WO2022041845A1 - Recovery method for removing fluorine from nickel-cobalt-manganese solution - Google Patents
Recovery method for removing fluorine from nickel-cobalt-manganese solution Download PDFInfo
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- WO2022041845A1 WO2022041845A1 PCT/CN2021/093182 CN2021093182W WO2022041845A1 WO 2022041845 A1 WO2022041845 A1 WO 2022041845A1 CN 2021093182 W CN2021093182 W CN 2021093182W WO 2022041845 A1 WO2022041845 A1 WO 2022041845A1
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- Prior art keywords
- fluorine
- cobalt
- filter residue
- nickel
- filtrate
- Prior art date
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- 239000011737 fluorine Substances 0.000 title claims abstract description 132
- 229910052731 fluorine Inorganic materials 0.000 title claims abstract description 132
- KFDQGLPGKXUTMZ-UHFFFAOYSA-N [Mn].[Co].[Ni] Chemical compound [Mn].[Co].[Ni] KFDQGLPGKXUTMZ-UHFFFAOYSA-N 0.000 title claims abstract description 59
- 238000000034 method Methods 0.000 title claims abstract description 48
- 238000011084 recovery Methods 0.000 title claims abstract description 19
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 title 1
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 claims abstract description 131
- 239000000706 filtrate Substances 0.000 claims abstract description 66
- 239000002253 acid Substances 0.000 claims abstract description 26
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 23
- 238000001914 filtration Methods 0.000 claims abstract description 23
- 238000002386 leaching Methods 0.000 claims abstract description 21
- 239000000047 product Substances 0.000 claims abstract description 21
- 239000011268 mixed slurry Substances 0.000 claims abstract description 19
- 239000000843 powder Substances 0.000 claims abstract description 16
- 239000012535 impurity Substances 0.000 claims abstract description 14
- 229910001610 cryolite Inorganic materials 0.000 claims abstract description 11
- 238000005406 washing Methods 0.000 claims abstract description 7
- 238000002156 mixing Methods 0.000 claims abstract description 6
- 238000006115 defluorination reaction Methods 0.000 claims description 42
- 239000000243 solution Substances 0.000 claims description 42
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 14
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims description 9
- 229910052708 sodium Inorganic materials 0.000 claims description 9
- 239000011734 sodium Substances 0.000 claims description 9
- 238000000605 extraction Methods 0.000 claims description 8
- 239000001569 carbon dioxide Substances 0.000 claims description 7
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 7
- 239000012670 alkaline solution Substances 0.000 claims description 5
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical compound [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 claims description 5
- 238000001035 drying Methods 0.000 claims description 5
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 claims description 4
- 150000001875 compounds Chemical class 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims description 3
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 claims description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 2
- 230000008901 benefit Effects 0.000 abstract description 5
- 230000000694 effects Effects 0.000 abstract description 5
- 238000003756 stirring Methods 0.000 abstract description 5
- 239000003513 alkali Substances 0.000 abstract description 3
- 238000010438 heat treatment Methods 0.000 abstract 1
- 239000007788 liquid Substances 0.000 abstract 1
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 16
- 239000002699 waste material Substances 0.000 description 14
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 10
- 239000011572 manganese Substances 0.000 description 10
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 8
- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 description 7
- 229910001416 lithium ion Inorganic materials 0.000 description 7
- 238000004519 manufacturing process Methods 0.000 description 5
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 4
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 4
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 4
- QXZUUHYBWMWJHK-UHFFFAOYSA-N [Co].[Ni] Chemical compound [Co].[Ni] QXZUUHYBWMWJHK-UHFFFAOYSA-N 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 4
- 229910052748 manganese Inorganic materials 0.000 description 4
- 239000002994 raw material Substances 0.000 description 4
- 229910000029 sodium carbonate Inorganic materials 0.000 description 4
- 229910052782 aluminium Inorganic materials 0.000 description 3
- 229910001570 bauxite Inorganic materials 0.000 description 3
- 229910000625 lithium cobalt oxide Inorganic materials 0.000 description 3
- BFZPBUKRYWOWDV-UHFFFAOYSA-N lithium;oxido(oxo)cobalt Chemical compound [Li+].[O-][Co]=O BFZPBUKRYWOWDV-UHFFFAOYSA-N 0.000 description 3
- 230000035484 reaction time Effects 0.000 description 3
- 235000011127 sodium aluminium sulphate Nutrition 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 2
- -1 aluminum sulfate Chemical class 0.000 description 2
- 238000001479 atomic absorption spectroscopy Methods 0.000 description 2
- 239000010941 cobalt Substances 0.000 description 2
- 229910017052 cobalt Inorganic materials 0.000 description 2
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 2
- 238000002354 inductively-coupled plasma atomic emission spectroscopy Methods 0.000 description 2
- 229910052744 lithium Inorganic materials 0.000 description 2
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 230000003472 neutralizing effect Effects 0.000 description 2
- 229910052759 nickel Inorganic materials 0.000 description 2
- 239000007774 positive electrode material Substances 0.000 description 2
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 2
- 238000002360 preparation method Methods 0.000 description 2
- 238000010298 pulverizing process Methods 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 239000006229 carbon black Substances 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- VNTQORJESGFLAZ-UHFFFAOYSA-H cobalt(2+) manganese(2+) nickel(2+) trisulfate Chemical compound [Mn++].[Co++].[Ni++].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O VNTQORJESGFLAZ-UHFFFAOYSA-H 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 150000007522 mineralic acids Chemical class 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- 229910000027 potassium carbonate Inorganic materials 0.000 description 1
- 238000004313 potentiometry Methods 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000002516 radical scavenger Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000004904 shortening Methods 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F7/00—Compounds of aluminium
- C01F7/48—Halides, with or without other cations besides aluminium
- C01F7/50—Fluorides
- C01F7/54—Double compounds containing both aluminium and alkali metals or alkaline-earth metals
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M10/00—Secondary cells; Manufacture thereof
- H01M10/54—Reclaiming serviceable parts of waste accumulators
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/80—Compositional purity
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/84—Recycling of batteries or fuel cells
Definitions
- the invention belongs to the technical field of lithium ion battery recycling, and in particular relates to a method for removing fluorine from a nickel-cobalt-manganese sulfate solution after acid leaching of battery waste powder.
- Lithium-ion batteries have been widely used in various electronic products and electric vehicles and other industries. According to statistics, my country's lithium-ion battery production and output accounted for more than 50% of the world's total, and the output in 2019 was 15.72 billion. The rapid expansion of lithium-ion battery production capacity also means In recent years, there will be a large number of lithium-ion batteries that need to be scrapped and recycled. Improper handling will cause environmental pollution and waste of resources. Therefore, the recycling of lithium-ion batteries is imminent, which is important for environmental protection and sustainable development of resources. significance.
- used lithium-ion batteries are mainly disassembled, crushed, and screened to obtain positive electrode powder and other components.
- the method of inorganic acid leaching is mainly used to transfer the valuable metal from the solid powder to the solution and effectively separate it from carbon black and organic binders.
- the fluorine introduced will enter the solution, which will affect the process of wet recovery of nickel, cobalt and manganese, which mainly includes: 1) affecting the product quality of the nickel-cobalt-manganese ternary precursor; 2) fluorine removal in the subsequent wastewater treatment process section
- the pressure is high, and the current fluorine removal process is difficult to meet the wastewater discharge requirements, and the treatment cost is high; 3)
- the fluorine in the wet system will be corrosive to the equipment, shortening the service life of the equipment; 4) It is easy to cause pipeline blockage.
