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JPH0236655B2 - - Google Patents
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JPH0236655B2 - - Google Patents

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Publication number
JPH0236655B2
JPH0236655B2 JP12930286A JP12930286A JPH0236655B2 JP H0236655 B2 JPH0236655 B2 JP H0236655B2 JP 12930286 A JP12930286 A JP 12930286A JP 12930286 A JP12930286 A JP 12930286A JP H0236655 B2 JPH0236655 B2 JP H0236655B2
Authority
JP
Japan
Prior art keywords
ruthenium
alkali hydroxide
free chlorine
roasted
melting
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 - Lifetime
Application number
JP12930286A
Other languages
Japanese (ja)
Other versions
JPS62287025A (en
Inventor
Yoshiro Sugimoto
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.)
NE Chemcat Corp
Original Assignee
Nippon Engelhard 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 Nippon Engelhard Ltd filed Critical Nippon Engelhard Ltd
Priority to JP61129302A priority Critical patent/JPS62287025A/en
Publication of JPS62287025A publication Critical patent/JPS62287025A/en
Publication of JPH0236655B2 publication Critical patent/JPH0236655B2/ja
Granted 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

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  • Inorganic Compounds Of Heavy Metals (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は金属ルテニウムやその酸化物を含有す
る廃滓からルテニウムを回収する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for recovering ruthenium from wastewater containing metal ruthenium or its oxides.

〔従来の技術〕[Conventional technology]

金属状態のルテニウム又はその酸化物を含有す
る廃滓は、触媒、電極及び電子部品の製造に伴う
作業屑、不良品及び使用済のもの、切削、研磨等
の加工工程における作業屑、電解精製時に生成す
るスライム等に含まれて発生する。
Waste containing ruthenium or its oxides in the metallic state is waste from the production of catalysts, electrodes, and electronic parts, defective and used products, work waste from processing processes such as cutting and polishing, and waste during electrolytic refining. It is included in the slime etc. that is generated.

従来このような金属ルテニウムや、その酸化物
を含有する廃滓からルテニウムを溶解する方法と
しては、特開昭60−65730号、特開昭60−92433号
に記載されているように過酸化ナトリウム又は硝
酸カリウムのような酸化剤と水酸化アルカリの合
剤を用いて溶融した後、水を加えて溶解する方法
がとられている。
Conventionally, as a method for dissolving ruthenium from waste containing ruthenium metal or its oxide, sodium peroxide was used as described in JP-A-60-65730 and JP-A-60-92433. Alternatively, a method is used in which the material is melted using a mixture of an oxidizing agent such as potassium nitrate and an alkali hydroxide, and then water is added to dissolve the material.

これらの廃滓中には炭素あるいは有機物が含ま
れている場合が多く、通常前処理として、炭素や
有機物の除去のために酸化焙焼が行われる。
These tailings often contain carbon or organic substances, and oxidative roasting is usually performed as a pretreatment to remove carbon and organic substances.

然しながらグラフアイト系炭素や、例えばSiC
やWCのような金属カーバイドが含まれていると
通常の焙焼では分解除去することは出来ず、また
前記酸化性アルカリ融剤を用いて溶融すること
は、発火あるいは爆発の危険を伴なうため実施で
きなかつた。
However, graphite carbon, e.g. SiC
If it contains metal carbides such as WC or WC, it cannot be decomposed and removed by normal roasting, and melting using the above-mentioned oxidizing alkaline flux carries the risk of ignition or explosion. Therefore, it could not be implemented.

また近年取扱いの危険性から過酸化ナトリウム
の工業生産の中止が相ついで価格が高騰してい
る。
In addition, in recent years, industrial production of sodium peroxide has been stopped due to the dangers of handling it, and the price has soared.

