CN105112674B - A kind of waste printed circuit board Whote-wet method recovery process - Google Patents

A kind of waste printed circuit board Whote-wet method recovery process Download PDF

Info

Publication number
CN105112674B
CN105112674B CN201510598245.3A CN201510598245A CN105112674B CN 105112674 B CN105112674 B CN 105112674B CN 201510598245 A CN201510598245 A CN 201510598245A CN 105112674 B CN105112674 B CN 105112674B
Authority
CN
China
Prior art keywords
circuit board
liquid
printed circuit
acid
waste printed
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
CN201510598245.3A
Other languages
Chinese (zh)
Other versions
CN105112674A (en
Inventor
郭学益
李栋
秦红
刘旸
田庆华
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.)
Central South University
Original Assignee
Central South University
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 Central South University filed Critical Central South University
Priority to CN201510598245.3A priority Critical patent/CN105112674B/en
Publication of CN105112674A publication Critical patent/CN105112674A/en
Application granted granted Critical
Publication of CN105112674B publication Critical patent/CN105112674B/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 discloses a kind of waste printed circuit board Whote-wet method recovery process, comprise the following steps:Waste printed circuit board is crushed, obtains the more metal dusts of waste printed circuit board after gravity treatment;The more metal dusts of waste printed circuit board are leached with the acid solution that concentration is 0.1~4mol/L, leachate and leached mud are obtained after separation of solid and liquid;It is 0.5~5mol/L acid solutions displacement stripping tin that copper compound and concentration are added in leached mud, is obtained after separation of solid and liquid containing tin liquor and divides scruff;It is 0.2~6mol/L acid solutions that concentration is added in scruff is divided, then is passed through oxygen and/or air progress oxidation reaction, obtains containing copper liquid and noble metal slag after separation of solid and liquid;Containing copper liquid tough cathode is obtained through eddy flow electrodeposition.The present invention proposes Whote-wet method PROCESS FOR TREATMENT waste printed circuit board, realizes the directional separation of valuable metal, enrichment, extraction in processing step, solves the problems such as waste circuit board value metallic element trend is scattered and later separation extraction is difficult.

