.0-6.0, and then carrying out solid-liquid separation to obtain the aluminum hydroxide filter residue.
And 7, roasting the aluminum hydroxide filter residue obtained in the step 6 at the temperature of 800-1500 ℃ for 3-6 h to obtain the high-purity aluminum oxide. Aluminum can be recovered from the gypsum tailings by this step and is recovered as alumina.
The leaching solution of the clay lithium ore sulfuric acid method contains a large amount of impurity ions such as aluminum and iron, and the impurity ions need to be separated in order to obtain a lithium-containing solution with simple components. In order to achieve the purpose, 35% of calcium carbonate in mass fraction is added into sulfuric acid leaching solution to adjust the pH =6, then the leaching solution after the pH adjustment is filtered, the filtrate is lithium-containing neutralization solution for removing aluminum and iron, and the filter residue is calcium sulfate containing aluminum and iron. In order to reasonably utilize filter residues as resources, the experiment explores the influence of different sulfuric acid concentrations, different solid-to-liquid ratios, different reaction temperatures and different reaction times on the leaching of the aluminum and the iron. The invention takes place the following reactions:
2Al(OH) 3 +3H 2 SO 4 =Al 2 (SO 4 ) 3 +6H2O
2Fe(OH) 3 +3H 2 SO 4 =Fe 2 (SO4) 3 +6H 2 O
Fe 2 (SO 4 ) 3 +6NaOH=2Fe(OH) 3 +3Na 2 SO 4
Al 2 (SO4) 3 +6NaOH=2Al(OH) 3 +3Na 2 SO 4
Al(OH) 3 +NaOH=NaAlO 2 +2H 2 O
the invention provides a method for treating gypsum tailings containing aluminum and iron obtained by a solid lithium ore neutralization process, which comprises the steps of treating the gypsum tailings with acid and alkali, and separating solid from liquid for multiple times to obtain high-strength gypsum, aluminum oxide and ferric oxide products with high added values. The process disclosed by the invention is green and environment-friendly, the environmental protection of the solid lithium ore treatment process is further improved, and the specific high practical value is achieved.
Drawings
FIG. 1 is a block flow diagram of the method of the present invention.
Detailed Description
Hereinafter, embodiments of the present invention will be described in detail with reference to specific data. This invention may, however, be embodied in many different forms and should not be construed as limited to the embodiments set forth herein. Rather, these embodiments are provided to explain the principles of the invention and its practical application to thereby enable others skilled in the art to understand the invention for various embodiments and with various modifications as are suited to the particular use contemplated.
The process of the present invention for comprehensively utilizing the waste slag containing aluminum and iron gypsum by an acid method will be described below by way of specific examples, but those skilled in the art will understand that the following examples are only specific examples of the preparation method of the present invention and are not intended to limit the entirety thereof.
Embodiment 1, as shown in fig. 1, this embodiment includes the following steps:
(1) and obtaining gypsum tailings left after the solid lithium ore neutralization process, crushing the gypsum tailings into powder, and drying the powder for 5 hours at the temperature of 60 ℃ to obtain gypsum tailing powder.
Selecting sulfuric acid from sulfuric acid, hydrochloric acid, nitric acid and perchloric acid as a required strong acid solution, and preparing the strong acid solution with the mass fraction of 30% of sulfuric acid.
Mixing the gypsum tailing powder with a strong acid solution according to the solid-liquid mass mixing ratio of 1:2, and reacting for 30 minutes at the temperature of 30 ℃.
(2) And (2) filtering the product obtained in the step (1) to realize solid-liquid separation, and respectively obtaining a filtrate and a filter cake.
(3) And (3) drying the filter cake obtained in the step (2) at the temperature of 50 ℃ for 3 hours to obtain the high-strength gypsum.
(4) Selecting a sodium hydroxide solution from an ammonia water solution, a sodium hydroxide solution, a potassium hydroxide solution, a sodium carbonate solution and an ammonium carbonate solution as a required strong alkali solution, and preparing the sodium hydroxide solution to enable the concentration of the sodium hydroxide solution to be 2 mol/L.
Sodium hydroxide solution was added to the filtrate obtained in step (2) at a dropping rate of 5rpm until the pH of the filtrate was adjusted to 3.0. Then filtering to realize solid-liquid separation, and obtaining an aluminum-containing solution and ferric hydroxide precipitates.
(5) And (5) roasting the ferric hydroxide precipitate obtained in the step (4) at the temperature of 400 ℃ for 3 hours to obtain ferric oxide solid.
(6) Selecting ammonia water from ammonia water, sodium carbonate and potassium carbonate as a needed weak alkaline solution, and preparing the ammonia water to enable the concentration of the ammonia water to be 3.5 mol/L.
And (4) adding an ammonia water solution dropwise into the aluminum-containing solution obtained in the step (4) until the pH value of the aluminum-containing solution is adjusted to 4.0, and then carrying out solid-liquid separation to obtain the aluminum hydroxide filter residue.
(7) And (4) roasting the aluminum hydroxide filter residue obtained in the step (6) at the temperature of 1500 ℃ for 3 hours to obtain the high-purity aluminum oxide.
In this example, the obtained high-strength gypsum, ferric oxide, and alumina had tastes of about 91%, 75%, and 83%/80%, respectively, and the recovery rates were 89%, 80%, and 83%/82%, respectively.
