CN110224115B - Lithium ion battery cathode material and preparation method and application thereof - Google Patents

Lithium ion battery cathode material and preparation method and application thereof Download PDF

Info

Publication number
CN110224115B
CN110224115B CN201810175305.4A CN201810175305A CN110224115B CN 110224115 B CN110224115 B CN 110224115B CN 201810175305 A CN201810175305 A CN 201810175305A CN 110224115 B CN110224115 B CN 110224115B
Authority
CN
China
Prior art keywords
lithium ion
electroplating sludge
ion battery
composite material
preparing
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201810175305.4A
Other languages
Chinese (zh)
Other versions
CN110224115A (en
Inventor
邓洪
叶旭村
林璋
熊训辉
刘炜珍
刘学明
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
South China University of Technology SCUT
Original Assignee
South China University of Technology SCUT
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by South China University of Technology SCUT filed Critical South China University of Technology SCUT
Priority to CN201810175305.4A priority Critical patent/CN110224115B/en
Publication of CN110224115A publication Critical patent/CN110224115A/en
Application granted granted Critical
Publication of CN110224115B publication Critical patent/CN110224115B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M10/00Secondary cells; Manufacture thereof
    • H01M10/05Accumulators with non-aqueous electrolyte
    • H01M10/052Li-accumulators
    • H01M10/0525Rocking-chair batteries, i.e. batteries with lithium insertion or intercalation in both electrodes; Lithium-ion batteries
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/36Selection of substances as active materials, active masses, active liquids
    • H01M4/362Composites
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/36Selection of substances as active materials, active masses, active liquids
    • H01M4/38Selection of substances as active materials, active masses, active liquids of elements or alloys
    • H01M4/387Tin or alloys based on tin
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/36Selection of substances as active materials, active masses, active liquids
    • H01M4/58Selection of substances as active materials, active masses, active liquids of inorganic compounds other than oxides or hydroxides, e.g. sulfides, selenides, tellurides, halogenides or LiCoFy; of polyanionic structures, e.g. phosphates, silicates or borates
    • H01M4/583Carbonaceous material, e.g. graphite-intercalation compounds or CFx
    • H01M4/587Carbonaceous material, e.g. graphite-intercalation compounds or CFx for inserting or intercalating light metals
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/62Selection of inactive substances as ingredients for active masses, e.g. binders, fillers
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/62Selection of inactive substances as ingredients for active masses, e.g. binders, fillers
    • H01M4/624Electric conductive fillers
    • H01M4/625Carbon or graphite
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/10Energy storage using batteries

Abstract

The invention provides a lithium ion battery cathode material and a preparation method and application thereof. According to the invention, bacteria are added into the pickle liquor to absorb tin and iron ions, a composite material precursor is obtained through stirring and filtering, and then the precursor is calcined in an inert gas atmosphere to obtain the Sn/Fe @ C lithium ion battery composite negative electrode material, so that the preparation process is simple, easy to operate and easy to control; can not only complete the recycling of the electroplating sludge, but also solve the problem of the swelling of the tin-based material, thereby realizing the technical route of high-value utilization of the wastes. The lithium ion battery cathode material can well relieve the volume change of metal tin in the charging and discharging processes, avoids the volume expansion of tin in the charging and discharging processes, and has excellent cycle stability and higher capacity; when the composite material is used as a lithium battery negative electrode material, the composite material shows good electrochemical performance and can better meet the requirements of the current market.

