JPS62120436A - Wet recovery of lead contained in paste of waste battery - Google Patents
Wet recovery of lead contained in paste of waste batteryInfo
- Publication number
- JPS62120436A JPS62120436A JP61270818A JP27081886A JPS62120436A JP S62120436 A JPS62120436 A JP S62120436A JP 61270818 A JP61270818 A JP 61270818A JP 27081886 A JP27081886 A JP 27081886A JP S62120436 A JPS62120436 A JP S62120436A
- Authority
- JP
- Japan
- Prior art keywords
- lead
- paste
- recovery method
- wet recovery
- waste
- 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.)
- Pending
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
- C25C—PROCESSES FOR THE ELECTROLYTIC PRODUCTION, RECOVERY OR REFINING OF METALS; APPARATUS THEREFOR
- C25C1/00—Electrolytic production, recovery or refining of metals by electrolysis of solutions
- C25C1/18—Electrolytic production, recovery or refining of metals by electrolysis of solutions of lead
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B13/00—Obtaining lead
- C22B13/04—Obtaining lead by wet processes
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M10/00—Secondary cells; Manufacture thereof
- H01M10/54—Reclaiming serviceable parts of waste accumulators
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/84—Recycling of batteries or fuel cells
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Manufacturing & Machinery (AREA)
- Mechanical Engineering (AREA)
- General Chemical & Material Sciences (AREA)
- Electrolytic Production Of Metals (AREA)
- Manufacture And Refinement Of Metals (AREA)
- Secondary Cells (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、廃電池の脱硫ペーストから鉛を電解採取する
湿式処理法に関するものである。DETAILED DESCRIPTION OF THE INVENTION [Industrial Field of Application] The present invention relates to a wet processing method for electrolytically extracting lead from desulfurization paste of waste batteries.
ペーストの種々の脱硫方法によれば、廃電池のスラジを
アルカリ金属又はアンモニウムの炭酸塩で処理すること
により、不溶性の鉛化合物の混合物ばかりでなく、全て
のイオウを可溶性のアルカリ金属又はアンモニウムの硫
酸塩として含む溶液が得られる。この鉛化合物の混合物
は、」1記の溶液から分離して水で完全に洗浄すること
によって。According to various desulfurization methods of pastes, waste battery sludge is treated with alkali metal or ammonium carbonates to remove not only the mixture of insoluble lead compounds but also all the sulfur into soluble alkali metal or ammonium sulfates. A solution containing it as a salt is obtained. This mixture of lead compounds was separated from the solution described in 1. by washing thoroughly with water.
実質的にイオウ成分を除去される。Sulfur components are substantially removed.
上記混合物は、比較的低温度(800〜900℃)で石
炭を用いることにより、二酸化イオウの実質的な放出及
び、鉛のかわを生じることなく、簡単に還元される。The above mixture is easily reduced using coal at relatively low temperatures (800-900 DEG C.) without substantial release of sulfur dioxide and without producing lead glue.
それ故、現在、乾式冶金法による上記生成物の還元方法
が最も盛んに用いられている。この方法には、また、高
い生産率、還元炉の長い寿命及び。Therefore, at present, the method for reducing the above-mentioned products by pyrometallurgy is most frequently used. This method also has high production rates, long life of the reduction furnace and.
抽出鉛の高収率等の利点がある。It has advantages such as high yield of extracted lead.
しかしながら、鉛含有物質の乾式冶金法は、運搬又は炉
への充填の際に特別な注意を必要とし。However, pyrometallurgy of lead-containing materials requires special care during transportation or charging into the furnace.
且つ、同様な炉によって、煙や揮発性ダストが放出され
る可能性を有している。Additionally, similar furnaces have the potential to emit smoke and volatile dust.
そこで2作業構内又は、工場の周辺の鉛汚染物質を監視
する為の広範で高価なシステム、或いは。2 Extensive and expensive systems for monitoring lead contaminants on the work premises or around the factory;
有効な巨大濾過プラントを設ける必要が生じてくる。こ
のため、ペースト中の鉛を金属として回収する方法とし
て、乾式冶金処理法に代わるべき。It becomes necessary to provide a large effective filtration plant. For this reason, pyrometallurgical processing should be replaced as a method for recovering lead in paste as metal.
とりわけ、電気分解法又は電解採取による抽出処理法の
ように完全な湿式冶金的手法により操作される処理方法
が重要となる。Particularly important are processing methods which operate in a completely hydrometallurgical manner, such as extraction processing methods by electrolysis or electrowinning.
尚脱硫ペーストの組成成分は、平均的には、下記の通り
である。The average composition of the desulfurization paste is as follows.