Description

A kind of waste printed circuit board Whote-wet method recovery process
Technical field
The present invention relates to waste resource recycling field, more particularly to a kind of waste printed circuit board Whote-wet method recovery process.
Background technology
In recent years, the production of electronic product remains stable growth.According to Chinese Ministry of Industry and Information announce as shown by data, 2013 January to November, China's scale above electronics product manufacturing industry increase by 11.2%.But the life cycle of electronic product is but with electricity The continuous development of sub- technology and increasingly shorten.1997 so far, and computer and CPU average life span were fallen to only 2 years by 4~6 years.And The rapid rising of the novel electronic products such as mobile phone and its update, accelerate eliminating for electronic product.According to European Union's relevant report, The growth rate of electron wastes was maintained at 11% or so during 2008 to 2014, was 4 times of common rubbish.Electronic waste Contain the metal of a large amount of recoverables in thing, such as aluminium, copper, lead, zinc, noble metal (gold, silver), platinum group metal and rare earth element (samarium, europium, yttrium, gadolinium and dysprosium etc.).Also containing a large amount of different types of engineering plastics and glass fibre in electron wastes, these are non- Metal is by can also bring considerable economic benefit after efficiently separating.
Patent publication No. is that CN101049955A Chinese patent discloses one kind using copper in waste printed circuit board for sulphur The method of sour copper, the air oxidation of copper sulphate system is added to be carried out at room temperature to copper in waste printed circuit board using dilute sulfuric acid, sodium chloride Leach, gained filtrate is evaporated crystallization after filtering;Sodium salt is introduced in this Leaching Systems, and only considered the element row of copper Not study other metallic elements.Patent publication No. is US20120318681A1 United States Patent (USP), discloses one kind Afforest without cyanogen wet processing recovery waste printed circuit board technique, the technique using Physical separation waste printed circuit board in metal with Nonmetallic, obtained metallic copper powder is cast as electrorefining after anode, then noble metal is reclaimed from the earth of positive pole;To thing in this method Reason separation requirement is high, and just research conditions domestic at present are seen is extremely difficult to directly cast wanting for electrolysis by physical partition method Ask.Patent publication No. is US2013033522A1 United States Patent (USP), discloses one kind from discarded object (including discarded circuit Plate) in recovery valuable metal method, wherein discarded printed circuit boards are without physical separation, directly after controlling Temperature Treatment, Separation of glasses fiber and valuable metal;Clearly show that valuable metal can not be with glass when treatment temperature is less than 400 DEG C in patent Glass fiber is separated from each other, it is therefore desirable to higher treatment temperature.Patent publication No. is that CN101049955A Chinese patent discloses Waste printed circuit board is placed in vacuum tank, heating pyrolysis, most of pyrolysis devolatilization thing cooling liquid is liquid oil, another portion Divide and enter gas collector;During pyrolysis, scolding tin is separated with circuit board using centrifugal separating device;Electricity after categorised collection pyrolysis Road plate substrate and electronic component are further separated and reclaimed;This method requires high to equipment temperature control, and energy consumption is also corresponding higher. Patent publication No. is that CN104532005A Chinese patent discloses a kind of side of discarded printed circuit boards comprehensive utilization of resources Method, ferriferous raw material and non iron raw material are isolated by broken, magnetic separation;Metalliferous material is gone out to non iron raw material high-voltage electrostatic sorting And non-metallic material;The metals such as copper, gold, silver are separated to metalliferous material again;The method is also concentrated mainly on physical separation and copper, expensive Metal recovery.Meanwhile above-mentioned patent could not consider the influence of other metallic elements in waste printed circuit board, all single concentrates on On some or several metals, this necessarily cause it to exist in industrial applications other metallic elements trend is not clear, each element The problems such as synthetical recovery difficulty.
The content of the invention
The technical problem to be solved in the present invention is overcome the deficiencies in the prior art, there is provided a kind of cost is cheap, clean environment firendly, A kind of strong waste printed circuit board Whote-wet method recovery process of reagent circulation usability.
In order to solve the above technical problems, technical scheme proposed by the present invention is:
A kind of waste printed circuit board Whote-wet method recovery process, comprises the following steps:
(1) waste printed circuit board crushed, obtain the more metal dusts of waste printed circuit board after gravity treatment;
(2) the more metal dusts of waste printed circuit board are leached with the acid solution that concentration is 0.1~4mol/L, the process exists Carried out in the reactor of design temperature, while start stirring, reacted separation of solid and liquid after a period of time, obtain leachate and leaching Slag;Contain the active metals, the main cupric of leached mud, tin, noble metal etc. such as zinc, aluminium, iron in leachate;
(3) the acid solution displacement stripping tin of copper compound and concentration for 0.5~5mol/L, separation of solid and liquid are added in leached mud After obtain containing tin liquor and dividing scruff;The copper compound is the one or more in copper sulphate, copper chloride, Cu oxide;It is stanniferous It is mainly tin, the soluble-salt of copper in liquid, divides the main cupric of scruff, noble metal slag;