Description

Lithium ion battery cathode material and preparation method and application thereof
Technical Field
The invention relates to a method for recovering and extracting metals from electroplating sludge, in particular to a lithium ion battery cathode material and a preparation method and application thereof.
Background
With the rapid development of the electroplating industry, the amount of electroplating sludge is also rapidly increasing. The electroplating sludge contains a large amount of metals (tin, iron, copper, chromium, nickel, zinc, etc.). If the electroplating sludge is not properly treated, the method can cause fatal threats to the physical health and the ecological environment of human beings. Therefore, the harmless treatment of the electroplating sludge and the high-value recovery of heavy metals in the electroplating sludge become the popular research direction in the industry.
At present, the following methods are mainly used for treating the electroplating sludge:
1. the sludge is directly buried after dehydration.
2. And (4) carrying out pyrometallurgical treatment.
3. Ion exchange membrane process.
4. Ammonia leaching method.
5. Acid leaching method.
6. Biological method.
However, because the electroplating sludge contains a large amount of undegradable heavy metals, the above treatment method has great disadvantages and risks, such as: high treatment cost, easy generation of secondary environmental pollution and the like.
The electroplating sludge contains a large amount of metal elements such as tin, iron, copper and the like. Wherein, the tin has high theoretical capacity of 994mAh/g, and is a lithium ion battery cathode material with a far-reaching application prospect. It has the advantages of low de-intercalation platform, high theoretical capacity of battery, etc. However, tin is likely to undergo volume expansion during charging and discharging, and electrode materials are pulverized and dropped, resulting in a decrease in battery capacity and deterioration in cycle performance, so that it is difficult to realize commercial production and application.
Disclosure of Invention
The invention aims to overcome the defects in the prior art and provides a method for preparing a lithium ion battery cathode material by using electroplating sludge. The characteristic that bacteria selectively absorb heavy metal is utilized to treat heavy metal ions in the electroplating sludge pickle liquor. Adding bacteria into the pickle liquor to absorb tin and iron ions, stirring and carrying out vacuum filtration to obtain a composite material precursor, and calcining the precursor in an inert gas atmosphere to obtain the Sn/Fe @ C lithium ion battery composite negative electrode material. And (3) selectively extracting and recovering tin in the electroplating sludge by using the bacillus subtilis as a carrier to prepare the high-performance lithium ion battery cathode material. Can not only complete the recycling of the electroplating sludge, but also solve the problem of the swelling of the tin-based material, thereby realizing the technical route of high-value utilization of the wastes.
The invention also aims to provide the lithium ion battery negative electrode material prepared by the method. The metal ion battery negative electrode composite material avoids volume expansion of tin in the charging and discharging processes, and shows good electrochemical performance when the composite material is used as a lithium battery negative electrode material.
The invention further aims to provide the method or the application of the lithium ion battery negative electrode material.
The purpose of the invention is realized by the following technical scheme:
a method for preparing a lithium ion battery cathode material by using electroplating sludge comprises the following preparation steps:
(1) adding inorganic acid into the electroplating sludge, uniformly stirring, and filtering to obtain electroplating sludge pickle liquor containing tin and iron;
(2) inoculating bacillus subtilis into the culture solution, and culturing to obtain a bacillus subtilis solution;
(3) adding the acid leaching solution of the electroplating sludge obtained in the step (1) into the bacillus subtilis liquid obtained in the step (2), and uniformly mixing to obtain a mixed solution;
(4) filtering the mixed solution obtained in the step (3), and drying to obtain a precursor of the bacillus subtilis and tin-iron composite material;
(5) and (2) calcining the precursor of the composite material of the bacillus subtilis and the tin iron at high temperature in an inert or reducing atmosphere to obtain the Sn/Fe @ C composite material.
The pH value of the pickle liquor in the step (1) is preferably 4-8.
The inorganic acid in the step (1) is preferably one or at least two of hydrochloric acid, sulfuric acid, nitric acid and phosphoric acid.
The concentration of the inorganic acid in the step (1) is preferably 0.1-3 mol/L.
The stirring time in the step (1) is preferably 1-3 h.
The inoculation amount of the bacillus subtilis in the step (2) is preferably 1-10%.