炭酸鉛(Pbco3) 50〜52チ硫酸鉛
(PbSO4) 2.5〜4チ過酸化鉛(P
bO2)14〜16チ
酸化鉛(PbO) 11〜12%鉛金属(
Pb) 5〜7%使い古した廃電池の
ペーストの湿式冶金法による処理方法の実用上の問題は
、既知のとおり、混合物中の全ての組成成分、特に、大
きな割合で含まれる過酸化鉛(Pb02 )を、電気分
解のために選択された溶液中に溶解させることである。Lead carbonate (Pbco3) 50-52 Lead sulfate (PbSO4) 2.5-4 Lead peroxide (P
bO2) 14-16 Lead thioxide (PbO) 11-12% Lead metal (
As is known, the practical problem with the hydrometallurgical treatment of paste from 5-7% worn-out waste batteries is that all of the compositional components in the mixture, especially lead peroxide (Pb02), which is present in a large proportion. ) in the solution selected for electrolysis.
実際に。actually.
混合物の酸溶解の残渣が、許容できない程の鉛の減損を
構成するものであってはならない。The residue of acid dissolution of the mixture must not constitute an unacceptable lead loss.
一方、良く知られているように、電気分解工程に適した
通常の酸中に過酸化鉛は不溶性であるので、過酸化鉛の
還元のだめの前処理を行なわない場合は、混合物の酸溶
解の残渣は鉛を非常に多く含み、乾式回収に戻さなけれ
ばならない。On the other hand, as is well known, lead peroxide is insoluble in ordinary acids suitable for electrolysis processes, so if no pretreatment is carried out to reduce the lead peroxide, the acid dissolution of the mixture will be difficult. The residue is highly lead-rich and must be returned to dry recovery.
従来技術によれば4種々の電解液にペーストの全ての組
成成分を溶解することが1種々の方法によって行なわれ
ている。According to the prior art, dissolving all the constituents of the paste in four different electrolytes is carried out by one different method.
先行技術文献を年代順に下記に示す。The prior art documents are listed below in chronological order.
C,E、Tuckerの米国特許IJ 48,062は
、 PbO2を可溶性のPbOとPb2Oに変換するた
めに、電池スラッジを加熱することを示している。US Patent IJ 48,062 to C.E. Tucker shows heating battery sludge to convert PbO2 to soluble PbO and Pb2O.
W、C,Sm1thによる米国特許1,752,356
は、力性アルカリ処理の観点から、 PbO2を可溶解
化するために、ペーストに対し、還元雰囲気中での加熱
(酸化鉛を生成する)を施すものである。U.S. Patent 1,752,356 by W.C.Sm1th
From the viewpoint of alkali treatment, the paste is heated in a reducing atmosphere (to generate lead oxide) in order to solubilize PbO2.
J、H,Ca1beckによる米国特許1,911,6
04は、酢酸ナトリウム溶液によシ、電池ペーストの浸
出を行うものである。電解溶液中では、酸化鉛と硫酸塩
は溶解されるのに対し、過酸化鉛は2通常、不溶性であ
る。U.S. Patent No. 1,911,6 by J. H. Calbeck
04 is for leaching the battery paste with a sodium acetate solution. In electrolytic solutions, lead oxide and sulfate are soluble, whereas lead peroxide is usually insoluble.
しかし、鉛金属の存在及び上述の電解溶液中では2局部
的シニ結合が形成され、そのために、過酸化鉛及び同等
量の鉛金属が溶解される。However, in the presence of lead metal and in the above-mentioned electrolytic solution, two local cyni bonds are formed, so that lead peroxide and an equivalent amount of lead metal are dissolved.
A 、F 、Gyumannによる米国特許4,107
,007は、糖ミツ、又は粗糖等を添加した水酸化アル
カリ金属の濃縮溶液でペーストを浸出するものである。U.S. Patent 4,107 by A.F. Gyumann
, 007, the paste is leached with a concentrated solution of alkali metal hydroxide to which sugar honey or raw sugar is added.
この方法によれば、酸化鉛と硫酸鉛とが溶解され、電気
分解に供することができる。pbo2の挙動については
詳しく記載されていない。According to this method, lead oxide and lead sulfate are dissolved and can be subjected to electrolysis. The behavior of pbo2 is not described in detail.
R,D、Prergmanによる米国特許4,229,
271は、ペーストから過酸化鉛を消去する方法aと、
電解採取工程のだめの慣用の酸(Customary
acids)に2−ストを完全に溶解させる方法すとの
二つの方法を提示している。U.S. Pat. No. 4,229 to R.D. Pregman,
271 is a method a for erasing lead peroxide from paste;
Customary acids in the electrowinning process
Two methods are proposed: one method for completely dissolving 2-st in acids).