(4) it is 0.2~6mol/L acid solutions concentration to be added in scruff is divided, then is passed through oxygen and/or air is aoxidized React, obtain containing copper liquid and noble metal slag after separation of solid and liquid;The temperature of the oxidation reaction is 45~90 DEG C;
(5) tough cathode is obtained through eddy flow electrodeposition containing copper liquid.
Above-mentioned technique, it is preferred that again to the more metal dusts of waste printed circuit board after acid adding in the leachate after step (2) Leached, valuable metal is enriched to the active metal in synthetical recovery leachate of opening a way after finite concentration in liquid to be leached.
Above-mentioned technique, it is preferred that containing in tin liquor after step (3) adds oxidant, is reacted at 50~90 DEG C Precipitated to stannic acid, stannic acid precipitation obtains tin ash through calcining, and the oxidant is in hydrogen peroxide, ozone, oxygen and air It is one or more of;It 1~20 (is oxidant theoretical amount needed for tetravalent tin by Bivalent Tin complete oxidation that the excess coefficient of oxidant, which is, 1-20 times).
Above-mentioned technique, it is preferred that in the step (3), when hydrogen ion concentration is big in the acid solution that stripping tin process is selected When 1mol/L, need first to carry out aoxidizing heavy tin to adding oxidant after being diluted containing tin liquor.
Above-mentioned technique, it is preferred that in the step (3), the excess coefficient (mol ratio of copper and tin) of copper compound is 1 ~10.
Above-mentioned technique, it is preferred that part copper compound is replaced in the return to step containing copper liquid (3) in the step (4).
Above-mentioned technique, it is preferred that in the eddy flow electrolytic deposition process of the step (5), cathode-current density be 200~ 900A/m2, sulfuric acid concentration is 0.2~1.5mol/L in electric effusion, and electrodeposition temperature is 10~40 DEG C, electrodeposition terminal copper ion concentration Control is in more than 5g/L.
Above-mentioned technique, it is preferred that oxygen caused by eddy flow electrolytic deposition process is used for the oxygen of step (4) in the step (5) Change reaction.
Above-mentioned technique, it is preferred that in the step (4), oxidation reaction process needs to stir, and mixing speed is not less than 200r/min, liquid-solid ratio are 3~40;The unit ratio of the liquid-solid ratio is mL/g;Gas flow (equivalent purity oxygen) is controlled with dividing The molar ratio of copper in scruff>1.2.
Above-mentioned technique, it is preferred that in the step (2), acid solution is one or both of hydrochloric acid and sulfuric acid;It is described Acid in step (3) and step (4) is sulfuric acid.
Above-mentioned technique, it is preferred that the granularity of the more metal dusts of waste printed circuit board is 200-50 mesh.
Acid reusable edible is in dividing tin and air oxygen caused by surplus acid and electrodeposition in above-mentioned technique after separation of solid and liquid Change leaching copper step.
The technological process of the present invention in technique as shown in figure 1, take the lead in proposing to have reached using diluted acid leaching active metal to subtract Light subsequent technique removal of impurities purpose, and the purpose of active metal enrichment can be reached by circulating leaching, so as to be advantageous to active metal Further separation and recovery;The tin replaced and peeled off in waste printed circuit board using mantoquita, hydrogen peroxide, ozone, oxygen are proposed first In one kind or its heavy tin of collocation oxidation, displaced liquid can be further used for lower step and leach, no any impurity introduces;Using sky The more metal dusts of gas oxidation acid leaching waste printed circuit board are environment-friendly, equipment investment is low;Copper is carried using eddy flow electrodeposition in nothing to appoint Cu-CATH-1 is made in the case of what additive.
Compared with prior art, the advantage of the invention is that:
1) conventional method relies primarily on the initial gross separation that physical separation realizes metal, and it is real that the present invention combines domestic equipment research and development Border, the reverse proposition that takes the lead in have developed the technique under conditions of mitigating premised on physical separation burden, and technique of the invention is not Need to carry out magnetic separation, electric separation etc., it is only necessary to carry out simply broken, roughing.
2) present invention proposes the more metal dusts of Whote-wet method PROCESS FOR TREATMENT waste printed circuit board, alleviates waste printed circuit board physics Separation burden, realizes the directional separation of valuable metal, enrichment, extraction in processing step, how golden solves waste printed circuit board Belong to the problems such as powder valuable metal element trend is scattered and later separation extraction is difficult.
3) present invention is replaced except active metal, mantoquita and shells tin in advance using diluted acid, molten copper, eddy flow electrodeposition system are leached in air oxidation Cu-CATH-1 technique, simple with equipment, easy to implement, reagent circulation is good, and cost is low, and environmentally safe.And For the present invention while valuable metal reclaim, organic matter and glass fibre in waste printed circuit board and pyrogenic process are than the destruction that is subjected to It is low, it can be reclaimed in subsequent step.
4) present invention proposes first for waste printed circuit board selectively leaches active valuable metal such as iron, zinc with diluted acid Deng, gained leachate concentration of metal ions can be enriched with the present invention, and open circuit can directly produce corresponding product salt after enrichment, with Conventional physical segregation ratio has advantage.
