JP3024396B2 - In recovery method - Google Patents

In recovery method

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Publication number
JP3024396B2
JP3024396B2 JP29913492A JP29913492A JP3024396B2 JP 3024396 B2 JP3024396 B2 JP 3024396B2 JP 29913492 A JP29913492 A JP 29913492A JP 29913492 A JP29913492 A JP 29913492A JP 3024396 B2 JP3024396 B2 JP 3024396B2
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JP
Japan
Prior art keywords
cement
added
plate
solution
metal
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
JP29913492A
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Japanese (ja)
Other versions
JPH06128664A (en
Inventor
晴俊 窪田
千秋 南
和彦 武井
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
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Publication date
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Priority to JP29913492A priority Critical patent/JP3024396B2/en
Publication of JPH06128664A publication Critical patent/JPH06128664A/en
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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

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、Zn製錬における中間
物からのInの回収に関し、効率良くしかも有害ガスの
発生を伴わない状態で粗Inを得る方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the recovery of In from intermediates in Zn smelting, and more particularly to a method for obtaining crude In efficiently and without generating any harmful gas.

【0002】[0002]

【従来の技術】従来より、Inは、主として、Cdと共
に、Znの製錬工程に於ける副産物として産出されるこ
とが知られている。Znの製錬工程においてInやCd
を分離して行く方法としては、先ず、Znの製錬工程に
おいて得られる中間物を鉱酸酸性下で還元浸出して、I
nを含有する浸出液を得、次いで、このInを含有する
浸出液に、浸出液中のIn量に対して1化学当量前後の
Zn粉末もしくはCd−Zn粉末を添加してセメントI
nを置換析出させ、さらに、このセメントInにNaO
Hを添加して加熱融解し、生成したソーダスラグと粗I
nとを分離回収し、この粗Inをさらに電解精製して高
純度のInを入手する方法が採られていた。
2. Description of the Related Art It is conventionally known that In is mainly produced together with Cd as a by-product in a smelting process of Zn. In and Cd in the Zn smelting process
First, an intermediate obtained in the smelting process of Zn is reduced and leached under the acidity of a mineral acid to obtain I
n-containing leachate is obtained, and then Zn powder or Cd-Zn powder is added to the leachate containing In at about 1 chemical equivalent relative to the amount of In in the leachate, and cement I is added.
n is replaced by precipitation, and NaO is added to the cement In.
H was added and melted by heating.
n is separated and recovered, and the crude In is further electrolytically purified to obtain high-purity In.

【0003】しかしながら、Inを含有する浸出液中の
Cd共存量が多くなると、セメントIn中に占めるCd
の含有量が高くなったり、セメントInを融解する時に
Cdと共存しているTeのためにセメントInが酸化し
やすい状態となり、結果的に、粗Inを高い歩留まりで
収集することが不可能になる等の不都合を生じていた。
However, when the coexisting amount of Cd in the leachate containing In increases, the Cd occupying in the cement In increases.
Or the cement In is easily oxidized due to Te coexisting with Cd when the cement In is melted. As a result, it becomes impossible to collect the crude In at a high yield. Inconvenience such as becoming.

【0004】特に、浸出液中にAsが0.5ppm以上
共存する場合には、Inの置換析出工程で、有害なAs
3 の発生を呼び起こしてしまうが、一端AsH3 を発
生させると、このAsH3 の無害化処理が必須とされ、
作業環境等の整備については高額な投資が余儀無くされ
る。
[0004] In particular, when As is present in the leachate in an amount of 0.5 ppm or more, harmful As is removed in the displacement precipitation step of In.
This will cause the generation of H 3 , but once AsH 3 is generated, this AsH 3 detoxification process is required,
Expensive investment is inevitable for improving the working environment.

【0005】このため、この投資を軽減させるために、
Zn粉末もしくはCd−Zn粉末を添加するに先立ち、
浸出液中のAsの含有量を0.5ppm未満まで低下さ
せた後、Inを置換析出させることが一般的であった。
Therefore, in order to reduce this investment,
Prior to adding Zn powder or Cd-Zn powder,
After reducing the content of As in the leaching solution to less than 0.5 ppm, it was common to replace and precipitate In.

【0006】Asの含有量を低下させる簡便な方法とし
て、イオン交換法や溶媒抽出法が提案されているが、こ
れらの方法にても充分に満足の行くほどAsを除去出来
るものではなく、最終的には、硫化処理を施すことによ
りAsをAs23 として固定して分離しなければなら
ない。
As a simple method for reducing the As content, ion exchange and solvent extraction have been proposed. However, these methods cannot sufficiently remove As, and are not satisfactory. Specifically, As must be fixed as As 2 S 3 by performing a sulfidation treatment and separated.