ここで、方法aとはペーストを100℃で乾燥後、29
0〜325℃の温度範囲の還元雰囲気中で焙焼すること
である。Here, method a means that after drying the paste at 100°C,
It is roasting in a reducing atmosphere at a temperature range of 0 to 325°C.
方法すとは、二酸化イオウ又は、アルカリ金属又はアン
モニウムの亜硫酸塩あるいは重硫酸塩によってR−スト
の懸濁水を処理することである。The method consists in treating the R-st suspension water with sulfur dioxide or with alkali metal or ammonium sulfites or bisulfates.
U、 I)caceLt7による米国特許4,460,
422は、フッ化ホウ素酸又はフッ化ケイ素酸の熱濃縮
溶液中に完全に溶解する性質を何する鉛丹沈殿金量るた
めに1強アルカリ溶液中で、100〜120’cで、電
池のペーストを反応させている。U. I) U.S. Patent No. 4,460 by caceLt7,
422 has the property of completely dissolving in a thermally concentrated solution of fluoroboric acid or fluorosilicate. Reacting the paste.
鉱物局のA、Y、LeeとE、R,Co1eは、 R,
1,8857の中で、ペースト中に含有されている過酸
化鉛の還元についての2つの方法を示唆している。A, Y, Lee and E, R, Cole of the Minerals Bureau are R,
No. 1,8857 suggests two methods for the reduction of lead peroxide contained in pastes.
一つは、炭酸アンモニウムですでに、脱硫された(−ス
トのフッ化ケイ素の浸出処理の間、鉛粉末を添加するこ
とにより行う方法である。One is by adding lead powder during the leaching process of the silicon fluoride, which has already been desulfurized with ammonium carbonate.
他方は、炭酸アンモニウムによる脱硫処理の間。On the other hand, during the desulfurization treatment with ammonium carbonate.
重硫酸アンモニウムの添加による方法である。This method involves the addition of ammonium bisulfate.
上記の還元雰囲気内の13b 02の熱還元の方法は。 The method of thermal reduction of 13b02 in the above reducing atmosphere is as follows.
乾燥と還元焙焼との二段階の作業周期を必要とするとい
う欠点を有している。これらの処理段階には、操作条件
の厳しい制御が要求されるだけでなく、適切なダスト排
出装置を備えた5装置(炉又は焙焼炉)を用いなければ
ならない。その−ト、仮に低温でも乾燥した物質の拡散
により、公害汚染を引き起すことになる。高温溶解中の
還元方法は。It has the disadvantage that it requires a two-step cycle of drying and reduction roasting. These processing steps not only require tight control of the operating conditions, but also require the use of equipment (furnaces or torrefaction furnaces) with suitable dust evacuation equipment. However, even if the temperature is low, the diffusion of dry substances will cause pollution. What is the reduction method during high temperature melting?
鉛粉末を添加するが、生成鉛の一部を粉末に変換するた
めの移動を含む。結果的に、この方法は。Add lead powder, but include transfer to convert some of the lead produced into powder. As a result, this method...
高価なものとなる。It becomes expensive.
炭酸化する前の二酸化イオウ、亜硫酸塩又は。Sulfur dioxide, sulfite or before carbonation.
重硫酸塩で還元する方法は2反応物の故にかなりのコス
トがかかるが、更に重要なことは、脱硫のだめの炭酸塩
の消費を約25俤増してしまうことである。この炭酸塩
の消費に対応する支出は2無視できるものではなく、今
日、炭酸塩に対する支出は、全工程における個々の出費
の中で、最も高価な項目となっている。The bisulfate reduction method is quite costly due to the two reactants, but more importantly it increases the consumption of carbonate for desulfurization by about 25 tons. The expenditure corresponding to the consumption of this carbonate is not negligible2, and today the expenditure on carbonate is the most expensive item among the individual expenditures in the entire process.
そとで1本発明の目的は、廃電池の脱硫ペーストの電解
抽出による湿式処理工程に関する上述の問題点を解決す
るものである。An object of the present invention is to solve the above-mentioned problems regarding the wet treatment process by electrolytic extraction of desulfurization paste of waste batteries.