The culture solution in step (2) is preferably prepared by the following method: dissolving 10g tryptone, 5g yeast extract and 5g sodium chloride in 1L deionized water, and stirring.
The culture time in the step (2) is preferably 12-24 h.
The mixing in step (3) is preferably carried out by shaking or stirring; the mixing time is preferably 1-24 h.
The bacillus subtilis liquid and the electroplating sludge acid leaching liquid in the step (3) are preferably mixed according to the volume ratio of 1: (0.1-5); further preferably, the amount of the water-soluble polymer is 1: (1-3) mixing.
The filtration in the step (4) is preferably one or at least two of gravity filtration, centrifugal filtration and vacuum filtration.
The drying in the step (4) is preferably one or at least two of atmospheric drying, vacuum drying and freeze drying.
The inert or reducing atmosphere in the step (5) is preferably one or a mixture of at least two of nitrogen, argon and hydrogen.
The high-temperature calcination in the step (5) is preferably performed by heating to 500-900 ℃ at a heating rate of 1-15 ℃/min for 1-10 h.
The lithium ion battery cathode material prepared by the method.
The preparation method or the application of the lithium ion battery negative electrode material in the field of lithium ion batteries.
Compared with the prior art, the invention has the following advantages and effects:
(1) the invention utilizes the electroplating sludge of industrial waste in a high-value way, uses the microorganism as the processing material, and has wide source and low cost. Can realize the purpose of high-value utilization of waste and solve the environmental problem. The research utilizes the electroplating sludge in a high-value manner, provides a new idea for harmless treatment of the electroplating sludge and also provides a new idea for preparing electrochemical energy storage materials.
(2) The preparation process is simple, easy to operate and easy to control.
(3) The bacteria in the composite material prepared by the invention are partially graphene-based after high-temperature calcination, which is beneficial to ion and electron transmission.
(4) In the Sn/Fe @ C composite material prepared by the invention, the volume change of the metallic tin in the charging and discharging process can be well relieved by using bacteria as a carrier of the metallic tin iron, and the obtained material has superior performanceHas a high capacity at a current density of 1A g-1The specific capacity can reach 620.4mAh g-1And the specific capacity retention rate is more than 95% after 1000 cycles. Compared with other methods for preparing electrode materials, such as the technical schemes described in patent documents with application numbers of CN201310715142.1 and CN200910193554.7, the method of the invention has superior cycling stability and high specific capacity, and can better meet the requirements of the current market.
Drawings
FIG. 1 is an XRD spectrum of the Sn-Fe @ C composite material prepared in example 1.
FIG. 2 is an SEM image of the Sn-Fe @ C composite material prepared in example 1.
FIG. 3 is a graph showing the first charge and discharge curves at a current density of 0.1A/g for a button cell assembled from the Sn-Fe @ C composite material prepared in example 2.
FIG. 4 is an SEM image of the Sn-Fe @ C composite material prepared in example 2.
FIG. 5 is a graph of the cycling performance of a button cell assembled from the Sn-Fe @ C composite material prepared in example 3 at a current density of 1A/g.
FIG. 6 is a graph of rate performance of button cells assembled from the Sn-Fe @ C composite material prepared in example 3 at different current densities.
FIG. 7 is an XRD pattern of the Sn-Fe @ C composite material prepared in example 4.
FIG. 8 is an SEM image of the Sn-Fe @ C composite material prepared in example 4.
FIG. 9 is an SEM photograph of a composite material obtained in comparative example 2.
FIG. 10 is a graph of the cycling performance of the button cell made of the composite material prepared in comparative example 2 at a current density of 1A/g.
Detailed Description
The present invention will be described in further detail with reference to examples and drawings, but the present invention is not limited thereto.
Example 1
(1) Preparing a culture medium: weighing 10g of tryptone, 5g of yeast extract and 5g of sodium chloride, dissolving in 1L of deionized water, and uniformly stirring to form a stable clear solution.
(2) Electroplating sludge acid leaching solution: the electroplating sludge is placed in an oven, dried for 12 hours at 90 ℃, ground and sieved by a two-hundred-mesh sieve. Taking 10g of dried electroplating sludge, adding 50mL of 1mol/L hydrochloric acid, stirring for 2h, and filtering to obtain filtrate which is electroplating sludge pickle liquor with pH of 5.4.
(3) Inoculating bacteria: inoculating a Bacillus subtilis ATCC-6633 strain to the culture medium prepared in the step (1) with the inoculation amount of 1%, and placing the culture medium in a constant-temperature shaking table for activation for 12 hours;
