JP2002327288A - Method for collecting hydrochloric acid and copper from copper chloride solution - Google Patents

Method for collecting hydrochloric acid and copper from copper chloride solution

Info

Publication number
JP2002327288A
JP2002327288A JP2001132339A JP2001132339A JP2002327288A JP 2002327288 A JP2002327288 A JP 2002327288A JP 2001132339 A JP2001132339 A JP 2001132339A JP 2001132339 A JP2001132339 A JP 2001132339A JP 2002327288 A JP2002327288 A JP 2002327288A
Authority
JP
Japan
Prior art keywords
copper
aqueous solution
hydrochloric acid
sulfuric acid
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.)
Withdrawn
Application number
JP2001132339A
Other languages
Japanese (ja)
Inventor
Masaaki Ansaki
雅章 庵崎
Hiromichi Matsumoto
博道 松本
Yuji Tanimura
裕次 谷村
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.)
Nittetsu Mining Co Ltd
Original Assignee
Nittetsu 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 Nittetsu Mining Co Ltd filed Critical Nittetsu Mining Co Ltd
Priority to JP2001132339A priority Critical patent/JP2002327288A/en
Publication of JP2002327288A publication Critical patent/JP2002327288A/en
Withdrawn legal-status Critical Current

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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

Landscapes

  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Removal Of Specific Substances (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • ing And Chemical Polishing (AREA)
  • Electrolytic Production Of Metals (AREA)
  • Manufacturing Of Printed Circuit Boards (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for collecting valuable substances from effluent of copper chloride etchant, which is suitable for a comparatively small factory or the case of collecting surplus effluent in the other location. SOLUTION: This method comprises adding a sulphuric acid solution to a copper chloride solution and concentrating it, collecting dilute hydrochloric acid, diluting the mixture of crystalline copper sulfate and aqueous solution of copper sulfate left after collecting hydrochloric acid in the concentration process, with water, redissolving the precipitated crystals into the aqueous solution without taking them out, collecting metallic copper by electrolyzing the aqueous solution containing the crystals redissolved in the dilution process, and circulating the aqueous solution after collecting metallic copper to the concentration process, to use it repeatedly.

Description

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

【0001】[0001]

【発明の属する技術分野】プリント配線板の製造工程に
おいて、塩化銅、塩酸を主成分とするエッチング゛液に
より銅箔を腐食させ所望のパターンを形成することが工
業的に行われており、その際に使用済みのエッチング液
は廃液として工場外で処理されている。本発明は、使用
済みのエッチング廃液を硫酸置換法と電解法を利用して
再生処理するための方法に関するものである。
BACKGROUND OF THE INVENTION In the manufacturing process of printed wiring boards, it is industrially performed to form a desired pattern by corroding a copper foil with an etching solution mainly containing copper chloride and hydrochloric acid. At this time, the used etching solution is treated outside the factory as a waste solution. The present invention relates to a method for regenerating a used etching waste liquid by using a sulfuric acid substitution method and an electrolytic method.

【0002】[0002]

【従来の技術】劣化した上記エッチング液に対しては、
一般的には、過酸化水素水を酸化剤として注入し、素材
の溶解に伴って生成した塩化第1銅又は塩化第1鉄を酸
化再生するとともに水で希釈して、塩酸を補充すること
が行われている。 (過酸化水素による塩化第1銅の酸化の反応式) CuCl+1/2H+HCl→CuCl+H
2. Description of the Related Art For the above-mentioned deteriorated etching solution,
In general, hydrogen peroxide water is injected as an oxidizing agent, and cuprous chloride or ferrous chloride generated along with dissolution of the material is oxidized and regenerated and diluted with water to replenish hydrochloric acid. Is being done. (Scheme oxidation of cuprous chloride with hydrogen peroxide) CuCl + 1 / 2H 2 O 2 + HCl → CuCl 2 + H 2 O

【0003】しかし、このような方法は銅イオンの酸化
力を回復することはできるが、別途塩素イオン補充のた
めに塩酸添加が必要で且つ溶解した銅成分を除去できず
に水で希釈することから、余剰となるエッチング液を廃
液として処分する必要がある。
[0003] However, such a method can restore the oxidizing power of copper ions, but requires the addition of hydrochloric acid to replenish chloride ions and dilutes with water without dissolving the dissolved copper component. Therefore, it is necessary to dispose excess etching liquid as waste liquid.