本発明の目的を達成するために2本発明は、廃電池のペ
ースト即ち脱硫ペースト中の鉛を純粋な金属体として、
電気分解法による抽出によって回その方法は、以下の工
程により特徴づけられる。In order to achieve the objects of the present invention, the present invention uses lead in a waste battery paste, that is, a desulfurization paste, as a pure metal,
The method of extraction by electrolysis is characterized by the following steps.
a)電解抽出に適したものから選択された酸の水溶液で
上記ペーストを浸出する浸出工程。a) A leaching step in which the paste is leached with an aqueous solution of an acid selected from those suitable for electrowinning.
b)上記浸出された(〜ストに含有されている過酸化鉛
の全てが定量還元に達するように、下記の反応を伴って
、上記浸出されだ投−ストを、過酸化水素で処理する処
理工程。b) Treatment of the leached waste with hydrogen peroxide, with the following reaction, so that all of the lead peroxide contained in the leached waste reaches quantitative reduction: Process.
(1) pb 十lI202 ++−> Pb
十o2+2r(2) Pb +Pb −−−>
2Pb”C)得られた鉛溶解液から固体残置を鉛の電
解抽出に直接供するために9分離する分離工程。(1) pb 11I202 ++-> Pb
10o2+2r(2) Pb +Pb --->
2Pb''C) A separation step in which the solid residue is separated from the obtained lead solution by 9 to directly provide it to electrolytic extraction of lead.
本発明の処理工程を実質的に定義し/こ上述の内容を更
に詳しく説明する。The process steps of the present invention will now be substantially defined and the foregoing will be explained in more detail.
本処理工程における出発物質は、使す古された廃電池か
ら分離されたペーストである。そのペーストは、・既に
公知の手段によυ脱硫処理に施されているものである。The starting material in this process is a paste separated from used waste batteries. The paste has already been subjected to υ desulfurization treatment by known means.
この物質は好ましくは、フッ化ホウ素酸又は。This material is preferably fluoroboric acid or.
フッ化ケイ素酸のような引き続く電解抽出に適し鉛化合
物、具体的には、過酸化鉛と鉛金属との最大限の可溶解
化を達成するだけの過酸化水素が添加される。A lead compound suitable for subsequent electrowinning, such as fluorosilicic acid, and specifically just enough hydrogen peroxide to achieve maximum solubilization of the lead peroxide and lead metal is added.
脱硫されたペーストの酸処理の間、過酸化水素は化学反
応(1)を生じる。During acid treatment of the desulfurized paste, hydrogen peroxide undergoes a chemical reaction (1).
Pb 十H2o2−−−>pb + 02+ 2H
(1)このため、過酸化鉛の全ては酸化鉛に還元され。Pb 10H2o2−->pb + 02+ 2H
(1) Therefore, all of the lead peroxide is reduced to lead oxide.
そして、酸中に溶解される。It is then dissolved in acid.
化学反応(1)の間に遊離された多量の酸素(02)は
。A large amount of oxygen (02) is liberated during the chemical reaction (1).
K−スト中に存在する鉛金属の分子を物理的に活性化し
、下記の化学反応(2)をよシ容易に起こす。It physically activates the lead metal molecules present in K-st to easily cause the following chemical reaction (2).
Pb + Pb −−−> 2Pb2+(2)そし
て、還元される鉛イオン(Pb” )に対応する過酸化
水素を節約しながら、適正な粒度(rightgran
ul ome t ry)を有する金属鉛の全てが、溶
解される。Pb + Pb ---> 2Pb2+ (2) and the proper particle size (rightgrain) while saving hydrogen peroxide corresponding to the lead ions (Pb'') to be reduced.
All of the lead metal with ul ome try is dissolved.
過酸化水素の添加で酸浸出した後、脱硫されたペースト
の有機物質(分離器の薄片と工がナイト。After acid leaching with the addition of hydrogen peroxide, the organic matter of the desulfurized paste (separator flakes and nitride) is removed.
繊維等)と、脱硫段階で変換されなかった硫酸鉛とが溶
解せずに残存する。fibers, etc.) and lead sulfate that was not converted in the desulfurization stage remain undissolved.
反応後の溶成と固体とは、濾過により分離される。濾過
後の固体残渣は、出発物質中に存在する鉛の5多しか含
有せず、そして、有機物質を破壊するための焙焼後に、
脱硫段階に戻すことができる。After the reaction, the melt and solids are separated by filtration. The solid residue after filtration contains only 50% of the lead present in the starting material, and after roasting to destroy organic matter,
It can be returned to the desulfurization stage.