【0007】したがって、イオン交換法や溶媒抽出法の
採用は、Inの回収工程をより複雑にするばかりでな
く、従来と同様、共存するCdも同時に硫化するためI
nとCdの同時回収効率を低くしてしまう。加えて、こ
れらの金属の硫化工程で発生する悪臭を除去することに
多くの配慮を重ねなければならない。
Therefore, the adoption of the ion exchange method and the solvent extraction method not only complicates the step of recovering In but also sulfides the coexisting Cd at the same time as in the conventional case.
The efficiency of simultaneous recovery of n and Cd is lowered. In addition, much attention must be paid to eliminating the odors generated during the sulfurization of these metals.

【0008】[0008]

【発明が解決しようとする課題】本発明は、Znの製錬
工程で発生する中間物よりInを回収するに際して、従
来にもまして効率的に、しかも、AsH3 の発生のない
Inの回収方法を開示することをその目的とする。
SUMMARY OF THE INVENTION The present invention provides a method for recovering In from an intermediate generated in a smelting process of Zn, which is more efficient than the conventional method and which does not generate AsH 3. Its purpose is to disclose.

【0009】[0009]

【課題を解決するための手段】本発明者等は、上記の課
題を解決するために鋭意研究試験を行った結果、Zn製
錬工程に於いて発生してくるCd、Zn、In、Te、
As等を含有した中間物よりInを回収するに際して、
還元剤としてTe化合物やAs化合物を生成させるに必
要な量の2当量以上の金属Cdと金属Inもしくはこの
ような量の金属Cdと金属Inを含有する還元用澱物を
用いて上記中間物を鉱酸酸性下で還元浸出して浸出液と
し、この浸出液に水酸化アルカリ水溶液を添加してpH
を1.5〜2.5に調整し、この液から残渣を分離して
得た濾液中に板状のCdを浸漬し、板状のCdの表面に
セメントInを置換析出させ、板状のCdの表面より剥
離して得たセメントInに、該セメントInに対して5
〜20重量%のNaOHを添加して後、摂氏200〜3
00度で融解して、発生したソーダスラグを層分離して
Inを回収すること、さらには、セメントInを置換析
出させた後の尾液に、アルカリ水溶液を添加して、その
pHを4〜6に調整し、生成した沈澱物を中間物の鉱酸
酸性下における還元浸出時に添加することで前記課題の
解決されることを見出し本発明に至ったものである。
Means for Solving the Problems The present inventors have conducted intensive research tests to solve the above-mentioned problems, and as a result, Cd, Zn, In, Te, and Cd generated in the Zn smelting process.
When recovering In from an intermediate containing As or the like,
The above-mentioned intermediate is obtained by using, as a reducing agent, two or more equivalents of metal Cd and metal In necessary for generating a Te compound or an As compound or a reducing precipitate containing such amounts of metal Cd and metal In. Leaching is performed by reducing and leaching under acidic acidic conditions with mineral acid.
Was adjusted to 1.5 to 2.5, and plate-like Cd was immersed in the filtrate obtained by separating the residue from this solution, and cement In was substituted and precipitated on the surface of the plate-like Cd to form a plate-like Cd. Cement In obtained by exfoliating from the surface of Cd
After addition of ~ 20 wt% NaOH, 200 ~ 3 Celsius
Melting at 00 degrees and layer separation of the generated soda slag to recover In. Further, an alkaline aqueous solution is added to the tail liquid after the substitution and precipitation of cement In, and the pH thereof is adjusted to 4-6. It has been found that the above-mentioned problem can be solved by adding the resulting precipitate during the reductive leaching of the intermediate under the acidic condition of mineral acid, thereby achieving the present invention.

【0010】[0010]

【作用】本発明において、Zn製錬の中間物よりInを
還元浸出させるのは、上記の中間物中に含有されるTe
とAsを難溶性のTe化合物とAs化合物とに変じて系
外に除去し易くするためのものであり、この場合、含有
するTeとAsの2当量をこえる金属CdおよびInを
還元剤として用いているのは、この量が2当量未満では
中間物中に含有されるTeとAsを難溶性のTe化合物
とAs化合物とに変じるのが不十分であるためである。
In the present invention, the reduction leaching of In from the Zn smelting intermediate is based on the Te contained in the intermediate.
And As are converted into a sparingly soluble Te compound and an As compound to facilitate removal from the system. In this case, metals Cd and In containing more than 2 equivalents of Te and As are used as reducing agents. The reason for this is that if this amount is less than 2 equivalents, it is insufficient to convert Te and As contained in the intermediate into a poorly soluble Te compound and an As compound.