【0004】上記したエッチング廃液に対する処理方法
として、硫酸を添加して濃縮し、硫酸銅の結晶と塩酸を
回収する方法(以下、硫酸置換法と称する)が特開平5
−33168号公報で提案されている。しかしながら、
当該方法により回収される硫酸銅は塩素成分を含むため
に高品位のものを得るのが困難である。
As a method of treating the above-mentioned etching waste liquid, a method of adding sulfuric acid and concentrating the same to recover copper sulfate crystals and hydrochloric acid (hereinafter referred to as a sulfuric acid substitution method) is disclosed in Japanese Patent Application Laid-Open No. Hei 5 (1993) -105.
No. 33168 is proposed. However,
It is difficult to obtain high quality copper sulfate recovered by this method because it contains a chlorine component.

【0005】上記特開平5−33168号によれば、得
られた硫酸銅結晶を水溶液として溶解した後に再結晶さ
せ、更に水洗して塩素成分を低減することも開示されて
いるが、硫酸銅の結晶を外部に取り出し遠心脱水する装
置、特に運転管理が自動化された装置の設置には多大な
コストがかかる。また、洗浄排水の処理が別途必要であ
る等の問題がある。
According to the above-mentioned Japanese Patent Application Laid-Open No. 5-33168, it is disclosed that the obtained copper sulfate crystal is dissolved in an aqueous solution, recrystallized, and further washed with water to reduce the chlorine component. A great deal of cost is required to install a device for taking out crystals to the outside and performing centrifugal dehydration, particularly a device whose operation management is automated. In addition, there is a problem that treatment of washing wastewater is required separately.

【0006】また一方、本発明の発明者らは、特開平5
−125564号公報、特開平5−117879号公報
において隔膜電解法による再生方法を提案し、これらの
電解再生プロセスに使用する電解槽の構造について特開
平6−158359号公報で提案し実用化している。
On the other hand, the inventors of the present invention have disclosed in
JP-A-125564 and JP-A-5-117879 propose a regeneration method using a diaphragm electrolysis method, and the structure of an electrolytic cell used for these electrolytic regeneration processes is proposed and put to practical use in JP-A-6-158359. .

【0007】更に特願平11−280011号等におい
て、塩化銅と塩酸を主成分とするエッチング液を電解
し、エッチング液中の銅イオンを金属銅として回収する
とともに生成する塩素ガスをエッチング液の再生に利用
するための方法及び装置について提案し実用化してい
る。
Further, in Japanese Patent Application No. 11-280011 or the like, an etching solution containing copper chloride and hydrochloric acid as main components is electrolyzed, copper ions in the etching solution are recovered as metallic copper, and chlorine gas generated is removed from the etching solution. A method and apparatus for use in reproduction have been proposed and put into practical use.

【0008】しかし、塩化銅エッチング液を直接電解す
る方法は塩素ガスの発生を伴うため、この塩素ガスの取
り扱いを考慮する必要があり、上記再生法ではこれを前
記過酸化水素の代わりにエッチング液の再生に使用する
ことにしている。
However, since the method of directly electrolyzing the copper chloride etching solution involves the generation of chlorine gas, it is necessary to consider the handling of the chlorine gas. In the above-mentioned regenerating method, this is replaced with the etching solution instead of the hydrogen peroxide. I'm going to use it for playback.

【0009】それ故に、過酸化水素を不要にできるメリ
ットを活かすべく、比較的大量の液処理を行う場合にエ
ッチング廃液の排出元であるエッチング工程内に組み入
れるには適する方法であるが、過酸化水素等の酸化剤使
用量が少ない比較的小規模の工場を対象とする場合や、
余剰となる廃液をエッチング工程から離れた別の場所で
回収する場合には不適である。
Therefore, in order to take advantage of the fact that hydrogen peroxide can be made unnecessary, when performing a relatively large amount of liquid treatment, this method is suitable for being incorporated into an etching process from which an etching waste liquid is discharged. When targeting relatively small factories that use less oxidizing agents such as hydrogen,
It is unsuitable when the surplus waste liquid is collected at another place away from the etching step.

【0010】[0010]

【発明が解決しようとする課題】以上の問題点に照らし
て、比較的小規模の工場を対象とする場合や余剰となる
廃液を別の場所で回収する場合に適した塩化銅エッチン
グ廃液からの有価物回収方法の提供を本発明の目的とす
る。
DISCLOSURE OF THE INVENTION In view of the above problems, a copper chloride etching waste solution suitable for a relatively small-scale factory or for recovering excess waste solution at another place. It is an object of the present invention to provide a valuable resource recovery method.