- a method for recovering fluorine removal in a nickel-cobalt-manganese solution is provided according to an embodiment of the present invention.
- the method of the embodiment of the present invention has a good fluorine removal effect in the nickel-cobalt-manganese solution in the first stage, without introducing other impurities, and the obtained fluorine-containing filter residue can meet the requirements of industrial cryolite products after being purified, and has a relatively large economy. benefit.
- the embodiment of the present invention provides a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
- the pH of the obtained mixed slurry is adjusted to 2-5, and a section of defluorinated filtrate and a section of fluorine-containing filter residue are obtained by filtration;
- a section of the fluorine-containing filter residue is washed and then added to the alkaline solution, heated and stirred, and filtered to obtain a fluorine-containing filtrate and a nickel-cobalt-manganese-containing filter residue.
- the battery powder can be obtained by pulverizing battery waste.
- the battery waste can be selected from waste positive electrode materials obtained by dismantling waste lithium batteries or waste positive electrode materials generated during the manufacturing process of lithium batteries.
- the removal of impurities includes removal of impurities such as iron, aluminum, and the like using processes known in the art.
- the resulting fluorine-containing nickel-cobalt-manganese solution contains a high concentration of fluorine.
- the nickel-cobalt-manganese concentration is 40-100 g/L, and the fluorine concentration is 1-5 g/L.
- the fluorine removing agent is a solid fluorine removing agent.
- the fluorine removing agent includes, but is not limited to, one or more of aluminum oxide, aluminum hydroxide and soluble aluminum salts.
- the soluble aluminum salts include single salts, such as aluminum sulfate, and double salts, such as sodium alum.
- the fluorine removing agent can be selected from natural and inexpensive materials whose main components are one or more of alumina, aluminum hydroxide and soluble aluminum salts, such as bauxite.
- the mass ratio of the volume of the nickel-cobalt-manganese solution to the defluorination agent is 50-300:1; preferably, 100-200:1.
- the applicant of the present invention has found and verified through previous research that the amount of fluorine removal agent added can be calculated according to the fluorine content in the nickel-cobalt-manganese solution, so that the minimum and appropriate amount of fluorine removal can be used on the premise of ensuring good fluorine removal effect.
- the agent reacts with fluorine to generate and preferentially generates sodium fluoroaluminate to avoid the generation of other impurity compounds.
- the pH of the obtained mixed slurry is adjusted to 2-5 with dilute acid.
- the dilute acid includes, but is not limited to, at least one of dilute sulfuric acid, dilute hydrochloric acid, and dilute nitric acid.
- the dilute acid is dilute sulfuric acid.
- the dilute acid concentration is 5-50%.
- the pH value of the obtained mixed slurry is adjusted to reduce to facilitate the conversion of aluminum in the fluorine scavenger into aluminum ions, which react with fluorine in the mixed slurry to generate sodium fluoroaluminate.
- the total reaction time of controlling the obtained mixed slurry to adjust pH to 2-5 is 0.5-2h. By controlling the speed and reaction time of adjusting pH value, it helps to form high-purity sodium fluoroaluminate precipitate and avoid the accumulation of new waste residue.
- the main component of a section of fluorine-containing filter residue obtained by filtration is sodium fluoroaluminate.
- the method further comprises: mixing the obtained section of defluorinated filtrate with a defluorinating agent, adjusting the pH to 2-5, and filtering to obtain a second section of defluorinated filtrate and The second-stage fluorine-containing filter residue.
- the fluorine content of the obtained second-stage defluorination filtrate is reduced to 20 mg/L or less
- the second-stage fluorine-containing filter residue contains a small amount of nickel, cobalt, and manganese
- the second-stage fluorine-containing filter residue is returned to the acid leaching process.
- the N-stage defluorination filtrate is further mixed with a defluorinating agent, adjusting The pH reaches 2-5, and N+1 stage defluorination filtrate and N+1 fluorine-containing filter residue are obtained by filtration.
- the second-stage fluorine-containing filter residue, ..., the N-stage fluorine-containing filter residue and the N+1 fluorine-containing filter residue are returned to the acid leaching process.
- N is greater than 1.
- the method further includes: adjusting the pH of the second-stage defluorination filtrate to 5-6.5, and performing subsequent extraction to obtain nickel-cobalt-manganese products.
- the N-stage defluorination filtrate is subjected to subsequent extraction to obtain Nickel Cobalt Manganese product. In this paper, N is greater than 1.
- the pH is adjusted to 5-6.5 with a neutralizing agent.
- the neutralizing agent includes but is not limited to one or more of sodium carbonate, potassium carbonate, sodium hydroxide, and potassium hydroxide.
- the neutralizer is a 10-30% concentration neutralizer solution.
- the alkali solution includes but is not limited to sodium hydroxide and potassium hydroxide solution.
- concentration of the lye solution is 5-30%.
- the ratio of the molar amount of the alkaline compound in the alkaline solution to the theoretical molar amount of sodium fluoroaluminate in the first-stage fluorine-containing filter residue is 0.9-1.5; preferably, the ratio is 1.0-1.4; more preferably, the ratio is is 1.1-1.3.
- a section of fluorine-containing filter residue is washed and then added to alkali solution, heated to 50-80° C., stirred for 0.5-2 h, and filtered to obtain fluorine-containing filtrate and nickel-cobalt-manganese-containing filter residue.
- the fluorine-containing filtrate and the nickel-cobalt-manganese-containing filter residue after obtaining the fluorine-containing filtrate and the nickel-cobalt-manganese-containing filter residue, it also includes:
- the obtained nickel-cobalt-manganese-containing filter residue is returned to the acid leaching process;
- the obtained fluorine-containing filtrate is passed into carbon dioxide to react, and the cryolite product is obtained after filtering, washing and drying.
- carbon dioxide is introduced into the reaction for 2-8h.
- the method of the embodiment of the present invention has a good defluorination effect in the nickel-cobalt-manganese solution in the first stage, and the loss of nickel-cobalt-manganese in the fluorine-containing filter residue is small; at the same time, the process of the embodiment of the present invention does not introduce other impurities, and the obtained fluorine-containing filter residue After the fluorine filter residue is purified, it can meet the requirements of industrial cryolite products, improve the added value of recycled raw materials, and have greater economic benefits.
- FIG. 1 is a flow chart of a method for removing fluorine in a nickel-cobalt-manganese solution according to an embodiment of the present invention.
- a kind of recovery method of removing fluorine in nickel-cobalt-manganese solution comprises the following steps:
- the obtained fluorine-containing nickel-cobalt-manganese solution is mixed with a defluorinating agent to obtain a mixed slurry;
- step (4) the gained one-stage defluorination filtrate is mixed with a defluorinating agent, and step (4) is repeated to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue; the second-stage fluorine-containing filter residue is returned to the acid leaching process;
- the raw materials mentioned below are all commercially available products; the concentrations of metal ions in the following examples are all obtained by atomic absorption spectrometry (AAS) or inductively coupled plasma atomic emission spectrometry (ICP-AES) ) determination; the fluoride ion concentration is determined by the fluorine electrode potentiometric method; the process steps or preparation methods not mentioned in detail are the process steps or preparation methods known to those skilled in the art.
