CN104630479B - A kind of method reclaiming various metals from electron wastes - Google Patents

A kind of method reclaiming various metals from electron wastes Download PDF

Info

Publication number
CN104630479B
CN104630479B CN201310549957.7A CN201310549957A CN104630479B CN 104630479 B CN104630479 B CN 104630479B CN 201310549957 A CN201310549957 A CN 201310549957A CN 104630479 B CN104630479 B CN 104630479B
Authority
CN
China
Prior art keywords
solution
electron wastes
various metals
acid
graphene
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.)
Active
Application number
CN201310549957.7A
Other languages
Chinese (zh)
Other versions
CN104630479A (en
Inventor
刘钢
李润伟
潘亮
张文斌
巫远招
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.)
Ningbo Institute of Material Technology and Engineering of CAS
Original Assignee
Ningbo Institute of Material Technology and Engineering of CAS
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 Ningbo Institute of Material Technology and Engineering of CAS filed Critical Ningbo Institute of Material Technology and Engineering of CAS
Priority to CN201310549957.7A priority Critical patent/CN104630479B/en
Publication of CN104630479A publication Critical patent/CN104630479A/en
Application granted granted Critical
Publication of CN104630479B publication Critical patent/CN104630479B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Abstract

The invention provides a kind of method reclaiming various metals from electron wastes.The method is: electron wastes after crushed, dissolves various metals composition by nitric acid liquid leaching and enters solution;Utilizing Polyviologen functional high molecule material to process gained solution, the non-ferrous metal such as copper, lead, nickel is enriched with and separates;Residue after hydrochloric acid, chloroazotic acid leaching, filters and is directly separated plastic fraction respectively;Solution obtained by utilizing the composite containing heteroatomic conducting function macromolecular material or this conducting function macromolecule with Graphene to process, is enriched with and reduces precious metal ion, then obtains highly purified precious metal after high melt.Compared with prior art, the method is capable of multiple non-ferrous metal, such as copper, lead, nickel, stannum etc., and precious metal Au Ag Pt Pd, hydrargyrum etc. gradually, orderly recovery, substantially increase the number reclaiming metal and recycle efficiency, adequately achieving effective recycling of electron wastes.