濾過された溶液は、鉛をイオン形状で暇1いかなる精製
をも一般には必要とはしない。何故ならば、それは、鉛
粉末と同一であシ、化学反応(1)において発生させら
れた酸素によって、活性化され、そして、酸浸出してい
る間に溶解さit /こ小量の不純物の置換反応(いわ
ゆる゛′セメンデーシコン″と呼ばれる。)が行なわれ
るからである。The filtered solution contains lead in ionic form and generally does not require any purification. This is because it is identical to the lead powder and is activated by the oxygen generated in the chemical reaction (1) and dissolved during acid leaching with a small amount of impurities. This is because a substitution reaction (so-called ``cementesicone'') takes place.
この自己精製された溶液は、続いて直接、鉛の電解抽出
に供することができる。この電解抽出は。This self-purified solution can then be directly subjected to electrowinning of lead. This electrolytic extraction.
不溶性の黒鉛からなる陽極と薄い鉛板からなる陰極とを
有する通常の電池において行なわれている。It is carried out in a conventional battery having an anode made of insoluble graphite and a cathode made of a thin lead plate.
適当な条件下で操作されることにより、非常に高品質で
純粋な陰極析出物を得ることができ、陽極でのpbo
2の析出は、はとんど阻止される。By operating under suitable conditions, very high quality and pure cathodic deposits can be obtained, with pBO at the anode
Precipitation of 2 is almost prevented.
希に、不可避的に形成されるPbO2の僅かな量は。In rare cases, a small amount of PbO2 is formed unavoidably.
過酸化水素による酸浸出工程に、戻さなければならない
。陰極物質は粗鉛に製練され、電解鉛として、市販され
る。電気分解が行なわれた溶液は。It must be returned to the acid leaching process with hydrogen peroxide. The cathode material is refined into crude lead and sold commercially as electrolytic lead. The solution that was electrolyzed.
ペーストの酸浸出工程に戻される。The paste is returned to the acid leaching process.
よく洗浄された脱硫ペーストの980g(乾燥物質で、
Pb70.5チ、Sb0.68チ、SO,18チからな
る。)が、電解採取で使い古された電解液の5tで浸出
された。この電解液は。980 g of well-washed desulphurization paste (in dry matter,
It consists of Pb 70.5chi, Sb 0.68chi, SO, 18chi. ) was leached with 5 tons of spent electrolyte from electrowinning. This electrolyte.
49.9/lのPb” 139 jl/lの遊離HBF’4 を含有している。49.9/l Pb” 139 jl/l free HBF'4 Contains.
50℃で30分間攪拌後、過酸化水素(35チ溶液)が
、処理されたペーストの4.6チの量に対して添加され
、30分以上2反応させた。After stirring for 30 minutes at 50° C., hydrogen peroxide (35% solution) was added to a 4.6% amount of treated paste and allowed to react for more than 30 minutes.
濾過により、下記の物質が分離された。The following substances were separated by filtration.
不溶性残渣の80g、その組成は。80 g of insoluble residue, its composition is.
Pb 34.2チ Sb 2.4チ 8 2.2係 及び鉛含有電解液の51.これは次のものテナ有する。Pb 34.2chi Sb 2.4chi 8 2.2 Section and 51. of lead-containing electrolytes. It has the following tena:
181.5.q/lのPb−
0,6jj/lのSb+0
25.19/lの遊離HBF4
フッ化ホウ素酸と過酸化水素とによる浸出によって、ペ
ースト中に含有される鉛のVt、 tの96o1チを抽
出された。イオウの全ては、残渣中に残っている。181.5. q/l Pb- 0.6jj/l Sb+0 25.19/l free HBF4 Extract 96o1 of lead Vt, t contained in the paste by leaching with fluoroboric acid and hydrogen peroxide. It was done. All of the sulfur remains in the residue.
予めpbo2で被膜された黒鉛の陽極と、電解鉛の薄い
板の陰極とを有する電池で電解採取するだめに、鉛含有
電解液5tを用いることにより、630gの陰極鉛と、
陽極に9.!iIのPbO2が生成された。For electrowinning in a battery having a graphite anode previously coated with pbo2 and a thin plate cathode of electrolytic lead, by using 5 tons of lead-containing electrolyte, 630 g of cathode lead,
9. to the anode. ! iI of PbO2 was produced.
電池は?7A#2.5Vで24時間にわたって動作され
た。What about batteries? 7A # operated at 2.5V for 24 hours.
陰極電流密度は、28OA/m2であシ、電流効率>、
1. !+ 7%であった。Cathode current density is 28OA/m2, current efficiency >,
1. ! +7%.
製練された陰極鉛は以下の組成分を有していた。The refined cathode lead had the following composition.