別の方法として特開昭58−194745号には金属ル
テニウムを次亜塩素酸塩を用いて溶解する方法が
記載されている。しかしこの方法ではルテニウム
含有率が高い場合にはかなり有効であるが、ルテ
ニウム含有品位が比較的低い場合には溶解率が低
くなる問題点がある。
As another method, JP-A-58-194745 describes a method in which ruthenium metal is dissolved using hypochlorite. However, although this method is quite effective when the ruthenium content is high, there is a problem in that the dissolution rate is low when the ruthenium content is relatively low.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

本発明は前記した問題点を解消し、安全に且つ
低コストで高い抽出率にて金属ルテニウム又はそ
の酸化物を含有する廃滓中のルテニウムを溶解さ
せる方法を提供するものである。
The present invention solves the above problems and provides a method for dissolving ruthenium in waste containing metal ruthenium or its oxides safely, at low cost, and at a high extraction rate.

〔問題点を解決するための手段〕[Means for solving problems]

本発明はこの目的を達成するために、金属ルテ
ニウム及びルテニウム酸化物の少くとも一方を含
有する廃滓を酸化焙焼し、焙焼物を水酸化アルカ
リと共に溶融した後、固化物を遊離塩素を含む水
酸化アルカリ水溶液により抽出するようにしてル
テニウムを回収しようとするものである。
In order to achieve this object, the present invention oxidizes and roasts waste containing at least one of metal ruthenium and ruthenium oxide, melts the roasted product together with an alkali hydroxide, and converts the solidified product to a waste containing free chlorine. The objective is to recover ruthenium by extraction with an aqueous alkali hydroxide solution.

本明細書において、金属ルテニウムおよびルテ
ニウムの少くとも一方を含有する廃滓とは、触
媒、電極および電子部品等の製造に伴なう作業
屑、不良品およびそれらの使用済のもの並びに不
用となつたもの、切削、研磨等に伴なう作業屑、
電解精製時に生成するスライム等、ルテニウムを
回収する必要のあるもの全てを意味するものとす
る。
In this specification, ruthenium metal and slag containing at least one of ruthenium refer to waste from the production of catalysts, electrodes, electronic parts, etc., defective products, used products thereof, and unused products. work scraps from cutting, polishing, etc.
This refers to everything that needs to be recovered from ruthenium, such as slime generated during electrolytic refining.

廃滓は一般に含有していることが多い水分を先
ず蒸発させ、さらにグラフアイト系を除く炭素、
有機化合物を酸化分解除去させるために、また金
属状態のルテニウムを酸化させるために空気中で
酸化焙焼することが行われる。焙焼温度、時間は
グラフアイト系を除く炭素や有機化合物及び金属
状態のルテニウムを酸化させることが出来れば良
く、対象とする廃滓によつても異なるが、一般的
には焙焼は、たとえば、焙焼温度400〜600℃、焙
焼時間30分間〜2時間で行なうことができる。
The water content in waste slag is first evaporated, and then carbon, excluding graphite, is removed.
Oxidative roasting is performed in air to oxidatively decompose and remove organic compounds and to oxidize ruthenium in a metallic state. The roasting temperature and time are sufficient as long as they can oxidize carbon, organic compounds other than graphite, and ruthenium in the metallic state, and they vary depending on the target waste, but in general, roasting is carried out at, for example, The roasting can be carried out at a roasting temperature of 400 to 600°C and a roasting time of 30 minutes to 2 hours.

この焙焼工程が不完全でグラフアイト系を除く
炭素や有機化合物が残存していると、アルカリ溶
融後の遊離塩素を含む水酸化アルカリ水溶液で抽
出する際に、一旦溶解したルテニウムの一部を再
還元して折出させることがあり、抽出効率が悪く
なる。
If this roasting process is incomplete and carbon and organic compounds other than graphite remain, some of the ruthenium that has been dissolved will be removed when extracted with an alkali hydroxide aqueous solution containing free chlorine after alkali melting. It may be re-reduced and precipitated, resulting in poor extraction efficiency.

