CN116002725A - Method for efficiently separating lithium element in waste lithium ion battery anode material - Google Patents

Method for efficiently separating lithium element in waste lithium ion battery anode material Download PDF

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CN116002725A
CN116002725A CN202211504773.4A CN202211504773A CN116002725A CN 116002725 A CN116002725 A CN 116002725A CN 202211504773 A CN202211504773 A CN 202211504773A CN 116002725 A CN116002725 A CN 116002725A
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lithium
ion battery
lithium ion
tower
elements
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杨伟
李登
林忠海
崔冰翔
冯耀玮
王伟
黎海洋
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Guangzhou University
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Guangzhou University
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Abstract

The invention relates to the field of solid waste recycling, in particular to a method for efficiently separating lithium elements in a waste lithium ion battery positive electrode material. The recovery process is simple, high-purity lithium elements are efficiently separated, no pollutant is discharged, and efficient closed-loop green recovery of lithium elements is realized. The lithium residue in the metal oxide obtained after the lithium element is separated is less, and convenience is brought to the subsequent recycling of metals or metal elements such as nickel, cobalt, manganese, iron and the like.

Description

Method for efficiently separating lithium element in waste lithium ion battery anode material
Technical Field
The invention relates to the field of solid waste recycling, in particular to a method for efficiently separating lithium elements in a positive electrode material of a waste lithium ion battery.
Background
As atmospheric environmental pollution worsens, new energy automobile industry is promoted in various countries in the world, global electric automobiles (including pure electric and plug-in hybrid electric automobiles) are exponentially increased, and estimated by international energy institutions, the cumulative sales of the global electric automobiles reaches 2150 ten thousand by 2030. With the rapid development of electric automobiles, the demand of lithium ion batteries is also increasing, so that a large number of waste lithium ion batteries are also generated. Waste lithium ion batteries contain many valuable metals such as lithium (Li), cobalt (Co), nickel (Ni), manganese (Mn), iron (Fe), copper (Cu), aluminum (Al), and the like. Compared with mineral resources, the waste lithium ion battery has higher metal resource content, and if the metal elements in the waste lithium ion battery can be efficiently recovered, the consumption of the mineral resources can be reduced, and on the other hand, the waste lithium ion battery is directly discarded under the condition of no proper treatment, and the metal substances contained in the waste lithium ion battery pollute soil and underground water. The waste lithium ion battery material is efficiently recycled, so that the pollution to the natural environment and the harm to the human health can be avoided, valuable metal resources can be reused, and the sustainable development is promoted.
At present, 35% of the global extracted lithium elements are mainly applied to lithium ion batteries, and the dependence of China on foreign lithium resources is extremely high, so that the lithium elements need to be efficiently recovered. At present, research on recycling of lithium elements in waste lithium ion batteries has been advanced to a certain extent, and reported methods of fractional precipitation after acid leaching or water dissolution after carbothermic reduction are adopted. The method of fractional precipitation after acid leaching can generate a lot of waste water, so that the method is difficult to popularize in the actual engineering process. After carbothermal reduction in the positive electrode material of the lithium ion battery, a mixture of lithium carbonate and metal oxide is produced, and researchers separate the mixture of lithium carbonate and metal oxide by using the dissolution of lithium carbonate in water. For example, chinese patent publication No. CN113921931A, CN113213544a adopts a method of directly dissolving lithium carbonate with water after carbothermic reduction. However, lithium carbonate has a low solubility in water, and a solubility of only 1.33g/100g of water at 20 ℃ (hydrodynamics 103 (2010) 12-18), which makes the separation efficiency extremely low, and brings many obstacles to mass production.
Disclosure of Invention
Aiming at the problems in the prior art, the invention aims to provide a method for efficiently separating lithium elements in the anode material of the waste lithium ion battery, which has high yield of separating lithium elements and high separation efficiency, and the obtained lithium carbonate has high purity.
The aim of the invention is realized by adopting the following technical scheme:
a method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) Mechanically and uniformly mixing the anode material of the waste lithium ion battery with coke;
(2) Carrying out carbothermic reduction treatment on the mixed powder obtained in the step (1) under an anoxic atmosphere;
(3) Mixing the mixed powder obtained after carbothermic reduction obtained in the step (2) with water, and mechanically stirring to obtain a suspension;
(4) Introducing the suspension obtained in the step (3) into a reaction absorption tower, and then gradually flowing through a tower plate, an overflow weir, a downcomer and the like until the bottom of the tower flows out;
(5) Introducing carbon dioxide from the bottom of the reaction tower in the step (4), and passing through holes of each tower plate step by step and suspension flowing through the tower plates until the carbon dioxide flows out from the top of the tower;
(6) Filtering and washing the suspension flowing out of the bottom of the step (4) for multiple times, and separating to obtain filtrate and a filter cake, wherein the filter cake is a metal or metal oxide mixture;
(7) And (3) evaporating the filtrate obtained in the step (6) to dryness to obtain the high-purity lithium carbonate.