Embodiment 2, this embodiment includes the following steps:
(1) and obtaining the gypsum tailings left after the solid lithium ore neutralization process, crushing the gypsum tailings into powder, and drying the powder for 5 hours at the temperature of 60 ℃ to obtain the gypsum tailing powder.
Selecting sulfuric acid from sulfuric acid, hydrochloric acid, nitric acid and perchloric acid as a required strong acid solution, and preparing the strong acid solution with the mass fraction of 30% of sulfuric acid.
Mixing the gypsum tailing powder with a strong acid solution according to the solid-liquid mixing mass ratio of 1:5, and reacting for 30 minutes at the temperature of 30 ℃.
(2) And (2) filtering the product obtained in the step (1) to realize solid-liquid separation, and respectively obtaining a filtrate and a filter cake.
(3) And (3) baking the filter cake obtained in the step (2) for 3 hours at the temperature of 50 ℃ to obtain the high-strength gypsum.
(4) Selecting a sodium hydroxide solution from an ammonia water solution, a sodium hydroxide solution, a potassium hydroxide solution, a sodium carbonate solution and an ammonium carbonate solution as a required strong alkali solution, and preparing the sodium hydroxide solution to enable the concentration of the sodium hydroxide solution to be 2 mol/L.
Sodium hydroxide solution was added to the filtrate obtained in step (2) at a dropping rate of 5rpm until the pH of the filtrate was adjusted to 4.0. Then filtering to realize solid-liquid separation, and obtaining an aluminum-containing solution and ferric hydroxide precipitates.
(5) And (5) roasting the ferric hydroxide precipitate obtained in the step (4) at the temperature of 400 ℃ for 6 hours to obtain ferric oxide solid.
(6) And selecting ammonia water from ammonia water, sodium carbonate and potassium carbonate as a required weak alkaline solution, and preparing the ammonia water to ensure that the concentration of the ammonia water is 2.0 mol/L.
And (5) adding an ammonia water solution dropwise into the aluminum-containing solution obtained in the step (4) until the pH value of the aluminum-containing solution is adjusted to 6.0, and then carrying out solid-liquid separation to obtain the aluminum hydroxide filter residue.
(7) And (4) roasting the aluminum hydroxide filter residue obtained in the step (6) at the temperature of 800 ℃ for 2 hours to obtain the high-purity aluminum oxide.
The high strength gypsum, ferric oxide, and alumina obtained in this example had tastes of about 94%, 81%, and 87%/85%, respectively, and the recovery rates were 93%, 84%, and 87%/85%, respectively.
Example 3:
(1) and obtaining gypsum tailings left after the solid lithium ore neutralization process, crushing the gypsum tailings into powder, and drying the powder for 10 hours at the temperature of 90 ℃ to obtain gypsum tailing powder.
Selecting sulfuric acid from sulfuric acid, hydrochloric acid, nitric acid and perchloric acid as a required strong acid solution, and preparing the strong acid solution with the mass fraction of 60% of sulfuric acid.
Mixing the gypsum tailing powder and the strong acid solution according to the solid-liquid mixing mass ratio of 1:3, and reacting for 30 minutes at the temperature of 30 ℃.
(2) And (2) filtering the product obtained in the step (1) to realize solid-liquid separation, and respectively obtaining a filtrate and a filter cake.
(3) And (3) baking the filter cake obtained in the step (2) at the temperature of 50 ℃ for 3 hours to obtain the high-strength gypsum.
(4) Selecting a sodium hydroxide solution from an ammonia water solution, a sodium hydroxide solution, a potassium hydroxide solution, a sodium carbonate solution and an ammonium carbonate solution as a required strong alkali solution, and preparing the sodium hydroxide solution to enable the concentration of the sodium hydroxide solution to be 3.5 mol/L.
Sodium hydroxide solution was added to the filtrate obtained in step (2) at a dropping rate of 5rpm until the pH of the filtrate was adjusted to 4.0. Then filtering to realize solid-liquid separation to obtain an aluminum-containing solution and ferric hydroxide precipitates.
(5) And (5) roasting the ferric hydroxide precipitate obtained in the step (4) at the temperature of 400 ℃ for 6 hours to obtain ferric oxide solid.
(6) Selecting ammonia water from ammonia water, sodium carbonate and potassium carbonate as a needed weak alkaline solution, and preparing the ammonia water to enable the concentration of the ammonia water to be 2.0 mol/L.
And (4) adding an ammonia water solution dropwise into the aluminum-containing solution obtained in the step (4) until the pH value of the aluminum-containing solution is adjusted to 6.0, and then carrying out solid-liquid separation to obtain the aluminum hydroxide filter residue.
(7) And (5) roasting the aluminum hydroxide filter residue obtained in the step (6) at the temperature of 800 ℃ for 2 hours to obtain the high-purity aluminum oxide.
The high strength gypsum, ferric oxide, and alumina obtained in this example had tastes of about 90%, 83%, 85%/83%, respectively, and recovery rates of 95%, 85%, 90%/88%, respectively.
The embodiments of the present invention are described only for the preferred embodiments of the present invention, and not for the limitation of the concept and scope of the present invention, and various modifications and improvements made to the technical solution of the present invention by those skilled in the art without departing from the design concept of the present invention shall fall into the protection scope of the present invention, and the technical content of the present invention which is claimed is fully set forth in the claims.