処理する廃滓が粉体の場合には焙焼物が焼結し
て塊状となることが多いので、それ以降の反応効
率を向上させるために塊状となつた焙焼物は−40
メツシユ程度に粉砕することが好ましい。
When the waste slag to be treated is powder, the roasted material is often sintered and becomes lumpy, so in order to improve the reaction efficiency after that, the roasted material that has become lumpy is -40
It is preferable to grind it to a mesh size.

次いで焙焼物は水酸化アルカリと混合して溶融
される。水酸化アルカリとしては通常水酸化ナト
リウムが用いられるが、他のものも使用可能であ
る。この水酸化アルカリの添加量は焙焼物の形状
により特定できないが、加温融解した時に焙焼物
が融液中に浸漬可能な量であれば良く、焙焼物が
粉砕されているときは焙焼物1重量部に対し、3
〜5重量部が好ましい。
The roasted product is then mixed with alkali hydroxide and melted. As the alkali hydroxide, sodium hydroxide is usually used, but other alkali hydroxides can also be used. The amount of alkali hydroxide added cannot be specified depending on the shape of the roasted product, but it may be sufficient as long as the roasted product can be immersed in the melt when heated and melted. 3 parts by weight
~5 parts by weight is preferred.

溶融に使用する容器の材質は、鉄、ニツケル、
アルミナ等の通常の溶融に用いられるものでよい
が、鉄板製トレーが最も経済的である。この容器
に焙焼物と水酸化アルカリを入れ混合後溶融を行
なう。一般に焙焼物と水酸化アルカリの混合物の
溶融は、たとえば、徐々に昇温し、500〜700℃で
15分間以上保持することによつて行なうことがで
きる。
The material of the container used for melting is iron, nickel,
Any material used for ordinary melting of alumina or the like may be used, but a tray made of iron plate is the most economical. The roasted material and alkali hydroxide are placed in this container, mixed, and then melted. Generally, the mixture of roasted material and alkali hydroxide is melted by gradually increasing the temperature, for example, at 500 to 700℃.
This can be done by holding it for 15 minutes or more.

アルカリ溶融によりルテニウムは遊離塩素含む
水酸化アルカリ水溶液に容易に溶解する状態に変
化する。これはルテニウム酸化物が水酸化アルカ
リにより含水化物となり膨潤してポーラスな状態
となるためと考えられる。
By alkali melting, ruthenium changes to a state where it can be easily dissolved in an aqueous alkali hydroxide solution containing free chlorine. This is thought to be because the ruthenium oxide becomes hydrated by the alkali hydroxide, swells, and becomes porous.

溶融物は冷却固化後適当な容器で遊離塩素を含
む水酸化アルカリ水溶液中で加温してルテニウム
を抽出溶解させる。遊離塩素を含む水酸化アルカ
リ水溶液としては市販の次亜塩素酸ナトリウム
(遊離塩素12%)をそのまま、あるいは水で希釈
して使用するのが一般的であるが、水酸化アルカ
リの水溶液中に塩素ガスを吸収させたものを用い
ることもできる。抽出溶解条件は対象とする溶融
固化物の形状、性質によつても異なるが、たとえ
粉状物であれば、抽出溶解は液温60〜80℃で2〜
5時間撹拌しながら行なうことができる。
After the melt is cooled and solidified, it is heated in an aqueous alkali hydroxide solution containing free chlorine in a suitable container to extract and dissolve ruthenium. As an aqueous alkali hydroxide solution containing free chlorine, it is common to use commercially available sodium hypochlorite (12% free chlorine) as it is or diluted with water. It is also possible to use a material that has absorbed gas. Extraction and dissolution conditions vary depending on the shape and properties of the target molten solidified material, but even if it is a powder, extraction and dissolution will take place at a liquid temperature of 60 to 80°C.
This can be carried out with stirring for 5 hours.