5) present invention proposes that added regent is few, and free from admixture introduces using mantoquita displacement stripping tin first for waste printed circuit board, Industrialization design is strong.
Brief description of the drawings
Fig. 1 is the process chart of the present invention.
Fig. 2 is tough cathode product photo prepared by the embodiment of the present invention 1.
Fig. 3 is tough cathode product photo prepared by the embodiment of the present invention 2.
Fig. 4 is that the stannic acid obtained by the heavy tin of the oxidation of the embodiment of the present invention 2 precipitates photo.
Tin ash product photo of the stannic acid of Fig. 5 embodiment of the present invention 2 precipitation through calcining gained.
The XRD of tin ash product of the stannic acid of Fig. 6 embodiment of the present invention 2 precipitation through calcining gained.
Fig. 7 is tough cathode product photo prepared by the embodiment of the present invention 3.
Embodiment
For the ease of understanding the present invention, the present invention is made below in conjunction with Figure of description and preferred embodiment more complete Face, meticulously describe, but protection scope of the present invention is not limited to embodiment in detail below.
Unless otherwise defined, the implication that all technical terms used hereinafter are generally understood that with those skilled in the art It is identical.Technical term used herein is intended merely to describe the purpose of specific embodiment, is not intended to the limitation present invention Protection domain.
Except there is a special instruction, the various reagents used in the present invention, raw material be can be commercially commodity or Person can pass through product made from known method.
The more metal dust chemistry compositions of waste printed circuit board used in following embodiments, as shown in table 1.
The mixed-powder chemical composition (%, ω) of table 1
Cu Fe Zn Sn Al Pb In Au Zr Ag
54.00 5.60 1.04 4.60 2.40 0.63 9.5μg/g 5μg/g 16.6μg/g 17.6μg/g
Embodiment 1:
A kind of waste printed circuit board Whote-wet method recovery process of the invention, comprises the following steps:
(1) waste printed circuit board use into shaking table roughing after jaw crusher is broken, much metal powder constituent such as tables 1 It is shown.
(2) the more metal dusts of waste printed circuit board in reactor are leached with 1mol/L sulfuric acid solution, sulfuric acid is molten The liquid-solid ratio of liquid and the more metal dusts of waste printed circuit board is 20:1 (unit:mL/g);Start stirring, mixing speed in leaching process 350r/min, 45 DEG C of extraction temperature, stirring are separated by filtration after 1.5 hours, obtain leachate and leached mud;Contain in leachate The active metals such as zinc, aluminium, iron, the main cupric of leached mud, tin, noble metal etc..Active metal assay is removed in advance by the diluted acid As shown in table 2.
(3) copper sulphate (excess coefficient of copper sulphate is 2) is added in leached mud and 2mol/L sulfuric acid solutions enter line replacement Stripping tin is leached, extraction time is 2 hours, and extraction temperature is 55 DEG C, is obtained after separation of solid and liquid containing tin liquor and divides scruff;Containing in tin liquor The predominantly soluble-salt of tin, copper, divide the main cupric of scruff, noble metal slag.
(4) 15 times of air is persistently blasted after 3 times being diluted containing tin liquor and carries out aoxidizing heavy tin and reacts 4h, after standing 2 hours It is separated by filtration, obtains stannic acid precipitation, tin ash product is obtained through calcining.
2mol/L sulfuric acid, which is added, in scruff is divided and is stirred with 300r/min mixing speed (sulfuric acid and divides scruff Liquid-solid ratio is 20:1, liquid-solid ratio unit is mL/g), while air is passed through with 120mL/min speed and carries out Oxidation Leaching, temperature For 70 DEG C, extraction time is 4 hours;Obtain containing copper liquid and noble metal slag after separation of solid and liquid.
(5) through eddy flow electrodeposition carry copper containing copper liquid (wherein carrying copper bar part is:Current density 400A/m2, circular flow 300L/ H, sulfuric acid concentration 1mol/L in electric effusion, 30 DEG C of feed temperature, it is 10g/L to control terminal copper ion concentration.), tough cathode is made Product photo is as shown in Fig. 2 tough cathode product analysis is as shown in table 5.
The diluted acid of table 2 removes active metal assay in advance
Diluted acid removes active metal in advance Cu Zn Fe Sn Al
Ion concentration/(g/L) 1.18 0.51 2.61 0.06 1.12
Leaching rate/% 4.37 98.08 93.39 2.72 93.32
Mantoquita displacement stripping tin rate is 97.8% in the present embodiment, and it is 95.2% to aoxidize heavy tin rate, and air oxidation leaching copper copper carries It is 98.2% to take rate.
Embodiment 2:
A kind of waste printed circuit board Whote-wet method recovery process of the invention, comprises the following steps:
(1) waste printed circuit board use into shaking table roughing after jaw crusher is broken, much metal powder constituent such as tables 1 It is shown.
(2) the more metal dusts of waste printed circuit board in reactor are leached with 0.8mol/L sulfuric acid solution, sulfuric acid The liquid-solid ratio of solution and the more metal dusts of waste printed circuit board is 20:1 (liquid-solid ratio unit ratio is mL/g);Start in leaching process Stirring, mixing speed 300r/min, 30 DEG C of extraction temperature, stirring are separated by filtration after 1.5 hours, obtain leachate and leached mud; Contain the active metals, the main cupric of leached mud, tin, noble metal etc. such as zinc, aluminium, iron in leachate.By the diluted acid in advance except active Metal inspection result is as shown in table 3.
