JPS586554B2 - High speed inoji youkahouhou - Google Patents

High speed inoji youkahouhou

Info

Publication number
JPS586554B2
JPS586554B2 JP50084669A JP8466975A JPS586554B2 JP S586554 B2 JPS586554 B2 JP S586554B2 JP 50084669 A JP50084669 A JP 50084669A JP 8466975 A JP8466975 A JP 8466975A JP S586554 B2 JPS586554 B2 JP S586554B2
Authority
JP
Japan
Prior art keywords
wastewater
electrolysis
ppm
aluminum
concentration
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
JP50084669A
Other languages
Japanese (ja)
Other versions
JPS528662A (en
Inventor
中出和彦
奈良部博
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.)
Mitsui Kinzoku Co Ltd
Original Assignee
Mitsui Mining and Smelting 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 Mitsui Mining and Smelting Co Ltd filed Critical Mitsui Mining and Smelting Co Ltd
Priority to JP50084669A priority Critical patent/JPS586554B2/en
Publication of JPS528662A publication Critical patent/JPS528662A/en
Publication of JPS586554B2 publication Critical patent/JPS586554B2/en
Expired legal-status Critical Current

Links

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  • Electrostatic Separation (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Description

【発明の詳細な説明】 本発明は陽極および陰極を配置した電解槽に廃水を入れ
、直流電解することによって廃水を浄化する方法に関す
る。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for purifying wastewater by charging wastewater into an electrolytic cell in which an anode and a cathode are arranged and performing direct current electrolysis.

最近各種の産義水を処理する方法として電解法が広く採
用されるに至り、種々の分野で卓越した効果をあげてい
る。
Recently, electrolysis has been widely adopted as a method for treating various types of industrial water, and has achieved outstanding effects in various fields.

電解法として最も一般的な方法は、陽極にアルミニウム
またはアルミニウム合金を使用し、陰極に鉄またはステ
ンレスを使用して廃水を直流電解する方法であって、そ
の浄化作用は陽極から溶解したアルミニウムから廃水中
に生成される活性なコロイド状の水酸化アルミニウムに
基づくものであるとされている。
The most common electrolysis method is to use aluminum or aluminum alloy for the anode and iron or stainless steel for the cathode to conduct direct current electrolysis of wastewater. It is said to be based on the active colloidal aluminum hydroxide formed in the aluminum hydroxide.

しかるにこのアルミニウムまたはアルミニウム合金陽極
の表面には、長期間の電解によってスケールが生成して
電流が流れ難くにり、その結果、電解の浄化作用も低下
する欠点があった。
However, the aluminum or aluminum alloy anode has the disadvantage that scale is formed on the surface of the anode due to long-term electrolysis, making it difficult for current to flow, and as a result, the purifying effect of the electrolysis is also reduced.

この欠点を除去するために、廃水中に生成される水酸化
アルミニウムの供給方法として、硫酸アルミニウム、塩
化アルミニウム、硝酸アルミニウム、ミョウバン、ポリ
塩化アルミなどの化学薬剤を直接廃水中に添加し、陽極
としては不溶性の電極を使って廃水を直流電解する浄化
方法がある。
In order to eliminate this drawback, as a method of supplying aluminum hydroxide produced in wastewater, chemical agents such as aluminum sulfate, aluminum chloride, aluminum nitrate, alum, polyaluminum chloride, etc. are directly added to the wastewater and used as an anode. There is a purification method using direct current electrolysis of wastewater using insoluble electrodes.

本発明者らは浄化作用の更に優れた化学薬剤を探求した
結果、アルミン酸ソーダが上記薬剤に比べて著しく好結
果を与えることを知った。
As a result of our search for a chemical agent with even better purifying action, the present inventors found that sodium aluminate gave significantly better results than the above-mentioned agents.

本発明は上記知見にもとづいたものであって、アルミン
酸ソーダを直接廃水中に添加することによって水酸化ア
ルミニウムを生成させ、且つ不溶性の陽極を用いて廃水
を直流電解する方法である。
The present invention is based on the above findings, and is a method in which aluminum hydroxide is generated by directly adding sodium aluminate to wastewater, and the wastewater is subjected to direct current electrolysis using an insoluble anode.