- AAS atomic absorption spectrometry
- ICP-AES inductively coupled plasma atomic emission spectrometry
- the present embodiment proposes a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
- step (3) (4) using 30% dilute sulfuric acid to adjust the pH value of the mixed slurry obtained in step (3) to about 4, adjusting the pH within 1 h, and filtering to obtain a section of defluorination filtrate and a section of fluorine-containing filter residue, wherein a section of defluorination filtrate contains Fluorine is 34.6 mg/L, and (Ni+Co+Mn) in a fluorine-containing filter residue is 0.029% (by weight);
- step (4) adding 10g of bauxite to the one-stage defluorination filtrate obtained in step (4), repeating step (4), and filtering to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue, wherein the second-stage defluorination filtrate contains fluorine 20.7mg/L, the (Ni+Co+Mn) in the second-stage fluorine-containing filter residue is 0.905%, the second-stage fluorine-containing filter residue is returned to acid leaching; the second-stage defluorination filtrate is adjusted to about 5.7 with 15% sodium carbonate solution, and the subsequent Extraction to obtain nickel-cobalt-manganese products;
- the present embodiment proposes a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
- step (3) (4) using 20% dilute sulfuric acid to adjust the pH value of the mixed slurry obtained in step (3) to about 3, adjusting the pH within 1 hour, and filtering to obtain a section of defluorination filtrate and a section of fluorine-containing filter residue, wherein a section of defluorination filtrate contains Fluorine is 37.4mg/L, and (Ni+Co+Mn) in the first-stage fluorine-containing filter residue is 0.033% (by weight);
- step (4) adding 5g of aluminum hydroxide to the first-stage defluorination filtrate obtained in step (4), repeating step (4), and filtering to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue, wherein the second-stage defluorination filtrate contains fluorine 20.3mg/L, the (Ni+Co+Mn) in the second-stage fluorine-containing filter residue is 0.967%, the second-stage fluorine-containing filter residue is returned to acid leaching; the second-stage defluorination filtrate is adjusted to about 6.1 with 15% sodium carbonate solution, and the subsequent Extraction to obtain nickel-cobalt-manganese products;
- the present embodiment proposes a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
- step (3) (4) using 10% dilute sulfuric acid to adjust the pH value of the mixed slurry obtained in step (3) to about 2, adjusting the pH within 1 h, and filtering to obtain a section of defluorination filtrate and a section of fluorine-containing filter residue, wherein a section of defluorination filtrate contains Fluorine is 52.6 mg/L, and (Ni+Co+Mn) in the first-stage fluorine-containing filter residue is 0.041% (by weight);
- step (4) adding 10g of sodium alum to the first-stage defluorination filtrate obtained in step (4), repeating step (4), and filtering to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue, wherein the second-stage defluorination filtrate contains 19.6% fluorine mg/L, the (Ni+Co+Mn) in the second-stage fluorine-containing filter residue is 0.915%, the second-stage fluorine-containing filter residue is returned to acid leaching; the second-stage defluorination filtrate is adjusted to pH 5.5 with 10% sodium carbonate solution, and the subsequent extraction is carried out , to obtain nickel-cobalt-manganese products;
- step (6) The fluorine-containing filtrate obtained in step (6) was passed into carbon dioxide for 8h, filtered, washed and dried to obtain a cryolite product with a purity of 97.8%.
- the nickel-cobalt-manganese solution is defluorinated by the method of the embodiment of the present invention, and the fluorine content in the nickel-cobalt-manganese solution can be reduced to 20 mg/L or less, and the nickel-cobalt in the fluorine-containing filter residue can be reduced. Manganese content ⁇ 1%, less loss.
- the reaction conditions are wide, the reagents and raw materials used are cheap and easy, and the effect of removing fluorine is good.
- the added value of the recovered raw materials is improved, and the valuable metals entrained in the defluorination residue are effectively recovered.
- the process of the embodiment of the present invention is simple, no other impurities are introduced or generated, and the purity of cryolite obtained after treatment and purification of the fluorine-containing filter residue can reach more than 98%, which meets the requirements of industrial cryolite products and has considerable economic benefits.
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- Engineering & Computer Science (AREA)
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- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
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- Manufacture And Refinement Of Metals (AREA)
Abstract
The present invention relates to a recovery method for removing fluorine from a nickel-cobalt-manganese solution, comprising the following steps: after carrying out acid leaching and impurity removal on battery powder, obtaining a fluorine-containing nickel-cobalt-manganese solution; mixing the obtained fluorine-containing nickel-cobalt-manganese solution with a fluorine removing agent to obtain a mixed slurry; adjusting the pH of the obtained mixed slurry to 2-5, and passing through filtering to obtain a first-stage defluorinated filtrate and first-stage fluorine-containing filter residue; and after washing the first-stage fluorine-containing filter residue, adding same into an alkali liquid, heating and stirring same, and passing same through filtering to obtain fluorine-containing filtrate and nickel-cobalt-manganese-containing filter residue. The method of the embodiments of the present invention has a relatively good fluorine removal effect in a front-section nickel-cobalt-manganese solution. Meanwhile, other impurities are not introduced, the obtained fluorine-containing filter residue may meet industrial cryolite product requirements after being purified, and the method has relatively large economic benefits.
Description
本发明属于锂离子电池回收技术领域,具体涉及一种电池废旧粉料酸浸后硫酸镍钴锰溶液中除氟的方法。The invention belongs to the technical field of lithium ion battery recycling, and in particular relates to a method for removing fluorine from a nickel-cobalt-manganese sulfate solution after acid leaching of battery waste powder.
锂离子电池已经广泛地应用于各类电子产品和电动汽车等行业,据统计,我国锂离子电池生产产量占全球50%以上,2019年产量为157.2亿只,锂离子电池产能的急剧扩张也意味着在近年内将出现大量需要报废回收处理的锂离子电池,若处理不当则会造成环境的污染和资源的浪费,因此,锂离子电池的回收迫在眉睫,对于保护环境、资源可持续发展都有重要意义。Lithium-ion batteries have been widely used in various electronic products and electric vehicles and other industries. According to statistics, my country's lithium-ion battery production and output accounted for more than 50% of the world's total, and the output in 2019 was 15.72 billion. The rapid expansion of lithium-ion battery production capacity also means In recent years, there will be a large number of lithium-ion batteries that need to be scrapped and recycled. Improper handling will cause environmental pollution and waste of resources. Therefore, the recycling of lithium-ion batteries is imminent, which is important for environmental protection and sustainable development of resources. significance.
目前,废旧锂离子电池主要通过拆解、破碎、筛分后得到正极粉料和其它组分。对于正极粉料的回收主要采用无机酸浸的方法,将有价金属从固体粉末中转移至溶液,与炭黑、有机粘结剂等有效分离,但同时电解液中的氟或后续除杂时引进的氟均会进入溶液中,对湿法回收镍钴锰过程造成影响,主要包括:1)对镍钴锰三元前驱体的产品质量产生影响;2)后段废水处理工序段的除氟压力较大,且目前采用的除氟工艺很难达到废水排放要求,处理成本高;3)湿法系统中的氟会对设备存在腐蚀性,缩短设备的使用寿命;4)容易导致管道堵塞。At present, used lithium-ion batteries are mainly disassembled, crushed, and screened to obtain positive electrode powder and other components. For the recovery of positive electrode powder, the method of inorganic acid leaching is mainly used to transfer the valuable metal from the solid powder to the solution and effectively separate it from carbon black and organic binders. The fluorine introduced will enter the solution, which will affect the process of wet recovery of nickel, cobalt and manganese, which mainly includes: 1) affecting the product quality of the nickel-cobalt-manganese ternary precursor; 2) fluorine removal in the subsequent wastewater treatment process section The pressure is high, and the current fluorine removal process is difficult to meet the wastewater discharge requirements, and the treatment cost is high; 3) The fluorine in the wet system will be corrosive to the equipment, shortening the service life of the equipment; 4) It is easy to cause pipeline blockage.