(3) copper sulphate (excess coefficient of copper sulphate is 1.5) is added in leached mud and 1mol/L sulfuric acid solutions are put Leaching stripping tin is changed, extraction time is 2 hours, and extraction temperature is 45 DEG C, is obtained after separation of solid and liquid containing tin liquor and divides scruff;Containing tin liquor In predominantly tin, the soluble-salt of copper, divide the main cupric of scruff, noble metal slag.
(4) by diluted containing tin liquor added after 2 times needed for 5 times of oxidant hydrogen peroxide and stir 2h and carry out aoxidizing heavy tin, it is quiet It is separated by filtration after putting 2 hours, obtains stannic acid precipitation (product photo is as shown in Figure 4), tin ash product is obtained through calcining.
2mol/L sulfuric acid, which is added, in scruff is divided and is stirred with 400r/min mixing speed (sulfuric acid and divides scruff Liquid-solid ratio is 15:1, liquid-solid ratio unit ratio is mL/g), while air is passed through with 120mL/min speed and carries out Oxidation Leaching, Temperature is 70 DEG C, and extraction time is 4 hours;Obtain containing copper liquid and noble metal slag after separation of solid and liquid.
(5) through eddy flow electrodeposition carry copper containing copper liquid (carrying copper bar part is:Current density 400A/m2, circular flow 400L/h, sulphur Acid concentration 1mol/L, 30 DEG C of feed temperature, it is 10g/L to control terminal copper ion concentration), tough cathode product photo such as Fig. 3 is made Shown, tough cathode product analysis is as shown in table 5.
The diluted acid of table 3 removes active metal assay in advance
Diluted acid removes active metal in advance Cu Zn Fe Sn Al
Ion concentration/(g/L) 0.83 0.47 2.67 0.13 1.13
Leaching rate/% 3.07 90.60 95.51 5.65 94.17
Mantoquita displacement stripping tin rate is 97.9% in the present embodiment, and it is 96.0% to aoxidize heavy tin rate, and air oxidation leaching copper copper carries It is 96.4% to take rate, sink products therefrom photo after the calcining of tin product as shown in figure 5, after heavy tin product calcining products therefrom XRD Analysis chart is as shown in Figure 6, the results showed that thing is mainly mutually tin ash.
Embodiment 3:
A kind of more metal dust Whote-wet method recovery process of waste printed circuit board of the invention, comprise the following steps:
(1) waste printed circuit board use shaking table roughing after jaw crusher is broken, much metal powder constituent such as institutes of table 1 Show.
(2) leachate that the step of embodiment 2 (2) obtains concentration sour after mending acid is reached into 1.21mol/L, with benefit acid Leachate leaches to the more metal dusts of waste printed circuit board in reactor, the liquid of solution and the more metal dusts of waste printed circuit board Gu than being 20:1 (liquid-solid ratio unit ratio is mL/g);Start stirring, mixing speed 300r/min, extraction temperature in leaching process 30 DEG C, stirring is separated by filtration after 1 hour, obtains leachate and leached mud;Contain the active metals such as zinc, aluminium, iron, leaching in leachate Slag tap main cupric, tin, noble metal etc..By the diluted acid in advance except active metal assay is as shown in table 4.
(3) add that the step of embodiment 2 (4) obtains in leached mud contains copper liquid, and adds the copper sulphate (excess of copper sulphate Coefficient is 1.5) to enter line replacement to leach stripping tin, and extraction time is 1.5 hours, and extraction temperature is 45 DEG C, the speed of leaching process stirring Spend for 300r/min, obtained after separation of solid and liquid containing tin liquor and divide scruff;Containing the soluble-salt in tin liquor being mainly tin, copper, divide tin The main cupric of slag, noble metal slag.
(4) hydrogen peroxide that 10 times of oxidant needed for addition after 3 times is diluted containing tin liquor is stirred 2 hours, mistake after standing 2 hours Filter separation, obtains stannic acid precipitation, and tin ash product is obtained through calcining.
2.13mol/L sulfuric acid, which is added, in scruff is divided and is stirred with 400r/min mixing speed (sulfuric acid and divides tin The liquid-solid ratio of slag is 15:1, liquid-solid ratio unit ratio is mL/g), while air is passed through with 120mL/min speed and aoxidized Leach, temperature is 70 DEG C, and extraction time is 4 hours;Obtain containing copper liquid and noble metal slag after separation of solid and liquid.
(5) through eddy flow electrodeposition carry copper containing copper liquid (carrying copper bar part is:Current density 400A/m2, circular flow 300L/h, sulphur Acid concentration 1mol/L, 30 DEG C of feed temperature, it is 10g/L to control terminal copper ion concentration), obtained tough cathode product photo is as schemed Shown in 7.
The diluted acid of table 4 removes active metal assay in advance
Diluted acid removes active metal in advance Cu Zn Fe Sn Al
Ion concentration/(g/L) 1.34 0.65 3.42 0.14 1.49
Leaching rate/% 3.97 93.71 90.59 4.32 93.68
Mantoquita displacement stripping tin rate is 94.9% in the present embodiment, and it is 95.3% to aoxidize heavy tin rate, and air oxidation leaching copper copper carries It is 97.3% to take rate.Tough cathode product analysis is as shown in table 5.
The tough cathode product analysis contrast table of table 5
Element Embodiment 1 Embodiment 2 Embodiment 3 Standard cathode copper
Cu 99.97% 99.98% 99.97% >99.95%
Se / / / /
Bi 5.9x10-4 4.2x10-4 6.3x10-4 6x10-3
Sb 5.2x10-4 5.9x10-4 6x10-4 1.5x10-3
As 70.5x10-4 68.2x10-4 70x10-4 1.5x10-3
S 15.1x10-4 10.3x10-4 9.1x10-4 2.5x10-3
Mn 1.0x10-4 0.9x10-4 0.5x10-4 /
Cd 1.6x10-4 1.1x10-4 2x10-4 /
P 11.1x10-4 9.9x10-4 7.2x10-4 1x10-3
Ni 6.3x10-4 6.9x10-4 5.2x10-4 2x10-2
Si 40.4x10-4 30x10-4 37x10-4 /
Co 6.7x10-4 5.1x10-4 4.5x10-4 /
Te / / / /
Cr / / / /
Pb 70.7x10-4 58.5x10-4 74x10-4 2x10-3
Sn 6.1x10-4 4.1x10-4 3.5x10-4 1x10-3
Fe 22.6x10-4 16.7x10-4 20.8x10-4 2.5x10-3
Zn 22.8x10-4 10.5x10-4 29.7x10-4 2x10-3
Ag 3.2x10-4 1.3x10-4 1.0x10-4 /
Summation 266.6x10-4 228.2x10-4 276x10-4 0.0166
It was found from the tough cathode product analysis contrast of table 5, tough cathode production obtained by waste printed circuit board handling process of the invention Product meet standard cathode copper standard.