本発明の方法において使用されるアルミン酸ソーダは、
前述した硫酸アルミニウム、塩化アルミニウム、硝酸ア
ルミニウム、ミョウバン、ポリ塩化アルミを使用する方
法に比較して、廃水の浄化作用が極めて優れている。
The sodium aluminate used in the method of the present invention is
Compared to the methods using aluminum sulfate, aluminum chloride, aluminum nitrate, alum, and polyaluminum chloride described above, the purification effect of wastewater is extremely superior.

その理由は、硫酸アルミニウム等上記薬剤は廃水中で加
水分解して水酸化アルミニウムと酸が生成するのに対し
、アルミン酸ソーダは廃水中で加水分解して水酸化アル
ミニウムとアルカリが生成する相違に基づくものである
と考えられる。
The reason for this is that the above chemicals, such as aluminum sulfate, are hydrolyzed in wastewater to produce aluminum hydroxide and acid, while sodium aluminate is hydrolyzed in wastewater to produce aluminum hydroxide and alkali. It is thought that it is based on

それ以外の詳細な機構については明らかではないが、実
験の結果から、アルミン酸ソーダの添加と不溶性の陽極
を用いた直流電解との併用が優れた効果をもつことが判
明している。
Although the other detailed mechanisms are not clear, experimental results have shown that the combination of addition of sodium aluminate and direct current electrolysis using an insoluble anode has an excellent effect.

本発明の方法において使用されるアルミン酸ソーダの添
加量は、廃水中のアルミニウム濃度が1〜1,500p
pmになる範囲が好適であり、廃水中えは電解を行う前
に予め添加してもよく、また電解が行われている槽に直
接添加してもよい。
The amount of sodium aluminate used in the method of the present invention is such that the aluminum concentration in wastewater is 1 to 1,500 p.
pm, and it may be added in advance to wastewater before electrolysis, or it may be added directly to the tank where electrolysis is being carried out.

また本発明の方法において使用される不溶性陽極の材質
は、例えばカーボン、鉛、チタン、白金、磁性酸化鉄、
高珪素鋳鉄などであって、これらの材質からなる陽極は
殆んど不溶である。
Further, the materials of the insoluble anode used in the method of the present invention include, for example, carbon, lead, titanium, platinum, magnetic iron oxide,
Anodes made of high-silicon cast iron or the like are almost insoluble.

陰極材質は電導性物質であればいずれでも使用可能であ
って特に制限はない。
The cathode material is not particularly limited and any conductive material can be used.

本発明の方法によって廃水を浄化すれば、浄化作用が著
しく優れているのみならず、長期間電解後も陽極にスケ
ールの生成が認められないので浄化作用が低下する傾向
も認められない。
When wastewater is purified by the method of the present invention, not only is the purification effect extremely excellent, but also there is no tendency for the purification effect to deteriorate because no scale is observed on the anode even after long-term electrolysis.

以下に実施例を示す。Examples are shown below.

実施例 亜鉛濃度10ppmニッケル濃度10ppmの酸性廃水
を苛性ソーダによりそのpHを7.5に調節し、定量分
析用のp紙にて炉過した沢液中の亜鉛およびニッケル濃
度を分析した結果、亜鉛濃度7.2ppm、ニッケル濃
度9. 3 ppmであった。
Example Acidic wastewater with a zinc concentration of 10 ppm and a nickel concentration of 10 ppm was adjusted to pH 7.5 with caustic soda, and the concentration of zinc and nickel in the sap was analyzed using P paper for quantitative analysis. 7.2 ppm, nickel concentration 9. It was 3 ppm.