Description

A kind of method reclaiming various metals from electron wastes
Technical field
The invention belongs to recycling of WEEE processing technology field, be specifically related to one and reclaim many from electron wastes Plant the coloured and method of precious metal.
Background technology
In recent years, China has been enter into the peak period that electronic product is eliminated, and the most at least to scrap and include 20,000,000 computers With 60,000,000 mobile phones at 2,300,000 tons of interior solid electronic rubbish, it it is the second-biggest-in-the-world electron wastes life being only second to the U.S. Produce state.Electron wastes (especially waste and old printed circuit board) contains substantial amounts of non-ferrous metal and gold, silver, palladium, platinum etc. expensive Heavy metal and rare metal, its grade is tens times of common primary ore, thus the recovery of electron wastes becomes current state The rising industry of inside and outside regenerated metal industry, contains huge economic worth.
The method of recycling electron wastes mainly includes Physical, chemical method and microbial method etc..Physical uses Between each component, the difference of physical property sorts, as utilized the method for broken, screening, electric separation and magnetic separation can realize discarded print In printed circuit board, gold, silver separate with ferrum, aluminum, zinc and stannum.Material after sorting need to could obtain metal through subsequent treatment, mould The regenerative raw materials such as material, glass, thus mainly as the auxiliary preprocessing means of additive method.Chemical method be divided into again pyrometallurgy and The techniques such as hydrometallurgy, are mainly used in purifying precious metal such as gold, ruthenium etc..Pyrometallurgy technology by burning, melting, sintering, The mode such as melted removes the plastics in electron wastes and other organic principles to carry out metal enrichment, can cause environment seriously Harm.Electronic waste composition granule after hydrometallurgical processes will crush is put in acidity or akaline liquid, then through extracting, sinking Form sediment, displacement, ion exchange, filter and a series of process such as distillation finally gives highly purified metal, but in removal process Waste liquid, waste gas and reclaim after waste residue the most serious to the pollution of environment.Biological technique method mainly utilizes certain micro-organisms The adsorption of the surface of solids and the Oxidation of microorganism make active metal become soluble substance enter solution, and then exposed also Extract the low content precious metal in electron wastes, there is the advantage that technique is simple, expense is low, easy to operate, but due to leaching The time that takes is longer, extraction rate is low, now still in research, the most really comes into operation.
It addition, metal species contained in most of electron wastes is various, such as include various non-ferrous metal (copper, lead, Nickel, stannum etc.) and precious metal (Au Ag Pt Pd, hydrargyrum, copper, stannum etc.), and current research focuses mostly on to single or few The recovery of several metals of number, carries out green reclaim gradually, in an orderly manner to various metals, returns improving the metal in electron wastes Research in terms of sowing class and organic efficiency is still rarely reported.
Summary of the invention
For the deficiency of above-mentioned existing recycling of WEEE technology, the present inventor explores through long term test, it is provided that A kind of method reclaiming various metals from electron wastes, utilizes the method to be capable of multiple non-ferrous metal, as copper, Lead, nickel, stannum etc., and precious metal Au Ag Pt Pd, chromium, hydrargyrum etc. gradually, green reclaim in an orderly manner, substantially increase institute Reclaim the number of metal, and substantially increase recycling efficiency, it is achieved that the abundant recycling of electron wastes.
The technical scheme is that a kind of method reclaiming various metals from electron wastes, as it is shown in figure 1, adopt With hydrometallurgical technology, leached by acid solution and separate various metal ingredient step by step, specifically comprise the following steps that
(1) Mechanical Crushing: electron wastes is crushed, it is thus achieved that particle diameter electronic waste between 0.05mm~5mm Composition granule;
(2) electronic waste composition granule is immersed in the aqueous solution of nitric acid that mass concentration is 3%~50% so that it is the gold contained by Belong to the reaction of one or more compositions in copper, nickel, lead, silver to be dissolved in aqueous solution of nitric acid, and metallic tin and nitric acid reaction generate solid State α stannic acid, filters and separates, and obtains the solution A of the metal ions such as solid slag X and cupric, nickel, lead, silver;
(3) solution A is carried out following process respectively with solid slag;
Solution A is handled as follows step (3-1) and (3-2):
(3-1) in solution A stirring add metal chloride inorganic salt so that it is in silver ion formed silver nitride precipitation analysis Go out;Filter and separate, obtain silver nitride precipitation and solution B;
(3-2) silver nitride precipitation recycling is obtained silver ion;In solution B, stirring adds Polyviologen family macromolecule Material so that it is in copper, lead, one or more in nickel ion form Precipitation with macromolecule complexation;Filter and separate, obtain Gu slag and solution C, Gu slag recycling obtains copper, lead, nickel ion, solution C recycling;
Gu slag X is handled as follows step (3-1 ') and (3-5 '):
(3-1 ') adds in the first aqueous hydrochloric acid solution in solid slag X so that it is in solid-state α stannic acid dissolve in the solution, mistake Filter separates, and obtains solid slag Y and solution D;
(3-2 ') is adding the second aqueous hydrochloric acid solution after solution D being concentrated, and separates out Tin tetrachloride pentahydrate, gained solution warp Recycling after concentration;Solid slag Y is immersed in wang aqueous solution so that it is the metallic element gold contained by, platinum, palladium, hydrargyrum, chromium are dissolved in Solution, filters and separates, and obtains solid slag Z and a kind of ion contained in gold, platinum, palladium, hydrargyrum, chromium ion or the solution E of several ion;
(3-3 ') adds carbamide in solution E, makes the nitric acid in solution E form urea nitrate precipitation, filters and separate, consolidate Slag urea nitrate and a kind of ion contained in gold, platinum, palladium, hydrargyrum, chromium ion or the solution F of several ion;Urea nitrate is reclaimed again Utilizing, added water or hydrochloric acid by solution F, make the pH value of this solution F be adjusted to 1~3, gold, platinum, palladium, hydrargyrum, the ion concentration of chromium are adjusted To 10~1000ppm;
Functional high molecule material is immersed in solution F by (3-4 ') so that it is in gold, platinum, palladium, hydrargyrum, one in chromium ion Ion or several ion are selectively adsorbed according to reduction potential from low to high on this functional polymer surface, and are reduced Adsorb on this functional polymer surface for elemental metals;Filter and separate, obtain the functional polymer of surface adsorption elemental metals with Solution F after process, repeats this step (3-4 ') for several times;Described functional polymer include but not limited to polyaniline, polypyrrole, Polythiophenes etc. are containing the one in heteroatomic macromolecular material and their ring substitutive derivative, heterosubstituted derivatives Or two or more compositionss;
The solution F that (3-5 ') obtains after step (3-4 ') processes carries out chlorine treatment and concentration, obtains chloroazotic acid Recycling, the functional polymer of surface adsorption elemental metals is placed in high melt in smelting furnace, obtain gold, platinum, palladium, hydrargyrum, One or several in chromium elemental metals.
Described electron wastes is the electron wastes after the useful components and parts such as battery, electric capacity, resistance are removed in dismounting, its Kind does not limits, the printed circuit board (PCB) such as including computer main board, computer memory bar, cell phone mainboard, bank card, public transport card, gate inhibition In the rfid card sheets such as card, the IC-card sheet such as SIM cards of mobile phones, IC phonecard and the leftover bits that produce when producing the said goods one Kind or two or more compositionss.
As preferably, in described step (2), electronic waste composition granule is 1 with the ratio of the quality volume of aqueous solution of nitric acid: 1~1:10 grams per milliliter;Reaction temperature is 50~70 DEG C, and the response time is 1~3 hour.
In described step (3-1), metal chloride inorganic salt includes but not limited to sodium chloride, potassium chloride, magnesium chloride, chlorine Change one or more the compositions in calcium, zinc chloride, copper chloride etc..As preferably, described metal chloride is inorganic Salt is 1:10~1:100 grams per milliliter with the ratio of the quality volume of nitrate solution A;Response time is 10~30 minutes.
In described step (3-2), Polyviologen macromolecule includes but not limited to that side chain contains the poly-of bipyridyl functional group Vinyl non-conjugate high molecular, polymethacrylic acid non-conjugate high molecular, polyimide non-conjugate high molecular and main chain In polysulfones non-conjugate high molecular containing bipyridyl functional group, polyfluorene class conjugated polymer one or more kinds of groups Compound.As preferably, the ratio of described Polyviologen family macromolecule material and the quality volume of solution B be 1:10~1:100 gram/ Milliliter;Response time is 10~30 minutes.