(4) and (3) amplification culture: inoculating the activated bacillus subtilis in the step (3) on the culture medium prepared in the step (1) by using the inoculation amount of 1%, and placing the culture medium in a constant-temperature shaking table for culturing for 12 hours to obtain a bacillus subtilis liquid;
(5) adding the electroplating sludge acid leaching solution obtained in the step (2) into the bacterial culture medium subjected to the enlarged culture in the step (4), wherein the volume ratio of the acid leaching solution to the culture medium is 1: 1, stirring for 6 hours;
(6) carrying out suction filtration on the solution to obtain a composite material precursor;
(7) and drying the composite material precursor, calcining for 2h at 600 ℃ in an argon atmosphere (the heating rate is 10 ℃/min), and cooling to obtain the Sn/Fe @ C composite material.
The physical and chemical properties of the prepared Sn/bacteria composite material are characterized as shown in figures 1 and 2, wherein figure 1 is an XRD (X-ray diffraction) pattern of the prepared Sn/Fe @ C composite material, and figure 2 is an SEM (scanning Electron microscope) pattern of the Sn/Fe @ C composite material prepared in example 1.
XRD shows that simple substance tin and iron-tin alloy exist in the Sn/Fe @ C composite material prepared in the embodiment, and SEM shows that the composite material is good in appearance, and tin and iron-tin alloy are uniformly distributed on the surface of bacteria.
The obtained product is assembled into a button cell to test the discharge capacity of the button cell, and charge and discharge are carried out within the range of 0.01-2.5V. FIG. 3 shows the first charge/discharge curve at a current density of 0.1A/g. Meanwhile, the capacity of the composite material reaches 898.2 mAh/g.
Example 2
(1) Preparing a culture medium: weighing 10g of tryptone, 5g of yeast extract and 5g of sodium chloride, dissolving in 1L of deionized water, and uniformly stirring to form a stable clear solution.
(2) Electroplating sludge acid leaching solution: the electroplating sludge is placed in an oven, dried for 12 hours at 90 ℃, ground and sieved by a two-hundred-mesh sieve. Taking 10g of dried electroplating sludge, adding 50mL of 0.1mol/L nitric acid, stirring for 3h, and filtering to obtain filtrate, namely electroplating sludge pickle liquor, wherein the pH value is 6.8.
(3) Inoculating bacteria: inoculating Bacillus subtilis ATCC-6633 to the culture medium prepared in the step (1) with the inoculation amount of 1%, and placing the culture medium in a constant-temperature shaking table for activation for 12 hours;
(4) and (3) amplification culture: inoculating the activated bacteria obtained in the step (3) on the culture medium prepared in the step (1) by an inoculation amount of 5%, and placing the culture medium in a constant-temperature shaking table for culturing for 24 hours to obtain a bacillus subtilis liquid;
(5) adding the acid leaching solution of the electroplating sludge obtained in the step (2) into the bacillus subtilis liquid obtained in the step (4), wherein the volume ratio of the acid leaching solution to the culture medium is 2: 1, stirring for 12 hours;
(6) carrying out suction filtration on the solution to obtain a composite material precursor;
(7) and drying the composite material precursor, calcining for 2h at 700 ℃ in a nitrogen atmosphere (the heating rate is 7 ℃/min), and cooling to obtain the Sn/Fe @ C composite material.
The physical and chemical properties of the prepared Sn/Fe @ C composite material are shown in figures 4 and 5, figure 4 is an SEM image of the prepared Sn/Fe @ C composite material, and figure 4 shows that tin and tin-iron alloy are uniformly distributed on the surface of bacteria. The obtained Sn/Fe @ C composite material is assembled into a button cell, a circulation performance diagram under the current density of 1A/g is shown in figure 5, the first specific capacity under the multiplying power reaches 620.4mAh/g, and the specific capacity retention rate is more than 95% after 1000 times of circulation.
Example 3
1) Preparing a culture medium: weighing 10g of tryptone, 5g of yeast extract and 5g of sodium chloride, dissolving in 1L of deionized water, and uniformly stirring to form a stable clear solution.
(2) Electroplating sludge acid leaching solution: the electroplating sludge is placed in an oven, dried for 12 hours at 90 ℃, ground and sieved by a two-hundred-mesh sieve. Taking 10g of dried electroplating sludge, adding 50mL of 2mol/L hydrochloric acid, stirring for 2h, and filtering to obtain filtrate, namely electroplating sludge pickle liquor, wherein the pH value is 8.0.
(3) Inoculating bacteria: inoculating Bacillus subtilis ATCC-6633 to the culture medium prepared in the step (1) with the inoculation amount of 1%, and placing the culture medium in a constant-temperature shaking table for activation for 12 hours;
(4) and (3) amplification culture: inoculating the activated bacteria in the step (3) on the culture medium prepared in the step (1) by 10 percent of inoculation amount, and placing the culture medium in a constant-temperature shaking table for culturing for 24 hours;