水酸化アルカリ水溶液中の遊離塩素の濃度とル
テニウムの抽出率の関係は一例によれば、遊離塩
素濃度1%のとき抽出率は41%であり、遊離塩素
濃度1.5%、2%のとき抽出率は夫々86%、99%
であり、遊離塩素の濃度は少くとも1.5%以上、
好ましくは2%以上とするのがよい。
According to one example, the relationship between the concentration of free chlorine in an aqueous alkali hydroxide solution and the extraction rate of ruthenium is that when the concentration of free chlorine is 1%, the extraction rate is 41%, and when the concentration of free chlorine is 1.5% and 2%, the extraction rate is 41%. are 86% and 99% respectively.
, the concentration of free chlorine is at least 1.5%,
The content is preferably 2% or more.

この工程によりルテニウム酸化物はルテニウム
酸のアルカリ塩として液中に抽出される。抽出率
は本発明によれば原料廃滓中のルテニウム含有量
の99%以上の抽出が可能となる。
Through this step, ruthenium oxide is extracted into the liquid as an alkali salt of ruthenic acid. According to the present invention, it is possible to extract 99% or more of the ruthenium content in the raw material waste.

抽出液は不溶解残渣を含有したまゝ、あるいは
残渣を、分離した後、公知の方法例えば蒸留法に
よりルテニウムを塩化ルテニウムとして収率99%
以上で分離精製回収することができる。
The extract may contain undissolved residue, or after separating the residue, ruthenium can be converted to ruthenium chloride using a known method such as distillation with a yield of 99%.
Separation, purification and recovery can be carried out in the above manner.

〔実施例〕〔Example〕

実施例 1 本実施例は酸化焙焼により分解できず、従来ル
テニウムを溶解することが極めて困難であつた金
属カーバイトを含有するルテニウムを含む廃滓を
用いてルテニウムを抽出する試験を行つた。すな
わち炭素(活性炭)49.8%、SiC27.5%、Ru22.7
(各重量)%の組成を有する廃滓を各3.0g宛3個
のトレーに入れ約600℃にて2時間酸化焙焼し、
得られた1.8gの焙焼物を40メツシユ以下に粉砕
し、各9gの水酸化ナトリウムを加えて混合して
元のトレーに移し、電気炉で夫々600℃、650℃、
700℃で30分間保持して溶融した。冷却後融塊は
トレーごと500mlのビーカーに移し、遊離塩素3
%を含む次亜塩素酸ナトリウム水溶液をトレー全
部が浸るところまで加え、70〜80℃で5時間溶解
した。水溶液は不溶解物を分離した後液中のルテ
ニウム含有量を求めて抽出率を計算したところ、
いずれも99%乃至それ以上の値が得られた。
Example 1 In this example, a test was conducted to extract ruthenium using waste slag containing ruthenium, which cannot be decomposed by oxidative roasting and contains metal carbide, in which it has been extremely difficult to dissolve ruthenium. Namely carbon (activated carbon) 49.8%, SiC27.5%, Ru22.7
(each weight)% of waste slag was placed in 3 trays of 3.0 g each and oxidized and roasted at approximately 600°C for 2 hours.
The obtained 1.8 g of roasted material was crushed into 40 meshes or less, 9 g of sodium hydroxide was added to each, mixed, transferred to the original tray, and heated at 600°C, 650°C, respectively in an electric furnace.
It was held at 700°C for 30 minutes to melt. After cooling, transfer the molten mass together with the tray to a 500ml beaker, and add 3 ml of free chlorine.
% sodium hypochlorite aqueous solution was added until the entire tray was submerged and dissolved at 70 to 80°C for 5 hours. After separating the insoluble matter from the aqueous solution, the extraction rate was calculated by determining the ruthenium content in the solution.
In all cases, values of 99% or higher were obtained.

