JPS5949291B2 - Method for recovering nickel and cadmium from waste nickel-cadmium storage batteries - Google Patents

Method for recovering nickel and cadmium from waste nickel-cadmium storage batteries

Info

Publication number
JPS5949291B2
JPS5949291B2 JP54057617A JP5761779A JPS5949291B2 JP S5949291 B2 JPS5949291 B2 JP S5949291B2 JP 54057617 A JP54057617 A JP 54057617A JP 5761779 A JP5761779 A JP 5761779A JP S5949291 B2 JPS5949291 B2 JP S5949291B2
Authority
JP
Japan
Prior art keywords
cadmium
nickel
waste
storage batteries
recovering
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP54057617A
Other languages
Japanese (ja)
Other versions
JPS55152138A (en
Inventor
政治 小野
隆義 木村
博之 島谷
隆良 石田
豊和 大久保
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.)
Sumitomo Metal Mining Co Ltd
Original Assignee
Sumitomo Metal Mining Co Ltd
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 Sumitomo Metal Mining Co Ltd filed Critical Sumitomo Metal Mining Co Ltd
Priority to JP54057617A priority Critical patent/JPS5949291B2/en
Publication of JPS55152138A publication Critical patent/JPS55152138A/en
Publication of JPS5949291B2 publication Critical patent/JPS5949291B2/en
Expired legal-status Critical Current

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
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/84Recycling of batteries or fuel cells

Landscapes

  • Manufacture And Refinement Of Metals (AREA)

Description

【発明の詳細な説明】 本発明は廃ニッケルカドミウム蓄電池からニッケルおよ
びカドミウムを回収する方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for recovering nickel and cadmium from waste nickel-cadmium storage batteries.

ニッケルカドミウム蓄電池はその主な構成材料はニッケ
ルとカドミウムで、また電解液として水酸化カリウムが
用いられていることから廃電池をそのまま捨てることは
環境汚染を惹き起すおそれがあり、また資源回収の点か
らも有価金属の回収が望まれている。
The main constituent materials of nickel-cadmium storage batteries are nickel and cadmium, and potassium hydroxide is used as the electrolyte, so throwing away waste batteries as they are may cause environmental pollution, and there are also concerns regarding resource recovery. It is also desired to recover valuable metals from

従来廃壬ツケルカドミウム蓄電池からのこれらの金属の
回収法としては、廃電池を解体して陰極板と陽極板を取
出し、水洗後500〜600℃で焙焼し、次いづ硝酸ア
ンモニウム水溶液でカドミウムを抽出後、炭酸カドミウ
ムとして沈澱分離して常法によりカドミウムを回収し、
ニッケルは抽出液より分離回収する方法、廃電池からの
ニッケル・カドミウム混合スラッジを亜鉛電解廃液など
を用いて浸出後沢過し、r液を亜鉛末で置換してスポン
ジカドミウムを作り、ニッケルは浸出滓として回収する
方法などが提案されているが、これらの方法はいずれも
処理工程が複雑で排水処理などの点に問題が多かった。
Conventional methods for recovering these metals from discarded cadmium storage batteries include disassembling the discarded battery, removing the cathode plate and anode plate, washing with water, roasting at 500 to 600°C, and then extracting cadmium with an aqueous ammonium nitrate solution. After that, cadmium is precipitated and separated as cadmium carbonate, and cadmium is recovered by a conventional method.
Nickel is separated and recovered from the extraction solution, nickel and cadmium mixed sludge from waste batteries is leached using zinc electrolysis waste solution, etc., and then filtered, and the R solution is replaced with zinc powder to create sponge cadmium, and nickel is leached out. Methods have been proposed to collect the waste as slag, but all of these methods involve complicated treatment processes and have many problems in terms of wastewater treatment.

本発明は上述の欠点を解消し、簡単な工程で抽出処理を
行わないでニッケルとカドミウムを回収する方法を提供
するものである。
The present invention overcomes the above-mentioned drawbacks and provides a method for recovering nickel and cadmium in a simple process and without any extraction process.

発明者はニッケルカドミウム蓄電池の構造につき検討し
、カドミウムはカドミウム塩の形で主として陰極板に含
浸電着されており、また陰極板、陽極板ともにニッケル
製またはニッケル合金製の網にニッケル微粉末を焼結し
たものであるので、該蓄電池外殻ケースに孔をあけると
か、切れ目を入れることなどによって開口部を設けた後
、非酸化性雰囲気中で700〜1,600℃の温度で加
熱すれば水酸化カリウム水溶液から成る電解液は蒸発し
、カドミウム塩は酸化カドミウムとなり、カドミウムと
二ツ゛ケルの両者の酸素との親和力の差によってニッケ
ルが還元剤の作用をなし、カドミウムが還元揮発し、こ
のカドミウム含有ガスを凝縮器に導入して冷却すれば金
属状のカドミウムが回収されニッケル分は残渣として残
留することに着目して本発明に到達した。
The inventor studied the structure of a nickel-cadmium storage battery, and found that cadmium is mainly impregnated and electrodeposited on the cathode plate in the form of cadmium salt, and that both the cathode plate and the anode plate are made of nickel or nickel alloy mesh with nickel fine powder. Since it is a sintered product, it can be heated at a temperature of 700 to 1,600°C in a non-oxidizing atmosphere after providing an opening by making a hole or cutting a hole in the outer shell case of the storage battery. The electrolytic solution consisting of an aqueous potassium hydroxide solution evaporates, and the cadmium salt becomes cadmium oxide.Due to the difference in affinity between cadmium and nickel for oxygen, nickel acts as a reducing agent, and the cadmium is reduced and volatilized. The present invention was developed based on the fact that if the contained gas is introduced into a condenser and cooled, metallic cadmium is recovered and nickel remains as a residue.