发明内容SUMMARY OF THE INVENTION
针对目前后段废水除氟工艺的缺点和不足之处,根据本发明的实施例提供一种镍钴锰溶液中除氟的回收方法。本发明实施例的方法在前段镍钴锰溶液中具有较好的除氟效果,同时不引入其它杂质,并且得到的含氟滤渣进行提纯处理后可以达到工业冰晶石产品要求,具有较大的经济效益。Aiming at the shortcomings and deficiencies of the current back-stage wastewater defluorination process, a method for recovering fluorine removal in a nickel-cobalt-manganese solution is provided according to an embodiment of the present invention. The method of the embodiment of the present invention has a good fluorine removal effect in the nickel-cobalt-manganese solution in the first stage, without introducing other impurities, and the obtained fluorine-containing filter residue can meet the requirements of industrial cryolite products after being purified, and has a relatively large economy. benefit.
有鉴于此,本发明实施例提供一种镍钴锰溶液中除氟的回收方法,包括以下步骤:In view of this, the embodiment of the present invention provides a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
将电池粉料进行酸浸、除杂后,得到含氟的镍钴锰溶液;After acid leaching and impurity removal of the battery powder, a fluorine-containing nickel-cobalt-manganese solution is obtained;
将所得含氟的镍钴锰溶液与除氟剂混合,得到混合浆料;Mixing the obtained fluorine-containing nickel-cobalt-manganese solution with a defluorination agent to obtain a mixed slurry;
将所得混合浆料调节pH至2-5,经过滤得到一段除氟滤液和一段含氟滤渣;The pH of the obtained mixed slurry is adjusted to 2-5, and a section of defluorinated filtrate and a section of fluorine-containing filter residue are obtained by filtration;
将一段含氟滤渣洗涤后加入碱液中,加热搅拌,经过滤得到含氟滤液和含镍钴锰滤渣。A section of the fluorine-containing filter residue is washed and then added to the alkaline solution, heated and stirred, and filtered to obtain a fluorine-containing filtrate and a nickel-cobalt-manganese-containing filter residue.
根据本发明实施例,所述电池粉料可通过将电池废料粉碎后得到。根据本发明实施例,所述电池废料可选自废旧锂电池拆解得到的废弃正极材料或锂电池制造过程中产生的废弃正 极材料。在一些实施例中,所述除杂包括采用本领域已知的工艺除去铁、铝等杂质。According to an embodiment of the present invention, the battery powder can be obtained by pulverizing battery waste. According to an embodiment of the present invention, the battery waste can be selected from waste positive electrode materials obtained by dismantling waste lithium batteries or waste positive electrode materials generated during the manufacturing process of lithium batteries. In some embodiments, the removal of impurities includes removal of impurities such as iron, aluminum, and the like using processes known in the art.
在一些实施例中,所得含氟的镍钴锰溶液中含有高浓度的氟。具体地,根据某些实施例,所得含氟的镍钴锰溶液中,镍钴锰浓度为40-100g/L,氟浓度为1-5g/L。根据本发明实施例,所述除氟剂为固体除氟剂。在一些实施例中,所述除氟剂中包含但不限于氧化铝、氢氧化铝和可溶性铝盐中的一种或几种。其中,所述可溶性铝盐包括单盐,例如硫酸铝,以及复盐,例如钠明矾。可选地,所述除氟剂可以选用主要成分为氧化铝、氢氧化铝和可溶性铝盐中的一种或几种的天然价廉材料,例如铝矾石。在本发明一些实施中,所述镍钴锰溶液的体积与所述除氟剂的质量比为50-300:1;优选为100-200:1。本发明申请人通过前期研究发现并验证,可根据镍钴锰溶液中氟的含量,计算加入除氟剂的用量,从而可以在确保除氟效果良好的前提下,使用最少且合适用量的除氟剂与氟反应生成且优先生成氟铝酸钠,避免其他杂质化合物的产生。In some embodiments, the resulting fluorine-containing nickel-cobalt-manganese solution contains a high concentration of fluorine. Specifically, according to certain embodiments, in the obtained fluorine-containing nickel-cobalt-manganese solution, the nickel-cobalt-manganese concentration is 40-100 g/L, and the fluorine concentration is 1-5 g/L. According to an embodiment of the present invention, the fluorine removing agent is a solid fluorine removing agent. In some embodiments, the fluorine removing agent includes, but is not limited to, one or more of aluminum oxide, aluminum hydroxide and soluble aluminum salts. Among them, the soluble aluminum salts include single salts, such as aluminum sulfate, and double salts, such as sodium alum. Optionally, the fluorine removing agent can be selected from natural and inexpensive materials whose main components are one or more of alumina, aluminum hydroxide and soluble aluminum salts, such as bauxite. In some implementations of the present invention, the mass ratio of the volume of the nickel-cobalt-manganese solution to the defluorination agent is 50-300:1; preferably, 100-200:1. The applicant of the present invention has found and verified through previous research that the amount of fluorine removal agent added can be calculated according to the fluorine content in the nickel-cobalt-manganese solution, so that the minimum and appropriate amount of fluorine removal can be used on the premise of ensuring good fluorine removal effect. The agent reacts with fluorine to generate and preferentially generates sodium fluoroaluminate to avoid the generation of other impurity compounds.
根据本发明实施例,将所得混合浆料用稀酸调节pH至2-5。所述稀酸包括但不限于稀硫酸、稀盐酸和稀硝酸中的至少一种。优选地,所述稀酸为稀硫酸。具体地,所述稀酸浓度为5-50%。According to the embodiment of the present invention, the pH of the obtained mixed slurry is adjusted to 2-5 with dilute acid. The dilute acid includes, but is not limited to, at least one of dilute sulfuric acid, dilute hydrochloric acid, and dilute nitric acid. Preferably, the dilute acid is dilute sulfuric acid. Specifically, the dilute acid concentration is 5-50%.
在本发明的一些实施例中,通过调节所得混合浆料的pH值降低以利于除氟剂中的铝转化成铝离子,与混合浆料中的氟反应生成氟铝酸钠。在本发明的实施例中,控制所得混合浆料调节pH至2-5的总反应时间为0.5-2h。通过控制调节pH值的速度与反应时间有助于形成高纯度的氟铝酸钠沉淀,避免新的废渣的堆积。In some embodiments of the present invention, the pH value of the obtained mixed slurry is adjusted to reduce to facilitate the conversion of aluminum in the fluorine scavenger into aluminum ions, which react with fluorine in the mixed slurry to generate sodium fluoroaluminate. In the embodiment of the present invention, the total reaction time of controlling the obtained mixed slurry to adjust pH to 2-5 is 0.5-2h. By controlling the speed and reaction time of adjusting pH value, it helps to form high-purity sodium fluoroaluminate precipitate and avoid the accumulation of new waste residue.
根据本发明的实施例,经过滤得到的一段含氟滤渣的主要成分为氟铝酸钠。According to the embodiment of the present invention, the main component of a section of fluorine-containing filter residue obtained by filtration is sodium fluoroaluminate.