比較例 1 実施例1と同じ廃滓を使用し、実施例1と同じ
条件で酸化廃焼した後アルカリ溶融することな
く、焙焼物を直接遊離塩素3%を含む次亜塩素酸
ナトリウム水溶液で実施例1と同条件で抽出した
ところ、ルテニウムの抽出率は53%であつた。
Comparative Example 1 The same waste slag as in Example 1 was used, and after being oxidized and burned under the same conditions as in Example 1, the roasted product was directly treated with an aqueous sodium hypochlorite solution containing 3% free chlorine without alkali melting. When extracted under the same conditions as in Example 1, the extraction rate of ruthenium was 53%.

比較例 2 実施例1と同じ廃滓を使用し、実施例1と同じ
条件で酸化焙焼した後焙焼物を水素を用いてルテ
ニウムを金属状態にまで還元し、これを遊離塩素
3%の次亜塩素酸ナトリウムを含むように調整し
た5%水酸化ナトリウム水溶液を用いて70〜80℃
の温度で5時間抽出したら、ルテニウムの抽出率
は77%であつた。
Comparative Example 2 The same waste slag as in Example 1 was used, and after oxidative roasting under the same conditions as in Example 1, ruthenium was reduced to a metallic state using hydrogen in the roasted product. 70-80℃ using 5% sodium hydroxide aqueous solution adjusted to contain sodium chlorite
After extraction at a temperature of 5 hours, the extraction rate of ruthenium was 77%.

実施例 2 直径5mmの球状のSiCにルテニウムが0.46重量
%担持されている使用済み触媒10gをアルミナル
ツボにとり、400℃で30分間酸化焙焼し、7.9gの
焙焼物を得た。焙焼物は粉砕することなく24gの
水酸化ナトリウムを加えて混合し、550℃で15分
間溶融した。冷却後融塊はルツボごと500mlのビ
ーカーに移し、遊離塩素3%を含む次亜酸素酸ナ
トリウム水溶液をルツボが全部浸るところまで加
え、70〜80℃で2時間溶解した。水溶液は不溶解
物を分離した後液中のルテニウム含有量を求め
た。ルテニウムの抽出率は96%であつた。
Example 2 10 g of a used catalyst in which 0.46% by weight of ruthenium was supported on spherical SiC with a diameter of 5 mm was placed in an aluminum crucible and oxidized and roasted at 400° C. for 30 minutes to obtain 7.9 g of roasted product. The roasted product was mixed with 24 g of sodium hydroxide without being crushed, and melted at 550° C. for 15 minutes. After cooling, the molten mass was transferred together with the crucible to a 500 ml beaker, and an aqueous solution of sodium hypoxite containing 3% free chlorine was added until the crucible was completely immersed, and dissolved at 70 to 80°C for 2 hours. After separating the insoluble matter from the aqueous solution, the ruthenium content in the solution was determined. The extraction rate of ruthenium was 96%.

実施例 3 実施例2において、熔融時間を30分間とし次亜
塩素酸ナトリウム水溶液による溶解温度を60〜70
℃とした以外は実施例2と同様に実施したとこ
ろ、ルテニウムの抽出率は99%であつた。
Example 3 In Example 2, the melting time was 30 minutes and the dissolution temperature with the sodium hypochlorite aqueous solution was 60 to 70 minutes.
The same procedure as in Example 2 was carried out except that the temperature was changed to .degree. C., and the extraction rate of ruthenium was 99%.

実施例 4 実施例2において、熔焼時間を500℃、溶融時
間を30分間とした以外は実施例2と同様に実施し
たところ、ルテニウムの抽出率は95%であつた。
Example 4 Example 2 was carried out in the same manner as in Example 2, except that the melting time was 500°C and the melting time was 30 minutes, and the extraction rate of ruthenium was 95%.

実施例 5 実施例2において、焙焼温度を500℃、焙焼時
間を60分間、熔融温度を500℃とした以外は実施
例2と同様に実施したところ、ルテニウムの抽出
率は79%であつた。
Example 5 Example 2 was carried out in the same manner as in Example 2, except that the roasting temperature was 500°C, the roasting time was 60 minutes, and the melting temperature was 500°C. The extraction rate of ruthenium was 79%. Ta.