【0011】[0011]

【課題を解決するための手段】本発明者らは、硫酸置換
法の実用化、特にエッチング工程を有する工場内又はそ
の近傍での実施を妨げる要因が、回収される硫酸銅の結
晶を分離回収する設備の設置に多大なコストが必要なこ
と、及び回収される硫酸銅結晶からの塩素成分除去が困
難で、上記設備コスト及び原料となる硫酸のコストに見
合う硫酸銅結晶の販売利益が得られないこと、にあり、
以上の解決には、塩化銅を主成分とする水溶液に、硫酸
を主成分とする水溶液を加えて濃縮し希塩酸を回収する
濃縮工程と、当該濃縮工程で塩酸を回収した後の、硫酸
銅の結晶及び硫酸銅と硫酸を主成分とする水溶液の混合
物を水で希釈し、析出した結晶を外部に取り出すことな
く当該水溶液中に再溶解する希釈工程と、当該希釈工程
で結晶を溶解した後の、硫酸銅と硫酸を主成分とする水
溶液を電解し金属銅を回収する電解工程と、当該電解工
程で金属銅を回収した後の、硫酸を主成分とする水溶液
を前記濃縮工程に循環し、繰り返し使用することにより
前記問題点を解決できることを見出し本発明を完成させ
た。
SUMMARY OF THE INVENTION The present inventors have found that a factor that hinders the practical use of the sulfuric acid substitution method, particularly in or near a factory having an etching step, is to separate and collect the recovered copper sulfate crystals. Large cost is required for the installation of the equipment to be performed, and it is difficult to remove the chlorine component from the recovered copper sulfate crystal, and the sales profit of the copper sulfate crystal is obtained in proportion to the above equipment cost and the cost of sulfuric acid as the raw material. There is no
In order to solve the above problems, a concentration step of adding an aqueous solution containing sulfuric acid as a main component to an aqueous solution containing copper chloride as a main component and concentrating the solution to recover dilute hydrochloric acid, and recovering hydrochloric acid in the concentration process, A dilution step of diluting a mixture of crystals and an aqueous solution mainly containing copper sulfate and sulfuric acid with water, and dissolving the precipitated crystals in the aqueous solution without taking out the precipitated crystals to the outside, and dissolving the crystals in the dilution step An electrolysis step of electrolyzing an aqueous solution containing copper sulfate and sulfuric acid as a main component to recover metallic copper, and after recovering metallic copper in the electrolysis process, circulating an aqueous solution containing sulfuric acid as a main component in the concentration step, The inventors have found that the above problem can be solved by repeated use, and have completed the present invention.

【0012】[0012]

【発明の実施の形態】実施例1 図1に示された設備において、塩化銅廃液計量槽1に1
25g/リットルの銅、250g/リットルの塩素成分
を含む液比重1.25の塩化銅水溶液80リットルを受
け入れた。一方、硫酸計量槽2にバレル電解槽5で銅回
収後の希硫酸約430リットルを硫酸受槽6を介して受
け入れた。希硫酸中のCu、Cl、SO は各々2.
1、3.9、179g/リットル、液比重1.12であ
った。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiment 1 In the equipment shown in FIG.
25g / l copper, 250g / l chlorine component
80 liters of copper chloride aqueous solution containing 1.25
I got it. On the other hand, the barrel electrolytic cell 5 feeds copper into the sulfuric acid measuring tank 2.
About 430 liters of dilute sulfuric acid after collection is received via sulfuric acid receiving tank 6.
I got it. Cu, Cl, SO in dilute sulfuric acid 4Are 2.
1, 3.9, 179 g / liter, liquid specific gravity 1.12
Was.

【0013】200リットルの内容積を有する強化ガラ
ス製の濃縮・希釈容器3に上記塩化銅水溶液と希硫酸を
一定の比率で回分式に送液した。すなわち1回当たり同
時に塩化銅26.7リットルと希硫酸143.3リット
ルの合計170リットルを、3回に分けて送液し、攪拌
機4で混合しながら電気ヒータ(図示せず)により加熱
濃縮した。
The copper chloride aqueous solution and the dilute sulfuric acid were fed in a batchwise manner to a concentrated / dilution container 3 made of tempered glass having an internal volume of 200 liters at a fixed ratio. That is, a total of 170 liters of 26.7 liters of copper chloride and 143.3 liters of dilute sulfuric acid were simultaneously sent per time, divided into three times, and heated and concentrated by an electric heater (not shown) while mixing with the stirrer 4. .