加熱に先立って蓄電池の外殻に開口部を設けるのは加熱
時の電解液やカドミウムの揮発を容易にするためであり
、外殻に多数の孔をあけるか複数箇所に切れ目を設ける
のが好ましい。
The purpose of making openings in the outer shell of the storage battery before heating is to facilitate the volatilization of the electrolyte and cadmium during heating, and it is preferable to make many holes in the outer shell or make cuts in multiple places. .

電池の製造工程で発生した極板層等を処理する場合は外
殻が電池として構成されていないので開口の必要はない
When processing electrode plate layers and the like generated during the battery manufacturing process, there is no need for openings because the outer shell is not configured as a battery.

熱処理温度の下限を700℃としたのはそれ以下の温度
ではカドミウムの還元並びに揮発が十分でなく、また上
限を1,600’Cとしたのはそれ以上の温度では熱処
理装置の損傷が犬となり好ましくない。
The lower limit of the heat treatment temperature was set at 700°C because the reduction and volatilization of cadmium would not be sufficient at lower temperatures, and the upper limit was set at 1,600'C because at higher temperatures the heat treatment equipment would be damaged. Undesirable.

熱処理中の雰囲気については、材料中のニッケルが還元
剤の作用をしてカドミウムを還元するので非酸化性雰囲
気であれば十分で、特に炭材等の固体還元剤の添加は必
要ないが、積極的に還元剤を加えて還元性雰囲気とすれ
ば処理時間を短縮することができる。
Regarding the atmosphere during heat treatment, a non-oxidizing atmosphere is sufficient as nickel in the material acts as a reducing agent and reduces cadmium, and there is no need to add a solid reducing agent such as carbonaceous material. If a reducing agent is added to create a reducing atmosphere, the processing time can be shortened.

以下実施例について述べる。Examples will be described below.

実施例 1 ニッケルカドミウム廃電池20個1量1460 P)を
油圧プレスで圧縮して、電池外殻を開口させて試験炉に
装入し、CO2ガスを14/分流しながら900℃で2
時間加熱し、炉に付設した凝縮器で金属カドミウムを回
収した。
Example 1 20 nickel-cadmium waste batteries (each weighing 1460 P) were compressed using a hydraulic press, the outer shell of the battery was opened, the battery was charged into a test furnace, and the battery was heated at 900°C for 2 hours while flowing CO2 gas at 14/min.
After heating for several hours, metal cadmium was recovered in a condenser attached to the furnace.

回収した金属カドミウムを分析したところ、Ni、Fe
、C1lはいずれも0.001%以下、Zn、Pbは夫
々0.005%以下(いずれも重量%)で純度のよいカ
ドミウムが回収できた。
When the recovered metal cadmium was analyzed, it was found that Ni, Fe
, C1l were all 0.001% or less, and Zn and Pb were each 0.005% or less (all by weight), and cadmium with good purity could be recovered.

また加熱処理後の残留物を取出し、これを加熱溶解して
得た金属塊の分析値はNi49,7%F e 48.7
%、CdO,01%(いずれも爪電伽)でCdが十分
分離できていた。
In addition, the analysis value of the metal lump obtained by removing the residue after the heat treatment and heating and melting it was Ni49, 7%Fe48.7
%, CdO, 01% (both Tsume Denga), Cd could be sufficiently separated.

実施例 2 ニッケルカドミウム蓄電池の製造工程で発生した陰陽両
極板屑の混合物201をアルミナ製ボートに入れて石英
反応管中でCO2ガスを0.5t/分の割合で流し、7
000乃至900℃で60分間加熱してカドミウムを揮
発させた。
Example 2 A mixture 201 of negative and positive plate scraps generated in the manufacturing process of a nickel-cadmium storage battery was placed in an alumina boat, and CO2 gas was passed through it at a rate of 0.5 t/min in a quartz reaction tube.
The mixture was heated at 000 to 900° C. for 60 minutes to volatilize the cadmium.