根据本发明的实施例,得到一段除氟滤液和一段含氟滤渣之后,还包括:将所得一段除氟滤液与除氟剂混合,调节pH至2-5,经过滤得到二段除氟滤液和二段含氟滤渣。在一些实施例中,所得二段除氟滤液的含氟量降至20mg/L或以下,二段含氟滤渣含少量镍钴锰,二段含氟滤渣返回至酸浸工序。在本发明实施例的启示下,本领域技术人员可以显而易见地根据实际生产需要,在得到N段除氟滤液和N段含氟滤渣之后,将N段除氟滤液进一步与除氟剂混合,调节pH至2-5,经过滤得到N+1段除氟滤液和N+1含氟滤渣。其中,二段含氟滤渣,……,N段含氟滤渣和N+1含氟滤渣返回至酸浸工序。在本文中,N大于1。According to an embodiment of the present invention, after obtaining a section of defluorinated filtrate and a section of fluorine-containing filter residue, the method further comprises: mixing the obtained section of defluorinated filtrate with a defluorinating agent, adjusting the pH to 2-5, and filtering to obtain a second section of defluorinated filtrate and The second-stage fluorine-containing filter residue. In some embodiments, the fluorine content of the obtained second-stage defluorination filtrate is reduced to 20 mg/L or less, the second-stage fluorine-containing filter residue contains a small amount of nickel, cobalt, and manganese, and the second-stage fluorine-containing filter residue is returned to the acid leaching process. Under the inspiration of the embodiments of the present invention, those skilled in the art can obviously according to the actual production needs, after obtaining the N-stage defluorination filtrate and the N-stage fluorine-containing filter residue, the N-stage defluorination filtrate is further mixed with a defluorinating agent, adjusting The pH reaches 2-5, and N+1 stage defluorination filtrate and N+1 fluorine-containing filter residue are obtained by filtration. Among them, the second-stage fluorine-containing filter residue, ..., the N-stage fluorine-containing filter residue and the N+1 fluorine-containing filter residue are returned to the acid leaching process. In this paper, N is greater than 1.
根据本发明的实施例,得到二段除氟滤液和二段含氟滤渣之后,还包括:将二段除氟滤液调节pH至5-6.5,进行后续萃取,得到镍钴锰产品。在本发明实施例的启示下,本领域技术人员可以显而易见地根据实际生产需要,在得到N段除氟滤液和N段含氟滤渣之后,将N段除氟滤液进行后续萃取,得到镍钴锰产品。在本文中,N大于1。According to the embodiment of the present invention, after obtaining the second-stage defluorination filtrate and the second-stage fluorine-containing filter residue, the method further includes: adjusting the pH of the second-stage defluorination filtrate to 5-6.5, and performing subsequent extraction to obtain nickel-cobalt-manganese products. Under the inspiration of the embodiments of the present invention, those skilled in the art can obviously according to the actual production needs, after obtaining the N-stage defluorination filtrate and the N-stage fluorine-containing filter residue, the N-stage defluorination filtrate is subjected to subsequent extraction to obtain Nickel Cobalt Manganese product. In this paper, N is greater than 1.
在本发明实施例的启示下,在不导致一段含氟滤渣复溶的前提下,本领域技术人员还可以容易想到,将所得一段除氟滤液与除氟剂混合,先调节pH至2-5,再调节pH至5-6.5,经 过滤得到二段除氟滤液和二段含氟滤渣,此时,二段除氟滤液不需调节pH即可进行后续萃取,得到镍钴锰产品。Under the inspiration of the embodiments of the present invention, on the premise that a section of fluorine-containing filter residue is not reconstituted, those skilled in the art can also easily imagine that the obtained section of fluorine-removing filtrate is mixed with a fluorine-removing agent, and the pH is first adjusted to 2-5 , and then adjust the pH to 5-6.5, and obtain the second-stage defluorination filtrate and the second-stage fluorine-containing filter residue after filtration. At this time, the second-stage defluorination filtrate can be subjected to subsequent extraction without adjusting the pH to obtain nickel-cobalt-manganese products.
根据本发明实施例,用中和剂调节pH至5-6.5。所述中和剂包括但不限于碳酸钠、碳酸钾、氢氧化钠、氢氧化钾中的一种或几种。优选地,所述中和剂为10-30%浓度的中和剂溶液。According to an embodiment of the present invention, the pH is adjusted to 5-6.5 with a neutralizing agent. The neutralizing agent includes but is not limited to one or more of sodium carbonate, potassium carbonate, sodium hydroxide, and potassium hydroxide. Preferably, the neutralizer is a 10-30% concentration neutralizer solution.
根据本发明的实施例,所述碱液包括但不限于氢氧化钠、氢氧化钾溶液。优选地,所述碱液的浓度为5-30%。所述碱液中的碱性化合物的摩尔量与一段含氟滤渣中的氟铝酸钠的理论摩尔量的比值为0.9-1.5;优选地,该比值为1.0-1.4;更优选地,该比值为1.1-1.3。According to an embodiment of the present invention, the alkali solution includes but is not limited to sodium hydroxide and potassium hydroxide solution. Preferably, the concentration of the lye solution is 5-30%. The ratio of the molar amount of the alkaline compound in the alkaline solution to the theoretical molar amount of sodium fluoroaluminate in the first-stage fluorine-containing filter residue is 0.9-1.5; preferably, the ratio is 1.0-1.4; more preferably, the ratio is is 1.1-1.3.
根据本发明的实施例,将一段含氟滤渣洗涤后加入碱液中,加热至50-80℃,搅拌0.5-2h,经过滤得到含氟滤液和含镍钴锰滤渣。According to the embodiment of the present invention, a section of fluorine-containing filter residue is washed and then added to alkali solution, heated to 50-80° C., stirred for 0.5-2 h, and filtered to obtain fluorine-containing filtrate and nickel-cobalt-manganese-containing filter residue.
根据本发明的实施例,得到含氟滤液和含镍钴锰滤渣之后,还包括:According to an embodiment of the present invention, after obtaining the fluorine-containing filtrate and the nickel-cobalt-manganese-containing filter residue, it also includes:
所得含镍钴锰滤渣返回至酸浸工序;The obtained nickel-cobalt-manganese-containing filter residue is returned to the acid leaching process;
将所得含氟滤液通入二氧化碳反应,过滤、洗涤、烘干后得到冰晶石产品。The obtained fluorine-containing filtrate is passed into carbon dioxide to react, and the cryolite product is obtained after filtering, washing and drying.
优选地,通入二氧化碳反应2-8h。Preferably, carbon dioxide is introduced into the reaction for 2-8h.
本发明实施例的方法具有如下优点及有益效果:The method of the embodiment of the present invention has the following advantages and beneficial effects:
本发明实施例的方法在前段镍钴锰溶液中具有较好的除氟效果,且含氟滤渣中镍钴锰损失量较少;同时本发明实施例的工艺不引入其它杂质,并且得到的含氟滤渣进行提纯处理后可以达到工业冰晶石产品要求,提高了回收原料的附加值,具有较大的经济效益。The method of the embodiment of the present invention has a good defluorination effect in the nickel-cobalt-manganese solution in the first stage, and the loss of nickel-cobalt-manganese in the fluorine-containing filter residue is small; at the same time, the process of the embodiment of the present invention does not introduce other impurities, and the obtained fluorine-containing filter residue After the fluorine filter residue is purified, it can meet the requirements of industrial cryolite products, improve the added value of recycled raw materials, and have greater economic benefits.
图1为本发明一实施例的镍钴锰溶液中除氟的方法流程图。1 is a flow chart of a method for removing fluorine in a nickel-cobalt-manganese solution according to an embodiment of the present invention.
下面结合实施例对本发明作进一步详细的描述,但本发明的实施方式不限于此。The present invention will be described in further detail below with reference to the examples, but the embodiments of the present invention are not limited thereto.