【0014】濃縮・希釈容器3内の圧力はエゼクタ8を
用いて絶対圧50〜80mmHOの真空とした。濃縮
・希釈容器3内での濃縮時の液温は40〜80℃であっ
た。送液量は塩化銅廃液計量槽1、硫酸計量槽2に設置
した各レベルスイッチによりポンプの起動・停止をする
ことにより制御した。
The pressure in the concentration / dilution vessel 3 was set to a vacuum of 50 to 80 mmH 2 O by using the ejector 8. The liquid temperature at the time of concentration in the concentration / dilution container 3 was 40 to 80 ° C. The amount of liquid sent was controlled by starting and stopping the pump with each level switch installed in the copper chloride waste liquid measuring tank 1 and the sulfuric acid measuring tank 2.

【0015】濃縮時に蒸発したベーパはエゼクタ8で吸
引し希塩酸受槽7内の希塩酸と直接接触させ液化した。
希塩酸は冷却器9で冷却し、凝縮熱を除去した。回収し
た希塩酸の総量は433.9リットル、Cl濃度45.
4g/リットル、比重1.03であった。
The vapor evaporated at the time of concentration was sucked by the ejector 8 and brought into direct contact with the dilute hydrochloric acid in the dilute hydrochloric acid receiving tank 7 to be liquefied.
The diluted hydrochloric acid was cooled by the cooler 9 to remove heat of condensation. The total amount of the diluted hydrochloric acid collected was 433.9 liters, and the Cl concentration was 45.
4 g / liter and specific gravity 1.03.

【0016】上記した濃縮工程及び希塩酸の分離回収工
程を経た後の濃縮・希釈容器3内には、クリーム状の硫
酸銅結晶を含むスラリーが残ったので、容器3内に希釈
水を注入し攪拌しながら溶解し、硫酸受槽6に送液し
た。希釈は濃縮の回数に合わせて3回行い、注入した希
釈水の総量は371.1リットルであった。硫酸受槽6
に送られた液の総量は419.9リットルで、Cu、C
l、SO濃度は各々25.7、5.0、180g/リ
ットル、液比重1.17であった。
After the concentration step and the dilute hydrochloric acid separation / recovery step, the slurry containing creamy copper sulfate crystals remains in the concentration / dilution vessel 3. Dilution water is poured into the vessel 3 and stirred. While dissolving, the solution was sent to the sulfuric acid receiving tank 6. Dilution was performed three times in accordance with the number of times of concentration, and the total amount of injected dilution water was 371.1 liters. Sulfuric acid receiving tank 6
The total amount of the liquid sent to 419.9 liters was Cu, C
1 and SO 4 concentrations were 25.7, 5.0 and 180 g / l, respectively, and the liquid specific gravity was 1.17.

【0017】上記硫酸受槽6に送られた液は更にバレル
電解槽5に送液され、オーバーフローで硫酸受槽6に戻
る循環のもとで電解され脱銅される。液中の銅成分は回
転する六角柱形のバレル内の、陰極ペレット(外径28
mm×長さ30mmの銅管)表面に金属銅として析出さ
せ回収した。脱銅後の液(希硫酸)は液量417.1リ
ットル、Cu、Cl、SO濃度は各々1.9、4.
3、181.2g/リットル、液比重1.12であっ
た。回収された金属銅は10kg、電解電流、電圧は各
々500A、6.5V、通電時間18時間で回収銅に対
する電流効率は93.7%であった。脱銅後の希硫酸は
硫酸計量槽2に送液し繰り返し使用した。
The solution sent to the sulfuric acid receiving tank 6 is further sent to the barrel electrolytic tank 5, where it is electrolyzed and decopperized in a circulation returning to the sulfuric acid receiving tank 6 by overflow. The copper component in the solution is converted into cathode pellets (outside diameter 28) in a rotating hexagonal barrel.
It was deposited and recovered as metallic copper on the surface of a copper tube (mm × 30 mm long). The liquid (dilute sulfuric acid) after the removal of copper has a liquid volume of 417.1 liters, and the concentrations of Cu, Cl and SO 4 are 1.9 and 4 .
3, 181.2 g / l, liquid specific gravity 1.12. The recovered metallic copper was 10 kg, the electrolytic current and the voltage were each 500 A and 6.5 V, and the current efficiency with respect to the recovered copper was 93.7% when the energizing time was 18 hours. The diluted sulfuric acid after copper removal was sent to the sulfuric acid measuring tank 2 and used repeatedly.

【0018】以上の処理をプロセスフローとして示した
ものが図2であり、これを表にまとめたものが表1であ
る。
FIG. 2 shows the above processing as a process flow, and Table 1 summarizes the processing in a table.