加熱残渣を分析してカドミウムの揮発率を求めたところ
700℃で94%、800℃及び900℃では夫々98
係以上であった。
When the heating residue was analyzed and the cadmium volatilization rate was determined, it was 94% at 700°C and 98% at 800°C and 900°C.
It was above the level of staff.

実施例 3 実施例2の材料を石英反応管中でco:co。Example 3 The materials of Example 2 were co:co in a quartz reaction tube.

二N2の比が1:1:4の混合ガスを0.6−7/分の
割合で流し、800℃及び900℃で加熱して加)熱時
間と揮発率との関係をしらべた。
A mixed gas having a ratio of 2N2 of 1:1:4 was flowed at a rate of 0.6-7/min and heated at 800°C and 900°C to examine the relationship between heating time and volatility rate.

その結果カドミウムの揮発率が95係以上となるために
は800℃では30分、900℃では20分で達成され
ることがわかった。
As a result, it was found that it takes 30 minutes at 800° C. and 20 minutes at 900° C. for the volatilization rate of cadmium to reach a factor of 95 or higher.

実施例 4 ニッケルカドミウム蓄電池の製造工程で発生した陰陽両
極板屑の混合物201に褐炭粉末を極板屑に対して5〜
25重量%添加混合し、アルミナ製ボートに入れて石英
反応管中で02二N2の比が1:10の混合ガスを0.
55.!/分(萼拾で流し、800℃で1時間加熱して
カドミウムの揮発率を測定した。
Example 4 Brown coal powder was added to a mixture 201 of negative and positive plate scraps generated in the manufacturing process of a nickel-cadmium storage battery at a ratio of 5 to 50% of the electrode plate scraps.
25% by weight was added and mixed, placed in an alumina boat, and mixed with 0.2 and N2 at a ratio of 1:10 in a quartz reaction tube.
55. ! /min (flowed with a calyx pick-up, heated at 800°C for 1 hour, and measured the volatilization rate of cadmium.

その結果褐炭の混合率5髪で揮発性92%、10%で9
5%、15%以上では99チ以上が得ちれた。
As a result, the volatility was 92% when the lignite mixture ratio was 5, and 9 when it was 10%.
At 5% and 15% or higher, scores of 99 or higher were obtained.

上述のように実施例1.2から加熱の場合の雰囲気は、
J■u生であねわ沖沖14心生にしなくても含有するカ
ドミウムの殆んどを金属カドミウムとして回収すること
ができる。
As mentioned above, from Example 1.2, the atmosphere for heating is as follows:
Most of the cadmium contained in J■u raw material can be recovered as metallic cadmium without converting it to Anewa Oki Oki 14 core raw material.

また回収された金属カドミウムは純度が高く、加熱処理
した残渣からはニッケルを回収することができ、ニッケ
ルカドミウム廃電池を有効に且つ容易に処理して、資源
の再利用を可能にした効果は犬である。
In addition, the recovered metal cadmium has a high purity, and nickel can be recovered from the heat-treated residue, making it possible to effectively and easily process nickel-cadmium waste batteries and reuse the resource. It is.

Claims (1)

【特許請求の範囲】[Claims] 1 廃ニッケルカドミウム蓄電池の外殻の少くとも一部
を開口し、非酸化性雰囲気で700〜1,600℃の温
度で熱処理し、カドミウムを揮発させて捕集することを
特徴とする廃ニッケルカドミウム蓄電池からのニッケル
とカドミウムの回収方法。
1 Waste nickel cadmium, characterized in that at least a part of the outer shell of a waste nickel cadmium storage battery is opened and heat treated at a temperature of 700 to 1,600°C in a non-oxidizing atmosphere to volatilize and collect cadmium. How to recover nickel and cadmium from storage batteries.
JP54057617A 1979-05-12 1979-05-12 Method for recovering nickel and cadmium from waste nickel-cadmium storage batteries Expired JPS5949291B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP54057617A JPS5949291B2 (en) 1979-05-12 1979-05-12 Method for recovering nickel and cadmium from waste nickel-cadmium storage batteries

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP54057617A JPS5949291B2 (en) 1979-05-12 1979-05-12 Method for recovering nickel and cadmium from waste nickel-cadmium storage batteries

Publications (2)

Publication Number Publication Date
JPS55152138A JPS55152138A (en) 1980-11-27
JPS5949291B2 true JPS5949291B2 (en) 1984-12-01

Family

ID=13060830

Family Applications (1)

Application Number Title Priority Date Filing Date
JP54057617A Expired JPS5949291B2 (en) 1979-05-12 1979-05-12 Method for recovering nickel and cadmium from waste nickel-cadmium storage batteries

Country Status (1)

Country Link
JP (1) JPS5949291B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SE450494B (en) * 1981-09-24 1987-06-29 Sab Nife Ab PROCEDURE FOR THE RECYCLING OF METALS OF SCRAP FROM NICKEL-CADMIUM ACCUMULATORS

Also Published As

Publication number Publication date
JPS55152138A (en) 1980-11-27

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