Sb < 0.001
As < 0.001
Sn < 0.001
Bi < 0.002
Cu=0.0003
Ag<0.0005
使い古された電解液は、新しいペーストの浸出工程に戻
されるべきものであり。Sb < 0.001 As < 0.001 Sn < 0.001 Bi < 0.002 Cu = 0.0003 Ag < 0.0005 The spent electrolyte should be returned to the leaching process for new paste.
53g/lのPb++ 131 g/lの遊離HBF4 を含有している。53g/l Pb++ 131 g/l free HBF4 Contains.
第1図は9本発明の処理工程の一例を示すブロックダイ
アダラムである。FIG. 1 is a block diagram showing one example of the processing steps of the present invention.
一般に2本発明によれば、過酸化鉛(Pb02)の還元
のために、従来方法によシ使用された他の還元剤に比較
して、過酸化水素の使用によって、下記の効果が得られ
る。In general, according to the present invention, the use of hydrogen peroxide for the reduction of lead peroxide (Pb02), compared to other reducing agents used in conventional methods, provides the following effects: .
■ 有毒性を示さない。■ Shows no toxicity.
■ 電気分解に供されるべき溶液に、異イオンを供給す
ることがなく、そして、その溶液は連続して再生するこ
とができる。■ Foreign ions are not supplied to the solution to be subjected to electrolysis, and the solution can be continuously regenerated.
■ 市場から容易に入手できる反応物であり。■ It is a reactant that can be easily obtained from the market.
価格もそれほど高くない。The price is also not that high.
■ 無駄なく正確に計ることができる。何故ならば、過
酸化鉛(Pbo2)の還元終了を、懸濁液の赤褐色(b
rown−rea)から灰褐色(brown−grey
)への急変により知シ得るからである。この色彩の変化
は。■ You can measure accurately without waste. This is because the reduction of lead peroxide (Pbo2) is stopped when the suspension is reddish brown (b
brown-rea to brown-gray
This is because knowledge can be gained from sudden changes in ). This color change.
視覚的に簡単に探知できるものである。It can be easily detected visually.
■ 35チ溶液の過酸化水素(H2O2)の4〜5チの
消費で、鉛(Pb)の抽出において、少なくとも95%
以」二の収率が達成される。■ At least 95% in the extraction of lead (Pb) with the consumption of 4-5 liters of hydrogen peroxide (H2O2) in 35 liters of solution.
The following yields are achieved.
第1図は本発明の処理工程を示すブロックダイヤグラム
である。FIG. 1 is a block diagram showing the processing steps of the present invention.
Claims (1)
して電気分解法による抽出により回収するための湿式回
収方法において、 a)電解抽出に適した酸から選択された酸の水溶液で上
記ペーストを浸出する浸出工程と、 b)上記浸出されたペーストに含有されている過酸化鉛
(lead dioxide)の全の定量還元に達する
迄に、 (1)Pb^4^++H_2O_2−−−→Pb^2^
+O_2+2H^+ (2)Pb+Pb^4^+−−−→2Pb^2^+ の反応を伴って、上記浸出されたペーストを、過酸化水
素で処理する処理工程と、 c)得られた鉛溶解液から固体残渣を、鉛の電解抽出に
直接供することができるように、分離する分離工程と を有することを特徴とする廃電池のペーストに含まれた
鉛の湿式回収方法。 2、特許請求の範囲第1項記載の廃電池のペーストに含
まれた鉛の湿式回収方法において、上記処理工程(b)
の上記反応(1)より発生した酸素によって上記反応(
2)が活性化されることを特徴とする廃電池のペースト
に含まれた鉛の湿式回収方法。 3、特許請求の範囲第2項記載の廃電池のペーストに含
まれた鉛の湿式回収方法において、上記反応(1)およ
び(2)と同時に不純物についてのセメンテーション作
用が上記反応(1)より発生したO_2により物理的に
活性化された上記金属鉛(Pb)によって引き起こされ
ることを特徴とする廃電池のペーストに含まれた鉛の湿
式回収方法。 4、特許請求の範囲第1項記載の廃電池のペーストに含
まれた鉛の湿式回収方法において、更にd)陰極での金
属鉛(Pb)の生成を伴う、電気分解法による抽出によ
り、上記分離工程における上記鉛溶解液を処理する溶液
処理工程と、 e)該溶液処理工程における廃電解液を上記浸出工程に
戻すことにより再生する再生工程とを付加することを特
徴とする廃電池のペーストに含まれた鉛の湿式回収方法
。 5、特許請求の範囲第1項記載の廃電池のペーストに含
まれた鉛の湿式回収方法において、上記浸出工程の上記
酸は、フッ化ホウ素酸又はフッ化ケイ素酸であることを
特徴とする廃電池のペーストに含まれた鉛の湿式回収方
法。[Claims] 1. A wet recovery method for recovering lead from waste battery paste or desulfurization paste as a pure metal by electrolytic extraction, comprising: a) an acid selected from acids suitable for electrolytic extraction; a leaching step of leaching the paste with an aqueous solution, and b) until reaching the total quantitative reduction of lead dioxide contained in the leached paste: (1) Pb^4^++H_2O_2-- −→Pb^2^
+O_2+2H^+ (2) A treatment step of treating the leached paste with hydrogen peroxide with the reaction of Pb+Pb^4^+----→2Pb^2^+; and c) the resulting lead dissolution. 1. A wet recovery method for lead contained in waste battery paste, comprising a separation step of separating a solid residue from a liquid so that it can be directly subjected to electrolytic extraction of lead. 2. In the wet method for recovering lead contained in waste battery paste as set forth in claim 1, the above treatment step (b)
The above reaction (1) is caused by the oxygen generated from the above reaction (1).