Preferably, in the step (1), the positive electrode material of the waste lithium ion battery comprises at least one of nickel cobalt lithium manganate, lithium cobaltate, lithium manganate and lithium iron phosphate.
Preferably, in the step (1), the mass ratio of the anode material of the waste lithium ion battery to the coke is 8:2.
preferably, in the step (2), the reaction temperature of the carbothermic reduction treatment is 650 ℃, the reaction time is 3 hours, and the carbothermic reduction treatment is ground into powder after being cooled to room temperature.
Preferably, in the step (3), the mixed powder obtained after carbothermic reduction is mixed with water for mechanical stirring for 0.5-6h.
Preferably, in the step (3), the concentration of the suspension solid-phase substance obtained by mixing the mixed powder obtained after carbothermic reduction with water is 1-60wt%.
Preferably, in the step (4), the operation pressure of the reaction absorption tower is 0.1-10MPa.
Preferably, in step (4), the reaction absorber operates at a temperature of 1-65 ℃.
Preferably, in the step (4), the flow rate of the suspension is 10-180m/min.
Preferably, in the step (5), the flow rate of the carbon dioxide is 0.2-20m/s.
Preferably, in the step (6), the filtration is performed 3 to 5 times of water washing.
The beneficial effects of the invention are as follows:
1. the invention adopts waste lithium ion battery anode materials to generate lithium carbonate and metals or metal oxides such as nickel, cobalt, manganese, iron and the like through carbothermal reduction, and lithium carbonate which is difficult to dissolve in water reacts with carbon dioxide in aqueous solution to generate lithium bicarbonate which is easy to dissolve in water, and then the lithium bicarbonate is separated from metals or metal oxides such as nickel, cobalt, manganese, iron and the like which are not dissolved in water. The recovery process is simple, high-purity lithium elements are efficiently separated, no pollutant is discharged, and efficient closed-loop green recovery of lithium elements is realized.
2. The lithium residue in the metal oxide obtained after the lithium element is separated is less, and convenience is brought to the subsequent recycling of metals or metal elements such as nickel, cobalt, manganese, iron and the like.
Drawings
The invention will be further described with reference to the accompanying drawings, in which embodiments do not constitute any limitation of the invention, and other drawings can be obtained by one of ordinary skill in the art without inventive effort from the following drawings.
FIG. 1 is an X-ray diffraction chart of a mixture obtained after carbothermic reduction of a nickel-cobalt-manganese ternary cathode material of a waste lithium ion battery in example 1 of the invention;
fig. 2 is an electron spectrum analysis of a mixture obtained after carbothermic reduction of the nickel-cobalt-manganese ternary cathode material of the waste lithium ion battery in example 1 of the present invention.
Detailed Description
The technical features, objects and advantages of the present invention will be more clearly understood from the following detailed description of the technical aspects of the present invention, but should not be construed as limiting the scope of the invention.
The method comprises the steps of adopting a waste lithium ion battery anode material for carbothermic reduction treatment, uniformly mixing a mixture obtained by carbothermic treatment with water, introducing carbon dioxide to react with lithium carbonate to generate lithium bicarbonate, dissolving the lithium bicarbonate in the water easily, filtering and separating insoluble matters such as lithium bicarbonate, metal or metal oxide and the like, evaporating and crystallizing a lithium bicarbonate filtrate to obtain the lithium carbonate, wherein a filter cake is metal or metal oxide. The method is suitable for the common waste lithium ion battery anode material, carbon dioxide and water used in the reaction process can be collected and reused, no other pollutant is discharged, green closed-loop recovery is realized, the operation is simple and convenient, the requirement on equipment is low, and the method can be industrially popularized on a large scale.
The method for calculating the yield of the lithium element comprises the following steps:
Figure BDA0003967780960000031
the starting materials, reagents or apparatus used in the following examples are all available from conventional commercial sources or may be obtained by methods known in the art unless otherwise specified.
The invention will be further described with reference to the following examples.