Claims (9)

1. The gypsum tailings treatment method of the solid lithium ore neutralization process is characterized by comprising the following steps of:
step 1, mixing gypsum tailing powder and a strong acid solution according to a solid-liquid mass mixing ratio of 1: 1-1: 5, and reacting for 30-90 minutes at a temperature of 30-80 ℃;
step 2, carrying out solid-liquid separation on the product obtained after the reaction in the step 1 to respectively obtain filtrate and filter cakes;
step 3, drying the filter cake obtained in the step 2 to obtain high-strength gypsum;
step 4, adding a strong alkali solution into the filtrate obtained in the step 2 until the pH value of the filtrate is adjusted to 3.0-4.0, and then carrying out solid-liquid separation to obtain an aluminum-containing solution and an iron hydroxide precipitate;
step 5, roasting the ferric hydroxide precipitate obtained in the step 4 to obtain ferric oxide solid;
step 6, adding a weak alkaline solution into the aluminum-containing solution obtained in the step 4 until the pH value of the aluminum-containing solution is adjusted to 4.0-6.0, and then carrying out solid-liquid separation to obtain aluminum hydroxide filter residue;
and 7, roasting the aluminum hydroxide filter residue obtained in the step 6 to obtain high-purity aluminum oxide.
2. The method for treating the gypsum tailings in the solid lithium ore neutralization process according to claim 1, wherein the gypsum tailing powder in the step 1 is obtained by crushing and pulverizing gypsum tailings, and drying at 60-100 ℃ for 5-12 hours.
3. The method for treating the gypsum tailings of the solid lithium ore neutralization process according to claim 1, wherein the mass fraction of the strong acid solution used in the step 1 is 30-80%, and the strong acid solution is one of sulfuric acid, hydrochloric acid, nitric acid and perchloric acid or a mixture of the sulfuric acid, the hydrochloric acid, the nitric acid and the perchloric acid in any proportion.
4. The method for treating the gypsum tailings in the solid lithium ore neutralization process according to claim 1, wherein the drying temperature in the step 3 is 50-100 ℃, and the drying time is 3-5 hours.
5. The method for treating the gypsum tailings of the solid lithium ore neutralization process according to claim 1, wherein the concentration of the strong alkali solution used in the step 4 is 2-5 mol/L, and the strong alkali solution is any one of an ammonia solution, a sodium hydroxide solution, a potassium hydroxide solution, a sodium carbonate solution and an ammonium carbonate solution or a mixture of the solutions in any proportion.
6. The method for treating the gypsum tailings in the solid lithium ore neutralization process according to claim 1, wherein the strong alkali solution is added into the filtrate at a dropping speed of 5 rpm-20 rpm in the step 4.
7. The method for treating gypsum tailings of the solid lithium ore neutralization process according to claim 1, wherein the calcination temperature in step 5 is 400 ℃ to 800 ℃.
8. The method for treating the gypsum tailings in the solid lithium ore neutralization process according to claim 1, wherein the concentration of the weak alkaline solution used in the step 6 is 0.5-3.5 mol/L, and the weak alkaline solution is any one of ammonia water, sodium carbonate and potassium carbonate or a mixture of the ammonia water, the sodium carbonate and the potassium carbonate in any proportion.
9. The method for treating gypsum tailings of the solid lithium ore neutralization process according to claim 1, wherein the calcination temperature in step 7 is 800-1500 ℃.
CN202210528492.6A 2022-05-16 2022-05-16 Gypsum tailing treatment method of solid lithium ore neutralization process Pending CN114988484A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210528492.6A CN114988484A (en) 2022-05-16 2022-05-16 Gypsum tailing treatment method of solid lithium ore neutralization process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210528492.6A CN114988484A (en) 2022-05-16 2022-05-16 Gypsum tailing treatment method of solid lithium ore neutralization process