2) A wet recovery method for lead contained in waste battery paste, characterized by activating. 3. In the wet recovery method for lead contained in the paste of waste batteries as set forth in claim 2, the cementation action for impurities is simultaneously carried out by the above reactions (1) and (2). A wet recovery method for lead contained in waste battery paste, characterized in that the process is caused by the metal lead (Pb) being physically activated by the generated O_2. 4. In the wet recovery method for lead contained in the paste of waste batteries as set forth in claim 1, the above-mentioned A waste battery paste characterized by adding a solution treatment step of treating the lead solution in the separation step, and e) a regeneration step of regenerating the waste electrolyte in the solution treatment step by returning it to the leaching step. Wet recovery method for lead contained in 5. The wet recovery method for lead contained in the paste of waste batteries as set forth in claim 1, characterized in that the acid in the leaching step is fluoroboric acid or fluorosilicic acid. A wet recovery method for lead contained in waste battery paste.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| IT2289285A IT1188203B (en) | 1985-11-19 | 1985-11-19 | HYDROMETALLURGIC PROCESS TO RECOVER IN LEAD METALLIC FORM THE LEAD CONTAINED IN THE ACTIVE MASS OF THE EXHAUSTED BATTERIES |
| IT22892-A/85 | 1985-11-19 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPS62120436A true JPS62120436A (en) | 1987-06-01 |
Family
ID=11201606
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP61270818A Pending JPS62120436A (en) | 1985-11-19 | 1986-11-13 | Wet recovery of lead contained in paste of waste battery |
Country Status (6)
| Country | Link |
|---|---|
| JP (1) | JPS62120436A (en) |
| CA (1) | CA1310837C (en) |
| DE (1) | DE3637270A1 (en) |
| FR (1) | FR2590277B1 (en) |
| GB (1) | GB2183623B (en) |
| IT (1) | IT1188203B (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2011505494A (en) * | 2007-11-30 | 2011-02-24 | エンジテック テクノロジーズ ソシエタ ペル アチオニ | Process for producing metallic lead starting from desulfurized pastels |
| JP2016502602A (en) * | 2012-11-13 | 2016-01-28 | ビーエーエスエフ ソシエタス・ヨーロピアBasf Se | Recovery of lead from mixed oxide materials. |
| CN107059053A (en) * | 2017-01-10 | 2017-08-18 | 富民薪冶工贸有限公司 | A kind of method that electrolyte being electrolysed for lead and its molten lead mend lead |
| JP2021516289A (en) * | 2018-03-08 | 2021-07-01 | エンジテック テクノロジーズ ソシエタ ペル アチオニ | Its use in methods of recovering lead from lead pastel and in recovering lead-acid battery components |
Families Citing this family (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| IT1223314B (en) * | 1987-10-20 | 1990-09-19 | Engitec Impianti | HYDRO-METALLURGIC PROCESS TO RECOVER IN LEAD METALLIC FORM ALL THE LEAD CONTAINED IN THE ACTIVE MASS OF THE EXHAUSTED BATTERIES |
| IL116753A0 (en) * | 1996-01-14 | 1996-05-14 | Margulead Ltd | A process for the manufacture of pure lead oxide from exhausted batteries |
| RU2120159C1 (en) * | 1997-05-23 | 1998-10-10 | Акционерное общество закрытого типа "Курский завод "Аккумулятор" | Device for cleaning storage battery plates |
| ITVA20070007A1 (en) | 2007-01-17 | 2008-07-18 | Millbrook Lead Recycling Techn | RECOVERY OF THE LEAD OF HIGH-PURITY CARBONATE UNIFORM PASTEL RECOVERY FROM THE CRUSHING OF EXHAUSTED LEAD ACCUMULATORS |
| CN109183069B (en) | 2013-11-19 | 2021-09-17 | 艾库伊金属有限公司 | Method for continuous treatment of lead material from lead-acid batteries, and electrolytic cell |