Example 1
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) And (3) grinding the waste lithium ion battery nickel cobalt lithium manganate ternary anode material (NCM 811) and coke (the mass ratio is 8:2) uniformly, mechanically mixing for 2 hours by using a ball mill, then placing the mixture in a nitrogen atmosphere furnace for carbothermic reduction treatment, wherein the reaction temperature is 650 ℃, the heating time is 3 hours, and grinding the mixture into powder after cooling to room temperature. The resulting powder was subjected to X-ray diffraction analysis (XRD) as shown in fig. 1. According to the analysis of the X-ray diffraction peak, the powder is a mixture of lithium carbonate, nickel oxide, manganese oxide and metallic nickel. The XRD pattern does not have a diffraction peak of cobalt element, probably because the Co element compound has a low crystallinity or is in an amorphous state. The electron spectroscopy analysis of the mixture obtained after carbothermic reduction shown in fig. 2 shows that elements such as oxygen, carbon, fluorine, silicon, aluminum and the like are also present in addition to the nickel, cobalt and manganese elements.
(2) And mixing the mixed powder obtained in the previous carbothermal reduction step with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 15wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 20m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 10m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 0.1MPa and an operating temperature of 20 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing with water for 3 times, and separating to obtain filtrate and filter cake. The content of Ni, co, mn, li metal element in the filter cake obtained by inductively coupled plasma emission spectrometer (icp-oes) was tested as shown in Table 1. Evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.81%, and the yield of lithium element was 95%. The content of Ni, co, mn, al, si and other impurity metal elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 2.
TABLE 1 content of Ni, co, mn, li metallic elements in Filter cake
Species of element Ni Co Mn Li
Content of 23.52wt% 9.05wt% 18.24wt% 42ppm
TABLE 2 content of Ni, co, mn, al, si metallic element in lithium carbonate
Species of element Ni Co Mn Al Si
Content of 4ppm 3ppm 3ppm 1ppm 1ppm
Example 2
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) The same as in example 1.
(2) And mixing the mixed powder obtained in the last step of carbothermic reduction with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 30wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 20m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 10m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 0.1MPa and an operating temperature of 20 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing with water for 3 times, and separating to obtain filtrate and filter cake. The content of Ni, co, mn, li metal element in the filter cake obtained by inductively coupled plasma emission spectrometer (icp-oes) was tested as shown in Table 3. Evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.91%, and the yield of lithium element was 93%. The content of Ni, co, mn, al, si and other impurity metal elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 4.
TABLE 3 content of Ni, co, mn, li metallic elements in Filter cake
Species of element Ni Co Mn Li
Content of 23.51wt% 9.08wt% 18.25wt% 92ppm
TABLE 4 content of Ni, co, mn, al, si metallic elements in lithium carbonate
Species of element Ni Co Mn Al Si
Content of 4ppm 3ppm 2ppm 1ppm 1ppm
Example 3
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) The same as in example 1.
(2) And mixing the mixed powder obtained in the last step of carbothermic reduction with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 30wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 20m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 10m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 1MPa and an operating temperature of 20 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing with water for 3 times, and separating to obtain filtrate and filter cake. The content of Ni, co, mn, li metal element in the filter cake obtained by inductively coupled plasma emission spectrometer (icp-oes) was tested as shown in Table 5. Evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.93%, and the yield of lithium element was 96%. The content of Ni, co, mn, al, si and other impurity metal elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 6.
TABLE 5 content of Ni, co, mn, li metallic elements in Filter cake
Species of element Ni Co Mn Li
Content of 23.52wt% 9.07wt% 18.23wt% 22ppm
TABLE 6 content of Ni, co, mn, al, si metallic element in lithium carbonate
Species of element Ni Co Mn Al Si
Content of 6ppm 5ppm 4ppm 2ppm 1ppm
Example 4
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) The same as in example 1.
(2) And mixing the mixed powder obtained in the last step of carbothermic reduction with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 30wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 20m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 10m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 1MPa and an operating temperature of 50 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing with water for 3 times, and separating to obtain filtrate and filter cake. The content of Ni, co, mn, li metal element in the filter cake obtained by inductively coupled plasma emission spectrometer (icp-oes) was tested as shown in Table 7. Evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.95%, and the yield of lithium element was 91%. The content of Ni, co, mn, al, si and other impurity metal elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 8.