As preferably, in described step (3-1 '), in the first aqueous hydrochloric acid solution, the mass percent concentration of hydrochloric acid is 1% ~5%;Gu the ratio of the quality volume of slag X and the first aqueous hydrochloric acid solution is 1:1~1:10 grams per milliliter;Reaction temperature is 50~70 DEG C, the response time is 10~30 minutes;In second aqueous hydrochloric acid solution, the mass percent concentration of hydrochloric acid is preferably 5%~10%.
As preferably, in described step (3-2 '), in wang aqueous solution, chloroazotic acid is 1:1~1:10 with the volume ratio of water;Gu Slag Y is 1:1~1:10 grams per milliliter with the ratio of the quality volume of wang aqueous solution;Reaction temperature is 70~100 DEG C, and the response time is 30 minutes~3 hours.
In described step (3-2), Polyviologen family macromolecule material includes but not limited to duplex pyridine or terpyridyl One or more kinds of compositionss in the copolymer formed with the monomer such as fluorenes, acid imide, polyacrylic acid.Its form is not Limit, can be powder, thin film and cotton thread complex etc..
In described step (3-4 '), the form of functional high molecule material does not limits, and can be that powder, thin film and cotton thread are multiple Compound etc..Its chemical structural formula includes but not limited to following structural formula:
As preferably, in described step (3-4 '), functional polymer is 1:1~1 with the ratio of the quality volume of solution F: 100 grams per milliliters;Reaction temperature is 20~50 DEG C, and the response time is 30 minutes~6 hours.、
As preferably, the gas produced in described each step is by outlet pipe recycling.Such as, in step (2), in (3-2 ') and (8), the nitrogenous gas produced in course of reaction utilize after leading to chlorine treatment aqueous solution absorb prepare nitric acid, Nitrous acid recycles with hydrochloric acid weak solution.
The chemical reaction that in described step (2) to (3), acid solutions at different levels leaching relates to includes but not limited to:
3Ag+4HNO3→3Ag(NO3)+NO+2H2O (1)
3Cu+8HNO3→3Cu(NO3)2+4H2O+2NO (2)
Pb+2HNO3→Pb(NO3)2+H2 (3)
Ni+4HNO3→Ni(NO3)2+2H2O+2NO2 (4)
Sn+4HNO3→H2SnO3+H2O+4NO2 (5)
H2SnO3+6HCl→H2SnCl6+3H2O (6)
2HNO3+6HCl→2NO+4H2O+3Cl2 (7)
2Au+11HCl+3HNO3→2HAuCl4+3NOCl+6H2O (8)
3Pt+12HCl+2HNO3→3H2PtCl4+2NO+4H2O (9)
3Pd+6HCl+2HNO3→3PdCl2+2NO+4H2O (10)
2NO+Cl2→2NOCl (12)
2NO2+H2O→HNO2+HNO3 (13)
AuCl4 -+3e→Au+4Cl- (14)
PtCl4 2-+2e→Pt+4Cl- (15)
Pd2++2e→Pd (16)
The precious metal related in described step (3-1 ') to (3-5 ') and other gold that can be reduced by functional polymer Belonging to and include but not limited to Cr VI, gold, palladium, platinum, hydrargyrum, their reduction potential is: and chromium (+1.330 volts, Cr2O7 2-→Cr3+), Gold (+0.930 volt, AuCl4 -→Au 0), palladium (+0.915 volt, Pd2+→Pd0), platinum (+0.758 volt, PtCl4 2-→Pt0), Hydrargyrum (+0.850 volt, Hg2+→Hg0(liquid)), chromium (+0.300 volt, Cr6+→Cr3+).
The reversible electrochemical oxygen of the functional polymer including polyaniline etc. related in described step (3-1 ') to (3-5 ') Change reduction reaction to include but not limited to:
In described step (3-4 '), in order to improve further described functional high molecule material to gold, platinum, palladium, hydrargyrum, The absorbing and reducing ability of the elemental metals such as chromium, the inventors discovered that, can after being combined with Graphene by this functional high molecule material It is effectively improved its absorbing and reducing ability.This composite is specifically by polymer, i.e. this functional high molecule material is constituted with Graphene, Described polymer, with Graphene as carrier, is dispersed in graphene sheet layer body structure surface, therefore effectively prevent this conductive polymer The problems such as the reunion of sub-material, adhesion, increase the specific surface area of this conducting polymer composite;On the other hand, due to Graphene Having good electric conductivity, the composite therefore obtained after compound with Graphene also improves leading of this macromolecular material simultaneously Electrical property.Described polymer is polyaniline, polypyrrole, polythiophene, and the replacement of their ring substitutive derivative, hetero atom is spread out It is biological that (i.e. the ring substitutive derivative of polyaniline, heterosubstituted derivatives, the ring substitutive derivative of polypyrrole, hetero atom replace Derivant, the ring substitutive derivative of polythiophene, heterosubstituted derivatives) in one.
As further preferably, described functional polymer monomer is 1:100~1:10 with the mass ratio of Graphene.
Present invention also offers a kind of method preparing this functional polymer-graphene nanocomposite material, use Fig. 2 institute The route shown prepares, specific as follows:
(1) by polyaniline, polypyrrole, polythiophene and their ring substitutive derivative, heterosubstituted derivatives A kind of corresponding monomer is dissolved in alkene hydrochloric acid, obtains solution A;Graphene oxide powder or graphene oxide fiber are disperseed In deionized water, obtain solution B;Stirring mixed solution A and solution B, makes the two react, then filter or at a high speed from The heart, obtains the functional polymer-Graphene solid product of protonation;
On the one hand in above-mentioned course of reaction, due to graphene oxide there is oxidability, trigger monomer generation polyreaction, It is polymerized to phase emergencing copolymer;Meanwhile, under sour environment, graphene oxide is reduced to Graphene;Therefore, the two stirring mixing After this polymer be dispersed in graphene film Rotating fields.
In above-mentioned course of reaction, the preparation technology of optimization is as follows:
Described monomer is preferably 1:100~1:10 with the mass ratio of Graphene;
The molar concentration of described dilute hydrochloric acid is preferably 0.1M~1M;
In described solution A, monomer is preferably 1:10~1:100 with the volume ratio of dilute hydrochloric acid;
In described solution B, solid-to-liquid ratio is preferably 1:1~1:10;
Described reaction is preferably carried out at 60 DEG C~80 DEG C, reacts 6 hours~24 hours;
(2) functional polymer of protonation-Graphene solid product is utilized ammonia weak solution deprotonation, remained ammonia Remove with deionized water rinsing, be then vacuum dried, then through broken, screening, obtain functional polymer-graphene nano composite wood Material.
The concentration of described ammonia weak solution is preferably 0.1M~1M.
Described baking temperature is preferably 60 DEG C~100 DEG C.
It is experimentally confirmed that utilize the gold in this functional polymer-graphene nanocomposite material absorbing and reducing solution F, platinum, When palladium, hydrargyrum, chromium plasma, its organic efficiency is higher.Method particularly includes: by this functional polymer-graphene nanocomposite material Immerse in solution F so that it is in gold, platinum, palladium, hydrargyrum, a kind of ion in chromium ion or several ion according to reduction potential by Low paramount it is selectively adsorbed at this composite material surface, and is reduced to elemental metals and adsorbs at this composite material surface.
In sum, the invention provides a kind of eco-friendly process electron wastes optionally reclaiming various to have Color and the hydrometallurgical processes route of precious metal.This process route is: electron wastes after crushed, by multiple acid solution by Level leaching, effectively dissolves various metal ingredient and enters solution;Polyviologen functional high molecule material is utilized to process nitrate leaching The acid solution obtained, by with metalloform-selective ground complexation form coordination compound Precipitation, it is achieved copper, lead, nickel etc. The enrichment of non-ferrous metal with separate;Residue after hydrochloric acid, chloroazotic acid leaching, is directly separated plastic fraction by filtration respectively, thus Eliminate the conventional metals/nonmetallic ingredient sorting step such as magnetic separation, electric separation, selecting crude drugs with winnower;Then utilize containing heteroatomic conduction merit Solution obtained by the composite process of energy macromolecular material or this conducting function macromolecule and Graphene, it is possible to efficient, high The enrichment of selectivity, Non-energy-consumption ground the precious metal ion that reduces;Adsorb the macromolecular material of elemental metals after high melt Obtain the precious metal of high-purity (>=99.9%), and macromolecular material Direct Resolution when melting is that gas is discharged, without any Side-product produces.Compared with prior art, this process route is capable of multiple non-ferrous metal, such as copper, lead, nickel, stannum etc., with And precious metal Au Ag Pt Pd, hydrargyrum etc. gradually, orderly recovery, substantially increase the number of reclaimed metal, and greatly Improve greatly recycling efficiency, adequately achieve effective recycling of electron wastes, be therefore that a kind of electron wastes closes Reason, efficient recovery process route.
It addition, the method low cost, simple and environmental protection, it is embodied in: acid solution leaching is produced useless Liquid can be again with through concentration and recovery;Nitrogenous waste gas can obtain nitric acid, nitrous acid and hydrochloric acid weak solution after aqueous solution processes, Concentrated recovery can be again with;The organic polymer functional material used is nontoxic, and polyaniline, polypyrrole, poly-thiophene The conducting polymers such as fen can regenerate to reuse in containing auric acid liquid certainly, until complete failure;Waste gas and waste liquid can realize zero-emission Put, metal recovery rate and selectivity high, can effectively solve existing wet processing process use in a large number severe toxicity chemical reagent and waste gas, The problem that waste liquid, waste sludge discharge easily cause secondary pollution.