| EP3294929B1 (en) | 2015-05-13 | 2021-04-14 | Aqua Metals Inc. | Closed loop systems and methods for recycling lead acid batteries |
| EP3294931A4 (en) | 2015-05-13 | 2018-12-26 | Aqua Metals Inc. | Electrodeposited lead composition, methods of production, and uses |
| CA2986022C (en) | 2015-05-13 | 2022-06-21 | Aqua Metals Inc. | Systems and methods for recovery of lead from lead acid batteries |
| ITUB20153182A1 (en) * | 2015-08-06 | 2017-02-06 | Pin Corp Ltd | HYDROTHERMAL PROCESS - ELECTROCHEMICAL FOR THE DIRECT RECOVERY OF METALLIC LEAD OR A MIXTURE OF METALLIC LEAD AND LEAD OXIDE (II) FROM ELECTRODIC BATTERY PASTES AT THE END OF LIFE OR FROM MINERALS OR WASTE OF PRODUCTION |
| US10316420B2 (en) | 2015-12-02 | 2019-06-11 | Aqua Metals Inc. | Systems and methods for continuous alkaline lead acid battery recycling |
Family Cites Families (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US2328089A (en) * | 1940-09-14 | 1943-08-31 | Lillian R Birkenstein | Recovery of soluble lead salts from insoluble lead compounds |
| NZ183268A (en) * | 1976-02-19 | 1978-09-20 | Gould Inc | Process for recycling junk lead-acid batteries comprising the formation of lead carbonate lead monoxide |
| US4269811A (en) * | 1978-10-10 | 1981-05-26 | Nl Industries, Inc. | Production of lead monoxide from lead sulfate with acetic acid |
| US4229271A (en) * | 1979-05-24 | 1980-10-21 | Rsr Corporation | Method of recovering lead values from battery sludge |
| GB2073725A (en) * | 1980-04-11 | 1981-10-21 | Ass Lead Mfg Ltd | A Method of Recovering Lead Values from Scrap Batteries |
| WO1984001964A1 (en) * | 1982-11-18 | 1984-05-24 | Extramet Sa | Process for selectively extracting lead from lead sulphides |
-
1985
- 1985-11-19 IT IT2289285A patent/IT1188203B/en active
-
1986
- 1986-11-03 DE DE19863637270 patent/DE3637270A1/en not_active Ceased
- 1986-11-04 GB GB8626274A patent/GB2183623B/en not_active Expired - Fee Related
- 1986-11-12 CA CA 522758 patent/CA1310837C/en not_active Expired - Fee Related
- 1986-11-13 JP JP61270818A patent/JPS62120436A/en active Pending
- 1986-11-17 FR FR868615937A patent/FR2590277B1/en not_active Expired - Fee Related
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2011505494A (en) * | 2007-11-30 | 2011-02-24 | エンジテック テクノロジーズ ソシエタ ペル アチオニ | Process for producing metallic lead starting from desulfurized pastels |
| JP2016502602A (en) * | 2012-11-13 | 2016-01-28 | ビーエーエスエフ ソシエタス・ヨーロピアBasf Se | Recovery of lead from mixed oxide materials. |
| CN107059053A (en) * | 2017-01-10 | 2017-08-18 | 富民薪冶工贸有限公司 | A kind of method that electrolyte being electrolysed for lead and its molten lead mend lead |
| JP2021516289A (en) * | 2018-03-08 | 2021-07-01 | エンジテック テクノロジーズ ソシエタ ペル アチオニ | Its use in methods of recovering lead from lead pastel and in recovering lead-acid battery components |
| US11667990B2 (en) | 2018-03-08 | 2023-06-06 | Engitec Technologies S.P.A. | Process for recovering lead from a lead pastel and use thereof in a process for recovering lead-acid accumulator components |
Also Published As
| Publication number | Publication date |
|---|---|
| IT1188203B (en) | 1988-01-07 |
| GB2183623A (en) | 1987-06-10 |
| GB8626274D0 (en) | 1986-12-03 |
| FR2590277A1 (en) | 1987-05-22 |
| IT8522892A0 (en) | 1985-11-19 |
| CA1310837C (en) | 1992-12-01 |
| DE3637270A1 (en) | 1987-05-21 |
| GB2183623B (en) | 1990-04-11 |
| FR2590277B1 (en) | 1990-05-11 |
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