(5) adding the acid leaching solution of the electroplating sludge obtained in the step (2) into the bacterial culture medium subjected to the enlarged culture in the step (4), wherein the volume ratio of the acid leaching solution of the electroplating sludge to the culture medium is 3: 1, stirring for 24 hours;
(6) carrying out suction filtration on the solution to obtain a composite material precursor;
(7) and drying the composite material precursor, calcining at 500 ℃ for 2h (the heating rate is 5 ℃/min) in a nitrogen-hydrogen mixed atmosphere (95% of nitrogen and 5% of hydrogen), and cooling to obtain the Sn/Fe @ C composite material.
And assembling the Sn/Fe @ C composite material into a button cell to test the charge-discharge capacity of the button cell, and carrying out cycle life test within the range of 0.01-2.5V. As shown in fig. 6, the rate capability of the button cell is shown under different current densities, and it can be seen that the Sn/Fe @ C composite material has excellent rate capability.
Comparative example 1
(1) Preparing a culture medium: weighing 10g of tryptone, 5g of yeast extract and 5g of sodium chloride, dissolving in 1L of deionized water, and uniformly stirring to form a stable clear solution.
(2) Electroplating sludge acid leaching solution: the electroplating sludge is placed in an oven, dried for 12 hours at 90 ℃, ground and sieved by a two-hundred-mesh sieve. Taking 10g of dried electroplating sludge, adding 50mL of 2mol/L nitric acid, stirring for 2h, and filtering to obtain filtrate, namely electroplating sludge pickle liquor, wherein the pH value is 5.4.
(3) Inoculating bacteria: inoculating Bacillus subtilis ATCC-6633 to the culture medium prepared in the step (1) with an inoculation amount of 5%, and placing the culture medium in a constant-temperature shaking table for activation for 12 hours;
(4) and (3) amplification culture: inoculating the activated bacillus subtilis in the step (3) on the culture medium prepared in the step (1) by 10% of inoculation amount, and placing the culture medium in a constant-temperature shaking table for culturing for 24 hours to obtain bacillus subtilis liquid;
(5) adding the acid leaching solution of the electroplating sludge obtained in the step (2) into the bacillus subtilis liquid obtained in the step (4), wherein the volume ratio of the acid leaching solution of the electroplating sludge to the culture medium is 3: 1, stirring for 12 hours;
(6) carrying out suction filtration on the solution to obtain a composite material precursor;
(7) and drying the composite material precursor, calcining at 900 ℃ for 5h (the heating rate is 1 ℃/min) in a nitrogen-argon mixed atmosphere, and cooling to obtain the Sn/Fe @ C composite material.
An XRD (X-ray diffraction) spectrum of the obtained Sn/Fe @ C composite material is shown in figure 7, and the existence form of tin in the composite material is proved to be metal simple substance tin through PDF card retrieval. However, as can be seen from the SEM result of fig. 8, the original morphology of the bacteria is not maintained in the composite material, and the morphology of the rod-shaped bacteria is destroyed, which has a great influence on the electrochemical performance of the composite material.
Comparative example 2
(1) Electroplating sludge acid leaching solution: the electroplating sludge is placed in an oven, dried for 12 hours at 90 ℃, ground and sieved by a two-hundred-mesh sieve. Taking 10g of dried electroplating sludge, adding 50mL of 2mol/L nitric acid, stirring for 2h, and filtering to obtain filtrate, namely electroplating sludge pickle liquor, wherein the pH value is 4.
(2) Adding 100mg of bacterial cellulose (high-fiber coconut, purchased from Hainan Cocos food Co., Ltd.) into the electroplating sludge pickle liquor obtained in the step (1), and stirring for 4 hours;
(3) carrying out suction filtration on the solution to obtain a composite material precursor;
(4) and drying the composite material precursor, calcining at 900 ℃ for 5h (the heating rate is 5 ℃/min) in a nitrogen-argon mixed atmosphere, and cooling to obtain the Sn/Fe @ C composite material.
As can be seen from fig. 9, in the composite material prepared from the bacterial cellulose, the metallic tin simple substance is aggregated into relatively large micron-scale small particles, and as can be seen from fig. 10, compared with the nano-scale composite material prepared from the bacillus subtilis, the electrochemical performance is far different, and the specific capacity is only about 420 mAh/g.
The above embodiments are preferred embodiments of the present invention, but the present invention is not limited to the above embodiments, and any other changes, modifications, substitutions, combinations, and simplifications which do not depart from the spirit and principle of the present invention should be construed as equivalents thereof, and all such changes, modifications, substitutions, combinations, and simplifications are intended to be included in the scope of the present invention.