【表1】 [Table 1]

【0019】実施例2 再び図1において、塩化銅廃液計量槽1に125g/リ
ットルの銅、250g/リットルの塩素成分を含む液比
重1.25の塩化銅水溶液80リットルを受け入れた。
一方、硫酸計量槽2にバレル電解槽5で銅回収後の希硫
酸407.9リットルを硫酸受槽6を介して受け入れ
た。希硫酸中のCu、C1、SOは各々1.1、5.
2、179.2g/リットル、液比重1.12であっ
た。
EXAMPLE 2 Referring again to FIG. 1, 80 liters of an aqueous copper chloride solution having a specific gravity of 1.25 and containing 125 g / l of copper and 250 g / l of a chlorine component was received in the copper chloride waste liquid measuring tank 1.
On the other hand, 407.9 liters of diluted sulfuric acid after copper recovery in the barrel electrolytic tank 5 was received in the sulfuric acid measuring tank 2 via the sulfuric acid receiving tank 6. Cu in dilute sulfuric acid, C1, SO 4 each 1.1,5.
It was 2,179.2 g / liter and the liquid specific gravity was 1.12.

【0020】濃縮・希釈容器3に上記塩化銅液と希硫酸
を一定の比率で回分式に送液した。すなわち1回当たり
同時に塩化銅26.7リットルと希硫酸136.0リッ
トルの合計162.7リットルを、3回に分けて送液
し、撹伴機4で混合しながら電気ヒータにより加熱濃縮
した。
The above-mentioned copper chloride solution and dilute sulfuric acid were fed to the concentration / dilution container 3 in a batchwise manner at a fixed ratio. That is, a total of 162.7 liters of 26.7 liters of copper chloride and 136.0 liters of dilute sulfuric acid were simultaneously sent per one batch in three portions, and the mixture was heated and concentrated by an electric heater while mixing with the stirrer 4.

【0021】濃縮・希釈容器内の圧力調整、濃縮時の液
温、送液量制御は実施例1の場合と全く同じである。濃
縮時に蒸発したベーパはエゼクタ8で吸引し希塩酸受槽
7内の希釈水と直接接触させ液化した。液化した塩酸を
希薄に含む水溶液は冷却器9で冷却し、凝縮熱を除去し
た。回収し増加した分の水溶液(希釈工程で希釈水とし
て用いる)の総量は281.4リットル、Cl濃度2
9.5g/リットル、比重1.025で、希硫酸を払出
した後の硫酸計量槽2に送液した。
The control of the pressure in the concentration / dilution vessel, the control of the liquid temperature during the concentration and the control of the amount of liquid sent are exactly the same as those in the first embodiment. The vapor evaporated at the time of concentration was sucked by the ejector 8 and brought into direct contact with dilution water in the dilute hydrochloric acid receiving tank 7 to be liquefied. The aqueous solution dilutely containing the liquefied hydrochloric acid was cooled by the cooler 9 to remove heat of condensation. The total amount of the aqueous solution recovered and increased (used as dilution water in the dilution step) is 281.4 liters, and the Cl concentration is 2
At 9.5 g / l and a specific gravity of 1.025, the diluted sulfuric acid was fed to the sulfuric acid measuring tank 2 after discharging it.

【0022】上記した濃縮工程及び希釈水の分離回収工
程を経た後の濃縮液を更に濃縮し(第2段濃縮)、希塩
酸の回収を行った。濃縮時に蒸発したベーパは第1段濃
縮の場合と同じく、エゼクタ8で吸引し、希塩酸受槽7
内の第1段濃縮時の残液たる希塩酸と直接接触させ液化
し、更に液化分を含む当該希塩酸は冷却器9で冷却し、
凝縮熱を除去した。回収した希塩酸の総量は138.1
リットル、Cl濃度118g/リットル、比重1.05
5であった。
The concentrate obtained after the above-mentioned concentration step and separation / recovery step of the dilution water was further concentrated (second-stage concentration), and the diluted hydrochloric acid was recovered. The vapor evaporated at the time of concentration is sucked by the ejector 8 as in the case of the first-stage concentration, and the diluted hydrochloric acid receiving tank 7 is used.
Liquefied by direct contact with dilute hydrochloric acid as a residual liquid at the time of the first-stage concentration, and further dilute hydrochloric acid containing a liquefied component is cooled by a cooler 9;
The heat of condensation was removed. The total amount of dilute hydrochloric acid recovered was 138.1
Liter, Cl concentration 118g / liter, specific gravity 1.05
It was 5.