Therefore, the method for recovery electron wastes provided by the present invention is a kind of reasonable, efficient, method of environmental protection, real Show the dual purpose of environmental conservation and resource reclaim, it is adaptable to large-scale industry utilizes, and has a good application prospect.
Accompanying drawing explanation
Fig. 1 is the flow chart that the present invention reclaims various metals from electron wastes;
Fig. 2 is the synthetic route schematic diagram of conducting polymer-graphene nanocomposite material of the present invention;
Fig. 3 is the conducting function macromolecule used in embodiment of the present invention 1-3: polyaniline film, polypyrrole powder, and Polythiophene-cotton cord complex;
Fig. 4 is in the embodiment of the present invention 1 before the noble metal in polyaniline film absorbing and reducing electron wastes Acid leaching liquid After outside drawing;
Fig. 5 is the x-ray photoelectron energy spectrogram reclaiming the golden simple substance-polyaniline film obtained in the embodiment of the present invention 1;
Fig. 6 is the kinetics result of gold ion in solution F in the embodiment of the present invention 1 step (3-3 ') to (3-4 ');
Fig. 7 is the graphene oxide in the embodiment of the present invention 1, polyaniline and polyaniline-graphite alkene nano composite material X-ray photoelectron energy spectrogram;
Fig. 8 is the graphene oxide in the embodiment of the present invention 2, polypyrrole and polypyrrole-graphene nanocomposite material X-ray photoelectron energy spectrogram;
Fig. 9 is the graphene oxide in the embodiment of the present invention 3, polythiophene-graphene nanocomposite material and removes The x-ray photoelectron energy spectrogram of the reduced graphene of polythiophene component.
Detailed description of the invention
The present invention is described in further detail with embodiment below in conjunction with accompanying drawing.Only it should be understood that these embodiments For the present invention is described, rather than limit the scope of the present invention.
Embodiment 1:
In the present embodiment, electron wastes is Nokia 2100 circuit board of mobile phone, reclaims multiple from this electron wastes The method of metal is as follows:
(1) single discarded Nokia 2100 circuit board of mobile phone, weighs 22 grams, clipped broken particle diameter be 0.1mm~ The electronic waste composition granule of 0.5mm.
(2), after electronic waste composition granule being loaded eluting post, immersing mass percent concentration at 70 DEG C is the nitric acid of 30% In aqueous solution, solid-to-liquid ratio is 1:3 so that it is the metallic element copper contained by, nickel, lead, silver reaction are dissolved in aqueous solution of nitric acid, and its Metallic tin contained by generates solid-state α stannic acid with nitric acid reaction, filters and separates, obtain rich in metal ion after leaching 1 hour Nitrate solution A and solid slag X.
(3) nitrate solution A is handled as follows step (3-1) and (3-2):
(3-1) by solid-to-liquid ratio be 1:100 stir in nitrate solution addition sodium chloride so that it is in silver ion formed chlorine Change silver Precipitation, filter after stirring 10 minutes and separate, obtain silver nitride precipitation and solution B, silver nitride precipitation is recycled.
(3-2) it is that 1:100 adds polyacrylic acid-bipyridyl polymeric powder in solution B and stirs rapidly by solid-to-liquid ratio Dissolve, stir 30 minutes so that it is in one or more and macromolecule complexation in contained metallic element copper, lead, nickel plasma Form Precipitation, obtain solid slag and solution C, Gu slag recycling obtains copper, lead, nickel plasma, solution C recycling.
Gu slag is handled as follows step (3-1 ') and (3-5 '):
(3-1 ') in eluting post by solid-to-liquid ratio be 1:5 add quality mass percent concentration be 3.7% hydrochloric acid water-soluble Liquid, leaches 15 minutes at 60 DEG C, dissolves α stannic acid, filters and separates, obtains solid slag Y and solution D.
Solution D is concentrated and adds a large amount of aqueous hydrochloric acid solution by (3-2 '), forms Tin tetrachloride pentahydrate precipitation and from solution Middle precipitation, the concentrated rear recycling of gained solution.Eluting post is that 1:4 soaks at 90 DEG C with newly joining chloroazotic acid by solid-to-liquid ratio Take solid slag 1 hour so that it is in contained precious metal gold, platinum, palladium, hydrargyrum etc. be completely dissolved entrance solution, obtain solid slag Z and solution E.
(3-3 ') is that 1:5 adds carbamide in solution E by solid-to-liquid ratio, makes nitric acid and carbamide form urea nitrate precipitation and from molten Liquid separates out.Filtering and obtain solid slag urea nitrate and solution F after separating, dilute this solution F with dilute hydrochloric acid, regulation pH value, will to 1.3 The ion concentration of contained noble metal is adjusted to about 100ppm.
The solution that (3-4 ') obtains in 50 milliliters above-mentioned (3-3 ') adds be heavily the polyaniline film of 10 milligrams not Disconnected stirring, reacts 5 hours under room temperature, makes the absorption of precious metal composition at this film surface and be reduced.Filter and separate, obtain table Solution F after the polyaniline film of face adsorbing metal simple substance and process, repeats this step (3-4 '), will this surface adsorption simple substance The functional polymer of metal is again dipped in the solution F after processing, and makes the precious metal composition in solution adsorb at this thin film table Face is also reduced, and so repeats 3 to 5 times;
Comparison diagram before and after this polyaniline film adsorbing metal simple substance is as shown in Figure 4, it can be seen that after adsorbing metal simple substance This thin film presents metallic luster.Learn through X-ray photoelectron spectroscopic analysis, be adsorbed in the metal ingredient of this polymer surface Including gold, platinum, palladium, all simple substance of these metal ingredients, such as it is illustrated in figure 5 the X-ray light reclaiming the golden simple substance obtained Electronic energy spectrum.
The functional polymer of surface adsorption elemental metals is placed in high melt in smelting furnace by (3-5 '), and organic component is complete Being decomposed into gas to discharge, precious metal forms microparticle retention in crucible.After processing the solution F that obtains carry out chlorine treatment with And concentration, obtain chloroazotic acid recycling.
During Fig. 6 is step (3-3 ') to (3-4 '), the precious metal composition in solution adsorbs at this film surface also It is reduced the kinetics interpretation of result figure of the gold ion of 1 time.It can be seen that GOLD FROM PLATING SOLUTION ion concentration dropped in 5 hours To below 2ppm, the response rate is close to 100%.
Above-mentioned reclaimed non-ferrous metal and precious metal are analyzed further and learns, above-mentioned each Nokia 2100 mobile phone Circuit board reclaims about 15 milligrams of gold, 0.5 milligram of platinum, 2 milligrams of palladiums, 37.5 milligrams of silver, 0.75 gram of stannum and 3 grams of copper.
In above-mentioned recovery method, the gas produced in each step is by outlet pipe recycling.Such as, in step (2), in (3-2 ') and (8), the nitrogenous gas produced in course of reaction utilize after leading to chlorine treatment aqueous solution absorb prepare nitric acid, Nitrous acid recycles with hydrochloric acid weak solution.Reuse after the concentrated recovery of nitric acid waste.Containing acid waste liquid through chlorine treatment with And reuse after concentration regeneration chloroazotic acid.
In order to improve the functional high molecule material absorbing and reducing to precious metal composition in above-mentioned steps (3-4 ') further Ability, in the present embodiment step (3-4 '), it is also possible to the composite preferably employing polyaniline and Graphene carries out absorbing and reducing. Composite is made up of with Graphene polyaniline, and polyaniline, with Graphene as carrier, is dispersed in graphene sheet layer body structure surface, structure Become polyaniline-graphite alkene nano composite material.As preferably, this functional polymer monomer is 1:100 with the mass ratio of Graphene ~1:10.
The preparation method of this polyaniline-graphite alkene nano composite material is as follows:
(1) 1ml aniline monomer is sufficiently mixed with the hydrochloric acid weak solution that 10ml concentration is 1M, obtains aniline hydrochloric acid dilute molten Liquid;100mg graphene oxide powder or fiber are scattered in 100ml deionized water, then aniline hydrochloric acid weak solution are added Wherein stir, then high degree of agitation at 70 DEG C, react 12 hours, at a high speed by mixture with the rotating speed of 12000rpm finally Centrifugal 10 minutes, obtain the polyaniline-graphite alkene complex precipitate of protonation;
(2) the ammonia weak solution that 200ml concentration is 0.5M is utilized to go the polyaniline-graphite alkene complex precipitate of protonation Protonation, then removes excessive ammonia with a large amount of deionized water rinsings, is then vacuum dried at 60 DEG C, then through broken, screening, I.e. obtain polyaniline-graphite alkene nano composite material.
