CN109841825A - A kind of method that tin prepares lithium ion battery negative material in recycling electroplating sludge - Google Patents

A kind of method that tin prepares lithium ion battery negative material in recycling electroplating sludge Download PDF

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Publication number
CN109841825A
CN109841825A CN201910248282.XA CN201910248282A CN109841825A CN 109841825 A CN109841825 A CN 109841825A CN 201910248282 A CN201910248282 A CN 201910248282A CN 109841825 A CN109841825 A CN 109841825A
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electroplating sludge
lithium ion
ion battery
battery negative
negative material
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CN201910248282.XA
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CN109841825B (en
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邓洪
叶旭村
林璋
刘学明
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South China University of Technology SCUT
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South China University of Technology SCUT
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    • 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 belongs to Electroplating Sludge Technology field, a kind of method that tin prepares lithium ion battery negative material in recycling electroplating sludge is disclosed.Inorganic alkali solution is added in electroplating sludge, after mixing evenly hydro-thermal reaction after drying and grinding is sieved, electroplating sludge purification liquid is obtained by filtration;Bacteria cellulose is added in PDDA solution, oscillation uses distilled water rinse after being stirred, and obtains modified bacteria cellulose;Gained modified bacteria cellulose is added in electroplating sludge purification liquid, is stirred, is washed out and is dried to obtain composite material precursor, finally the high-temperature calcination under inertia or reducing atmosphere, obtain Sn@C lithium cell negative pole material.Preparation method of the invention not only solves the environmental problem of electroplating sludge, and prepares high-valued lithium ion battery negative material using the unique pattern of inner bacteria cellulose, to realize that turning waste into wealth for Environmental waste provides feasible thinking.