【0011】また、この処理に際して、還元剤の量が2
当量を超える場合には、HClやH2 SO4 等の鉱酸酸
性度には特にこだわらない。さらに、還元剤の濃度は5
0〜200g/リットルとなるように調整することが望
ましい。
In this treatment, the amount of the reducing agent is 2
When the amount exceeds the equivalent, there is no particular restriction on the acidity of mineral acids such as HCl and H 2 SO 4 . Further, the concentration of the reducing agent is 5
It is desirable to adjust so as to be 0 to 200 g / liter.

【0012】なお、上記の中間物中に金属Znを含有せ
ず、一方、充分な量の金属Cdや金属Inを含有する場
合には、還元浸出工程として特にこのような還元剤を添
加する必要はない。
When the above intermediate does not contain metal Zn, but contains a sufficient amount of metal Cd or metal In, it is particularly necessary to add such a reducing agent in the reduction leaching step. There is no.

【0013】また、粗Inを得るに際して生成するソー
ダスラグの中には一般に粒状の金属Inが懸濁している
ので還元剤として適している。この金属Inが還元剤の
代用をなすばかりでなく、ソーダスラグの利用はInの
回収率の面から見ても有効である。
[0013] Soda slag produced when obtaining crude In is generally suitable as a reducing agent since granular metal In is suspended therein. Not only does this metal In substitute for the reducing agent, but the use of soda slag is also effective from the viewpoint of the recovery rate of In.

【0014】次いで、浸出液のpH値を1.5〜2.5
に規定したのは、金属Cd板を用いた置換反応を有効に
作用させるためのものであり、pH値が1.5未満では
InとCdの酸化還元電位の差が殆ど無いのでInの析
出速度が遅くなってくるためであり、逆に、pH値が
2.5を超えるとIn(OH)3 の生成が加速されこと
から、Cd板表面へのInの析出現象が妨げられて来る
ようになるためである。
Next, the pH value of the leachate is adjusted to 1.5 to 2.5.
The reason for this is to make the substitution reaction using a metal Cd plate work effectively. When the pH value is less than 1.5, there is almost no difference between the oxidation-reduction potentials of In and Cd, so the deposition rate of In is small. Conversely, when the pH value exceeds 2.5, the generation of In (OH) 3 is accelerated, so that the precipitation of In on the Cd plate surface is prevented. It is because it becomes.

【0015】金属Cdとして板を用いたのは、その表面
に析出してくるセメントInをはぎ取って工程を進める
際に、剥ぎ取りを容易にすると共に、その剥ぎ取ったセ
メントInの中に未反応のCdを介在させないためであ
り、金属Cdを粉末やショットの形状で工程中に供した
のではこの目的が充分に達成出来ないからである。
The reason why the plate is used as the metal Cd is that, when the cement In deposited on the surface is peeled off and the process is carried out, the peeling is facilitated, and the unreacted cement In is removed. This is because metal Cd is not interposed in the process in the form of powder or shot during the process.

【0016】剥ぎ取ったセメントInに対して5〜20
重量%のNaOHを添加して融解するのは、NaOHの
添加量が5%未満では融解時にセメントInが酸化され
やすくなるためであり、その量が逆に20重量%を超え
ると処理するソーダスラグの量がいたずらに多くなって
くるためである。また、融解温度を摂氏200〜300
度とするのは、200度未満の融解温度で処理したので
はスラグの流動性が悪くなってソーダスラグと粗Inと
の分離が容易でなくなるためであり、300度を超えて
の融解処理ではInの回収性に問題はないものの、高温
処理による作業効率に向上が認められないことと省エネ
ルギーの面から見て得策とは成り得ないためである。
5 to 20 with respect to the peeled cement In
The reason why NaOH is added and melted by weight is that if the amount of NaOH is less than 5%, the cement In is easily oxidized at the time of melting, and if the amount exceeds 20% by weight, the amount of soda slag to be treated is increased. This is because the amount becomes unnecessarily large. Further, the melting temperature is set to 200 to 300 degrees Celsius.
The reason for this is that if the treatment is performed at a melting temperature of less than 200 degrees, the fluidity of the slag deteriorates and it becomes difficult to separate the soda slag and the crude In. Although there is no problem in the recoverability of the wastewater, no improvement in the working efficiency due to the high-temperature treatment is recognized, and this is not a good measure from the viewpoint of energy saving.