Claims (7)

1. a kind of waste printed circuit board Whote-wet method recovery process, it is characterised in that comprise the following steps:
(1) waste printed circuit board crushed, obtain the more metal dusts of waste printed circuit board after cradle roughing;
(2) the more metal dusts of the waste printed circuit board are leached with the acid solution that concentration is 0.1~4mol/L, separation of solid and liquid After obtain leachate and leached mud;Wherein, the liquid-solid ratio of acid solution and the more metal dusts of waste printed circuit board is 20:1, liquid-solid ratio list Position ratio is mL/g;Start stirring, mixing speed 300r/min, 30 DEG C of extraction temperature, mistake after stirring 1.5 hours in leaching process Filter separation;Acid is sulfuric acid;
(3) it is 0.5~5mol/L acid solutions displacement stripping tin that copper compound and concentration are added in leached mud, is obtained after separation of solid and liquid Containing tin liquor and divide scruff;The copper compound is the one or more in copper sulphate, copper chloride, Cu oxide;The acid is sulphur Acid;
(4) concentration is added in scruff is divided and is 0.2~6mol/L acid solution, then be passed through oxygen and/or air aoxidize it is anti- Should, obtain containing copper liquid and noble metal slag after separation of solid and liquid;The temperature of the oxidation reaction is 45~90 DEG C;The acid is sulfuric acid; Need to stir in oxidation reaction process, and mixing speed is not less than 200r/min, liquid-solid ratio is 3~40, the unit of the liquid-solid ratio Than for mL/g;
(5) it is described to obtain tough cathode through eddy flow electrodeposition containing copper liquid;Oxygen caused by eddy flow electrolytic deposition process is used to walk in the step (5) Suddenly the oxidation reaction of (4).
2. technique as claimed in claim 1, it is characterised in that again to discarded electricity after acid adding in the leachate after step (2) Plate more metal dusts in road are leached.
3. technique as claimed in claim 1, it is characterised in that oxidant is added in step (3) is containing tin liquor, 50~90 Reaction obtains stannic acid precipitation at DEG C, and stannic acid precipitation obtains tin ash through calcining, and the oxidant is hydrogen peroxide, ozone, oxygen With the one or more in air;The excess coefficient of oxidant is 1~20.
4. technique as claimed in claim 3, it is characterised in that in the step (3), when in the acid solution that stripping tin process is selected When hydrogen ion concentration is more than 1mol/L, need first to carry out aoxidizing heavy tin to adding oxidant after being diluted containing tin liquor.
5. the technique as described in any one of Claims 1 to 4, it is characterised in that in the step (3), the excess of copper compound Coefficient is 1~10.
6. the technique as described in any one of Claims 1 to 4, it is characterised in that the return to step containing copper liquid in the step (4) (3) part copper compound is replaced in.
7. the technique as described in any one of Claims 1 to 4, it is characterised in that in the eddy flow electrolytic deposition process of the step (5), Cathode-current density is 200~900A/m2, sulfuric acid concentration is 0.2~1.5mol/L in electric effusion, and electrodeposition temperature is 10~40 DEG C, electrodeposition terminal copper ion concentration is controlled in more than 5g/L.
CN201510598245.3A 2015-09-18 2015-09-18 A kind of waste printed circuit board Whote-wet method recovery process Active CN105112674B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510598245.3A CN105112674B (en) 2015-09-18 2015-09-18 A kind of waste printed circuit board Whote-wet method recovery process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510598245.3A CN105112674B (en) 2015-09-18 2015-09-18 A kind of waste printed circuit board Whote-wet method recovery process