Above-mentioned graphene oxide, polyaniline and the x-ray photoelectron of prepared polyaniline-graphite alkene nano composite material Can spectrogram as it is shown in fig. 7, there it can be seen that obtained by Graphene has been reduced to low-oxidation-state, and polyaniline exists in Nano composite material in.
In above-mentioned steps (3-4 '), this polyaniline is used to replace polyaniline film to carry out reality with the composite of Graphene Test, and the response time is 2 hours, particularly as follows:
Adding in the solution obtained in 50 milliliters above-mentioned (3-3 ') is heavily the answering of this polyaniline and Graphene of 10 milligrams Condensation material is also stirred continuously, and reacts 5 hours under room temperature, makes the absorption of precious metal composition at this film surface and be reduced.Filter Separate, the solution F after obtaining the polyaniline film of surface adsorption metal simple-substance and processing, repeat this step (3-4 ') 3 to 5 times, The functional polymer of this surface adsorption elemental metals will be again dipped in the solution F after processing, make the precious metal in solution Composition absorption at this film surface and is reduced.
Comparison diagram before and after this polyaniline composite material film adsorbing metal simple substance with Graphene is it can be seen that adsorb After metal simple-substance, this thin film presents metallic luster.Learn through X-ray photoelectron spectroscopic analysis, be adsorbed in this polymer surface Metal ingredient include gold, platinum, palladium, all simple substance of these metal ingredients.Step (3-3 ') to (3-4 ') is obtained through mensuration During, the absorption of precious metal composition in solution can in the kinetics of this film surface the gold ion that is reduced 1 time Knowing, GOLD FROM PLATING SOLUTION ion concentration was down to below 2ppm in 2 hours, and the response rate is close to 100%.That is, polyaniline-graphite alkene is utilized Nano composite material is higher than the response rate utilizing polyaniline material to the response rate of gold ion.In like manner, mensuration is obtained by gathering Aniline-graphene nanocomposite material is higher than the response rate utilizing polyaniline material to the response rate of platinum, palladium ion.
Embodiment 2:
In the present embodiment, electron wastes is certain discarded bank IC card, reclaims various metals from this electron wastes Method is as follows:
(1) certain discarded bank IC card, clipped broken to obtain the electronic waste composition granule that particle diameter is 0.5mm~1mm.
(2), after electronic waste composition granule being loaded eluting post, immersing mass percent concentration at 70 DEG C is the nitric acid of 3% In aqueous solution, solid-to-liquid ratio is 1:1 so that it is the metallic element copper contained by, nickel, lead, silver reaction are dissolved in aqueous solution of nitric acid, and its Metallic tin contained by generates solid-state α stannic acid with nitric acid reaction, filters and separates, obtain rich in metal ion after leaching 3 hours Nitrate solution A and solid slag X.
(3) nitrate solution A is handled as follows step (3-1) and (3-2):
(3-1) by solid-to-liquid ratio be 1:100 stir in nitrate solution addition sodium chloride so that it is in silver ion formed chlorine Change silver Precipitation, filter after stirring 10 minutes and separate, obtain silver chloride and solution B, silver nitride precipitation is recycled.
(3-2) it is that 1:100 adds polyimides-bipyridyl polymeric particles in solution B by solid-to-liquid ratio, stirs 10 points Clock so that it is in one or more in contained metallic element copper, lead, nickel plasma form Precipitation with macromolecule complexation, Obtain solid slag and solution C, Gu slag recycling obtains copper, lead, nickel plasma, solution C recycling.
Gu slag is handled as follows step (3-1 ') and (3-5 '):
(3-1 ') in eluting post by solid-to-liquid ratio be 1:1 add mass percent fraction concentration be 3.7% hydrochloric acid water-soluble Liquid, leaches 30 minutes at 70 DEG C, dissolves α stannic acid, filters and separates, obtains solid slag Y and solution D.
Solution D is concentrated and adds a large amount of aqueous hydrochloric acid solution by (3-2 '), forms Tin tetrachloride pentahydrate precipitation and from solution Middle precipitation, the concentrated rear recycling of gained solution.In eluting post by chloroazotic acid by solid-to-liquid ratio be 1:1 close to 100 DEG C (or Close to boiling) at a temperature of the solid slag of leaching 3 hours, acid in chloroazotic acid: water ratio is for 1:10 so that it is in contained precious metal gold, platinum, Palladium, hydrargyrum etc. are completely dissolved entrance solution, obtain solid slag Z and solution E.
(3-3 ') is that 1:1 adds carbamide in solution E by solid-to-liquid ratio, makes nitric acid and carbamide form urea nitrate precipitation and from molten Liquid separates out.Filtering and obtain solid slag urea nitrate and solution F after separating, dilute this solution F with dilute hydrochloric acid, regulation pH value is to 1, by institute The ion concentration of the noble metal contained is adjusted to about 100ppm.
Adding in the solution that (3-4 ') obtains in 50 milliliters of above-mentioned steps (3-3 ') solution is heavily the polypyrrole of 10 milligrams Powder is also stirred continuously, and reacts 1 hour, make precious metal composition all adsorb at powder particle surface and be reduced under room temperature. Filter and separate, the solution F after obtaining the polypyrrole powder of surface adsorption metal simple-substance and processing, repeats this step (3-4 '), i.e. The functional polymer of this surface adsorption elemental metals is again dipped in the solution F after processing, makes the precious metal in solution become Divide absorption on this polypyrrole powder surface and to be reduced, so repeat 3 to 5 times;
The polypyrrole powder of surface adsorption elemental metals is placed in high melt in smelting furnace by (3-5 '), and organic component is complete Being decomposed into gas to discharge, precious metal forms microparticle retention in crucible.After processing the solution F that obtains carry out chlorine treatment with And concentration, obtain chloroazotic acid recycling.
Above-mentioned reclaimed non-ferrous metal and precious metal are learnt through analyzing further, above-mentioned each IC-card reclaims about 2 milligrams of gold, 0.2 gram of stannum and 0.5 gram of copper.
In above-mentioned recovery method, the gas produced in each step is by outlet pipe recycling.Such as, in step (2), in (3-2 ') and (8), the nitrogenous gas produced in course of reaction utilize after leading to chlorine treatment aqueous solution absorb prepare nitric acid, Nitrous acid recycles with hydrochloric acid weak solution.Reuse after the concentrated recovery of nitric acid waste.Containing acid waste liquid through chlorine treatment with And concentration regenerates chloroazotic acid and reuses.
In order to improve the functional high molecule material absorbing and reducing to precious metal composition in above-mentioned steps (3-4 ') further Ability, in the present embodiment step (3-4 '), it is also possible to the composite preferably employing polypyrrole and Graphene carries out absorbing and reducing. Composite is made up of with Graphene polyaniline, and polyaniline, with Graphene as carrier, is dispersed in graphene sheet layer body structure surface, structure Become polyaniline-graphite alkene nano composite material.As preferably, this functional polymer monomer is 1:100 with the mass ratio of Graphene ~1:10.
The preparation method of this polyaniline-graphite alkene nano composite material is as follows:
(1) 1ml pyrrole monomer is sufficiently mixed with the hydrochloric acid weak solution that 50ml concentration is 1M, obtains pyrroles's hydrochloric acid dilute molten Liquid;100mg graphene oxide powder or fiber are scattered in 500ml deionized water, then pyrroles's hydrochloric acid weak solution are added Wherein stir, then high degree of agitation at 80 DEG C, react 6 hours, finally mixture is separated with filter type, obtain matter The polypyrrole of sonization-graphene complex precipitation;
(2) the ammonia weak solution that 200ml concentration is 0.5M is utilized to go the polypyrrole of protonation-graphene complex precipitation Protonation, then removes excessive ammonia with a large amount of deionized water rinsings, is then vacuum dried at 70 DEG C, then through broken, screening, I.e. obtain polypyrrole-graphene nanocomposite material.
Above-mentioned graphene oxide, polypyrrole and the x-ray photoelectron of prepared polypyrrole-graphene nanocomposite material As shown in Figure 8, there it can be seen that Graphene has been reduced to low-oxidation-state, and polypyrrole exists in obtained energy spectrogram Nano composite material in.
In above-mentioned steps (3-4 '), this polypyrrole is used to replace film of poly pyrrole to carry out reality with the composite of Graphene Test, and the response time is 0.5 hour, particularly as follows:
Adding in the solution obtained in 50 milliliters of above-mentioned steps (3-3 ') solution is heavily polypyrrole and the graphite of 10 milligrams The composite of alkene is also stirred continuously, and reacts 0.5 hour, make precious metal composition all adsorb at powder particle surface under room temperature And be reduced.Filter and separate, the solution F after obtaining the polypyrrole powder of surface adsorption metal simple-substance and processing, repeats this step (3-4 '), will the functional polymer of this surface adsorption elemental metals be again dipped in the solution F after processing, and make in solution is expensive Heavy metal component absorption on this polypyrrole powder surface and is reduced, and so repeats 3 to 5 times;