【0023】上記第2段濃縮後の濃縮・希釈容器3内に
は、クリーム状の硫酸銅結晶を含むスラリーが残ったの
で、上記第1段濃縮時に硫酸計量槽2に送液された希釈
水を濃縮・希釈容器3内に送り、攪拌しながら硫酸銅の
結晶を溶解し、溶解後の硫酸銅水溶液を硫酸受槽6に送
液した。濃縮・希釈容器3に注入した希釈水の総量は第
1段濃縮時に回収した量と同じ281.4リットルであ
る。硫酸受槽6に送られた液の総量は410.7リット
ルで、Cu、Cl、SO濃度は各々27.0、13.
4、178g/リットル、液比重1.17であった。
Since the slurry containing creamy copper sulfate crystals remained in the concentration / dilution vessel 3 after the second-stage concentration, the dilution water fed to the sulfuric acid measuring tank 2 during the first-stage concentration was used. Was sent into the concentration / dilution vessel 3 to dissolve the copper sulfate crystals with stirring, and the dissolved copper sulfate aqueous solution was sent to the sulfuric acid receiving tank 6. The total amount of dilution water injected into the concentration / dilution container 3 is 281.4 liters, which is the same as the amount recovered during the first-stage concentration. The total amount of the liquid sent to the sulfuric acid receiving tank 6 was 410.7 liters, and the concentrations of Cu, Cl and SO 4 were 27.0 and 13.
4, 178 g / liter and liquid specific gravity 1.17.

【0024】上記硫酸受槽6に送られた液は更にバレル
電解槽5に送液され、オーバーフローで硫酸受槽6に戻
る循環のもとで電解され脱銅される。液中の銅成分は回
転する六角柱形のバレル内の、陰極ペレット(外径28
mm×長さ30mmの銅管)表面に金属銅として析出さ
せ回収した。脱銅後の液(希硫酸)は液量407.9リ
ットル、Cu、Cl、SO濃度は各々2.7、12.
7、179.2g/リットル、液比重1.12であっ
た。回収された金属銅は10kg、電解電流、電圧は各
々500A、6.3V、通電時間18.5時間で回収銅
に対する電流効率は91.2%であった。脱銅後の希硫
酸は硫酸計量槽2に送液し繰り返し使用した。
The solution sent to the sulfuric acid receiving tank 6 is further sent to the barrel electrolytic tank 5 and electrolyzed and copper-removed under circulation returning to the sulfuric acid receiving tank 6 by overflow. The copper component in the solution is converted into cathode pellets (outer diameter 28) in a rotating hexagonal barrel.
It was deposited and recovered on the surface of a copper tube (mm × 30 mm length) as metallic copper. The liquid (dilute sulfuric acid) after the removal of copper had a liquid volume of 407.9 liters, and the concentrations of Cu, Cl and SO 4 were 2.7 and 12 respectively.
7, 179.2 g / liter and liquid specific gravity 1.12. The recovered metallic copper was 10 kg, the electrolytic current and the voltage were 500 A and 6.3 V, respectively, the energizing time was 18.5 hours, and the current efficiency with respect to the recovered copper was 91.2%. The diluted sulfuric acid after copper removal was sent to the sulfuric acid measuring tank 2 and used repeatedly.

【0025】以上の処理をプロセスフローとして示した
ものが図3であり、これを表にまとめたものが表2であ
る。
FIG. 3 shows the above processing as a process flow, and Table 2 summarizes the processing in a table.

【表2】 [Table 2]

【0026】[0026]

【発明の効果】本方法によれば、硫酸を原料として消費
することなく、塩素成分を含む硫酸銅結晶よりも販売利
益を得られる金属銅として回収でき好都合である。
According to the present method, it is convenient to recover as metallic copper which can obtain a sales profit more than a copper sulfate crystal containing a chlorine component without consuming sulfuric acid as a raw material.

【0027】また、回転バレルを使用する電解装置は、
同じ銅成分の回収能力を有する硫酸銅結晶の分離回収用
自動遠心脱水機と比較すると、少なくとも1/3以下の
コストで製作できる。
Further, an electrolysis apparatus using a rotating barrel is:
Compared with an automatic centrifugal dehydrator for separating and recovering copper sulfate crystals having the same copper component recovery capability, it can be manufactured at least at a cost of 1/3 or less.