【0017】Inを置換析出した後の尾液に対してアル
カリ溶液を添加することにより尾液のpH値を4〜6に
調整して尾液中に残存しているInの回収を計っている
が、この場合、そのpH値を4〜6に調整したのは、p
Hの値が4未満ではInを回収するためのIn(OH)
3 が充分に生成されず、逆に、その値が6を超えるとC
dまでが水酸化物になってしまい、繰り返す水酸化物が
増加するのみでなく、尾液よりのCdの直接回収率を低
下させてしまうことになるからである。
The pH of the tail liquor is adjusted to 4 to 6 by adding an alkali solution to the tail liquor after the substitution precipitation of In, and the remaining In in the tail liquor is measured. However, in this case, the pH value was adjusted to 4 to 6 because p
If the value of H is less than 4, In (OH) for recovering In
3 is not generated sufficiently, and conversely, if its value exceeds 6, C
This is because up to d becomes hydroxide, which not only increases the number of repeated hydroxides but also lowers the direct recovery rate of Cd from the tail liquor.

【0018】以上のようにして回収した粗Inは1〜3
重量%のCdを含むものの、TeやAsを殆ど含まれな
いことから高純度Inを製造するに際して、塩素錯体と
してのCdを形成させたのち、アニオン交換樹脂を利用
した電解精製装置を用いてCdを捕捉し、ここにZn製
錬の中間物からその最終目的とする精製Inを容易に電
解精製して純度が99.99%のInを容易に入手し得
た。
The crude In recovered as described above is 1 to 3
In producing high-purity In because it contains Cd by weight but contains little Te or As, Cd is formed as a chlorine complex, and then Cd is formed using an electrolytic refining apparatus using an anion exchange resin. , And the purified In which was the final target was easily electrorefined from the intermediate of Zn smelting and In with a purity of 99.99% could be easily obtained.

【0019】なお、板状のCdの表面にセメントInを
置換析出させるために、以下の実施例では、板状のCd
の周囲に液循環を行わせているが、本発明は液循環に限
られない。すなわち、板状のCdを液中で揺動させた
り、液を単に攪拌させてもよい。
In order to replace and precipitate cement In on the surface of the plate-like Cd, the following examples will be described.
Is circulated around the liquid, but the present invention is not limited to the liquid circulation. That is, the plate-shaped Cd may be swung in the liquid, or the liquid may be simply stirred.

【0020】[0020]

【実施例】以下、本発明の実施例について詳述する。Embodiments of the present invention will be described below in detail.

【0021】[0021]

【実施例1】重量%にて、水分が24.3%であり、I
nが48.4%であり、Cdが40.6%であり、Te
が1.7%であり、Asが0.02%であり、湿量が3
35kg(乾量が254kg)である含Inセメントに
対して、35重量%のHClを550リットル添加した
状態で凡そ18時間にわたって攪拌した後、250g/
リットルの濃度に調整されているNaOHを160リッ
トル添加してpHが2.0の溶液を作成し、この溶液を
濾過して黒色を呈する残渣を湿量で24kgと濾液13
40リットルを得た。
Example 1 In terms of% by weight, the water content was 24.3%.
n is 48.4%, Cd is 40.6%, and Te
Is 1.7%, As is 0.02%, and the moisture content is 3%.
35 g of In-cement containing 254 kg (dry weight) was stirred for about 18 hours with 550 liters of 35% by weight HCl added thereto, and then 250 g /
A solution having a pH of 2.0 was prepared by adding 160 liters of NaOH adjusted to a concentration of 1 liter, and the solution was filtered.
40 liters were obtained.

【0022】この場合、得られた残渣の組成は重量%に
て水分が38.1%であり、Cdが20.8%であり、
Inが9.8%であり、Teが25.4%であり、As
が0.28%であった。
In this case, the composition of the obtained residue has a water content of 38.1% by weight and a Cd of 20.8%,
In is 9.8%, Te is 25.4%, and As
Was 0.28%.

【0023】また、得られた濾液の組成はInが98.
0g/リットルであり、Cdが88.7g/リットルで
あり、Teが0.005g/リットル以下であり、As
が0.0005g/リットルであって、濾液の組成とし
てはTeとAsが殆ど含まれていなかった。
The composition of the obtained filtrate was 98.
0 g / liter, Cd is 88.7 g / liter, Te is 0.005 g / liter or less, and As
Was 0.0005 g / liter, and the composition of the filtrate contained almost no Te and As.

【0024】このTeとAsが殆ど含まれていない濾液
の中に総表面積が4.9m2 となるように金属Cdの板
材を浸漬して、この金属Cdの板材の周囲を毎分40リ
ットルの割合で72時間にわたって上記の濾液を循環さ
せた後、Cd板の表面に析出していたセメントInをC
d板の表面から剥ぎ取り、充分に水洗し、乾燥し、さら
にNaOHの15kgを合わせた混合物をステンレス製
のるつぼを用いて摂氏250度にて融解し、上下に分離
したソーダスラグ28kgと粗In126kgとを得
た。ソーダスラグはすくい取って粗Inから分離した。
A metal Cd plate is immersed in the filtrate containing little Te and As so as to have a total surface area of 4.9 m 2, and around the metal Cd plate at a rate of 40 liters per minute. After the above filtrate was circulated for 72 hours at a rate, the cement In deposited on the surface of the Cd plate was removed by C
d. Peel off the surface of the plate, wash thoroughly with water, dry, and further melt a mixture of 15 kg of NaOH at 250 degrees Celsius using a stainless steel crucible, and separate 28 kg of soda slag and 126 kg of coarse In separated vertically. I got The soda slag was scooped and separated from the crude In.

【0025】この場合に得られたソーダスラグの組成は
重量%にて、Inが19.3%であり、Cdが0.90
%であり、Teが0.022%であり、Asが0.00
4%であった。
The composition of the soda slag obtained in this case is 19.3% by weight of In and Cd is 0.90% by weight.
%, Te is 0.022%, and As is 0.00
4%.

【0026】また、粗Inの組成は重量%にて、Inが
98.6%であり、Cdが1.22%であり、Teが
0.001%以下であり、Asが0.001%以下であ
って、粗InにはTeとAsが殆ど認められない状態で
あった。TeとAsが実質的にソーダスラグに分配され
ていることがわかる。
The composition of the crude In is as follows: in terms of% by weight, In is 98.6%, Cd is 1.22%, Te is 0.001% or less, and As is 0.001% or less. In the crude In, Te and As were hardly recognized. It can be seen that Te and As are substantially distributed to the soda slag.

【0027】なお、金属Cdの板材の周囲を毎分40リ
ットルの割合で72時間にわたって上記の濾液を循環さ
せた後、Cd板の表面に析出していたセメントInをC
d板の表面から剥ぎ取った時点で得られた尾液の組成
は、1リットルの尾液の中にInを6.3gと、Cdを
208gと、Teを0.005g以下と、Asを0.0
005g以下とを含むものであって、この尾液にNaO
Hが250g/リットルの割合で含まれる水溶液を35
リットル使用してpHを5.5に調整し、16時間かけ
て静置沈降させて450リットルのIn(OH)3 相と
1040リットルのCdSO4 相を得た。
After the above filtrate was circulated at a rate of 40 liters per minute for 72 hours around the metal Cd plate, the cement In deposited on the surface of the Cd plate was removed from the Cd plate.
The composition of the tail liquid obtained at the time of peeling off from the surface of the d-plate was as follows: 6.3 g of In, 208 g of Cd, 0.005 g or less of Te, and 0% of As in 1 liter of tail liquid. .0
005 g or less.
An aqueous solution containing H at a rate of 250 g / liter in 35
The pH was adjusted to 5.5 using 1 liter and allowed to settle for 16 hours to give 450 liters of the In (OH) 3 phase and 1040 liters of the CdSO 4 phase.

【0028】この場合、In(OH)3 相の組成は1リ
ットル当たりInが20.6gであり、CdSO4 相の
組成は1リットル当たり、Cdが195gであり、In
が0.004gであり、Teが0.005g以下であ
り、Asが0.0005g以下であった。CdSO4
の不純物が極めて少なく、Cd回収に有利であることが
わかる。
In this case, the composition of the In (OH) 3 phase is 20.6 g of In per liter, the composition of the CdSO 4 phase is 195 g of Cd per liter, and
Was 0.004 g, Te was 0.005 g or less, and As was 0.0005 g or less. It can be seen that the CdSO 4 phase has very few impurities, which is advantageous for Cd recovery.

【0029】なお、AsH3 ガスの発生を検知器で調べ
たが浸出時及び置換析出時とも検出されなかった。
When the generation of AsH 3 gas was examined by a detector, it was not detected at the time of leaching nor at the time of displacement precipitation.

【0030】[0030]

【実施例2】1リットル中にCdを83.9gと、In
を10.6gと、Teを0.42gと、Asを0.01
8gと、遊離H2 SO4 を110gの割合で含んだ含I
n水溶液を1070リットル用意すると共に、組成が重
量%にて、Inが19.3%であり、Cdが0.90%
であり、Teが0.022%であり、Asが0.004
%であるソーダスラグを28kgと、実施例1で得たI
n(OH)3 相を450リットルと、粉末状で湿量5k
g(乾量4.6kg)のCd品位が98.4重量%であ
る還元剤としてのセメントCdとを約1時間にわたって
撹拌し、混合した後、さらに、1リットル中に250g
の割合でNaOHが含まれる苛性ソーダ水溶液を290
リットル加えpHを2.0の水溶液とし、この水溶液を
濾過して湿量9.4kgの残渣と1840リットルの濾
液とを得た。
Embodiment 2 83.9 g of Cd in 1 liter and In
Is 10.6 g, Te is 0.42 g, and As is 0.01.
8 g and 110 g of free H 2 SO 4 containing I
A 1070 liter aqueous solution was prepared, and the composition was 19.3% by weight and the Cd content was 0.90% by weight%.
And Te is 0.022% and As is 0.004%.
% Of soda slag and 28 kg of the soda slag obtained in Example 1.
n (OH) 3 phase, 450 liters, powder form, wet weight 5k
g (4.6 kg dry weight) of cement Cd as a reducing agent having a Cd grade of 98.4% by weight was stirred for about 1 hour, mixed, and then further mixed with 250 g / l.
Caustic soda aqueous solution containing NaOH at a ratio of 290
One liter was added to make an aqueous solution having a pH of 2.0, and this aqueous solution was filtered to obtain a residue having a wet weight of 9.4 kg and a filtrate of 1840 liters.

【0031】この場合、得られた残渣の組成は重量%に
て、水分が36.1%であり、Cdが24.6%であ
り、Inが7.8%であり、Teが7.6%であり、A
sが0.31%であると共に、濾液の組成は1リットル
当たりCdが93.9gであり、Inが14.6gであ
り,Teが0.005g以下であり、Asが0.000
7gであった。
In this case, the composition of the obtained residue is 36.1% of water, Cd is 24.6%, In is 7.8%, and Te is 7.6% by weight. % And A
s is 0.31%, and the composition of the filtrate is 93.9 g of Cd per liter, 14.6 g of In, 0.005 g of Te or less, and 0.000 g of As.
7 g.

【0032】上記の濾液に総表面積が4.9m2 となる
ようにCd板を浸漬し、毎分40リットルの循環量にて
48時間にわたって上記のCd板の周囲を循環させてそ
の表面にセメントInを析出させたのち、このセメント
InをCd板から剥ぎ取り、次いで充分に水洗したセメ
ントInに対して、さらに、NaOHの3kgを添加
し、ステンレスのるつぼの中で摂氏250度で融解し、
上下に分離したソーダスラグの6.9kgと粗Inの2
3.2kgとを得た。
A Cd plate was immersed in the above filtrate so as to have a total surface area of 4.9 m 2 , circulated around the Cd plate at a circulation rate of 40 liters per minute for 48 hours, and cemented on the surface. After precipitation of In, the cement In was peeled off from the Cd plate, and then 3 kg of NaOH was further added to the sufficiently washed cement In and melted at 250 degrees Celsius in a stainless steel crucible.
6.9 kg of vertically separated soda slag and 2 of coarse In
3.2 kg were obtained.

【0033】この場合に得られたソーダスラグの組成は
重量%にて、Inが17.4%であり、Cdが1.1%
であり、Teが0.061%であり、Asが0.010
%であった。
The composition of the soda slag obtained in this case is, by weight%, 17.4% of In and 1.1% of Cd.
And Te is 0.061% and As is 0.010%.
%Met.

【0034】一方、粗Inの組成は、重量%で、Inが
98.04%であり、Cdが1.76%であり、Teが
0.0015以下であり、Asが0.001%以下であ
った。Te、Asがほとんどソーダスラグに分配された
ことがわかる。
On the other hand, the composition of crude In is as follows: in terms of% by weight, In is 98.04%, Cd is 1.76%, Te is 0.0015 or less, and As is 0.001% or less. there were. It can be seen that Te and As were almost distributed to the soda slag.

【0035】また、置換析出後の尾液は、1リットル当
たり、Cd116g、In0.97g、Te0.005
g以下、As0.0005g以下を含有し、1リットル
当たり250gのNaOH水溶液を55リットル使用し
てpH5.0に調整し、16時間静置沈降させてIn
(OH)3 相100リットルとCdSO4 相1830リ
ットルを得た。In(OH)3 相の品位は、1リットル
当たりIn19.6gでInが濃縮され、CdSO4
の品位は、1リットル当たりCd111g、In0.0
09g、Te0.005g以下、As0.0005g以
下であり、不純物の少ないCdSO4 水溶液を得た。
The tail solution after the displacement precipitation was Cd 116 g, In 0.97 g and Te 0.005 g per liter.
g, containing not more than 0.0005 g of As, and adjusting the pH to 5.0 using 55 liters of a 250 g NaOH aqueous solution per liter, and allowing it to settle for 16 hours.
100 liters of (OH) 3 phase and 1830 liters of CdSO 4 phase were obtained. The quality of the In (OH) 3 phase is 19.6 g of In per liter, and In is concentrated. The quality of the CdSO 4 phase is 111 g of Cd per liter and In0.0.
An aqueous solution of CdSO 4 containing only 09 g, 0.005 g of Te or less and 0.0005 g of As or less and having few impurities was obtained.

【0036】なお、AsH3 ガスの発生は、検知器で調
べたが、浸出時及び置換析出時とも検出されなかった。
The generation of AsH 3 gas was examined by a detector, but was not detected at the time of leaching or at the time of displacement precipitation.

【0037】[0037]

【従来例】実施例2と同様に調整された含In水溶液1
020リットルに対して、NaOHを250g/リット
ルの濃度割合で含むアルカリ水溶液の210リットルを
添加してpHが2.0の含In水溶液を用意し、この含
In水溶液を濾過したところ、発生残渣は0.2kgと
少なく、1240リットルの濾液を得た。
Conventional Example In-containing aqueous solution 1 prepared in the same manner as in Example 2.
To 020 liters, 210 liters of an alkaline aqueous solution containing NaOH at a concentration of 250 g / liter was added to prepare an In-containing aqueous solution having a pH of 2.0, and this In-containing aqueous solution was filtered. As little as 0.2 kg, a 1240 liter filtrate was obtained.

【0038】この場合、濾液の組成は、1リットル当た
り、Cdを69.0gと,Inを8.7gと、Teを
0.34gと、Asを0.015g含有していた。
In this case, the composition of the filtrate contained 69.0 g of Cd, 8.7 g of In, 0.34 g of Te, and 0.015 g of As per liter.

【0039】上記の組成を持った濾液に対して、金属Z
n粉末を9.2kg添加して緩やかに撹拌し、AsH3
の発生状況を調査したところ、その検出量はピーク時に
2.8ppmを示した。
The filtrate having the above composition was added to the metal Z
gently stirring the n powder was added 9.2 kg, AsH 3
As a result of investigating the state of occurrence, the detected amount was 2.8 ppm at the peak.

【0040】16時間の撹拌作業の後に得たセメントI
nは実施例2の場合に比較して泥状であると共に、その
水溶液も黒色を示していた。
Cement I obtained after 16 hours of stirring
n was muddy as compared with the case of Example 2, and the aqueous solution was black.

【0041】この様にして泥状のセメントInを得た後
の尾液の組成は、1リットル中にCdを68.1gと、
Inを1.32gと、Teを0.02g以下と、Asを
0.001gとを含んでいた。
After obtaining the muddy cement In in this way, the composition of the tail liquid is 68.1 g of Cd in 1 liter,
It contained 1.32 g of In, 0.02 g or less of Te, and 0.001 g of As.

【0042】また、ここで得た泥状のセメントInにN
aOHを1.2kg添加し、ステンレス製のるつぼを用
いて摂氏250度で融解したところ、セメントInの一
部が燃焼現象を示したため、直ちにNaOHを1.0k
g添加した。
Further, N is added to the muddy cement In obtained here.
When 1.2 kg of aOH was added and melted at 250 degrees Celsius using a stainless steel crucible, a part of cement In showed a combustion phenomenon.
g was added.

【0043】この様にして得られたソーダスラグの重量
は6.7kgであり、粗Inの重量は8.1kgであっ
た。
The weight of the soda slag thus obtained was 6.7 kg, and the weight of crude In was 8.1 kg.

【0044】また、この場合のソーダスラグの組成は重
量%でInが19.8%であり、Cdが5.8%であ
り、Teが5.1%であり、Asが0.09%であり、
同じく粗Inの組成は、Inが94.8%であり、Cd
が4.13%であり、Teが0.001%以下であり、
Asが0.001%以下であった。
The composition of the soda slag in this case is 19.8% by weight of In, Cd is 5.8%, Te is 5.1%, and As is 0.09% by weight. ,
Similarly, the composition of crude In is that In is 94.8% and Cd
Is 4.13%, Te is 0.001% or less,
As was 0.001% or less.

【0045】以上のように、本発明によるときは、In
の含有度の高い製品を安易な方法で製造できるようにす
ると共に、硫化作業にて精製除去せざるを得ないTeや
Asなどの有害物質の巻き込みを殆ど防止することの可
能性を開示し得た。
As described above, according to the present invention, In
It is possible to disclose the possibility of producing a product having a high content of carbon dioxide by an easy method, and to almost prevent the entrapment of harmful substances such as Te and As which must be purified and removed in the sulfidation operation. Was.

【0046】[0046]

【発明の効果】以上に述べたように、本発明によれば、
極めて簡便な手段にてTeやAs等の含有量の極めて少
ない粗Inの回収を可能にし、これが、高純度Inを製
造する際の環境汚染物質である硫化物の生成を極めて極
小にする方法を開示出来たので斯る手段によって市場に
In製品を送り出している産業界に寄与するところ大な
るものがある。
As described above, according to the present invention,
A very simple means makes it possible to recover crude In containing a very small amount of Te, As, etc., and this makes it possible to minimize the production of sulfide, an environmental pollutant, when producing high-purity In. As disclosed, there are significant contributions to the industry that is sending In products to the market by such means.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の方法の実施例に係るフローチャートで
ある。
FIG. 1 is a flowchart according to an embodiment of the method of the present invention.

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) C22B 58/00 ──────────────────────────────────────────────────続 き Continued on front page (58) Field surveyed (Int. Cl. 7 , DB name) C22B 58/00

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 Zn製錬工程に於いて発生してくるC
d、Zn、In、Te、As等を含有した中間物よりI
nを回収するに際して、還元剤としてTe化合物やAs
化合物を生成させるに必要な量の2当量以上の金属Cd
と金属Inもしくはこのような量の金属CdとInを含
有する還元用澱物を用いて上記中間物を鉱酸酸性下で還
元浸出して浸出液とし、この浸出液に水酸化アルカリ水
溶液を添加してpHを1.5〜2.5に調整し、この液
から残渣を分離して得た濾液中に板状のCdを浸漬し、
板状のCdの表面にセメントInを置換析出させ、板状
のCdの表面より剥離して得たセメントInに、該セメ
ントInに対して5〜20重量%のNaOHを添加して
後、摂氏200〜300度で融解して、発生したソーダ
スラグを層分離して粗Inを回収することを特徴とする
Inの回収方法。
1. C generated in a Zn smelting process
from intermediates containing d, Zn, In, Te, As, etc.
When recovering n, a Te compound or As
Two or more equivalents of metal Cd required to form the compound
And a metal In or a reducing precipitate containing such amounts of metal Cd and In, the above intermediate is reduced and leached under acidic mineral acid to form a leaching solution, and an aqueous solution of alkali hydroxide is added to the leaching solution. The pH was adjusted to 1.5 to 2.5, and plate-like Cd was immersed in the filtrate obtained by separating the residue from this solution,
Cement In is substituted and precipitated on the surface of the plate-shaped Cd, and NaOH is added to the cement In obtained by exfoliating from the surface of the plate-shaped Cd in an amount of 5 to 20% by weight based on the cement In. A method for recovering In, which comprises melting at 200 to 300 degrees, separating the generated soda slag into layers, and recovering crude In.
【請求項2】 セメントInを置換析出させた後の尾液
に、アルカリ水溶液を添加して、そのpHを4〜6に調
整し、生成した沈澱物を中間物の鉱酸酸性下における還
元浸出時に添加することを特徴とする請求項1に記載の
Inの回収方法。
2. An aqueous alkaline solution is added to the tail solution after substitution precipitation of the cement In to adjust the pH to 4 to 6, and the resulting precipitate is subjected to reductive leaching under the acidic condition of a mineral acid of an intermediate. The method for recovering In according to claim 1, wherein the In is added occasionally.
JP29913492A 1992-10-13 1992-10-13 In recovery method Expired - Lifetime JP3024396B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP29913492A JP3024396B2 (en) 1992-10-13 1992-10-13 In recovery method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP29913492A JP3024396B2 (en) 1992-10-13 1992-10-13 In recovery method

Publications (2)

Publication Number Publication Date
JPH06128664A JPH06128664A (en) 1994-05-10
JP3024396B2 true JP3024396B2 (en) 2000-03-21

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ID=17868568

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Country Status (1)

Country Link
JP (1) JP3024396B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4723878B2 (en) * 2005-02-28 2011-07-13 三井金属鉱業株式会社 Method for producing indium-containing metal
JP5016895B2 (en) * 2006-03-06 2012-09-05 株式会社神鋼環境ソリューション Indium recovery method and apparatus
JP5068772B2 (en) * 2007-01-23 2012-11-07 シャープ株式会社 Method for recovering indium from an etching waste solution containing indium and ferric chloride
CN101589164B (en) * 2007-01-23 2011-03-02 夏普株式会社 Method and apparatus for collection of indium from etching waste solution containing indium and ferric chloride

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Publication number Publication date
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