Comparison diagram before and after this polypyrrole composite material film adsorbing metal simple substance with Graphene is it can be seen that adsorb After metal simple-substance, this thin film presents metallic luster.Learn through X-ray photoelectron spectroscopic analysis, be adsorbed in this polymer surface Metal ingredient be modern, all simple substance of this metal ingredient.During mensuration obtains step (3-3 ') to (3-4 '), solution In precious metal composition absorption this film surface and be reduced 1 time gold ion kinetics understand, utilize polyphenyl Amine-graphene nanocomposite material is higher than the response rate utilizing polyaniline material to the response rate of gold ion.
Embodiment 3:
In the present embodiment, electron wastes is to give up in the corner producing printed circuit board (PCB), rfid card sheet and the generation of IC-card sheet Material, the process reclaiming various metals from this electron wastes is as follows:
(1) leftover bits that produce when producing printed circuit board (PCB), rfid card sheet and IC-card sheet etc. are clipped broken to obtain grain Footpath is the electronic waste composition granule of 1mm~5mm.
(2), after electronic waste composition granule being loaded eluting post, immersing mass percent concentration at 50 DEG C is the nitric acid of 50% In aqueous solution, solid-to-liquid ratio is 1:10 so that it is the metallic element copper contained by, nickel, lead, silver reaction are dissolved in aqueous solution of nitric acid, and Metallic tin contained therein generates solid-state α stannic acid with nitric acid reaction, filters and separates, obtain rich in metal ion after leaching 1 hour Nitrate solution A and solid slag X.
(3) nitrate solution A is handled as follows step (3-1) and (3-2):
(3-1) by solid-to-liquid ratio be 1:100 stir in nitrate solution addition sodium chloride so that it is in silver ion formed chlorine Change silver Precipitation, filter after stirring 30 minutes and separate, obtain silver nitride precipitation and solution B, silver nitride precipitation is recycled.
(3-2) it is that 1:100 adds chitin-bipyridyl powder rapidly stirring and dissolving, stirring in solution B by solid-to-liquid ratio 30 minutes so that it is in one or more in contained metallic element copper, lead, nickel plasma form precipitation analysis with macromolecule complexation Go out rear copper ion all with macromolecule complexation form Precipitation, obtain solid slag and solution C, Gu slag recycling obtain copper, Lead, nickel plasma, solution C recycling.
Gu slag is handled as follows step (3-1 ') and (3-5 '):
(3-1 ') in eluting post by solid-to-liquid ratio be 1:10 add mass percent concentration be the aqueous hydrochloric acid solution of 3.7%, Leach 15 minutes at 50 DEG C, dissolve α stannic acid, filter and separate, obtain solid slag Y and solution D.
Solution D is concentrated and adds a large amount of aqueous hydrochloric acid solution by (3-2 '), forms Tin tetrachloride pentahydrate precipitation and from solution Middle precipitation, the concentrated rear recycling of gained solution.Chloroazotic acid diluent is that 1:10 is at 70 DEG C by solid-to-liquid ratio by eluting post The solid slag of lower leaching 30 minutes, acid in chloroazotic acid diluent: water ratio is for 1:1 so that it is in contained precious metal gold, platinum, palladium, hydrargyrum etc. complete CL, obtains solid slag Z and solution E.
(3-3 ') is that 1:10 adds carbamide in E solution by solid-to-liquid ratio, make nitric acid and carbamide formed urea nitrate precipitation and from Solution separates out.Filtering and obtain solid slag urea nitrate and solution F, dilute with water this solution F after separating, regulation pH value is to 3, by contained The ion concentration of noble metal be adjusted to about 1000ppm.
Adding in the solution that (3-4 ') obtains in 50 milliliters of above-mentioned steps (3-3 ') is heavily the polythiophene-cotton cord of 50 milligrams Complex is also stirred continuously, and reacts 30 minutes, make precious metal composition all adsorb at this polythiophene-cotton cord complex under room temperature Surface is also reduced.Filter and separate, the solution F after obtaining the polyaniline film of surface adsorption metal simple-substance and processing, repeats this Step (3-4 '), the functional polymer of this surface adsorption elemental metals will be again dipped in the solution F after processing, makes in solution The absorption of precious metal composition in this polythiophene-cotton cord composite surface and be reduced, so repeat 3 to 5 times;
The polythiophene of surface adsorption elemental metals-cotton cord complex is placed in high melt in smelting furnace by (3-5 '), organic Component is completely decomposed into gas and discharges, and precious metal forms microparticle retention in crucible.The solution F obtained after processing carries out chlorine Gas disposal and concentration, obtain chloroazotic acid recycling.
Above-mentioned reclaimed non-ferrous metal and precious metal are analyzed further and learns, above-mentioned per kilogram leftover bits return Receive about 80 milligrams of palladiums, 0.45 gram of gold, 2 grams of silver, 20 grams of stannum and 130 grams of copper.
In above-mentioned removal process, the gas produced in each step is by outlet pipe recycling.Such as, in step (2), in (3-2 ') and (8), the nitrogenous gas produced in course of reaction utilize after leading to chlorine treatment aqueous solution absorb prepare nitric acid, Nitrous acid recycles with hydrochloric acid weak solution.Reuse after the concentrated recovery of nitric acid waste.Containing acid waste liquid through chlorine treatment with And reuse after concentration regeneration chloroazotic acid.
In order to improve the functional high molecule material absorbing and reducing to precious metal composition in above-mentioned steps (3-4 ') further Ability, in the present embodiment step (3-4 '), it is also possible to the composite preferably employing polythiophene and Graphene carries out absorbing and reducing. Composite is made up of with Graphene polythiophene, and polythiophene, with Graphene as carrier, is dispersed in graphene sheet layer body structure surface, structure Become polythiophene-graphene nanocomposite material.As preferably, this functional polymer monomer is 1:100 with the mass ratio of Graphene ~1:10.
The preparation method of this polythiophene-graphene nanocomposite material is as follows:
(1) 1g thiophene monomer is sufficiently mixed with the hydrochloric acid weak solution that 100ml concentration is 1M, obtains thiophene hydrochloric acid dilute molten Liquid;100mg graphene oxide powder or fiber are scattered in 1000ml deionized water, then thiophene hydrochloric acid weak solution are added Wherein stirring, then high degree of agitation at 90 DEG C, mixture, after 24 hours, is finally separated by question response with filter type, Obtain the polythiophene-graphene complex precipitation of protonation;
(2) the ammonia weak solution that 200ml concentration is 0.5M is utilized to go the polythiophene of protonation-graphene complex precipitation Protonation, then removes excessive ammonia with a large amount of deionized water rinsings, is then vacuum dried at 80 DEG C, then through broken, screening, I.e. can get polypyrrole-graphene nanocomposite material.
Above-mentioned graphene oxide, prepared polythiophene-graphene nanocomposite material, and use organic solvent this to be gathered Polythiophene in thiophene-graphene nanocomposite material passes through the x-ray photoelectron of the reduced graphene being dried to obtain after removing Can spectrogram as it is shown in figure 9, there it can be seen that obtained by Graphene has been reduced to low-oxidation-state, and polythiophene exists in Nano composite material in.
In above-mentioned steps (3-4 '), this polythiophene is used to replace polythiophene film to carry out reality with the composite of Graphene Test, and the response time is 10 minutes, particularly as follows:
Adding in the solution obtained in 50 milliliters of above-mentioned steps (3-3 ') solution is heavily polythiophene and the graphite of 10 milligrams The composite of alkene is also stirred continuously, and reacts 0.5 hour, make precious metal composition all adsorb at powder particle surface under room temperature And be reduced.Filter and separate, the solution F after obtaining the polythiophene powder of surface adsorption metal simple-substance and processing, repeats this step (3-4 '), will the functional polymer of this surface adsorption elemental metals be again dipped in the solution F after processing, and make in solution is expensive Heavy metal component absorption on this polythiophene powder surface and is reduced, and so repeats 3 to 5 times;
Comparison diagram before and after this polythiophene composite material film adsorbing metal simple substance with Graphene is it can be seen that adsorb After metal simple-substance, this thin film presents metallic luster.Learn through X-ray photoelectron spectroscopic analysis, be adsorbed in this polymer surface Metal ingredient include gold, palladium, all simple substance of these metal ingredients.Step (3-3 ') to (3-4 ') process is obtained through mensuration In, the absorption of precious metal composition in solution understands in the kinetics of this film surface the gold ion that is reduced 1 time, profit With polythiophene-graphene nanocomposite material the response rate of gold ion is higher than the response rate utilizing polythiophene material.
Technical scheme has been described in detail by embodiment described above, it should be understood that the above is only For the specific embodiment of the present invention, be not limited to the present invention, all made in the spirit of the present invention any amendment, Supplement or similar fashion replacement etc., should be included within the scope of the present invention.