Publications (2)

Publication Number Publication Date
CN105112674A CN105112674A (en) 2015-12-02
CN105112674B true CN105112674B (en) 2017-11-21

Family

ID=54660775

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510598245.3A Active CN105112674B (en) 2015-09-18 2015-09-18 A kind of waste printed circuit board Whote-wet method recovery process

Country Status (1)

Country Link
CN (1) CN105112674B (en)

Families Citing this family (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105297077A (en) * 2015-12-03 2016-02-03 陈梦君 Recovery method for metals in waste printed circuit boards
CN105779770B (en) * 2016-03-10 2017-04-12 中南大学 Method for recycling valuable metal in waste circuit board
CN105624681B (en) * 2016-03-11 2018-07-13 中南大学 The method of electronic component and a kind of etching agent in a kind of wet separation waste printed circuit board
CN106468630A (en) * 2016-09-30 2017-03-01 珠海格力电器股份有限公司 Metal ingredient analysis method in a kind of wiring board
CN107502920A (en) * 2017-08-10 2017-12-22 云南龙蕴科技环保股份有限公司 A kind of method of the hydrometallurgic recovery copper from circuit board
CN107574310A (en) * 2017-09-19 2018-01-12 南京工业大学 A kind of method for efficiently leaching copper in waste printed circuit board
CN108160683A (en) * 2018-02-06 2018-06-15 湖南科技大学 A kind of method that waste and old tin plating copper-clad plate resource utilization utilizes
CN108346715A (en) * 2018-02-09 2018-07-31 中南大学 The recovery method of silicon solar cell
CN109825716A (en) * 2019-03-28 2019-05-31 湖南科技大学 A method of recycling copper and tin in waste and old tin plating copper-clad plate
CN111172398A (en) * 2020-01-17 2020-05-19 广东华越环保科技有限公司 Wet harmless extraction process for metal in waste mobile phone circuit board
CN111139360B (en) * 2020-01-17 2021-10-26 广东华越环保科技有限公司 Method for recovering metals in IC (integrated circuit) chip and component in waste mobile phone circuit board
CN111154979A (en) * 2020-01-17 2020-05-15 广东华越环保科技有限公司 Cyanide-free recovery process for gold and palladium in IC (integrated circuit) chip and component in waste mobile phone circuit board
CN111663045B (en) * 2020-06-16 2021-05-14 中南大学 Comprehensive waste circuit board resource recovery process
CN112143899B (en) * 2020-09-16 2022-07-01 励福(江门)环保科技股份有限公司 Method for recovering copper and enriching precious metals from waste circuit boards
CN112921356B (en) * 2021-01-22 2022-05-27 西南科技大学 Method for recovering copper from waste printed circuit board