参见图1,具体地,一种镍钴锰溶液中除氟的回收方法,包括以下步骤:Referring to Fig. 1, specifically, a kind of recovery method of removing fluorine in nickel-cobalt-manganese solution, comprises the following steps:
(1)将电池废料粉碎过筛,得到电池粉料;(1) Pulverize and sieve the battery waste to obtain battery powder;
(2)将电池粉料进行酸浸、除杂后,得到含氟的镍钴锰溶液;(2) after the battery powder is subjected to acid leaching and impurity removal, a fluorine-containing nickel-cobalt-manganese solution is obtained;
(3)按体积与质量比为50-300:1,将所得含氟的镍钴锰溶液与除氟剂混合,得到混合浆料;(3) by volume to mass ratio of 50-300:1, the obtained fluorine-containing nickel-cobalt-manganese solution is mixed with a defluorinating agent to obtain a mixed slurry;
(4)将所得混合浆料用5-50%稀酸调节pH至2-5,反应时间控制在0.5-2h,经过滤得到一段除氟滤液和一段含氟滤渣;(4) adjusting the pH of the obtained mixed slurry to 2-5 with 5-50% dilute acid, the reaction time is controlled at 0.5-2h, and a section of defluorinated filtrate and a section of fluorine-containing filter residue are obtained by filtration;
(5)将所得一段除氟滤液与除氟剂混合,重复步骤(4),得到二段除氟滤液和二段含氟滤渣;二段含氟滤渣返回至酸浸工序;(5) the gained one-stage defluorination filtrate is mixed with a defluorinating agent, and step (4) is repeated to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue; the second-stage fluorine-containing filter residue is returned to the acid leaching process;
(6)将二段除氟滤液用10-30%中和剂调节pH至5-6.5,进行后续萃取,得到镍钴锰产品;(6) adjusting the pH of the second-stage defluorination filtrate to 5-6.5 with a 10-30% neutralizer, and carrying out subsequent extraction to obtain a nickel-cobalt-manganese product;
(7)将一段含氟滤渣洗涤后加入碱液中,加热至50-80℃,搅拌0.5-2h,经过滤得到含氟滤液和含镍钴锰滤渣;所得含镍钴锰滤渣返回至酸浸工序;(7) After washing a section of fluorine-containing filter residue, add it to the alkaline solution, heat to 50-80 ° C, stir for 0.5-2 h, and obtain fluorine-containing filtrate and nickel-cobalt-manganese-containing filter residue by filtration; The obtained nickel-cobalt-manganese-containing filter residue is returned to acid leaching process;
(8)将所得含氟滤液通入二氧化碳反应2-8h,过滤、洗涤、烘干后得到冰晶石产品。(8) Passing the obtained fluorine-containing filtrate into carbon dioxide to react for 2-8h, filtering, washing and drying to obtain a cryolite product.
下面结合实施例对本发明作进一步详细的描述,以便于所属技术领域的人员对本发明的理解。有必要在此特别指出的是,实施例只是用于对本发明作进一步说明,不能理解为对本发明保护范围的限制,所属领域技术熟练人员,根据上述发明内容对本发明作出的非本质性的改进和调整,应仍属于本发明的保护范围。同时下述所提及的原料未详细说明的,均为市售产品;以下实施例中金属离子的浓度均为通过原子吸收光谱法(AAS)或电感耦合等离子体原子发射光谱法(ICP-AES)测定;氟离子浓度通过氟电极电位法测定;未详细提及的工艺步骤或制备方法均为本领域技术人员所知晓的工艺步骤或制备方法。The present invention will be further described in detail below with reference to the embodiments, so as to facilitate the understanding of the present invention by those skilled in the art. It is necessary to point out that the embodiments are only used to further illustrate the present invention, and should not be construed as limiting the scope of protection of the present invention. Those skilled in the art make non-essential improvements and The adjustment should still belong to the protection scope of the present invention. At the same time, the raw materials mentioned below are all commercially available products; the concentrations of metal ions in the following examples are all obtained by atomic absorption spectrometry (AAS) or inductively coupled plasma atomic emission spectrometry (ICP-AES) ) determination; the fluoride ion concentration is determined by the fluorine electrode potentiometric method; the process steps or preparation methods not mentioned in detail are the process steps or preparation methods known to those skilled in the art.
实施例1Example 1
本实施例提出一种镍钴锰溶液中除氟的回收方法,包括以下步骤:The present embodiment proposes a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
(1)将三元废旧电池废料粉碎过筛,得到三元电池粉料;(1) Pulverize and sieve the waste ternary battery waste to obtain ternary battery powder;
(2)将三元电池粉料进行酸浸、除杂后,得到含氟量为4.03g/L的镍钴锰溶液;(2) After the ternary battery powder is subjected to acid leaching and impurity removal, a nickel-cobalt-manganese solution with a fluorine content of 4.03 g/L is obtained;
(3)将1L含氟镍钴锰溶液与10g铝矾石混合后进行搅拌,得到混合浆料;(3) 1L fluorine-containing nickel-cobalt-manganese solution is mixed with 10g bauxite and stirred to obtain mixed slurry;
(4)将步骤(3)得到的混合浆料使用30%稀硫酸调节pH值至4左右,调节pH在1h内完成,过滤得到一段除氟滤液和一段含氟滤渣,其中一段除氟滤液含氟34.6mg/L,一段含氟滤渣中(Ni+Co+Mn)为0.029%(按重量百分比计);(4) using 30% dilute sulfuric acid to adjust the pH value of the mixed slurry obtained in step (3) to about 4, adjusting the pH within 1 h, and filtering to obtain a section of defluorination filtrate and a section of fluorine-containing filter residue, wherein a section of defluorination filtrate contains Fluorine is 34.6 mg/L, and (Ni+Co+Mn) in a fluorine-containing filter residue is 0.029% (by weight);
(5)将步骤(4)得到的一段除氟滤液再添加10g铝矾石反应,重复步骤(4),过滤得到二段除氟滤液和二段含氟滤渣,其中二段除氟滤液含氟20.7mg/L,二段含氟滤渣中(Ni+Co+Mn)为0.905%,二段含氟滤渣返回酸浸;二段除氟滤液使用15%碳酸钠溶液调节pH至5.7左右,进行后续萃取,得到镍钴锰产品;(5) adding 10g of bauxite to the one-stage defluorination filtrate obtained in step (4), repeating step (4), and filtering to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue, wherein the second-stage defluorination filtrate contains fluorine 20.7mg/L, the (Ni+Co+Mn) in the second-stage fluorine-containing filter residue is 0.905%, the second-stage fluorine-containing filter residue is returned to acid leaching; the second-stage defluorination filtrate is adjusted to about 5.7 with 15% sodium carbonate solution, and the subsequent Extraction to obtain nickel-cobalt-manganese products;
(6)将步骤(4)得到的一段含氟滤渣中加入氟铝酸钠理论摩尔量1.1倍的30%氢氧化钠溶液,80℃下水浴加热搅拌1h,过滤得到含氟滤液和含镍钴锰滤渣,含镍钴锰滤渣返回酸浸;(6) Add a 30% sodium hydroxide solution with 1.1 times the theoretical molar weight of sodium fluoroaluminate to the fluorine-containing filter residue obtained in step (4), heat and stir in a water bath at 80° C. for 1 h, and filter to obtain fluorine-containing filtrate and nickel-cobalt-containing filtrate. Manganese filter residue, nickel-cobalt-manganese filter residue is returned to acid leaching;
(7)将步骤(6)得到的含氟滤液通入二氧化碳4h,过滤、洗涤、烘干后得到冰晶石产品,纯度为98.2%。(7) Passing the fluorine-containing filtrate obtained in step (6) into carbon dioxide for 4 h, filtering, washing and drying to obtain a cryolite product with a purity of 98.2%.