Description

A kind of method that tin prepares lithium ion battery negative material in recycling electroplating sludge
Technical field
The invention belongs to Electroplating Sludge Technology fields, and in particular to tin prepares lithium ion in a kind of recycling electroplating sludge The method of cell negative electrode material.
Background technique
Electroplating sludge has unstability, migration is strong, the feature more than water content, mainly as one of danger wastes Contain the metal ions such as Sn, Fe, Cu, Ni, Cr, Cd.And all there is difference in various electroplating sludges caused by different types of plating Not, it also has nothing in common with each other for different metal ion treatment methods.Electroplating sludge is broadly divided into two classes, one is sub-prime sludge, Institute's metal ion is single, and such sludge is more easy to be recycled;It is another then be mixing sludge, ingredient is more complex, metal Ionic species is more, and there are also Cr, the hazardous metals ions such as Cd to bring extreme difficulties for post-processing disposition and separation for some.Sn is wide It is general to be used for electroplating industry, the one kind recycled is difficult in one of primary metal ion as electroplating sludge and sludge.Mesh The preceding electroplating sludge processing method generally used mainly has: curing agent processing, heat treatment, thermal process, wet processing, acid system leaching Out, ammonia process leaches, biological treatment etc., also needs to carry out for leachate or solid waste product after above-mentioned processing method Processing disposition.Therefore it is highly important for developing new electroplating sludge processing method.
Summary of the invention
In place of the above shortcoming and defect of the existing technology, the purpose of the present invention is to provide a kind of recycling plating The method that tin prepares lithium ion battery negative material in sludge.The method of the present invention by electroplating sludge higher value application, not only without Evilization processing electroplating sludge provides new thinking, also provides new idea for preparation electrochemical energy storage materials.
The object of the invention is achieved through the following technical solutions:
A kind of method that tin prepares lithium ion battery negative material in recycling electroplating sludge, including following preparation step:
(1) inorganic alkali solution is added in electroplating sludge, after mixing evenly hydro-thermal reaction after drying and grinding is sieved, filtered Liquid is purified to electroplating sludge;
(2) bacteria cellulose is added in PDDA (polydimethyl diallyl ammonium chloride) solution, oscillation is stirred Distilled water rinse is used afterwards, obtains modified bacteria cellulose;
(3) modified bacteria cellulose obtained by step (2) is added in the electroplating sludge purification liquid of step (1), stirring is mixed It closes, is washed out and is dried to obtain composite material precursor;
(4) by composite material precursor high-temperature calcination under inertia or reducing atmosphere obtained by step (3), Sn@C lithium is obtained Cell negative pole material.
Further, drying and grinding sieving refers to 90 DEG C of dry 12h, ground 200 mesh in step (1).
Further, in step (1) inorganic alkali solution be concentration be 0.1~3mol/L sodium hydroxide, potassium hydroxide or Lithium hydroxide solution.
Further, hydrothermal temperature is 150~230 DEG C in step (1), and the time is 12~18h.
Further, the additional amount of bacteria cellulose is 0.1~3g/L in step (2).
Further, the mass concentration of PDDA solution is 1%~10% in step (2).
Further, the time that oscillation is stirred in step (2) is 0.5~2h.
Further, the time being stirred in step (3) is 1~48h.
Further, the solution of washing described in step (3) is the mixing of one or both of distilled water, dehydrated alcohol Solution.
Further, dry described in step (3) is at least one of constant pressure and dry, vacuum drying, freeze-drying.
Further, inertia described in step (4) or reducing atmosphere be nitrogen, argon gas, in hydrogen any one or Two or more mixed atmospheres.
Further, high-temperature calcination described in step (4) refer to be warming up to 500 with the heating rate of 1~10 DEG C/min~ 900 DEG C of 1~10h of calcining.
Compared with prior art, the invention has the following advantages and beneficial effects:
(1) for the bacteria cellulose that uses of the present invention as a kind of nano-fiber materials, preparation is simple, purity is high and Without containing the lignin and hemicellulose in plant cellulose, crystallinity is high, is in special hyperfine nanometer three in configuration aspects Tie up reticular structure;Carbon skeleton after being carbonized using bacteria cellulose can carry out tin particles as the carrier of tin micro-nano particle Cladding prevents Sn metal micro-nano particle to reduce the mechanical stress that Sn metal generates in charge and discharge process to a certain extent Reunion improve the cyclical stability of material to guarantee that material is not destroyed;Bacteria cellulose itself has excellent simultaneously Mechanical property can bring buffer function during charge and discharge for tin particles, and acquired material has superior circulation steady Qualitative and higher capacity, is able to satisfy the demand of Vehicles Collected from Market.
(2) the part graphite alkylene after calcination at high temperature of the bacteria cellulose in composite material prepared by the present invention, is conducive to The transfer and diffusion of Li ion.
(3) present invention is by industrial waste electroplating sludge higher value application, and can solve environmental problem.
(4) preparation method simple process of the present invention, easy to operate, easily controllable.
Detailed description of the invention
Fig. 1 is the XRD diagram of the Sn@C composite prepared in embodiment 1;
Fig. 2 is the SEM figure of the Sn@C composite prepared in embodiment 1;
Fig. 3 is that the composite material prepared in embodiment 2 is assembled into button cell cycle performance when current density is 1A/g Figure;
Fig. 4 is the Raman spectrogram of the composite material prepared in embodiment 2;
Fig. 5 is that the composite material prepared in embodiment 3 is assembled into button cell cyclicity when current density is 0.1A/g It can figure;
Fig. 6 is that the composite material prepared in embodiment 3 is assembled into high rate performance of the button cell under different current densities Figure.
Specific embodiment
Present invention will now be described in further detail with reference to the embodiments and the accompanying drawings, but embodiments of the present invention are unlimited In this.
Embodiment 1
(1) electroplating sludge purifies liquid: electroplating sludge being placed in baking oven, 90 DEG C, 12 hours dry, grinding crosses 200 Mesh sieve.50ml 0.7mol/L sodium hydroxide, 150 DEG C of hydro-thermal 48h, filtering gained is added in electroplating sludge after taking 10g dry Filtrate is that electroplating sludge purifies liquid.
(2) bacteria cellulose is modified: 100mg bacteria cellulose being added in 1wt.%PDDA solution, with 200rpm rate Oscillation stirring 1h, then uses distilled water rinse three times, obtains modified bacteria cellulose;
(3) modified bacteria cellulose is added in 50ml electroplating sludge purification liquid, oscillation is stirred for 24 hours.
(4) freeze-drying obtains composite material precursor after above-mentioned the rinse of composite material distilled water three times.
(5) composite material precursor is warming up to 600 DEG C of calcining 2h in a nitrogen atmosphere with the heating rate of 5 DEG C/min, It is cooling to obtain Sn C composite.
The physical and chemical performance characterization of composite material made from the present embodiment is shown in that Fig. 1 and Fig. 2, Fig. 1 are the Sn@C composite woods prepared The XRD spectrum of material, Fig. 2 are the SEM figures of the Sn@C composite prepared.
XRD shows in the Sn@C composite of this method preparation that SEM shows that the pattern of composite material is good there are simple substance tin Good, tin particles are evenly distributed in the three-dimensional net structure of bacteria cellulose.
Embodiment 2
(1) electroplating sludge purifies liquid: electroplating sludge being placed in baking oven, 90 DEG C, 12 hours dry, grinding crosses 200 Mesh sieve.50ml 1.0mol/L sodium hydroxide, 230 DEG C of hydro-thermal 48h, filtering gained is added in electroplating sludge after taking 10g dry Filtrate is that electroplating sludge purifies liquid.
(2) bacteria cellulose is modified: 100mg bacteria cellulose being added in 2%PDDA solution, with 150rpm rate oscillation 2h is stirred, is then used distilled water rinse three times;
(3) modified bacteria cellulose is added in 50ml electroplating sludge purification liquid, oscillation is stirred for 24 hours.
(4) freeze-drying obtains composite material precursor after above-mentioned the rinse of composite material distilled water three times.
(5) composite material precursor is warming up to 700 DEG C of calcining 2h in a nitrogen atmosphere with the heating rate of 1 DEG C/min, It is cooling to obtain Sn C composite.
The present embodiment products therefrom is assembled into button cell and tests its discharge capacity, and charge and discharge is carried out within the scope of 0.01-3V Electricity.Current density is illustrated in figure 3 as the test of 1A/g long circulating stability.Meanwhile composite material can be stablized and be recycled to 2000 It is more than circle.The physical and chemical performance characterization of Sn@C composite obtained is shown in that Fig. 4, Fig. 4 are the Raman numbers of the Sn@C composite prepared According to Fig. 4 shows the part graphene in high-temperature annealing process of the bacteria cellulose in composite material, this is conducive to lithium ion Diffusion, facilitates the raising of material specific capacity.
Embodiment 3
(1) electroplating sludge purifies liquid: electroplating sludge being placed in baking oven, 90 DEG C, 12 hours dry, grinding crosses 200 Mesh sieve.Electroplating sludge after taking 10g dry, is added 50ml 1.5mol/L sodium hydroxide, and 200 DEG C of hydro-thermals for 24 hours, filter gained Filtrate is that electroplating sludge purifies liquid.
(2) bacteria cellulose is modified: 250mg bacteria cellulose being added in 5%PDDA solution, with 200rpm rate oscillation 0.5h is stirred, is then used distilled water rinse three times;
(3) modified bacteria cellulose is added in 50ml electroplating sludge purification liquid, oscillation is stirred 12h.
(4) freeze-drying obtains composite material precursor after above-mentioned the rinse of composite material distilled water three times.
(5) composite material precursor is warming up to 700 DEG C of calcining 2h in a nitrogen atmosphere with the heating rate of 10 DEG C/min, It is cooling to obtain Sn C composite.
Sn@C composite obtained by the present embodiment is assembled into button cell and tests its charge/discharge capacity, in 0.01-3V model Enclose interior progress cycle life test.Fig. 5 is the cyclical stability test chart of composite material.It is illustrated in figure 6 obtained button electricity High rate performance of the pond under different current densities, as can be seen from the figure this Sn@C composite has superior high rate performance.
The above embodiment is a preferred embodiment of the present invention, but embodiments of the present invention are not by above-described embodiment Limitation, other any changes, modifications, substitutions, combinations, simplifications made without departing from the spirit and principles of the present invention, It should be equivalent substitute mode, be included within the scope of the present invention.