比較例 3 実施例2において、熔融温度を400℃とした以
外は実施例2と同様に実施したところ、ルテニウ
ムの抽出率は10%であつた。
Comparative Example 3 Example 2 was carried out in the same manner as in Example 2 except that the melting temperature was changed to 400°C, and the extraction rate of ruthenium was 10%.

比較例 4 実施例2において、焙焼温度を500℃、熔融温
度を400℃とした以外は実施例2と同様に実施し
たところ、ルテニウムの抽出率は8%であつた。
Comparative Example 4 Example 2 was carried out in the same manner as in Example 2, except that the roasting temperature was 500°C and the melting temperature was 400°C, and the extraction rate of ruthenium was 8%.

比較例 5 実施例2で用いたと同じ使用済み触媒10gをア
ルミナルツボにとり400℃で30分間焙焼した。焙
焼物は300mlのビーカーに移し、遊離塩素2%を
含む次亜塩素酸ナトリウム水溶液に水酸化ナトリ
ウムを5重量%になるように溶解した液100mlを
加え、60〜70℃で2時間溶解した。水溶液は不溶
解物を分離した後、液中のルテニウム含有量を求
めた。ルテニウムの抽出率は0.4%であつた。
Comparative Example 5 10 g of the same used catalyst used in Example 2 was placed in an aluminum crucible and roasted at 400°C for 30 minutes. The roasted product was transferred to a 300 ml beaker, and 100 ml of a 5% by weight solution of sodium hydroxide in an aqueous sodium hypochlorite solution containing 2% free chlorine was added and dissolved at 60 to 70°C for 2 hours. After separating the insoluble matter from the aqueous solution, the ruthenium content in the solution was determined. The extraction rate of ruthenium was 0.4%.

実施例 6 比較例5で得られた不溶解残渣は一旦乾燥した
後24gの水酸化ナトリウムを用いて実質的に実施
例2と同様の処理を行つたところ、ルテニウムの
抽出率は99%であつた。
Example 6 The undissolved residue obtained in Comparative Example 5 was once dried and then treated in substantially the same manner as in Example 2 using 24 g of sodium hydroxide, and the extraction rate of ruthenium was 99%. Ta.

実施例 7 活性炭にルテニウムが5重量%担持された使用
済み触媒を600℃で2時間焙焼した。この焙焼物
のルテニウム含有量を定量したところ、ルテニウ
ム含有量は51.1重量%であつた。
Example 7 A used catalyst in which 5% by weight of ruthenium was supported on activated carbon was roasted at 600°C for 2 hours. When the ruthenium content of this roasted product was determined, the ruthenium content was 51.1% by weight.

この焙焼物1.00gをアルミナルツボにとり、水
酸化ナトリウム5gを加えて混合し、700℃30分
間熔融した。冷却後融塊はルツボごと500mlのビ
ーカーに移し純水200mlと遊離塩素12%を含む次
亜塩素酸ナトリウム水溶液70mlを加え、70〜80℃
で2時間溶解した。
1.00 g of this roasted material was placed in an aluminum crucible, 5 g of sodium hydroxide was added thereto, mixed, and melted at 700° C. for 30 minutes. After cooling, transfer the molten mass together with the crucible to a 500 ml beaker, add 200 ml of pure water and 70 ml of sodium hypochlorite aqueous solution containing 12% free chlorine, and heat at 70 to 80℃.
It was dissolved for 2 hours.

水溶液は不溶解物を分離した後、液中のルテニ
ウム含有量を求めた。ルテニウムの抽出率は95.3
%であつた。
After separating the insoluble matter from the aqueous solution, the ruthenium content in the solution was determined. Ruthenium extraction rate is 95.3
It was %.