【0028】また、装置の運転管理に要する人員も10
日に一回程度の陰極ペレットの交換以外ほとんど不要で
あり更に好都合である。
The number of personnel required for operation management of the apparatus is also 10
It is almost unnecessary other than changing the cathode pellets once a day, which is more convenient.

【0029】エッチング工程で利用可能な希塩酸は、そ
の濃度下限が普通は10%以上必要であるが、濃縮工程
を二段階とすれば、そのような濃度確保が容易となる。
濃縮工程においては、攪拌手段を備えた回分式の容器を
使用することが考えられるが、二段階で濃縮を行う際に
は、両方の段階で同じ容器を使用することが可能であ
る。
The concentration of dilute hydrochloric acid that can be used in the etching step usually needs to be 10% or more. However, if the concentration step is performed in two steps, it is easy to secure such a concentration.
In the concentration step, it is conceivable to use a batch type vessel equipped with a stirring means. However, when the concentration is performed in two steps, the same vessel can be used in both steps.

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

【図1】本発明に係る塩酸と銅を回収する方法を実施す
るための設備を概念的に示した図である。
FIG. 1 is a diagram conceptually showing equipment for carrying out a method for recovering hydrochloric acid and copper according to the present invention.

【図2】本発明の第1の実施形態に係る回収方法のプロ
セスを示すフロー図である。
FIG. 2 is a flowchart showing a process of a collection method according to the first embodiment of the present invention.

【図3】本発明の第2の実施形態に係る回収方法のプロ
セスを示すフロー図である。
FIG. 3 is a flowchart showing a process of a collection method according to a second embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 塩化銅廃液計量槽 2 硫酸計量槽 3 濃縮・希釈容器 4 攪拌機 5 バレル電解槽 6 硫酸受槽 7 希塩酸受槽 8 エゼクタ 9 冷却器 1 Copper chloride waste liquid measuring tank 2 Sulfuric acid measuring tank 3 Concentration / dilution container 4 Stirrer 5 Barrel electrolytic tank 6 Sulfuric acid receiving tank 7 Dilute hydrochloric acid receiving tank 8 Ejector 9 Cooler

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 1/58 C02F 1/62 ZABC 5E339 1/62 ZAB C23F 1/46 C23F 1/46 C25C 7/06 301A C25C 7/06 301 H05K 3/06 Z H05K 3/06 C02F 1/46 101B (72)発明者 谷村 裕次 東京都西多摩郡日の出町平井8−1 日鉄 鉱業株式会社内 Fターム(参考) 4D034 AA27 BA01 CA12 4D038 AA08 AB39 AB68 BA02 BA04 BB02 BB10 4D061 DA08 DB18 EA02 EA05 EB02 EB04 EB16 EB31 EB33 FA02 FA05 4K057 WB04 WE08 WH01 WH07 WM19 WN01 4K058 AA22 BA21 BB04 CA04 EB01 EB13 FA17 FA24 FC07 FC26 5E339 AB01 BC02 BE11 BE13 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C02F 1/58 C02F 1/62 ZABC 5E339 1/62 ZAB C23F 1/46 C23F 1/46 C25C 7/06 301A C25C 7/06 301 H05K 3/06 Z H05K 3/06 C02F 1/46 101B (72) Inventor Yuji Tanimura 8-1 Hiraicho Hiraicho, Nishitama-gun, Tokyo Nippon Steel Mining Co., Ltd. F-term (reference) 4D034 AA27 BA01 CA12 4D038 AA08 AB39 AB68 BA02 BA04 BB02 BB10 4D061 DA08 DB18 EA02 EA05 EB02 EB04 EB16 EB31 EB33 FA02 FA05 4K057 WB04 WE08 WH01 WH07 WM19 WN01 4K058 AA22 BA21 BB04 FC04 FA17 BE13 FC13 BC01 FC13