Claims (10)

1. the method reclaiming various metals from electron wastes, described various metals include copper, lead, nickel, stannum, gold, At least one in silver, platinum, palladium, chromium, hydrargyrum, is characterized in that: specifically comprise the following steps that
(1) Mechanical Crushing: electron wastes is crushed, it is thus achieved that particle diameter is the electronic waste composition granule of 0.05mm~5mm;
(2) electronic waste composition granule is immersed in the aqueous solution of nitric acid that mass concentration is 3%~50% so that it is the metal contained by Copper, nickel, lead, silver composition reaction are dissolved in aqueous solution of nitric acid, and metallic tin and nitric acid reaction generate solid-state α stannic acid, then filtration point From, obtain solid slag X and cupric, nickel, lead, the solution A of silver ion;
(3) solution A is handled as follows step (3-1) and (3-2):
(3-1) in solution A stirring add metal chloride inorganic salt so that it is in silver ion formed silver nitride precipitation separate out; Filter and separate, obtain silver nitride precipitation and solution B;
(3-2) silver nitride precipitation recycling is obtained silver ion;In solution B, stirring adds Polyviologen family macromolecule material Material so that it is the copper contained by, lead, nickel ion form Precipitation with macromolecule complexation;Filter and separate, obtain solid slag and solution C, Gu slag recycling obtains copper, lead, nickel ion, solution C recycling;
Gu slag X is handled as follows step (3-1 ') to (3-5 '):
(3-1 ') adds the first aqueous hydrochloric acid solution in solid slag X so that it is in solid-state α stannic acid dissolve in the solution, filter separate, Obtain solid slag Y and solution D;
(3-2 ') adds the second aqueous hydrochloric acid solution after solution D being concentrated, separate out Tin tetrachloride pentahydrate, after gained solution is concentrated Recycling;Solid slag Y is immersed in wang aqueous solution so that it is in one in contained metallic element gold, platinum, palladium, chromium, hydrargyrum or Several solution that is dissolved in of person, filters and separates, and obtains solid slag Z and contains gold, platinum, palladium, chromium, the solution E of mercury ion;
(3-3 ') adds carbamide in solution E, makes the nitric acid in solution E form urea nitrate precipitation, filters and separate, obtain solid slag nitre Acid urea with containing gold, platinum, palladium, chromium, the solution F of mercury ion;By urea nitrate recycling, solution F is added water or hydrochloric acid, makes The pH value of this solution F is adjusted to 1~3, and gold, platinum, palladium, chromium, the ion concentration of hydrargyrum are adjusted to 10~1000ppm;
Functional high molecule material is immersed in solution F by (3-4 ') so that it is in gold, platinum, palladium, chromium, mercury ion is according to reduction potential It is selectively adsorbed from low to high on this functional polymer surface, and is reduced to elemental metals absorption at this functional polymer Surface;Filter and separate, the solution F after obtaining the functional polymer of surface adsorption elemental metals and processing, repeats this step (3- 4 ') for several times;Described functional high molecule material is polyaniline, polypyrrole, polythiophene and their ring substitutive derivative, miscellaneous former One or more kinds of compositionss in sub-substitutive derivative, or, described functional high molecule material be polymer with The composite that Graphene is constituted, wherein Graphene is carrier, and polymer is dispersed in graphene sheet layer body structure surface, this polymer For polyaniline, polypyrrole, polythiophene, and their ring substitutive derivative, heterosubstituted derivatives (i.e. the ring of polyaniline takes For derivant, heterosubstituted derivatives, the ring substitutive derivative of polypyrrole, heterosubstituted derivatives, the ring of polythiophene takes For derivant, heterosubstituted derivatives) in one;
The solution F that (3-5 ') obtains after step (3-4 ') processes carries out chlorine treatment and concentration, obtains chloroazotic acid and reclaims Recycling, the functional polymer of surface adsorption elemental metals is placed in high melt in smelting furnace, obtains gold, platinum, palladium, chromium, hydrargyrum list Matter metal.
2. the method reclaiming various metals from electron wastes as claimed in claim 1, is characterized in that: described each step The gas of middle generation passes through outlet pipe recycling.
3. the method reclaiming various metals from electron wastes as claimed in claim 1, is characterized in that: described step (3-1), in, metal chloride inorganic salt includes the one in sodium chloride, potassium chloride, magnesium chloride, calcium chloride, zinc chloride, copper chloride Or two or more compositionss.
4. the method reclaiming various metals from electron wastes as claimed in claim 1, is characterized in that: described step (3-2), in, Polyviologen family macromolecule includes the polyethylene kind non-conjugate high molecular that side chain contains bipyridyl functional group, poly-methyl The polysulfones that acrylic compounds non-conjugate high molecular, polyimide non-conjugate high molecular and main chain contain bipyridyl functional group is non- One or more kinds of compositionss in conjugated polymer, polyfluorene class conjugated polymer.
5. the method reclaiming various metals from electron wastes as described in any claim in Claims 1-4, it is special Levying and be: in described step (2), the ratio of electronic waste composition granule and the quality volume of aqueous solution of nitric acid is 1:1~1:10 gram/in the least Rise;Reaction temperature is 50~70 DEG C.
6. the method reclaiming various metals from electron wastes as described in any claim in Claims 1-4, it is special Levying and be: in described step (3-1), metal chloride inorganic salt is 1:10~1 with the ratio of the quality volume of nitrate solution A: 100 grams per milliliters.
7. the method reclaiming various metals from electron wastes as described in any claim in Claims 1-4, it is special Levying and be: in described step (3-2), described Polyviologen family macromolecule material is 1:10 with the ratio of the quality volume of solution B ~1:100 grams per milliliter.
8. the method reclaiming various metals from electron wastes as described in any claim in Claims 1-4, it is special Levying and be: in described step (3-1 '), in the first aqueous hydrochloric acid solution, the mass percent concentration of hydrochloric acid is 1%~5%;Gu slag X It is 1:1~1:10 grams per milliliter with the ratio of the quality volume of the first aqueous hydrochloric acid solution;Reaction temperature is 50~70 DEG C;Second hydrochloric acid In aqueous solution, the mass percent concentration of hydrochloric acid is preferably 5%~10%.
9. the method reclaiming various metals from electron wastes as described in any claim in Claims 1-4, it is special Levying and be: in described step (3-2 '), in wang aqueous solution, chloroazotic acid is 1:1~1:10 with the volume ratio of water;Gu slag Y and wang aqueous solution The ratio of quality volume be 1:1~1:10 grams per milliliter;Reaction temperature is 70~100 DEG C.
10. the method reclaiming various metals from electron wastes as described in any claim in Claims 1-4, its Feature is: in described step (3-4 '), and functional polymer is 1:1~1:100 grams per milliliter with the ratio of the quality volume of solution F; Reaction temperature is 20~50 DEG C.
CN201310549957.7A 2013-11-07 2013-11-07 A kind of method reclaiming various metals from electron wastes Active CN104630479B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310549957.7A CN104630479B (en) 2013-11-07 2013-11-07 A kind of method reclaiming various metals from electron wastes