上記ろ液中にアルミン酸ソーダをアルミニウムとして5
ppmになるように添加し、更に塩酸にてpHを7.5
に調節し、この状態の液を電解液とし、カーボン板を陽
極、鉄板を陰極とし、電解液1リットル当り0.1アン
ペアの直流電流を30分間通じた。
Add sodium aluminate to the above filtrate as aluminum.
ppm, and further adjust the pH to 7.5 with hydrochloric acid.
The solution in this state was used as an electrolyte, the carbon plate was used as an anode, the iron plate was used as a cathode, and a direct current of 0.1 ampere per liter of electrolyte was passed for 30 minutes.

電解前と電解後の電解液について、定量分析用のp紙に
て涙過したP液中の亜鉛およびニッケルの濃度を分析し
た結果、電解前の亜鉛濃度5. 4ppm,ニッケル濃
度7. 7ppm、電解後の亜鉛濃度0.8ppm、ニ
ッケル濃度0.8ppmであった。
As a result of analyzing the concentration of zinc and nickel in the electrolyte before and after electrolysis, the concentration of zinc and nickel in the P solution was analyzed using P paper for quantitative analysis.The zinc concentration before electrolysis was 5. 4ppm, nickel concentration 7. The zinc concentration after electrolysis was 0.8 ppm, and the nickel concentration was 0.8 ppm.

なお上記の亜鉛濃度7. 2ppm、ニッケル濃度9.
3ppmの液に、一方は硫酸アルミニウムを、他方はポ
リ塩化アルミを各々アルミニウムとして5ppmになる
ように添加し、その後の操作を上記と全く同様にした結
果、硫酸アルミニウムを添加したときの電解前の亜鉛濃
度6.6ppm、ニッケル濃度8.2ppm,電解後の
亜鉛濃度3. 8ppm、ニッケル濃度4.5ppmで
あり、ポリ塩化アルミを添加したときの電解前の亜鉛濃
度6. 9ppm、ニッケル濃度8. 4 ppm,電
解後の亜鉛濃度4. 1 1ppm、ニッケル濃度5.
3ppmであった。
Note that the above zinc concentration 7. 2ppm, nickel concentration 9.
To a 3 ppm solution, aluminum sulfate was added to one side, and polyaluminum chloride was added to the other to give an aluminum content of 5 ppm, and the subsequent operations were exactly the same as above. As a result, the results before electrolysis when aluminum sulfate was added Zinc concentration 6.6 ppm, nickel concentration 8.2 ppm, zinc concentration after electrolysis 3. 8 ppm, nickel concentration 4.5 ppm, and zinc concentration before electrolysis when polyaluminum chloride is added. 9ppm, nickel concentration 8. 4 ppm, zinc concentration after electrolysis 4. 1 1ppm, nickel concentration 5.
It was 3 ppm.

Claims (1)

【特許請求の範囲】[Claims] 1 廃水を電解して浄化する方法において、電解槽に供
給する廃水中にアルミン酸ソーダを加えることによって
廃水中に水酸化アルミニウムを生成させ、且つ不溶性陽
極を使用して電解することを特徴とする廃水の浄化法。
1. A method for purifying wastewater by electrolysis, characterized by adding sodium aluminate to the wastewater supplied to the electrolytic cell to generate aluminum hydroxide in the wastewater, and electrolyzing using an insoluble anode. Wastewater purification method.
JP50084669A 1975-07-10 1975-07-10 High speed inoji youkahouhou Expired JPS586554B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP50084669A JPS586554B2 (en) 1975-07-10 1975-07-10 High speed inoji youkahouhou

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP50084669A JPS586554B2 (en) 1975-07-10 1975-07-10 High speed inoji youkahouhou

Publications (2)

Publication Number Publication Date
JPS528662A JPS528662A (en) 1977-01-22
JPS586554B2 true JPS586554B2 (en) 1983-02-04

Family

ID=13837109

Family Applications (1)

Application Number Title Priority Date Filing Date
JP50084669A Expired JPS586554B2 (en) 1975-07-10 1975-07-10 High speed inoji youkahouhou

Country Status (1)

Country Link
JP (1) JPS586554B2 (en)

Also Published As

Publication number Publication date
JPS528662A (en) 1977-01-22

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