Claims (9)

1. A method for preparing a lithium ion battery cathode material by using electroplating sludge is characterized by comprising the following preparation steps:
(1) adding inorganic acid into the electroplating sludge, uniformly stirring, and filtering to obtain electroplating sludge pickle liquor containing tin and iron;
(2) inoculating bacillus subtilis into the culture solution, and culturing to obtain a bacillus subtilis solution;
(3) adding the acid leaching solution of the electroplating sludge obtained in the step (1) into the bacillus subtilis liquid obtained in the step (2), and uniformly mixing to obtain a mixed solution;
(4) filtering the mixed solution obtained in the step (3), and drying to obtain a precursor of the bacillus subtilis and tin-iron composite material;
(5) calcining the precursor of the composite material of the bacillus subtilis and the tin iron at high temperature in an inert or reducing atmosphere to obtain the Sn/Fe @ C composite material;
wherein the pH value of the electroplating sludge pickle liquor in the step (1) is 4-8.
2. The method for preparing the lithium ion battery anode material by using the electroplating sludge according to claim 1, wherein the method comprises the following steps:
the concentration of the inorganic acid in the step (1) is 0.1-3 mol/L.
3. The method for preparing the lithium ion battery anode material by using the electroplating sludge according to claim 1, wherein the method comprises the following steps:
the inoculation amount of the bacillus subtilis in the step (2) is 1-10%.
4. The method for preparing the lithium ion battery anode material by using the electroplating sludge according to claim 1, wherein the method comprises the following steps:
mixing in the step (3) by oscillating or stirring; the mixing time is 1-24 h.
5. The method for preparing the lithium ion battery anode material by using the electroplating sludge according to claim 1, wherein the method comprises the following steps:
the ratio of the bacillus subtilis liquid to the electroplating sludge acid leaching liquid in the step (3) by volume is 1: (0.1-5).
6. The method for preparing the lithium ion battery anode material by using the electroplating sludge according to claim 1, wherein the method comprises the following steps:
the high-temperature calcination in the step (5) is carried out by heating to 500-900 ℃ at a heating rate of 1-15 ℃/min for 1-10 h.
7. The method for preparing the lithium ion battery anode material by using the electroplating sludge according to claim 1, wherein the method comprises the following steps:
the inorganic acid in the step (1) is one or at least two of hydrochloric acid, sulfuric acid, nitric acid and phosphoric acid;
the filtration in the step (4) is one or at least two of gravity filtration, centrifugal filtration and vacuum filtration;
the drying in the step (4) is one or at least two of normal pressure drying, vacuum drying and freeze drying;
the inert or reducing atmosphere in the step (5) is one or a mixture of at least two of nitrogen, argon and hydrogen.
8. A lithium ion battery negative electrode material is characterized in that:
the method for preparing the lithium ion battery anode material by using the electroplating sludge as claimed in any one of claims 1 to 7.
9. The method for preparing the lithium ion battery anode material by using electroplating sludge according to any one of claims 1 to 7 or the application of the lithium ion battery anode material according to claim 8 in the field of lithium ion batteries.
CN201810175305.4A 2018-03-02 2018-03-02 Lithium ion battery cathode material and preparation method and application thereof Expired - Fee Related CN110224115B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810175305.4A CN110224115B (en) 2018-03-02 2018-03-02 Lithium ion battery cathode material and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810175305.4A CN110224115B (en) 2018-03-02 2018-03-02 Lithium ion battery cathode material and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN110224115A CN110224115A (en) 2019-09-10
CN110224115B true CN110224115B (en) 2020-12-22