TABLE 7 content of Ni, co, mn, li metallic elements in Filter cake
Species of element Ni Co Mn Li
Content of 23.51wt% 9.04wt% 18.23wt% 112ppm
TABLE 8 content of Ni, co, mn, al, si metallic element in lithium carbonate
Species of element Ni Co Mn Al Si
Content of 4ppm 2ppm 2ppm 1ppm 1ppm
Example 5
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) The same elements as in example 1.
(2) And mixing the mixed powder obtained in the last step of carbothermic reduction with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 30wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 100m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 20m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 1MPa and an operating temperature of 50 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing with water for 3 times, and separating to obtain filtrate and filter cake. The content of Ni, co, mn, li metal element in the filter cake obtained by inductively coupled plasma emission spectrometer (icp-oes) was tested as shown in Table 9. Evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.92%, and the yield of lithium element was 83%. The content of Ni, co, mn, al, si and other impurity metal elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 10.
TABLE 9 content of Ni, co, mn, li metallic elements in Filter cake
Species of element Ni Co Mn Li
Content of 23.55wt% 9.07wt% 18.25wt% 115ppm
Table 10 content of Ni, co, mn, al, si Metal element in lithium carbonate
Species of element Ni Co Mn Al Si
Content of 4ppm 2ppm 3ppm 1ppm 1ppm
Example 6
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) And (3) grinding the lithium cobalt oxide anode material of the waste lithium ion battery and coke (the mass ratio is 8:2) uniformly, mechanically mixing for 2 hours by using a ball mill, then placing the mixture in a nitrogen atmosphere furnace for carbothermic reduction treatment, cooling to room temperature for 2 hours at the reaction temperature of 550 ℃, and grinding into powder.
(2) And mixing the mixed powder obtained in the last step of carbothermic reduction with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 20wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 25m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 2m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 0.5MPa and an operating temperature of 25 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing with water for 5 times, and separating to obtain filtrate and filter cake. The filter cake is a mixture of cobalt and cobalt oxide, and the content of metal elements in the filter cake obtained by adopting an inductively coupled plasma emission spectrometer (icp-oes) is shown in table 11; evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.74%, and the yield of lithium element was 93%. The content of metal impurity elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 12.
TABLE 11 Co, li Metal element content in Filter cake
Species of element Co Li
Content of 41.57wt% 21ppm
Table 12 content of impurity metal element such as Ni, co, mn, al, si in lithium carbonate
Species of element Ni Co Mn Al Si
Content of 4ppm 1ppm
Example 7
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) Grinding the lithium manganate positive electrode material of the waste lithium ion battery and coke (the mass ratio is 8:2) uniformly, mechanically mixing for 2 hours by using a ball mill, then placing the mixture in a nitrogen atmosphere furnace for carbothermic reduction treatment, cooling to room temperature for 2 hours at the reaction temperature of 650 ℃, and grinding into powder.
(2) And mixing the mixed powder obtained in the last step of carbothermic reduction with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 20wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 40m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 10m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 1.5Mpa and an operating temperature of 25 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing for 4 times, and separating to obtain filtrate and filter cake. The filter cake is a mixture of manganese and manganese oxide, and the content of metal elements in the filter cake is obtained by adopting an inductively coupled plasma emission spectrometer (icp-oes) as shown in table 13; evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.79%, and the yield of lithium element was 97%. The content of metal impurity elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 14.
TABLE 13 Mn, li Metal element content in Filter cake
Species of element Mn Li
Content of 44.52wt% 25ppm
Table 14 content of impurity metal element such as Ni, co, mn, al, si in lithium carbonate
Species of element Ni Co Mn Al Si
Content of 9ppm 1ppm
Example 8
A method for efficiently separating lithium elements in a waste lithium ion battery anode material comprises the following steps:
(1) Grinding the waste lithium ion battery lithium iron phosphate anode material and coke (the mass ratio is 8:2) uniformly, mechanically mixing for 2 hours by using a ball mill, then placing the mixture in a nitrogen atmosphere furnace for carbothermic reduction treatment, cooling to room temperature for 2 hours at the reaction temperature of 700 ℃, and grinding into powder.
(2) And mixing the mixed powder obtained in the last step of carbothermic reduction with water, and mechanically stirring for 1h to obtain a uniform suspension with the solid content of 20wt%.
(3) Introducing the suspension obtained in the last step into a reaction absorption tower at a flow rate of 10m/min, and enabling the suspension to gradually flow through a column plate, an overflow weir, a downcomer and the like until the suspension flows out of the bottom of the tower; introducing carbon dioxide into the bottom of the reaction absorption tower at a flow rate of 10m/s, and passing through holes of each tower plate step by step and the suspension flowing through the tower plates until the carbon dioxide flows out of the tower top; the reaction absorption tower has an operating pressure of 1MPa and an operating temperature of 25 ℃.