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN86101938B (en) * 1986-03-21 1987-05-20 个旧市化工研究所 Preparation of stannic oxide from medium grade tin ore by liquid phasing oxidization
ZA987217B (en) * 1997-08-15 2000-02-14 Cominco Eng Services Chloride assisted hydrometallurgical extraction of metal from sulphide or laterite ores.
CN101864519A (en) * 2009-04-17 2010-10-20 中国科学院过程工程研究所 Method for selectively leaching and separating tin, lead and copper from waste circuit board
CN101643852B (en) * 2009-09-02 2011-10-12 北京科技大学 Heap-leaching method for separating copper and tin from tin-plated copper wires
CN101787547B (en) * 2010-02-09 2011-06-15 中南大学 Method for recovering valuable metals from waste printed circuit board
CN103725879A (en) * 2013-12-24 2014-04-16 戴元宁 Method for producing tungsten and tin chemical products through chemical metallurgical separation of tungsten-tin paragenic ore
CN104843770B (en) * 2015-03-30 2017-09-26 中国钢研科技集团有限公司 A kind of method that tin mud resource is utilized

Also Published As

Publication number Publication date
CN105112674A (en) 2015-12-02

Similar Documents

Publication Publication Date Title
CN105112674B (en) A kind of waste printed circuit board Whote-wet method recovery process
Cocchiara et al. Dismantling and electrochemical copper recovery from Waste Printed Circuit Boards in H2SO4–CuSO4–NaCl solutions
CN100400683C (en) Method for producing metallic lead and zinc by using lead-zinc containing waste slag or lead-zinc monoxide mine
Xiao et al. Hydrometallurgical recovery of copper from complex mixtures of end-of-life shredded ICT products
CN101575715B (en) Method for extracting valuable metals from electronic waste
US20140065037A1 (en) Treatment of indium gallium alloys and recovery of indium and gallium
CN101974689A (en) Method for processing material containing copper
CN102051478B (en) Wet process for treating lead copper matte
CN105779770B (en) Method for recycling valuable metal in waste circuit board
CN103160691A (en) Process method of recycling gold and copper from abandoned electronic components
CN102912138A (en) Method of recycling zinc, manganese, lead and silver from zinc electrowinning anode mud
KR101567499B1 (en) A selectively recovery method for valuable metal from the LED wastes
Fan et al. Extraction of tellurium and high purity bismuth from processing residue of zinc anode slime by sulfation roasting-leaching-electrodeposition process
CN102747229B (en) Method for separating and recycling valuable metals in powder rich in multiple metals of waste circuit board
CN102399992B (en) Method for recovering valuable metals from waste plastic plating layer containing copper and nickel
EP2147128A1 (en) Process for producing pure metallic indium from zinc oxide and/or solution containing the metal
Ashiq et al. Electrochemical enhanced metal extraction from E-waste
CN105887118B (en) A kind of method that Selective Separation from materials containing tellurium reclaims tellurium
Bo et al. Selective separation of copper and cadmium from zinc solutions by low current density electrolysis
JP6744981B2 (en) How to concentrate and recover precious metals
Hao et al. Study of gold leaching from pre-treated waste printed circuit boards by thiosulfate‑cobalt-glycine system and separation by solvent extraction
CN104419826A (en) Method for preparing electrodeposited zinc by ammonia leaching of zinc oxide
Kumar et al. Recovery of cadmium from hydrometallurgical zinc smelter by selective leaching
CN102650000A (en) Method for recovering bismuth and arsenic from bismuth and arsenic-containing solution
CN107299228A (en) A kind of method that zinc hydrometallurgy purification copper ashes extracts metallic copper

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant