JPH04308097A - Device for removing metallic ion - Google Patents

Device for removing metallic ion

Info

Publication number
JPH04308097A
JPH04308097A JP3099427A JP9942791A JPH04308097A JP H04308097 A JPH04308097 A JP H04308097A JP 3099427 A JP3099427 A JP 3099427A JP 9942791 A JP9942791 A JP 9942791A JP H04308097 A JPH04308097 A JP H04308097A
Authority
JP
Japan
Prior art keywords
cathode
pipe
electrolytic cell
copper
liquid
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.)
Granted
Application number
JP3099427A
Other languages
Japanese (ja)
Other versions
JP2796903B2 (en
Inventor
Tadashi Hiraide
平出 忠
Ryoji Takakuwa
高桑 良二
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.)
Tsurumi Soda Co Ltd
Original Assignee
Tsurumi Soda 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 Tsurumi Soda Co Ltd filed Critical Tsurumi Soda Co Ltd
Priority to JP3099427A priority Critical patent/JP2796903B2/en
Publication of JPH04308097A publication Critical patent/JPH04308097A/en
Application granted granted Critical
Publication of JP2796903B2 publication Critical patent/JP2796903B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime 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

Landscapes

  • Water Treatment By Electricity Or Magnetism (AREA)
  • Electrolytic Production Of Metals (AREA)

Abstract

PURPOSE:To remove the trace copper ion in a liq. having a high content of Fe<2+> ion, for example. CONSTITUTION:An insulating pipe 3 is allowed to pierce an electrolytic cell 1, and a conductive filter bed 5 also used as a cathode is laminated oh the pipe 3. A meshy cathode feeder 6 is provided around the filter bed 5, and a rod-shaped anode 4 is inserted into the pipe 3. Since the pipe 3 to be laminated with the filter bed 5 is pierced with many water passage holes 31, a liq. to be treated in the electrolytic cell 1 is introduced into the pipe 3 through the filter bed 5. As the surface area of the cathode can be increased, the current density of the cathode is reduced while supplied with a requisite current, and the metal ion is selectively and effectively electrodialyzed.

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、例えば銅系塩化鉄廃液
中の銅イオンを除去するための装置に関するものである
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for removing copper ions from, for example, a copper-based iron chloride waste solution.

【0002】0002

【従来の技術】一般にプリント基板のエッチングや製鋼
所における銅系鋼板等のピックリングから生じる廃液中
には銅イオンが含まれているため、公害防止上、下水道
に排出する前にその銅イオンを除去する必要がある。こ
のような廃液の処理方法としては無隔膜電解槽や隔膜電
解槽を用いた電解法、あるいは溶媒抽出法等が知られて
いるが、いずれも十分な除去率を得ることができない。
[Prior Art] Generally, copper ions are contained in the waste liquid generated from the etching of printed circuit boards and the pickling of copper-based steel sheets in steel mills. Therefore, in order to prevent pollution, the copper ions are removed before being discharged into the sewer. Needs to be removed. As methods for treating such waste liquid, electrolytic methods using diaphragmless electrolytic cells or diaphragm electrolytic cells, solvent extraction methods, and the like are known, but none of them can provide a sufficient removal rate.

【0003】また、塩化第2鉄溶液によりプリント基板
をエッチングした後の銅系塩化鉄廃液を多量に処理する
場合には、操作の容易性から、鉄スクラップを廃液中に
投入して鉄と銅イオンとの置換により銅イオンを金属と
して取り除き、その後当該廃液中に塩素ガスを通じ、こ
れにより塩化第1鉄を塩素化して塩化第2鉄を再製する
ようにしている。
[0003] When processing a large amount of copper-based iron chloride waste solution after etching printed circuit boards with ferric chloride solution, for ease of operation, iron scraps are thrown into the waste solution to separate iron and copper. Copper ions are removed as metal by substitution with ions, and then chlorine gas is passed into the waste liquid, thereby chlorinating ferrous chloride to remanufacture ferric chloride.

【0004】この様子を化学式で表わすと次のように表
わされる。
[0004] This situation can be expressed as a chemical formula as follows.

【0005】[0005]

【化1】 即ち処理前の廃液中には、エッチングにより還元された
塩化第1鉄、生成物である塩化第2銅、塩酸及び未反応
の塩化第2鉄が含まれており、この中に鉄スクラップを
投入すると、先ず塩化第2鉄が鉄と反応して塩化第1鉄
とされ、次いで塩化第2銅と鉄とが反応して、銅粉が生
成され、固液分離により除去される。その後塩化第1鉄
を塩素化して塩化第2鉄とする。
[Chemical 1] That is, the waste liquid before treatment contains ferrous chloride reduced by etching, cupric chloride as a product, hydrochloric acid, and unreacted ferric chloride. When iron scrap is input, ferric chloride first reacts with iron to form ferrous chloride, then cupric chloride and iron react to produce copper powder, which is removed by solid-liquid separation. . The ferrous chloride is then chlorinated to form ferric chloride.

【0006】[0006]

【発明が解決しようとする課題】しかしながらこのよう
な方法で再製される塩化第2鉄溶液中には、銅の再溶解
も含めて銅イオンが50〜200ppm程度含まれてい
る。この程度の銅イオン濃度であれば銅をエッチングす
る場合には問題ないが、鉄系やニッケル系の材料例えば
シャドーマスクをエッチングする場合には、エッチング
液中の銅が被エッチング材上に析出し問題となるし、そ
のまま下水道に排出されると公害防止の面からも好まし
くない。
[Problems to be Solved by the Invention] However, the ferric chloride solution remanufactured by such a method contains about 50 to 200 ppm of copper ions, including the redissolution of copper. This level of copper ion concentration poses no problem when etching copper, but when etching iron-based or nickel-based materials, such as shadow masks, copper in the etching solution may precipitate on the material to be etched. This poses a problem, and it is also undesirable from the standpoint of pollution prevention if it is discharged directly into the sewer system.

【0007】本発明はこのような背景のもとになされた
ものであり、例えば銅系塩化鉄廃液中の銅イオンを高い
除去率で除去することのできる金属イオンの除去装置を
提供することにある。
The present invention has been made against this background, and an object of the present invention is to provide a metal ion removal device capable of removing copper ions from, for example, copper-based iron chloride waste liquid at a high removal rate. be.

【0008】[0008]

【課題を解決するための手段】先ず本発明の着眼点につ
いて説明すると、例えば先述した、塩化第2鉄溶液でプ
リント基板をエッチングした後の廃液を、鉄、グラファ
イトフェルトを夫々陽極、陰極として対向させて電気分
解すると、陽極では化学式2、陰極では化学式3で示す
反応が起こる。
[Means for Solving the Problems] First, to explain the point of view of the present invention, for example, as mentioned above, the waste liquid after etching a printed circuit board with a ferric chloride solution is used as an anode and a graphite felt as an anode and a cathode, respectively. When electrolyzed, reactions shown by chemical formula 2 occur at the anode and chemical formula 3 at the cathode.

【0009】[0009]

【化2】[Case 2]

【0010】0010

【化3】 ここで平衡論にもとづいて陰極反応を考察すると、銅の
電析の起こり得る電流密度が一番小さく、水素発生の起
こり得る電流密度、鉄の電析の起こり得る電流密度の順
に大きくなっていく。従って電極間を通電すると、銅の
電析が最初に起こるはずである。しかしながら上記の廃
液においては、鉄イオンの濃度が銅イオンの濃度に対し
て例えば約1600倍と大きいため、実際には鉄の電析
及び水素ガスの発生が副反応として多量に起こる。また
pHが低く、水素イオン濃度が高い場合には鉄の電析は
起こらず、水素ガスの発生が主反応となる。なお、鉄の
電析を抑えるために電流値を小さくした場合には反応が
遅くなって、電解槽内の銅を除去するのに非常に長い時
間を要するか、あるいは装置が過大となる。
[Chemical 3] Considering the cathode reaction based on equilibrium theory, the current density that can cause copper electrodeposition is the lowest, followed by the current density that can cause hydrogen evolution, and then the current density that can cause iron deposition. It's getting bigger. Therefore, when current is passed between the electrodes, copper electrodeposition should occur first. However, in the above-mentioned waste liquid, the concentration of iron ions is, for example, about 1600 times higher than the concentration of copper ions, so in reality, a large amount of iron electrodeposition and generation of hydrogen gas occur as side reactions. Further, when the pH is low and the hydrogen ion concentration is high, iron deposition does not occur, and the main reaction is the generation of hydrogen gas. Note that if the current value is reduced in order to suppress the electrodeposition of iron, the reaction will be slow and it will take a very long time to remove the copper in the electrolytic cell, or the device will become too large.

【0011】そこで本発明者は、陰極の表面積をできる
だけ大きくとるという発想をもって、次のような装置を
生み出した。即ち本発明の金属イオンの除去装置は、棒
状の可溶性の陽極体と、この陽極体を間隙を介して取り
囲むように配設され、導電性の濾過層よりなる陰極体と
、を電解槽内に配置して成り、除去対象となる金属イオ
ンを含む被処理液は、電解槽に供給されて、陰極体の外
方側から内方側に流れ、その流路は陰極体自体であるこ
とを特徴とする。
Therefore, the inventor of the present invention created the following device based on the idea of increasing the surface area of the cathode as much as possible. That is, the metal ion removal device of the present invention includes a rod-shaped soluble anode body and a cathode body, which is arranged so as to surround the anode body through a gap and is made of a conductive filtration layer, in an electrolytic cell. A liquid to be treated containing metal ions to be removed is supplied to the electrolytic cell and flows from the outside to the inside of the cathode body, and the flow path is the cathode body itself. shall be.

【0012】0012

【作用】例えば上述の銅系塩化鉄廃液よりなる被処理液
は、電解槽内に圧送され、陰極体を構成する濾過層内を
通過する。この濾過層はいわば液体の抵抗体であるため
、被処理液は濾過層に対して局所的に入り込むことなく
分散されて入り込み、そしてここを通過した後、例えば
陽極体に沿って上昇し、その上方から排出される。  
ここで陰極体は例えばグラファイトフェルトにより円筒
状に成形されているため、その表面積は非常に大きく、
従って所要の除去速度を得ながら電流密度を大きくする
ことができ、このため先述した分散作用も加わって被処
理液は電流密度の小さい電極部分に広範囲に亘って接触
することができる。この結果鉄の電析及び水素の発生が
抑えられ、銅の電析が主体となり、しかも広範囲で起こ
る。そして陰極自体が濾過層であるから、析出脱落した
銅粉は、ここで濾過される。
[Operation] The liquid to be treated, for example, the above-mentioned copper-based iron chloride waste liquid, is pumped into the electrolytic cell and passes through the filtration layer constituting the cathode body. Since this filtration layer is a liquid resistor, the liquid to be treated does not enter the filtration layer locally but is dispersed and enters the filtration layer, and after passing through this layer, it rises along, for example, the anode body. It is discharged from above.
Here, the cathode body is formed into a cylindrical shape by, for example, graphite felt, so its surface area is extremely large.
Therefore, the current density can be increased while obtaining the required removal rate, and with the addition of the above-mentioned dispersion effect, the liquid to be treated can come into contact with the electrode portion where the current density is low over a wide range. As a result, the electrodeposition of iron and the generation of hydrogen are suppressed, and the electrodeposition of copper becomes main and occurs over a wide range. Since the cathode itself is a filtration layer, the deposited and fallen copper powder is filtered here.

【0013】[0013]

【実施例】図1は本発明の実施例の全体を示す断面図で
あり、図2は、その要部を示す斜視図である。この実施
例では、下部に被処理液の吸水口11を備えた円筒状の
電解槽1の上部に、排水口21を備えた排水室2が設け
られており、電解槽1内の中心部には、上端が排水室2
内に開口すると共に下端が電解槽1を貫通して外部に突
出した絶縁性の例えばPVC等のプラスチックよりなる
パイプ3が設置されている。このパイプ3は下端部より
上方位置にて、管壁に多数の通水孔31が形成されてい
る。またパイプ3の上端付近にはフランジ32が形成さ
れており、このフランジ32を介して排水室2の底面に
固定される。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is a sectional view showing the entire embodiment of the present invention, and FIG. 2 is a perspective view showing the main parts thereof. In this embodiment, a drain chamber 2 equipped with a drain port 21 is provided at the top of a cylindrical electrolytic cell 1 having a water intake port 11 for the liquid to be treated at the bottom. The upper end is the drain chamber 2
An insulating pipe 3 made of an insulating plastic such as PVC is installed, which is open inward and whose lower end penetrates the electrolytic cell 1 and protrudes to the outside. This pipe 3 has a large number of water passage holes 31 formed in the pipe wall above the lower end. Further, a flange 32 is formed near the upper end of the pipe 3, and is fixed to the bottom surface of the drainage chamber 2 via this flange 32.

【0014】前記パイプ3内には、外部から排水室2を
貫通した鉄丸棒よりなる陽極体4が電解槽1の下端部付
近まで、間隙を介して突入されている。
[0014] An anode body 4 made of a round iron rod that penetrates the drain chamber 2 from the outside is inserted into the pipe 3 to near the lower end of the electrolytic cell 1 through a gap.

【0015】前記パイプ3の外周面には、通水孔31が
形成されていない下端部付近を除いて、例えばカーボン
もしくはグラファイト等の導電繊維製のフェルトあるい
はシートが巻装され、これによって陰極体を兼用する濾
過層5が構成されている。更にこの濾過層5の外周面に
は、この全面を密着して覆うように例えばチタンよりな
るメッシュ状の陰極給電体6が配置されている。この陰
極給電体6の取り付けについては、例えば図2に示すよ
うに、両縁に取り付け部材61、62を備えた横断面が
半円状ユニット60を2個用意して、これらを互に取り
付け部材61、62を介して接合すればよい。
The outer circumferential surface of the pipe 3 is wrapped with felt or sheet made of conductive fiber such as carbon or graphite, except for the vicinity of the lower end where the water passage hole 31 is not formed. A filtration layer 5 is constructed which also serves as a filter. Furthermore, a mesh-shaped cathode power supply body 6 made of, for example, titanium is arranged on the outer peripheral surface of the filter layer 5 so as to tightly cover the entire surface. In order to attach the cathode power supply body 6, for example, as shown in FIG. They may be joined via 61 and 62.

【0016】次に上述実施例の作用について述べる。先
ず被処理液である銅廃液を図示しないポンプにより吸水
口11を通じて電解槽1内に圧送すると共に、陽極体4
及び陰極給電体6の間に直流電源Eにより電圧を印加す
る。原料銅廃液としては、例えば塩化第2鉄溶液により
銅をエッチングした後の廃液について、鉄スクラップを
用いてセメンテーションにより脱銅し、依然微量の銅イ
オンが含まれている銅廃液を用いる。
Next, the operation of the above embodiment will be described. First, copper waste liquid, which is a liquid to be treated, is pumped into the electrolytic cell 1 through the water inlet 11 by a pump (not shown), and the anode body 4 is
A voltage is applied between the cathode power supply body 6 and the cathode power supply body 6 by a DC power supply E. As the raw material copper waste liquid, for example, a waste liquid obtained after etching copper with a ferric chloride solution is decoppered by cementation using iron scrap, and a copper waste liquid that still contains trace amounts of copper ions is used.

【0017】そして上記の構造からわかるように、電解
槽1内の被処理液が排水室2に達するためには、陰極体
を兼用する濾過層5を通じてパイプ3の通水孔31を通
らなければならないので、当該濾過層5が水の抵抗体の
役割を果たし、被処理液が濾過層5に対して均一に分散
された状態で透過し、パイプ3内を陽極体に沿って上昇
する。従って陰極体を兼用する当該濾過層5の全範囲に
亘って被処理液が通流する。
As can be seen from the above structure, in order for the liquid to be treated in the electrolytic cell 1 to reach the drainage chamber 2, it must pass through the water passage hole 31 of the pipe 3 through the filtration layer 5, which also serves as a cathode body. Therefore, the filtration layer 5 acts as a water resistor, and the liquid to be treated permeates through the filtration layer 5 in a uniformly dispersed state, rising inside the pipe 3 along the anode body. Therefore, the liquid to be treated flows through the entire range of the filter layer 5, which also serves as a cathode body.

【0018】ここで「作用」の項にて詳述したように、
陰極体は陽極体4を取り囲むように配置されており、し
かも陰極体自体がフェルト等の濾過層を構成しているの
で、所要の大きさの電流を流しながら電流密度を小さく
でき、このため鉄の電析が抑えられて銅の電析が主体と
なる。そして析出脱落した銅粉も濾過層5内にて濾過さ
れるが、そのまま透過したものはパイプ3内を降下し、
その下端から排出される。一方銅が除去された被処理液
は排水室2を介して排水口より排出される。上述実施例
では、陽極体、陰極体を組み合わせた電極体を電解槽内
に1個配設した構成としているが、本発明ではこうした
電極体を電解槽内に複数個配置して処理量を大きくする
ことができるし、また図3に示すように、電極体を複数
備えた電解槽を例えばシリーズに2個接続して多段処理
を行うようにしてもよい。
[0018] As explained in detail in the "effect" section,
The cathode body is arranged so as to surround the anode body 4, and since the cathode body itself constitutes a filter layer such as felt, it is possible to reduce the current density while passing the required amount of current. Electrodeposition of copper is suppressed and copper becomes the main electrodeposition. The copper powder that has precipitated and fallen out is also filtered within the filtration layer 5, but the permeated material descends within the pipe 3,
It is discharged from its lower end. On the other hand, the liquid to be treated from which copper has been removed is discharged from the drain port via the drain chamber 2. In the above embodiment, one electrode body, which is a combination of an anode body and a cathode body, is arranged in the electrolytic cell, but in the present invention, a plurality of such electrode bodies are arranged in the electrolytic cell to increase the throughput. Alternatively, as shown in FIG. 3, for example, two electrolytic cells each having a plurality of electrode bodies may be connected in series to perform multistage treatment.

【0019】次に図3に示す2段型の装置を用いて処理
した実験結果について述べる。先ず装置としては、1段
目の電解槽1Aの排水口に気液分離器7を介して2段目
の電解槽1Bの吸水口を接続し、各電解槽1A、1Bに
、実施例で述べた構造の10個の電極体を設置したもの
を用いる。そして塩化第1鉄、塩化第2鉄及び塩化第2
銅を含む被処理液を100l/hrの流量でかつ1槽当
り20Aの電流で電解槽1Aに供給したところ、各部に
おける金属イオン濃度は表1に示す通りであった。
Next, the results of an experiment conducted using the two-stage apparatus shown in FIG. 3 will be described. First, as an apparatus, the water inlet of the second-stage electrolytic cell 1B is connected to the drain port of the first-stage electrolytic cell 1A via the gas-liquid separator 7, and the water inlet of the second-stage electrolytic cell 1B is An electrode body with 10 electrode bodies having a similar structure is used. and ferrous chloride, ferric chloride and ferric chloride
When the liquid to be treated containing copper was supplied to the electrolytic cell 1A at a flow rate of 100 l/hr and a current of 20 A per cell, the metal ion concentration in each part was as shown in Table 1.

【0020】[0020]

【表1】 この実験例からわかるように、上述の装置によれば銅イ
オンを高い除去率で除去できる。なおこの例では電解槽
1Aにて再酸化したFe3+が主として除去されている
が、流量や陰極体を兼用する濾過層の巻き径等を調整す
ることによって、必ずしも2段型としなくても同様の機
能が得られることは勿論である。
[Table 1] As can be seen from this experimental example, copper ions can be removed at a high removal rate with the above-mentioned apparatus. Note that in this example, Fe3+ reoxidized in electrolytic cell 1A is mainly removed, but by adjusting the flow rate and the winding diameter of the filtration layer that also serves as the cathode body, it is not necessary to use a two-stage type. Of course, functions can be obtained.

【0021】以上において上述実施例では、絶縁性のパ
イプ3は濾過層5の保持体としての役割を果たしている
が、濾過層5として頑強なものを用いる場合には不要で
ある。  またメッシュ状の陰極給電体は、フェルトあ
るいはシート状の陰極体に対して大きな接触面積が得ら
れるものであればよく、線状体が縦横に広がるもののみ
ならず、板状体に多数の孔を有するもの等を用いてもよ
い。更に電解槽内に被処理液を圧送するためには、ポン
プを用いることなく、例えば被処理液の貯液タンクと電
解槽とに落差をもたせるといった手法を採用してもよい
In the above-described embodiment, the insulating pipe 3 serves as a holder for the filtration layer 5, but it is not necessary when a strong filtration layer 5 is used. In addition, the mesh-like cathode feeder may be of any type as long as it can provide a large contact area with the felt or sheet-like cathode. You may use the thing which has. Furthermore, in order to force-feed the liquid to be treated into the electrolytic cell, a method may be adopted, for example, by providing a head difference between the storage tank for the liquid to be treated and the electrolytic cell, without using a pump.

【0022】なお、析出金属により濾過層が目詰まりす
る時点と陽極体が溶解して使用できなくなるまでの時点
とを揃うようにすれば電極体全体を交換すればよいので
メンテナンスが容易であるし、また陽極体を無駄に使用
しなくて済む。
[0022] Furthermore, if the point at which the filter layer is clogged with deposited metal and the point at which the anode body melts and becomes unusable are aligned, maintenance will be easy because the entire electrode body can be replaced. Also, there is no need to waste the anode body.

【0023】[0023]

【発明の効果】本発明によれば、棒状の陽極体を取り囲
むように、導電性の濾過層よりなる陰極体を配置してい
るため、被処理液中における陰極体の表面積が非常に大
きく、この結果所要の電流を通電しながら陰極体におけ
る電流密度を小さくでき、従って金属イオンの電析を選
択的に行うことができる。しかも濾過層は被処理液の抵
抗体の役割を果たすので、被処理液が広範囲に亘って濾
過層の中に流れ込み、このため例えば銅系のエッチング
鉄廃液のように、多量のFe2+が存在する液中の微量
の銅イオンを高い効率で除去できる。
According to the present invention, since the cathode body made of a conductive filter layer is arranged to surround the rod-shaped anode body, the surface area of the cathode body in the liquid to be treated is extremely large. As a result, the current density in the cathode body can be reduced while passing the required current, and therefore metal ions can be selectively deposited. Moreover, since the filtration layer acts as a resistor for the liquid to be treated, the liquid to be treated flows into the filtration layer over a wide range, and for this reason, a large amount of Fe2+ is present in, for example, copper-based etching iron waste liquid. Trace amounts of copper ions in the liquid can be removed with high efficiency.

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

【図1】本発明の実施例を示す断面図である。FIG. 1 is a sectional view showing an embodiment of the present invention.

【図2】同実施例の要部を示す斜視図である。FIG. 2 is a perspective view showing essential parts of the same embodiment.

【図3】本発明の他の実施例を示す説明図である。FIG. 3 is an explanatory diagram showing another embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1  電解槽 2  排液室 3  パイプ 4  陽極体 5  陰極体を兼用する濾過層 6  陰極給電体 1 Electrolytic cell 2 Drainage chamber 3 Pipe 4 Anode body 5. Filtration layer that also serves as a cathode body 6 Cathode power supply

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】  棒状の可溶性の陽極体と、この陽極体
を間隙を介して取り囲むように配設され、導電性の濾過
層よりなる陰極体と、を電解槽内に配置して成り、除去
対象となる金属イオンを含む被処理液は、電解槽に供給
されて、陰極体の外方側から内方側に流れ、その流路は
陰極体自体であることを特徴とする金属イオンの除去装
置。
Claim 1: A rod-shaped soluble anode body and a cathode body, which is arranged so as to surround the anode body through a gap and is made of a conductive filtration layer, are placed in an electrolytic cell, Removal of metal ions characterized in that a liquid to be treated containing target metal ions is supplied to an electrolytic cell and flows from the outside to the inside of the cathode body, and the flow path is the cathode body itself. Device.
JP3099427A 1991-04-04 1991-04-04 Metal ion removal equipment Expired - Lifetime JP2796903B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3099427A JP2796903B2 (en) 1991-04-04 1991-04-04 Metal ion removal equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3099427A JP2796903B2 (en) 1991-04-04 1991-04-04 Metal ion removal equipment

Publications (2)

Publication Number Publication Date
JPH04308097A true JPH04308097A (en) 1992-10-30
JP2796903B2 JP2796903B2 (en) 1998-09-10

Family

ID=14247159

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3099427A Expired - Lifetime JP2796903B2 (en) 1991-04-04 1991-04-04 Metal ion removal equipment

Country Status (1)

Country Link
JP (1) JP2796903B2 (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002126692A (en) * 2000-10-26 2002-05-08 Kowa Eng:Kk Separation and recovery method of heavy metals contained in fly ash etc.
JP2002535493A (en) * 1999-01-22 2002-10-22 リノヴェア・インターナショナル・インコーポレーテッド Electrochemical cell for removing metals from solution
KR101029472B1 (en) * 2010-10-25 2011-04-18 (주)에코앤파워 Copper recovery device by electrolysis
JP2013538997A (en) * 2010-09-08 2013-10-17 コミッサリア ア レネルジー アトミーク エ オ ゼネルジ ザルタナテイヴ Leakage detection device and coating of fluid transportation or storage member including leakage detection device
CN104911637A (en) * 2014-09-02 2015-09-16 李新华 Direct electrodeposition equipment
JP2017172007A (en) * 2016-03-24 2017-09-28 田中貴金属工業株式会社 Metal recovery device

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5016286A (en) * 1973-06-07 1975-02-20
JPS5633492A (en) * 1979-08-17 1981-04-03 Sam Ahmad Method and apparatus for recovering metal from solution
JPS616289A (en) * 1984-01-09 1986-01-11 イブ エロギユエ−ル Galvani recovery apparatus of metal

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5016286A (en) * 1973-06-07 1975-02-20
JPS5633492A (en) * 1979-08-17 1981-04-03 Sam Ahmad Method and apparatus for recovering metal from solution
JPS616289A (en) * 1984-01-09 1986-01-11 イブ エロギユエ−ル Galvani recovery apparatus of metal

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002535493A (en) * 1999-01-22 2002-10-22 リノヴェア・インターナショナル・インコーポレーテッド Electrochemical cell for removing metals from solution
JP2002126692A (en) * 2000-10-26 2002-05-08 Kowa Eng:Kk Separation and recovery method of heavy metals contained in fly ash etc.
JP2013538997A (en) * 2010-09-08 2013-10-17 コミッサリア ア レネルジー アトミーク エ オ ゼネルジ ザルタナテイヴ Leakage detection device and coating of fluid transportation or storage member including leakage detection device
US9304056B2 (en) 2010-09-08 2016-04-05 Commisariat A L'energie Atomique Et Aux Energies Alternatives Leak detection device, and coating intended for a fluid transport or storage member and comprising said detection device
JP2016148456A (en) * 2010-09-08 2016-08-18 コミッサリア ア レネルジー アトミーク エ オ ゼネルジ ザルタナテイヴ Leakage detection device, duct and method using leakage detection device
KR101029472B1 (en) * 2010-10-25 2011-04-18 (주)에코앤파워 Copper recovery device by electrolysis
CN104911637A (en) * 2014-09-02 2015-09-16 李新华 Direct electrodeposition equipment
JP2017172007A (en) * 2016-03-24 2017-09-28 田中貴金属工業株式会社 Metal recovery device
WO2017164271A1 (en) * 2016-03-24 2017-09-28 田中貴金属工業株式会社 Metal recovery device

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