(4) Filtering the suspension flowing out from the bottom of the tower in the last step, washing with water for 3 times, and separating to obtain filtrate and filter cake. The filter cake is a mixture of ferric oxide and ferric phosphide, and the content of metal elements in the filter cake obtained by adopting an inductively coupled plasma emission spectrometer (icp-oes) is shown in table 15; evaporating the obtained filtrate to obtain high-purity lithium carbonate, and determining Li in the obtained high-purity lithium carbonate by acid-base titration (GB/T11064.1-2013) 2 CO 3 The content was 99.81%, and the yield of lithium element was 95%. The content of metal impurity elements in lithium carbonate obtained by using an inductively coupled plasma emission spectrometer (icp-oes) is shown in Table 16.
TABLE 15 Fe, li Metal element content in Filter cake
Species of element Fe Li
Content of 25.24wt% 34ppm
TABLE 16 content of impurity Metal elements such as Fe, al in lithium carbonate
Species of element Fe Al
Content of 4ppm 1ppm
Finally, it should be noted that the above embodiments are only for illustrating the technical solution of the present invention, and not for limiting the scope of the present invention, and although the present invention has been described in detail with reference to the preferred embodiments, it should be understood by those skilled in the art that modifications or equivalent substitutions can be made to the technical solution of the present invention without departing from the spirit and scope of the technical solution of the present invention.

Claims (8)

1. A method for efficiently separating lithium elements in a waste lithium ion battery anode material is characterized by comprising the following steps:
(1) Mechanically and uniformly mixing the anode material of the waste lithium ion battery with coke;
(2) Carrying out carbothermic reduction treatment on the mixed powder obtained in the step (1) under an anoxic atmosphere;
(3) Mixing the mixed powder obtained after carbothermic reduction obtained in the step (2) with water, and mechanically stirring to obtain a suspension;
(4) Introducing the suspension obtained in the step (3) into a reaction absorption tower, and then gradually flowing through a tower plate, an overflow weir, a downcomer and the like until the bottom of the tower flows out;
(5) Introducing carbon dioxide from the bottom of the reaction tower in the step (4), and passing through holes of each tower plate step by step and suspension flowing through the tower plates until the carbon dioxide flows out from the top of the tower;
(6) Filtering and washing the suspension flowing out of the bottom of the step (4) for multiple times, and separating to obtain filtrate and a filter cake, wherein the filter cake is a metal or metal oxide mixture;
(7) And (3) evaporating the filtrate obtained in the step (6) to dryness to obtain the high-purity lithium carbonate.
2. The method for efficiently separating lithium elements from the waste lithium ion battery positive electrode material according to claim 1, wherein in the step (1), the waste lithium ion battery positive electrode material comprises at least one of nickel cobalt lithium manganate, lithium cobaltate, lithium manganate and lithium iron phosphate.
3. The method for efficiently separating lithium elements from the anode material of the waste lithium ion battery according to claim 1, wherein in the step (3), the mixed powder obtained after carbothermic reduction is mixed with water for mechanical stirring for 0.5-6h.
4. The method for efficiently separating lithium elements from the anode material of the waste lithium ion battery according to claim 1, wherein in the step (3), the concentration of the suspension solid phase substance obtained by mixing the mixed powder obtained by carbothermic reduction with water is 1-60wt%.
5. The method for efficiently separating lithium elements from the anode material of the waste lithium ion battery according to claim 1, wherein in the step (4), the operation pressure of the reaction absorption tower is 0.1-10MPa, and the operation temperature is 1-65 ℃.
6. The method for efficiently separating lithium elements from the anode material of the waste lithium ion battery according to claim 1, wherein in the step (4), the flow rate of the suspension is 10-180m/min.
7. The method for efficiently separating lithium elements from the anode material of the waste lithium ion battery according to claim 1, wherein in the step (5), the flow rate of the carbon dioxide is 0.2-20m/s.
8. The method for efficiently separating lithium element from the anode material of the waste lithium ion battery according to claim 1, wherein in the step (6), the filtering is performed for 3-5 times.
CN202211504773.4A 2022-11-28 2022-11-28 Method for efficiently separating lithium element in waste lithium ion battery anode material Pending CN116002725A (en)

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