Claims (10)

1. a kind of method that tin prepares lithium ion battery negative material in recycling electroplating sludge, it is characterised in that including preparing as follows Step:
(1) inorganic alkali solution is added in electroplating sludge, after mixing evenly hydro-thermal reaction after drying and grinding is sieved, electricity is obtained by filtration It plates sludge and purifies liquid;
(2) bacteria cellulose is added in PDDA solution, oscillation uses distilled water rinse after being stirred, and obtains modified bacteria fibre Dimension element;
(3) modified bacteria cellulose obtained by step (2) is added in the electroplating sludge purification liquid of step (1), is stirred, so Washing is dried to obtain composite material precursor afterwards;
(4) by composite material precursor high-temperature calcination under inertia or reducing atmosphere obtained by step (3), it is negative to obtain Sn@C lithium electricity Pole material.
2. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: drying and grinding sieving refers to 90 DEG C of dry 12h, ground 200 mesh in step (1).
3. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: inorganic alkali solution is sodium hydroxide, potassium hydroxide or the lithium hydroxide that concentration is 0.1~3mol/L in step (1) Solution.
4. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: hydrothermal temperature is 150~230 DEG C in step (1), and the time is 12~18h.
5. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: the additional amount of bacteria cellulose is 0.1~3g/L in step (2);The mass concentration of PDDA solution be 1%~ 10%.
6. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: the time that oscillation is stirred in step (2) is 0.5~2h;The time being stirred in step (3) be 1~ 48h。
7. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: the solution of washing described in step (3) is the mixed solution of one or both of distilled water, dehydrated alcohol.
8. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: dry described in step (3) is at least one of constant pressure and dry, vacuum drying, freeze-drying.
9. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: inertia described in step (4) or reducing atmosphere be nitrogen, argon gas, in hydrogen any one or it is two or more Mixed atmosphere.
10. the method that tin prepares lithium ion battery negative material in a kind of recycling electroplating sludge according to claim 1, Be characterized in that: high-temperature calcination described in step (4), which refers to, is warming up to 500~900 DEG C of calcinings with the heating rate of 1~10 DEG C/min 1~10h.
CN201910248282.XA 2019-03-29 2019-03-29 Method for preparing lithium ion battery cathode material by recycling tin in electroplating sludge Expired - Fee Related CN109841825B (en)

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