实施例2Example 2
本实施例提出一种镍钴锰溶液中除氟的回收方法,包括以下步骤:The present embodiment proposes a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
(1)将钴酸锂电池废料粉碎过筛,得到钴酸锂电池粉料;(1) pulverizing and sieving the waste of lithium cobalt oxide battery to obtain lithium cobalt oxide battery powder;
(2)将钴酸锂电池粉料进行酸浸、除杂后,得到含氟量为4.54g/L的镍钴锰溶液;(2) after the lithium cobalt oxide battery powder is subjected to acid leaching and impurity removal, a nickel-cobalt-manganese solution with a fluorine content of 4.54 g/L is obtained;
(3)将1L含氟镍钴锰溶液与5g氢氧化铝混合后进行搅拌,得到混合浆料;(3) 1L of fluorine-containing nickel-cobalt-manganese solution is mixed with 5g of aluminum hydroxide and stirred to obtain a mixed slurry;
(4)将步骤(3)得到的混合浆料使用20%稀硫酸调节pH值至3左右,调节pH在1h内完成,过滤得到一段除氟滤液和一段含氟滤渣,其中一段除氟滤液含氟37.4mg/L,一段含氟滤渣中(Ni+Co+Mn)为0.033%(按重量百分比计);(4) using 20% dilute sulfuric acid to adjust the pH value of the mixed slurry obtained in step (3) to about 3, adjusting the pH within 1 hour, and filtering to obtain a section of defluorination filtrate and a section of fluorine-containing filter residue, wherein a section of defluorination filtrate contains Fluorine is 37.4mg/L, and (Ni+Co+Mn) in the first-stage fluorine-containing filter residue is 0.033% (by weight);
(5)将步骤(4)得到的一段除氟滤液再添加5g氢氧化铝反应,重复步骤(4),过滤得到二段除氟滤液和二段含氟滤渣,其中二段除氟滤液含氟20.3mg/L,二段含氟滤渣中(Ni+Co+Mn)为0.967%,二段含氟滤渣返回酸浸;二段除氟滤液使用15%碳酸钠溶液调节pH至6.1左右,进行后续萃取,得到镍钴锰产品;(5) adding 5g of aluminum hydroxide to the first-stage defluorination filtrate obtained in step (4), repeating step (4), and filtering to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue, wherein the second-stage defluorination filtrate contains fluorine 20.3mg/L, the (Ni+Co+Mn) in the second-stage fluorine-containing filter residue is 0.967%, the second-stage fluorine-containing filter residue is returned to acid leaching; the second-stage defluorination filtrate is adjusted to about 6.1 with 15% sodium carbonate solution, and the subsequent Extraction to obtain nickel-cobalt-manganese products;
(6)将步骤(4)得到的一段含氟滤渣中加入氟铝酸钠理论摩尔量1.2倍的25%氢氧化钠溶液,75℃下水浴加热搅拌2h,过滤得到含氟滤液和含镍钴锰滤渣,含镍钴锰滤渣返回酸浸;(6) Add a 25% sodium hydroxide solution with 1.2 times the theoretical molar weight of sodium fluoroaluminate to the fluorine-containing filter residue obtained in step (4), heat and stir in a water bath at 75° C. for 2 hours, and filter to obtain fluorine-containing filtrate and nickel-cobalt-containing filtrate. Manganese filter residue, nickel-cobalt-manganese filter residue is returned to acid leaching;
(7)将步骤(6)得到的含氟滤液通入二氧化碳6h,过滤、洗涤、烘干后得到冰晶石产品,纯度为98.1%。(7) Passing the fluorine-containing filtrate obtained in step (6) into carbon dioxide for 6 h, filtering, washing and drying to obtain a cryolite product with a purity of 98.1%.
实施例3Example 3
本实施例提出一种镍钴锰溶液中除氟的回收方法,包括以下步骤:The present embodiment proposes a recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:
(1)将极片废料粉碎过筛,得到极片粉料;(1) Pulverize and sieve the pole piece waste to obtain pole piece powder;
(2)将极片粉料进行酸浸、除杂后,得到含氟量为2.65g/L的镍钴锰溶液;(2) after the pole piece powder is subjected to acid leaching and impurity removal, obtaining a nickel-cobalt-manganese solution with a fluorine content of 2.65 g/L;
(3)将1L含氟镍钴锰溶液与10g钠明矾混合后进行搅拌,得到混合浆料;(3) 1L of fluorine-containing nickel-cobalt-manganese solution is mixed with 10g of sodium alum and stirred to obtain mixed slurry;
(4)将步骤(3)得到的混合浆料使用10%稀硫酸调节pH值至2左右,调节pH在1h内完成,过滤得到一段除氟滤液和一段含氟滤渣,其中一段除氟滤液含氟52.6mg/L,一段含氟滤渣中(Ni+Co+Mn)为0.041%(按重量百分比计);(4) using 10% dilute sulfuric acid to adjust the pH value of the mixed slurry obtained in step (3) to about 2, adjusting the pH within 1 h, and filtering to obtain a section of defluorination filtrate and a section of fluorine-containing filter residue, wherein a section of defluorination filtrate contains Fluorine is 52.6 mg/L, and (Ni+Co+Mn) in the first-stage fluorine-containing filter residue is 0.041% (by weight);
(5)将步骤(4)得到的一段除氟滤液再添加10g钠明矾反应,重复步骤(4),过滤得到二段除氟滤液和二段含氟滤渣,其中二段除氟滤液含氟19.6mg/L,二段含氟滤渣中(Ni+Co+Mn)为0.915%,二段含氟滤渣返回酸浸;二段除氟滤液使用10%碳酸钠溶液调节pH至5.5左右,进行后续萃取,得到镍钴锰产品;(5) adding 10g of sodium alum to the first-stage defluorination filtrate obtained in step (4), repeating step (4), and filtering to obtain a second-stage defluorination filtrate and a second-stage fluorine-containing filter residue, wherein the second-stage defluorination filtrate contains 19.6% fluorine mg/L, the (Ni+Co+Mn) in the second-stage fluorine-containing filter residue is 0.915%, the second-stage fluorine-containing filter residue is returned to acid leaching; the second-stage defluorination filtrate is adjusted to pH 5.5 with 10% sodium carbonate solution, and the subsequent extraction is carried out , to obtain nickel-cobalt-manganese products;
(6)将步骤(4)得到的一段含氟滤渣中加入氟铝酸钠理论摩尔量1.3倍的25%氢氧化钠溶液,70℃下水浴加热搅拌3h,过滤得到含氟滤液和含镍钴锰滤渣,含镍钴锰滤渣返回酸浸;(6) Add a 25% sodium hydroxide solution with 1.3 times the theoretical molar weight of sodium fluoroaluminate to the fluorine-containing filter residue obtained in step (4), heat and stir in a water bath at 70° C. for 3 hours, and filter to obtain fluorine-containing filtrate and nickel-cobalt-containing filtrate. Manganese filter residue, nickel-cobalt-manganese filter residue is returned to acid leaching;
(7)将步骤(6)得到的含氟滤液通入二氧化碳8h,过滤、洗涤、烘干后得到冰晶石产 品,纯度为97.8%。(7) The fluorine-containing filtrate obtained in step (6) was passed into carbon dioxide for 8h, filtered, washed and dried to obtain a cryolite product with a purity of 97.8%.