Publications (1)

Publication Number Publication Date
CN114988484A true CN114988484A (en) 2022-09-02

Family

ID=83027665

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210528492.6A Pending CN114988484A (en) 2022-05-16 2022-05-16 Gypsum tailing treatment method of solid lithium ore neutralization process

Country Status (1)

Country Link
CN (1) CN114988484A (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104528798A (en) * 2014-12-16 2015-04-22 中国科学院青海盐湖研究所 Method for purifying low-grade natural gypsum or gypsum tailings by recrystallization
CN104532339A (en) * 2014-12-16 2015-04-22 青海博川矿业开发有限公司 Method for preparing calcium sulfate whisker from low-grade natural gypsum or gypsum tailings
CN109437264A (en) * 2018-12-06 2019-03-08 山东泰和水处理科技股份有限公司 A method of aluminium oxide is prepared from mentioning in lithium waste residue
CN110015855A (en) * 2019-04-01 2019-07-16 中国地质科学院郑州矿产综合利用研究所 Treatment method of lithium slag
CN113060752A (en) * 2021-03-23 2021-07-02 力上资源科技开发有限公司 Recycling method of fluorite flotation tailings

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104528798A (en) * 2014-12-16 2015-04-22 中国科学院青海盐湖研究所 Method for purifying low-grade natural gypsum or gypsum tailings by recrystallization
CN104532339A (en) * 2014-12-16 2015-04-22 青海博川矿业开发有限公司 Method for preparing calcium sulfate whisker from low-grade natural gypsum or gypsum tailings
CN109437264A (en) * 2018-12-06 2019-03-08 山东泰和水处理科技股份有限公司 A method of aluminium oxide is prepared from mentioning in lithium waste residue
CN110015855A (en) * 2019-04-01 2019-07-16 中国地质科学院郑州矿产综合利用研究所 Treatment method of lithium slag
CN113060752A (en) * 2021-03-23 2021-07-02 力上资源科技开发有限公司 Recycling method of fluorite flotation tailings

Similar Documents

Publication Publication Date Title
CN104016393B (en) A kind of by dolomite for light calcium carbonate and method of magnesium oxide
CN101235440A (en) Method of comprehensively utilizing serpentine
CN102897810B (en) Method for producing aluminum oxide by using fly ash
CN110028111B (en) Preparation method of ternary positive electrode material precursor and lithium carbonate
CN111498820A (en) Process for simultaneously preparing high-quality calcium sulfate whiskers from phosphorus concentrate enriched by medium-low-grade phosphate ore or phosphorus tailings
CN111218566B (en) Method for separating iron and chromium in process of treating laterite-nickel ore by nitric acid
CN115216645B (en) Method for extracting lithium from electrolytic aluminum waste residue by mixed salt calcination
CN113651342A (en) Method for producing lithium product by processing lepidolite through nitric acid atmospheric pressure method
CN109336147B (en) Method for producing alumina by using industrial solid waste rich in alumina
CN111762804B (en) Iron removal method for pickle liquor in acid process aluminum extraction
CN111792650A (en) Full-element recycling process of coal ash or coal gangue by hot-melt salt method
CN113562770B (en) Method for recycling iron and sodium resources in red mud in gradient manner and fully utilizing tailings
CN102417980B (en) Method for producing nickel sulfate by leaching Lateritic nickle ores with both sulfuric acid and ammonia
CN115466854B (en) Comprehensive extraction method of lithium ore
CN115072749B (en) Method for extracting lithium from spodumene without slag
CN113753924B (en) Method for extracting lithium carbonate and co-producing sodium aluminosilicate from lithium-rich clay by activated water dissolution method
CN115744864A (en) Method for efficiently recycling and reusing waste lithium iron phosphate battery positive electrode material
CN113735179B (en) Method for preparing high-purity ferric sulfate by utilizing ferro-manganese
CN114988484A (en) Gypsum tailing treatment method of solid lithium ore neutralization process
CN114231732A (en) Method for deeply extracting vanadium from vanadium-containing slurry
CN112758965A (en) Method for preparing magnesium hydroxide and secondary element water-soluble fertilizer from calcium-magnesium-containing leaching solution by-product of chemical mineral separation
CN102115813A (en) Comprehensive utilization method for low-grade magnesite
CN113930609B (en) Vanadium extraction and comprehensive utilization method for fluidized bed calcined stone coal
CN114836631B (en) Recycling method of copper-manganese liquid generated by extraction and recovery of battery materials
CN111041249B (en) Method for treating magnesium and/or calcium-containing waste liquid in rare earth smelting separation process

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