Family

ID=67821903

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810175305.4A Expired - Fee Related CN110224115B (en) 2018-03-02 2018-03-02 Lithium ion battery cathode material and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN110224115B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114634181B (en) * 2022-02-21 2023-06-16 华南理工大学 Lithium-sulfur battery positive electrode material prepared by recycling iron in electroplating sludge and preparation method thereof

Family Cites Families (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101502898B1 (en) * 2008-11-10 2015-03-25 삼성에스디아이 주식회사 Composite anode active material for lithium rechargeable battery, its preparation and lithium battery using same
KR101264343B1 (en) * 2011-06-13 2013-05-14 한국전기연구원 Negative Active Material, Manufacturing Method thereof And Lithium Secondary Battery Comprising The Same
KR101340523B1 (en) * 2012-05-22 2013-12-11 아주대학교산학협력단 Method for Multiphasic Tin-based Nano Structures/Amorphous Carbon Nano Composite and Anode Active Materials Comprising the Same
CN102912155A (en) * 2012-09-20 2013-02-06 福建省固体废物处置有限公司 Recovery processing process of stanniferous electrofacing sludge
DE102014210086A1 (en) * 2014-05-27 2015-12-03 Robert Bosch Gmbh Silicon particles with a microorganism-shaped cavity
CN104143632A (en) * 2014-07-30 2014-11-12 吉林大学 Tin-based iron-carbon composite lithium battery negative electrode material, preparation method and application
CN104835946A (en) * 2015-05-30 2015-08-12 田东 Tin and carbon composite cathode material of lithium ion battery and preparation method of tin and carbon composite cathode material
CN105161721B (en) * 2015-08-04 2018-07-06 天津大学 The composite material of three-dimensional grapheme interlayer filling carbon coating tin particles and preparation
CN107665972B (en) * 2017-07-05 2020-04-17 中国矿业大学 Preparation method of Sn @ C material of high-performance potassium ion battery negative electrode material

Also Published As

Publication number Publication date
CN110224115A (en) 2019-09-10

Similar Documents

Publication Publication Date Title
CN107226475B (en) Potassium ion battery positive electrode material, preparation method thereof and potassium ion battery
CN108059144B (en) Hard carbon prepared from biomass waste bagasse, and preparation method and application thereof
CN102382987B (en) Method for recovering and regenerating positive electrode material of lithium ion battery
CN108091871A (en) A kind of porous spherical ternary cathode material of lithium ion battery and preparation method thereof
CN110518213A (en) A kind of porous silicon-carbon nano tube compound material and its preparation method and application
CN109148828B (en) Comprises cluster Co-Fe of rice straw2O3Electrode of nano composite material and preparation method thereof
CN113501511A (en) Method for adjusting nitrogen-doped carbon structure based on phytic acid and application of method
CN113299928A (en) Preparation method of high-performance flexible secondary zinc-silver-zinc-air hybrid battery positive electrode material
CN108550841A (en) A kind of preparation method of hard carbon cathode material, preparation method, lithium ion battery and the battery
CN110364778B (en) Method for recovering waste lithium ion battery negative plate
CN115621598A (en) Method for recycling and regenerating waste NCM523 type ternary lithium battery positive electrode material
CN108539158B (en) rGO/WS2Preparation method of composite material and application of composite material in positive electrode material of lithium-sulfur battery
CN109713259B (en) Lithium ion battery silicon-carbon composite negative electrode material and preparation method and application thereof
CN114702614A (en) Cathode material for improving cycling stability of vulcanized polyacrylonitrile battery and preparation method thereof
CN107732209B (en) Method for preparing lithium ion carbon negative electrode material from mixed bacteria residue waste
CN110224115B (en) Lithium ion battery cathode material and preparation method and application thereof
CN112174119B (en) Method for preparing graphene foam from antibiotic fungi residues
CN113735180B (en) Method for preparing sodium ion battery anode material by using LDH-based precursor to obtain cobalt iron sulfide
CN109841825B (en) Method for preparing lithium ion battery cathode material by recycling tin in electroplating sludge
CN112607787B (en) Method for recycling lithium cobaltate high-iron material
CN109671923A (en) A kind of preparation method and lithium-sulfur cell of ordered nano array nitrogen sulphur codope carbon sulphur composite carbon bar material
CN114824204A (en) Preparation method of carbon-coated cobalt-nickel binary transition metal sulfide negative electrode material
CN110902660B (en) Preparation method of GaN nanowire lithium ion battery cathode material
CN114497792A (en) Efficient electrode material recovery and re-preparation method and application
CN111468502B (en) Heavy metal polluted plant stem treatment and high-value utilization method

Legal Events

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

Granted publication date: 20201222