相比于相关技术,采用本发明实施例的方法在前段对镍钴锰溶液进行除氟,可将镍钴锰溶液中的含氟量降至20mg/L或以下,且含氟滤渣中镍钴锰含量<1%,损失量较少。本发明实施例在对镍钴锰溶液除氟的反应中,反应条件宽泛,所用的试剂原料价廉易,除氟效果好,同时对除氟后的滤渣进行了回收提纯制成氟铝酸钠,提高了回收原料的附加值,并对除氟渣夹带的有价金属进行了有效回收,根据本发明实施例工艺系统中没有废水废渣的产生。本发明实施例的工艺简单,未引入或产生新的其它杂质,对于含氟滤渣处理提纯后得到的冰晶石纯度可达98%以上,达到工业冰晶石产品要求,具有可观的经济效益。Compared with the related art, the nickel-cobalt-manganese solution is defluorinated by the method of the embodiment of the present invention, and the fluorine content in the nickel-cobalt-manganese solution can be reduced to 20 mg/L or less, and the nickel-cobalt in the fluorine-containing filter residue can be reduced. Manganese content <1%, less loss. In the reaction of removing fluorine from nickel-cobalt-manganese solution in the embodiment of the present invention, the reaction conditions are wide, the reagents and raw materials used are cheap and easy, and the effect of removing fluorine is good. , the added value of the recovered raw materials is improved, and the valuable metals entrained in the defluorination residue are effectively recovered. According to the embodiment of the present invention, there is no waste water and waste residue in the process system. The process of the embodiment of the present invention is simple, no other impurities are introduced or generated, and the purity of cryolite obtained after treatment and purification of the fluorine-containing filter residue can reach more than 98%, which meets the requirements of industrial cryolite products and has considerable economic benefits.
上述实施例为本发明较佳的实施方式,但本发明的实施方式并不受上述实施例的限制,其它的任何未背离本发明的精神实质与原理下所作的改变、修饰、替代、组合、简化,均应为等效的置换方式,都包含在本发明的保护范围之内。The above-mentioned embodiments are preferred embodiments of the present invention, but the embodiments of the present invention are not limited by the above-mentioned embodiments, and any other changes, modifications, substitutions, combinations, The simplification should be equivalent replacement manners, which are all included in the protection scope of the present invention.
Claims (10)
- 一种镍钴锰溶液中除氟的回收方法,其特征在于,包括以下步骤:A recovery method for removing fluorine in a nickel-cobalt-manganese solution, comprising the following steps:将电池粉料进行酸浸、除杂后,得到含氟的镍钴锰溶液;After acid leaching and impurity removal of the battery powder, a fluorine-containing nickel-cobalt-manganese solution is obtained;将所得含氟的镍钴锰溶液与除氟剂混合,得到混合浆料;Mixing the obtained fluorine-containing nickel-cobalt-manganese solution with a defluorination agent to obtain a mixed slurry;将所得混合浆料调节pH至2-5,经过滤得到一段除氟滤液和一段含氟滤渣;The pH of the obtained mixed slurry is adjusted to 2-5, and a section of defluorinated filtrate and a section of fluorine-containing filter residue are obtained by filtration;将一段含氟滤渣洗涤后加入碱液中,加热搅拌,经过滤得到含氟滤液和含镍钴锰滤渣。A section of the fluorine-containing filter residue is washed and then added to the alkaline solution, heated and stirred, and filtered to obtain a fluorine-containing filtrate and a nickel-cobalt-manganese-containing filter residue.
- 根据权利要求1所述的回收方法,其特征在于,所述除氟剂为固体除氟剂。The recovery method according to claim 1, wherein the defluorinating agent is a solid defluorinating agent.
- 根据权利要求1所述的回收方法,其特征在于,所述除氟剂中包含氧化铝、氢氧化铝和可溶性铝盐中的一种或几种。The recovery method according to claim 1, wherein the fluorine removing agent comprises one or more of alumina, aluminum hydroxide and soluble aluminum salts.
- 根据权利要求1所述的回收方法,其特征在于,所述镍钴锰溶液的体积与所述除氟剂的质量比为50-300:1。The recovery method according to claim 1, wherein the mass ratio of the volume of the nickel-cobalt-manganese solution to the defluorinating agent is 50-300:1.
- 根据权利要求1所述的回收方法,其特征在于,将所得混合浆料用稀酸调节pH至2-5。The recovery method according to claim 1, wherein the obtained mixed slurry is adjusted to pH 2-5 with dilute acid.
- 根据权利要求1所述的回收方法,其特征在于,得到一段除氟滤液和一段含氟滤渣之后,还包括:将所得一段除氟滤液与除氟剂混合,调节pH至2-5,经过滤得到二段除氟滤液和二段含氟滤渣。The recovery method according to claim 1 is characterized in that, after obtaining a section of defluorinated filtrate and a section of fluorine-containing filter residue, the method further comprises: mixing the obtained section of defluorinated filtrate with a defluorinating agent, adjusting pH to 2-5, and filtering The second-stage defluorination filtrate and the second-stage fluorine-containing filter residue are obtained.
- 根据权利要求6所述的回收方法,其特征在于,得到二段除氟滤液和二段含氟滤渣之后,还包括:将二段除氟滤液调节pH至5-6.5进行萃取,得到镍钴锰产品。The recovery method according to claim 6, characterized in that, after obtaining the second-stage defluorination filtrate and the second-stage fluorine-containing filter residue, further comprising: adjusting the pH of the second-stage defluorination filtrate to 5-6.5 for extraction to obtain nickel cobalt manganese product.
- 根据权利要求6所述的回收方法,其特征在于,在得到N段除氟滤液和N段含氟滤渣之后,还包括:将N段除氟滤液与除氟剂混合,调节pH至2-5,经过滤得到N+1段除氟滤液和N+1含氟滤渣,其中N大于1。The recovery method according to claim 6, characterized in that, after obtaining the N-stage defluorination filtrate and the N-stage fluorine-containing filter residue, the method further comprises: mixing the N-stage defluorination filtrate with a defluorinating agent, and adjusting the pH to 2-5 , and N+1 stage fluoride removal filtrate and N+1 fluorine-containing filter residue are obtained by filtration, wherein N is greater than 1.
- 根据权利要求1所述的回收方法,其特征在于,所述碱液中的碱性化合物的摩尔量与一段含氟滤渣中的氟铝酸钠的理论摩尔量的比值为0.9-1.5。The recovery method according to claim 1, wherein the ratio of the molar amount of the alkaline compound in the alkaline solution to the theoretical molar amount of the sodium fluoroaluminate in the first-stage fluorine-containing filter residue is 0.9-1.5.
- 根据权利要求1所述的回收方法,其特征在于,得到含氟滤液和含镍钴锰滤渣之后,还包括:recovery method according to claim 1, is characterized in that, after obtaining fluorine-containing filtrate and nickel-cobalt-manganese-containing filter residue, also comprises:所得含镍钴锰滤渣返回至酸浸工序;The obtained nickel-cobalt-manganese-containing filter residue is returned to the acid leaching process;将所得含氟滤液通入二氧化碳反应,过滤、洗涤、烘干后得到冰晶石产品。The obtained fluorine-containing filtrate is passed into carbon dioxide to react, and the cryolite product is obtained after filtering, washing and drying.
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