比較例 6 実施例7で用いた焙焼物1.00gを磁性ルツボに
とり、750℃で30分間水素で還元をした。還元し
た試料はボートごと500mlのビーカーに移し、5
%水酸化ナトリウム水溶液70mlと遊離塩素を12%
含む次亜塩素酸ナトリウム水溶液20mlを加え、70
〜80℃で2時間溶解した。
Comparative Example 6 1.00 g of the roasted product used in Example 7 was placed in a magnetic crucible and reduced with hydrogen at 750°C for 30 minutes. Transfer the reduced sample to a 500ml beaker with the boat, and
% sodium hydroxide aqueous solution 70ml and free chlorine 12%
Add 20ml of sodium hypochlorite aqueous solution containing 70ml
Dissolved at ~80°C for 2 hours.

水溶液は不溶解物を分離した後、液中のルテニ
ウム含有量を求めた。ルテニウムの抽出率は16.8
%であつた。
After separating the insoluble matter from the aqueous solution, the ruthenium content in the solution was determined. Ruthenium extraction rate is 16.8
It was %.

〔効果〕〔effect〕

本発明方法によれば金属ルテニウム又はルテニ
ウム酸化物を含有する廃滓からルテニウムを回収
する際に、従来実施されていたアルカリ性酸化剤
による溶融法あるいは遊離塩素を含む水酸化アル
カリ水溶液で直接抽出する方法に比して、遥かに
高いルテニウム抽出率を得ることができるのでそ
の工業的価値は大なるものである。
According to the method of the present invention, when recovering ruthenium from waste containing ruthenium metal or ruthenium oxide, the conventional method of melting with an alkaline oxidizing agent or the direct extraction method with an aqueous alkali hydroxide solution containing free chlorine Since it is possible to obtain a much higher ruthenium extraction rate than that of conventional methods, its industrial value is great.

Claims (1)

【特許請求の範囲】 1 金属ルテニウム及びルテニウム酸化物の少な
くとも一方を含有する廃滓を酸化焙焼し、焙焼物
を水酸化アルカリと共に溶融した後、固化物を遊
離塩素を含む水酸化アルカリ水溶液により抽出す
ることを特徴とするルテニウムの回収方法。 2 焙焼物の溶融用水酸化アルカリの使用量は焙
焼物に対して重量比で3〜5倍であることを特徴
とする特許請求の範囲第1項記載のルテニウムの
回収方法。 3 水酸化アルカリ水溶液中の遊離塩素濃度は2
重量%以上であることを特徴とする特許請求の範
囲第1項記載のルテニウムの回収方法。
[Scope of Claims] 1. After oxidizing and roasting waste containing at least one of metal ruthenium and ruthenium oxide, and melting the roasted product with an alkali hydroxide, the solidified product is treated with an aqueous alkali hydroxide solution containing free chlorine. A method for recovering ruthenium characterized by extraction. 2. The method for recovering ruthenium according to claim 1, wherein the amount of alkali hydroxide used for melting the roasted product is 3 to 5 times the weight of the roasted product. 3 The free chlorine concentration in the aqueous alkali hydroxide solution is 2
The method for recovering ruthenium according to claim 1, characterized in that the amount is at least % by weight.
JP61129302A 1986-06-05 1986-06-05 Method for recovering ruthenium Granted JPS62287025A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61129302A JPS62287025A (en) 1986-06-05 1986-06-05 Method for recovering ruthenium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61129302A JPS62287025A (en) 1986-06-05 1986-06-05 Method for recovering ruthenium

Publications (2)

Publication Number Publication Date
JPS62287025A JPS62287025A (en) 1987-12-12
JPH0236655B2 true JPH0236655B2 (en) 1990-08-20

Family

ID=15006208

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61129302A Granted JPS62287025A (en) 1986-06-05 1986-06-05 Method for recovering ruthenium

Country Status (1)

Country Link
JP (1) JPS62287025A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101316656A (en) 2005-11-30 2008-12-03 住友化学株式会社 Method for producing supported ruthenium and method for producing chlorine

Also Published As

Publication number Publication date
JPS62287025A (en) 1987-12-12

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