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 塩化銅を主成分とする水溶液に、硫酸を
主成分とする水溶液を加えて濃縮し希塩酸を回収する濃
縮工程と、 当該濃縮工程で塩酸を回収した後の、硫酸銅の結晶及び
硫酸銅と硫酸を主成分とする水溶液の混合物を希釈水で
希釈し、析出した結晶を外部に取り出すことなく当該水
溶液中に再溶解する希釈工程と、 当該希釈工程で結晶を溶解した後の、硫酸銅と硫酸を主
成分とする水溶液を電解し金属銅を回収する電解工程
と、 当該電解工程で金属銅を回収した後の、硫酸を主成分と
する水溶液を前記濃縮工程に循環し、繰り返し使用する
ことを特徴とする塩化銅液からの塩酸と銅の回収方法。
1. A concentration step of adding an aqueous solution containing sulfuric acid as a main component to an aqueous solution containing copper chloride as a main component and concentrating the aqueous solution to recover dilute hydrochloric acid, and forming a crystal of copper sulfate after collecting hydrochloric acid in the concentrating process. A dilution step of diluting a mixture of an aqueous solution mainly containing copper sulfate and sulfuric acid with diluting water, and re-dissolving the precipitated crystals in the aqueous solution without taking them out, and dissolving the crystals in the dilution step. An electrolysis step of electrolyzing an aqueous solution containing copper sulfate and sulfuric acid as a main component and recovering metallic copper, and after recovering the metallic copper in the electrolysis process, circulating the aqueous solution containing sulfuric acid as a main component in the concentration step, A method for recovering hydrochloric acid and copper from a copper chloride solution, wherein the method is used repeatedly.
【請求項2】 前記濃縮工程を二段階とし、第一段階濃
縮工程で蒸発する塩酸を希薄に含む水溶液を、前記希釈
工程における希釈水として使用し、 第二段階濃縮工程で蒸発する塩酸を第一段階と比較して
濃厚に含む水溶液を、希塩酸として回収することを特徴
とする請求項1に記載の塩化銅液からの塩酸と銅の回収
方法。
2. The method according to claim 1, wherein the concentration step is performed in two stages, and an aqueous solution containing hydrochloric acid diluted in the first concentration step is used as dilution water in the dilution step. 2. The method for recovering hydrochloric acid and copper from a copper chloride solution according to claim 1, wherein the aqueous solution that is more concentrated than in one step is recovered as dilute hydrochloric acid.
【請求項3】 前記濃縮工程において、攪拌手段を備え
た一又は複数の回分式の容器を使用することを特徴とす
る請求項1又は2に記載の塩化銅液からの塩酸と銅の回
収方法。
3. The method for recovering hydrochloric acid and copper from a copper chloride solution according to claim 1, wherein in the concentration step, one or a plurality of batch-type vessels provided with a stirring means are used. .
【請求項4】 前記電解工程において、複数の、流動す
る陰極ペレットを内蔵した回転バレルを備えた電解槽を
使用することを特徴とする請求項1又は2に記載の塩化
銅液からの塩酸と銅の回収方法。
4. The method according to claim 1, wherein in the electrolysis step, an electrolytic cell having a rotating barrel containing a plurality of flowing cathode pellets is used. How to recover copper.
JP2001132339A 2001-04-27 2001-04-27 Method for collecting hydrochloric acid and copper from copper chloride solution Withdrawn JP2002327288A (en)

Priority Applications (1)

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ID=18980363

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Country Link
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008127266A (en) * 2006-11-24 2008-06-05 Nittetsu Mining Co Ltd Method for producing cupric oxide from copper etching waste liquid
CN103274559A (en) * 2013-05-27 2013-09-04 天津市环境保护科学研究院 Method for treating and recycling waste chemical copper-plating liquid in iron and steel industry
CN105087930A (en) * 2015-08-31 2015-11-25 贵州大学 Method for extracting copper from structured rubble alterated rocks
WO2022059535A1 (en) * 2020-09-18 2022-03-24 栗田工業株式会社 Distillation apparatus
CN117448826A (en) * 2023-10-30 2024-01-26 天水华洋电子科技股份有限公司 Recycling process of etching solution of integrated circuit lead frame

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008127266A (en) * 2006-11-24 2008-06-05 Nittetsu Mining Co Ltd Method for producing cupric oxide from copper etching waste liquid
CN103274559A (en) * 2013-05-27 2013-09-04 天津市环境保护科学研究院 Method for treating and recycling waste chemical copper-plating liquid in iron and steel industry
CN105087930A (en) * 2015-08-31 2015-11-25 贵州大学 Method for extracting copper from structured rubble alterated rocks
WO2022059535A1 (en) * 2020-09-18 2022-03-24 栗田工業株式会社 Distillation apparatus
JP2022051045A (en) * 2020-09-18 2022-03-31 栗田工業株式会社 Distillation apparatus
JP7120283B2 (en) 2020-09-18 2022-08-17 栗田工業株式会社 distillation apparatus
CN117448826A (en) * 2023-10-30 2024-01-26 天水华洋电子科技股份有限公司 Recycling process of etching solution of integrated circuit lead frame
CN117448826B (en) * 2023-10-30 2024-05-17 天水华洋电子科技股份有限公司 Recycling process of etching solution of integrated circuit lead frame

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