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310549957.7A CN104630479B (en) 2013-11-07 2013-11-07 A kind of method reclaiming various metals from electron wastes

Publications (2)

Publication Number Publication Date
CN104630479A CN104630479A (en) 2015-05-20
CN104630479B true CN104630479B (en) 2016-08-17

Family

ID=53209722

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310549957.7A Active CN104630479B (en) 2013-11-07 2013-11-07 A kind of method reclaiming various metals from electron wastes

Country Status (1)

Country Link
CN (1) CN104630479B (en)

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105506289B (en) * 2015-11-24 2018-01-26 四川长虹格润再生资源有限责任公司 The recovery method of gold and silver in waste and old printed board
CN108346715A (en) * 2018-02-09 2018-07-31 中南大学 The recovery method of silicon solar cell
CN111630193B (en) * 2018-02-09 2022-05-03 贺利氏德国有限两合公司 Method for processing noble metal-tin alloy by wet metallurgy
CN113355515A (en) * 2021-05-26 2021-09-07 昆明理工大学 Method for separating tin-silver alloy by chlorination
CN113403478B (en) * 2021-06-15 2024-01-26 苏州市富荣环保科技有限公司 Method for separating metal from electronic waste based on nano carbon material
WO2023087114A1 (en) * 2021-11-22 2023-05-25 Pyrocycle Inc. A process for recovering a metallic fraction from electronic waste and producing value-added products
CN115282945B (en) * 2022-07-15 2023-12-08 宁波新材料测试评价中心有限公司 Application of polyimide resin powder containing sulfonic acid group as solid phase extraction material
CN115181327A (en) * 2022-08-30 2022-10-14 湖北恒驰电子科技有限公司 Method for recycling waste multiphase flexible copper clad laminate by subcritical technology

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5368632A (en) * 1993-04-06 1994-11-29 Board Of Regents, The University Of Texas System Redox polymer films for metal recovery applications
CN1718784A (en) * 2005-07-07 2006-01-11 孙涛 Method of recovery copper, nickel and noble metal in waste water and slag by combined technology of wet method and fire method
CN101311280A (en) * 2007-05-24 2008-11-26 董蜀希 Process for recovering non-ferrous metal and noble metal from electronic waste material
CN101575715A (en) * 2009-06-22 2009-11-11 中南大学 Method for extracting valuable metals from electronic waste

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5368632A (en) * 1993-04-06 1994-11-29 Board Of Regents, The University Of Texas System Redox polymer films for metal recovery applications
CN1718784A (en) * 2005-07-07 2006-01-11 孙涛 Method of recovery copper, nickel and noble metal in waste water and slag by combined technology of wet method and fire method
CN101311280A (en) * 2007-05-24 2008-11-26 董蜀希 Process for recovering non-ferrous metal and noble metal from electronic waste material
CN101575715A (en) * 2009-06-22 2009-11-11 中南大学 Method for extracting valuable metals from electronic waste

Also Published As

Publication number Publication date
CN104630479A (en) 2015-05-20

Similar Documents

Publication Publication Date Title
CN104630479B (en) A kind of method reclaiming various metals from electron wastes
Ashiq et al. Hydrometallurgical recovery of metals from e-waste
Rao et al. Challenges and opportunities in the recovery of gold from electronic waste
Gunarathne et al. Hydrometallurgical processes for heavy metals recovery from industrial sludges
CN104629360A (en) Conductive polymer-graphene nanocomposite material, and preparation method and use thereof
Cui et al. Metallurgical recovery of metals from electronic waste: A review
Muir et al. Thiosulphate as an alternative to cyanide for gold processing–issues and impediments
CN101392325B (en) Method for extracting gold from waste printed circuit board
CN104549147A (en) Preparation method and application of activated carbon for recycling gold
CN107400780A (en) A kind of method that gold, silver and bronze are extracted in the plate from cell phone lines
CN103114202B (en) Comprehensive recovery process for environment-friendly type refractory gold-silver ore multi-metals
CN109852816B (en) Method for adsorbing noble metal complex ions in thiosulfate leaching solution by sulfide ore
Do et al. Advances in hydrometallurgical approaches for gold recovery from E-waste: A comprehensive review and perspectives
Rezaee et al. A cleaner approach for high-efficiency regeneration of base and precious metals from waste printed circuit boards through stepwise oxido-acidic and thiocyanate leaching
CN113667833A (en) Purification and cadmium removal method for zinc hydrometallurgy
US5411573A (en) Recovery of precious metals from acid solutions by N-containing electroactive polymers
CN114134337B (en) Low-cost and high-efficiency method for recovering noble metal in circuit board components
Duan et al. Recent advances in recovering technology for recycling gold from waste printed circuit boards: a review
Ashiq et al. Electrochemical enhanced metal extraction from E-waste
CN104073639A (en) Method for recycling copper and gold from waste electronic material through two-step method
CN104629047A (en) Conductive polymer-supporter composite material, preparation method and applications
CN109652658B (en) Method for recovering noble metal complex ions from thiosulfate leaching solution by utilizing sulfide ore
CN106148704B (en) One kind recycles gold from waste mobile phone electronic component(Au)Method
CN104745819B (en) Utilize the method that metal is reclaimed in conducting polymer nanometer spinning from electron wastes
Xia et al. Sustainable technologies for the recycling and upcycling of precious metals from e-waste

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant