JPH0625771A - Production of alkaline earth metal chloride and method for recovering valuable copper component - Google Patents

Production of alkaline earth metal chloride and method for recovering valuable copper component

Info

Publication number
JPH0625771A
JPH0625771A JP10087891A JP10087891A JPH0625771A JP H0625771 A JPH0625771 A JP H0625771A JP 10087891 A JP10087891 A JP 10087891A JP 10087891 A JP10087891 A JP 10087891A JP H0625771 A JPH0625771 A JP H0625771A
Authority
JP
Japan
Prior art keywords
alkaline earth
earth metal
copper
sulfide
chloride
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.)
Pending
Application number
JP10087891A
Other languages
Japanese (ja)
Inventor
Kennosuke Imamura
健之助 今村
Akihide Yamada
明英 山田
Yukimitsu Uno
幸光 宇野
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.)
BARAITO KOGYO KK
Nippon Chemical Industrial Co Ltd
Original Assignee
BARAITO KOGYO KK
Nippon Chemical Industrial 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 BARAITO KOGYO KK, Nippon Chemical Industrial Co Ltd filed Critical BARAITO KOGYO KK
Priority to JP10087891A priority Critical patent/JPH0625771A/en
Publication of JPH0625771A publication Critical patent/JPH0625771A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To obtain a high-purity alkaline earth metal chloride and to recover a valuable copper-component by bringing a soln. of an alkaline earth metal sulfide and a waste liquid of copper board etching into reaction. CONSTITUTION:The soln. of the alkaline earth metal sulfide, such as barium sulfide, and the etching liquid of copper printed circuit boards are mixed and are brought into reaction under stirring. These solns. are converted to the alkaline earth metal chloride, such as barium chloride and copper sulfide which are then respectively recovered by a sepn. of a liquid from solid. The leaching liquid of the product of reduction and roasting of barite ore or celestite ore is usable as the alkaline earth metal sulfide.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明はアルカリ土類金属塩化物
の製造並びに銅有価成分の回収方法に関し、更に言え
ば、電子材料工業の分野で多量に発生する銅板のエッチ
ング廃液の処理を図ると共にアルカリ土類金属塩化物を
高純度で製造する方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing an alkaline earth metal chloride and a method for recovering a valuable copper component, and more specifically, for treating an etching waste liquid of a copper plate which is generated in a large amount in the field of electronic materials industry. The present invention relates to a method for producing an alkaline earth metal chloride with high purity.

【0002】[0002]

【従来の技術】従来、アルカリ土類金属塩化物の工業的
製造法は、主としてバライト鉱またはセレスタイト鉱の
還元焙焼および浸出によって得られる硫化バリウム水溶
液または硫化ストロンチウム水溶液に塩酸を添加する方
法により、下記の(1)式の反応に基づいて行われてい
る。 MeS+2HCl=MeCl2+H2S (1) (式中、MeはBa、Srを表す)
2. Description of the Related Art Conventionally, the industrial production method of an alkaline earth metal chloride is mainly a method of adding hydrochloric acid to a barium sulfide aqueous solution or a strontium sulfide aqueous solution obtained by reducing roasting and leaching of barite or celesite ore. It is carried out based on the reaction of the following formula (1). MeS + 2HCl = MeCl 2 + H 2 S (1) (In the formula, Me represents Ba and Sr)

【0003】しかしながら、この方法においては、上記
の反応の際に硫化水素ガスが副生するが、この硫化水素
ガスは有毒で、しかも腐食性が大きいために、その安全
な取り扱い並びに無害化処理の諸対策が不可欠であり、
その無害化処理に要する付帯設備に多額の費用がかかる
だけではなく、塩化バリウムや塩化ストロンチウム等の
アルカリ土類金属塩化物自体の生産がしばしば硫化水素
ガス処理の事情で左右されるという不都合があった。
In this method, however, hydrogen sulfide gas is produced as a by-product during the above reaction, but since this hydrogen sulfide gas is toxic and highly corrosive, its safe handling and detoxification treatment are required. Various measures are essential,
Not only is the incidental equipment required for the detoxification treatment costly, but the production of alkaline earth metal chlorides such as barium chloride and strontium chloride itself is often affected by the treatment of hydrogen sulfide gas. It was

【0004】一方、このような有毒な硫化水素ガスの発
生を伴わない塩化バリウムの製造法としては、例えば、 重晶石と炭素と塩化カルシウムを混合し、高温で焙焼
して下記の(2)式の反応を行わせる方法、 BaSO4+4C+CaCl2=BaCl2+CaS+4CO (2) 炭酸バリウムに塩酸を添加して下記の(3)式の反応を
行わせる方法、 BaCO3+2HCl=BaCl2+CO2+H2O (3) 600〜800℃で塩化バリウムに塩素ガスを反応さ
せる方法、 等が知られている。
On the other hand, as a method for producing barium chloride without generation of such toxic hydrogen sulfide gas, for example, barite, carbon and calcium chloride are mixed and roasted at a high temperature and the following (2) ), The reaction of BaSO 4 + 4C + CaCl 2 = BaCl 2 + CaS + 4CO (2) The method of adding hydrochloric acid to barium carbonate to carry out the reaction of the following formula (3), BaCO 3 + 2HCl = BaCl 2 + CO 2 + H 2 O (3) A method of reacting barium chloride with chlorine gas at 600 to 800 ° C., and the like are known.

【0005】しかしながら、これらの方法では、硫化カ
ルシウムのような不安定でかつ有毒な副産物が多量に生
じたり、また炭酸バリウムのような高価な原料を必要と
したり、さらに腐食性の強い塩素ガスを高温で取り扱わ
ねばならず、しかも反応率が低い等の欠点を有するため
に何れの方法も実用的ではない。
However, in these methods, unstable and toxic by-products such as calcium sulfide are produced in large amounts, expensive raw materials such as barium carbonate are required, and chlorine gas, which is highly corrosive, is added. None of these methods are practical because they have to be handled at high temperatures and have drawbacks such as a low reaction rate.

【0006】また、塩化バリウムの他の製造法として、
硫化バリウム水溶液に不活性ガスで希釈した塩素ガスを
導入して塩化バリウムを製造する方法が知られている
(特公昭53−27238号公報)。
[0006] As another method for producing barium chloride,
A method for producing barium chloride by introducing chlorine gas diluted with an inert gas into a barium sulfide aqueous solution is known.
(Japanese Patent Publication No. 53-27238).

【0007】他方、電子工業界では、銅のプリント配線
基板のエッチングを行った処理液(以下、「銅板エッチ
ング廃液」という)が多量に発生している。従来、係る
銅板エッチング廃液は、船底塗料などの防汚顔料である
亜酸化銅として回収利用されている(例えば、特開昭55
−71629号公報、特開昭56−155020号公報)。他の方法と
して、銅塩類又は銅粉として回収することも知られてい
る。
On the other hand, in the electronic industry, a large amount of processing liquid for etching a copper printed wiring board (hereinafter referred to as "copper plate etching waste liquid") is generated. Conventionally, such copper plate etching waste liquid is collected and utilized as cuprous oxide which is an antifouling pigment such as a ship bottom paint (for example, JP-A-55).
-71629, JP-A-56-155020). As another method, it is known to recover copper salts or copper powder.

【0008】[0008]

【発明が解決しようとする課題】上記のように、バリウ
ム塩またはストロンチウム塩製造工業では、通常、バラ
イト鉱またはセレスタイト鉱の還元焙焼物を水で浸出し
たアルカリ土類金属硫化物溶液を出発原料とするため、
バリウム塩類等の製造コストは、この多量に発生するH
2Sガスの処理コストに関係し、多くの場合H2Sガスの
無害化に困難を伴い高いものにしている。
As described above, in the barium salt or strontium salt manufacturing industry, usually, an alkaline earth metal sulfide solution obtained by leaching a reduced roasted product of barite or celestite ore with water is used as a starting material. In order to
The production cost of barium salts, etc.
In connection with the processing cost of 2 S gas, in many cases, it is difficult to render H 2 S gas harmless and the cost is high.

【0009】また、H2Sガスを副生しない塩化バリウ
ムの製造法はいずれも工業的な有利性が見いだされず、
実施の段階に至ってはいない。一方、銅板エッチング廃
液は、上記のとおり、各種銅有価物としての回収が試み
られているものの、二次廃水として塩化物の処理が問題
あるのみならず、現在の処理方法には限界があって消化
されないため、依然として、銅板エッチング廃液の処分
は当該産業界における重大な今日的問題としてその解決
が迫られている。
Further, none of the methods for producing barium chloride, which does not produce H 2 S gas as a by-product, has no industrial advantage.
It has not reached the stage of implementation. On the other hand, although the copper plate etching waste liquid has been attempted to be recovered as various copper valuable substances as described above, not only is there a problem in treating chloride as secondary waste water, but there are limits to the current treatment method. Since it is not digested, the disposal of copper plate etching waste liquid is still required to be solved as a serious contemporary problem in the industry.

【0010】本発明者らは、叙上の問題を真剣に受け止
め、鋭意研究したところ、アルカリ土類金属硫化物溶液
と銅板エッチング廃液とを反応させることにより、極め
て高純度のアルカリ土類金属塩化物と硫化物とが回収で
きることを知見し本発明を完成した。
The inventors of the present invention took the above problems seriously and conducted diligent research. As a result, by reacting an alkaline earth metal sulfide solution with a copper plate etching waste liquid, an extremely high purity alkaline earth metal chloride was obtained. The inventors have completed the present invention by discovering that substances and sulfides can be recovered.

【0011】すなわち、本発明は、バリウム塩等の製造
者および銅のプリント配線基板の製造者がかかえる問題
を一挙に解決することを意図としてアルカリ土類金属硫
化物溶液と銅板エッチング廃液とを反応させることによ
り、高純度のアルカリ土類金属塩化物およびアルカリ土
類金属塩化物を製造および回収することにある。
That is, the present invention intends to solve all the problems of manufacturers of barium salts and the like and manufacturers of printed wiring boards of copper by reacting an alkaline earth metal sulfide solution with a copper plate etching waste solution. By doing so, it is intended to produce and recover high-purity alkaline earth metal chlorides and alkaline earth metal chlorides.

【0012】[0012]

【課題を解決するための手段】本発明が提供しようとす
る方法は、アルカリ土類金属硫化物(以下、「硫化バリ
ウム等」という)溶液と銅板エッチング廃液とを反応さ
せることを構成上の特徴としてアルカリ土類金属塩化物
(以下、「塩化バリウム等」という)並びに銅有価成分を
製造並びに回収するものである。
A method to be provided by the present invention is characterized in that an alkaline earth metal sulfide (hereinafter referred to as "barium sulfide etc.") solution and a copper plate etching waste liquid are reacted. As an alkaline earth metal chloride
(Hereinafter referred to as "barium chloride etc.") and copper valuable components are manufactured and recovered.

【0013】本発明において、出発原料たる硫化バリウ
ム等溶液は、製造履歴や濃度など臨界的である必要はな
いけれども、多くの場合バライト鉱またはセレスタイト
鉱の還元焙焼物の浸出液が、特に工業的に有利である。
In the present invention, the solution such as barium sulfide as a starting material does not have to be critical in terms of production history and concentration, but in many cases, a leachate of a reduced roasted product of barite or Celestite ore is particularly industrially useful. It is advantageous.

【0014】このような浸出液は、濃い方が後の工程を
考えると良く、多くの場合Me(MeはBa、Srを表
す)として100〜500g/リットル、好ましくは2
00〜500g/リットルが実用的である。
The richer the leachate, it is better to consider the later step. In many cases, Me (Me represents Ba and Sr) is 100 to 500 g / liter, preferably 2
Practical use is from 0 to 500 g / liter.

【0015】尤も、還元焙焼物の洗液の如き、MeS濃
度の低いものであっても差し支えない。また、本発明に
おいて、硫化バリウム等溶液の意味はアルカリ土類金属
硫化物は勿論のこと、多硫化物、水硫化物など溶液中に
含む可溶性アルカリ土類金属硫化物を総称するものであ
る。
However, a solution having a low MeS concentration, such as a washing solution of a reduced roasted product, may be used. Further, in the present invention, the meaning of a solution such as barium sulfide is a generic term of not only alkaline earth metal sulfides but also soluble alkaline earth metal sulfides contained in a solution such as polysulfides and hydrosulfides.

【0016】一方、銅板エッチング廃液というのは、塩
化第2銅水溶液あるいは過酸化水素の如き酸化剤を含有
する塩酸溶液で、銅のプリント配線基板のエッチングを
行った処理液であって、通常次のものが含まれている。 CuCl:0〜50g/リットル CuCl2:30〜300g/リットル 遊離HCl:10〜200g/リットル その他:0〜30g/リットル
On the other hand, the copper plate etching waste liquid is a treatment liquid obtained by etching a copper printed wiring board with a cupric chloride aqueous solution or a hydrochloric acid solution containing an oxidizing agent such as hydrogen peroxide. Stuff is included. CuCl: 0~50g / l CuCl 2: 30~300g / l free HCl: 10 to 200 g / l Other: 0~30g / l

【0017】その他の成分として、Ni2+、Zn2+、F
3+等の重金属イオン、PO4 3-、F-などの陰イオンあ
るいは有機物等で若干量含むが、その主組成は、遊離塩
酸を含有する塩化第2銅水溶液である。
Other components include Ni 2+ , Zn 2+ , F
Heavy metal ions such as e 3+ , anions such as PO 4 3− and F , or organic substances are contained in a small amount, but the main composition is an aqueous cupric chloride solution containing free hydrochloric acid.

【0018】本発明において、上記銅板エッチング液を
そのまま原料として用いることができるが、必要に応
じ、濾過または空気酸化や過酸化水素など酸化処理を施
して用いる。
In the present invention, the above copper plate etching solution can be used as it is as a raw material, but if necessary, it is used after being filtered or subjected to oxidation treatment such as air oxidation or hydrogen peroxide.

【0019】本発明は、係る両液を混合し反応させて、
塩化バリウムと硫化銅に転換せしめ、次いで、固液分離
してそれぞれを回収する。反応方式としては、両液と同
時添加する方法、硫化バリウム溶液に銅板エッチング廃
液を添加する方法またはその逆の添加方法など、いずれ
の方式も差し支えないが、同時添加方法が操業上遊離で
ある。
According to the present invention, the two solutions are mixed and reacted,
It is converted into barium chloride and copper sulfide, and then solid-liquid separation is performed to recover each. As the reaction method, any method may be used, such as a method of simultaneously adding both solutions, a method of adding a copper plate etching waste solution to a barium sulfide solution, or the opposite method, but the simultaneous addition method is operationally free.

【0020】なお、本反応において両液の性質上、量的
バランスが問題となるが、銅板エッチング廃液を利用し
て硫化バリウム等をより多く消費させたい場合は、必要
に応じ、該廃液に設計量の塩酸および/または塩化第2
銅を加えて反応させることにより、両液を合理的かつ任
意に処分させることができる。
In this reaction, a quantitative balance is a problem due to the properties of both solutions, but if it is desired to consume more barium sulfide etc. by using the copper plate etching waste solution, design the waste solution as needed. Amount of hydrochloric acid and / or chloride second
By adding copper and reacting, both liquids can be disposed reasonably and arbitrarily.

【0021】本発明は、極めて量論的かつ速やかに進行
するので、温度や濃度は臨界的である必要はないが、後
の固液分離の操作上、濾過性は、硫化銅が生成するよう
な条件を設定し、また反応終了後必要に応じ加温下で熟
成処理を施すことが好ましい。
Since the present invention proceeds extremely stoichiometrically and rapidly, it is not necessary for the temperature and concentration to be critical, but in terms of the subsequent solid-liquid separation operation, the filterability is such that copper sulfide is produced. It is preferable to set various conditions and, if necessary, perform an aging treatment under heating after the completion of the reaction.

【0022】また、硫化バリウム溶液および銅板エッチ
ング廃液は後の濃縮および晶析などの操作を考慮すれ
ば、濃い方が有利である。
Further, it is advantageous that the barium sulfide solution and the copper plate etching waste liquid are concentrated in consideration of the subsequent operations such as concentration and crystallization.

【0023】更に、本反応は硫化バリウム等の中和反応
でありながら、Cu2+が反応系に存在する限り硫化銅の
沈殿反応が優先し硫化水素の発生を認めることはない。
もっとも、硫化水素ガスの発生を抑制してより安全性の
高い操業を行うには、本反応は酸性側特にpH4以下の
方がよい。
Further, although this reaction is a neutralization reaction of barium sulfide and the like, as long as Cu 2+ is present in the reaction system, the precipitation reaction of copper sulfide has priority and hydrogen sulfide generation is not recognized.
However, in order to suppress the generation of hydrogen sulfide gas and perform a safer operation, it is preferable that the pH of the reaction is 4 or less, especially on the acidic side.

【0024】従って、反応系の酸化還元電位を測定する
ことにより、安全に操作でき、かつ反応終点を知ること
ができる。
Therefore, by measuring the redox potential of the reaction system, it is possible to operate safely and to know the end point of the reaction.

【0025】反応終了後、暫時熟成してから、濾過また
は遠心処理等による固液分離を行い沈殿物は、洗浄およ
び乾燥して硫化銅の有価成分として回収し、これを銅の
製錬原料に再利用できる。
After completion of the reaction, after aging for a while, solid-liquid separation is performed by filtration or centrifugal treatment, and the precipitate is washed and dried to recover as a valuable component of copper sulfide, which is used as a raw material for smelting copper. Can be reused.

【0026】他方、回収母液は、必要に応じ精製および
濃縮操作を施した後、晶析することにより、塩化バリウ
ム等結晶物(BaCl2・2H2O、またはSrCl2・6
2O)として回収する。
On the other hand, the recovered mother liquor is subjected to purification and concentration operations, if necessary, and then crystallized to obtain a crystalline substance such as barium chloride (BaCl 2 .2H 2 O or SrCl 2 .6).
H 2 O).

【0027】本発明に係る方法で得られる塩化バリウム
等は、銅エッチング廃液を原料とするにも拘わらず、従
来法である硫化バリウム等浸出液と塩酸との反応に基づ
く塩化バリウム等よりも、予想外に高純度であることが
判った。この理由は、銅板エッチング廃液中に若干含有
する重金属イオン等や他の不純物は、全て硫化銅の沈殿
と共に硫化物として沈殿またはこの沈殿物に吸着し、か
つ硫化物の溶解度が極めて小であることから、母液は高
純度の塩化バリウム等に転換するからである。
Despite the fact that the copper etching waste liquid is used as a raw material, barium chloride and the like obtained by the method according to the present invention are more predictable than barium chloride and the like which is based on the reaction between a leachate such as barium sulfide and hydrochloric acid, which is a conventional method. It turned out to be highly pure. The reason for this is that all heavy metal ions and other impurities contained in the copper plate etching waste liquid are precipitated or adsorbed as sulfide with copper sulfide precipitation, and the solubility of sulfide is extremely low. Therefore, the mother liquor is converted into high-purity barium chloride or the like.

【0028】なお、本発明において、アルカリ土類金属
塩としてバリウム塩、ストロンチウム塩が工業的である
が、カルシウム塩も全く同様に適用できる。
In the present invention, barium salts and strontium salts are industrially used as the alkaline earth metal salts, but calcium salts can be applied in the same manner.

【0029】[0029]

【作用】本発明は、硫化バリウム等溶液と銅板エッチン
グ廃液とを混合処理して塩化バリウム等と銅有価成分を
それぞれ回収することにある。上記混合処理において、
バリウムで代表して示すが、Sr、Caも同様であり、
次式の主反応が生じる。 BaS+CuCl2→BaCl2+CuS↓ (4)
The present invention resides in that a barium sulfide solution and a copper plate etching waste liquid are mixed to recover barium chloride and a valuable copper component, respectively. In the above mixing process,
Barium is shown as a representative, but Sr and Ca are also the same,
The main reaction of the following formula occurs. BaS + CuCl 2 → BaCl 2 + CuS ↓ (4)

【0030】また、銅板エッチング廃液中のCu2+以下
の重金属イオンは(4)式の反応と同様に硫化物として沈
殿すると共に他の溶存する不純物もこの沈殿物に実質的
に吸着される。
Further, the heavy metal ions of Cu 2+ or less in the copper plate etching waste liquid are precipitated as sulfides as in the reaction of the formula (4), and other dissolved impurities are also substantially adsorbed by this precipitate.

【0031】すなわち、銅エッチング廃液は遊離塩酸を
含有するから、硫化バリウム溶液との中和の際、次式 BaS+2HCl→BaCl2+H2S↑ (5) の反応により、硫化水素ガスが発生するはずであるが、
反応系にCu2+等の重金属イオンが溶存している限り、 Me2++S2-→MeS↓ (6) (式中、Me2+はCu2+、Ni2+、Zn2+などを表す)の
反応によって全て非常に溶解度の小さい金属硫化物とし
て沈殿する。
That is, since the copper etching waste liquid contains free hydrochloric acid, hydrogen sulfide gas should be generated by the reaction of the following formula BaS + 2HCl → BaCl 2 + H 2 S ↑ (5) during neutralization with the barium sulfide solution. In Although,
As long as heavy metal ions such as Cu 2+ are dissolved in the reaction system, Me 2+ + S 2- → MeS ↓ (6) (In the formula, Me 2+ is Cu 2+ , Ni 2+ , Zn 2+, etc. All of the above reactions precipitate as metal sulfides with very low solubility.

【0032】結局、本発明に係る方法では、実質的に
(5)式のような硫化水素ガスの発生を認めることなく、
極めて化学量論的かつ迅速に塩化バリウムおよび硫化銅
を生成させる。
Finally, in the method according to the present invention, substantially
Without observing the generation of hydrogen sulfide gas as in formula (5),
Extremely stoichiometric and rapid production of barium chloride and copper sulfide.

【0033】従って、本発明によれば、母液からは高純
度塩化バリウム等を製造できると共に、硫化銅を製錬原
料として銅資源のリサイクルの一助とすることができ
る。
Therefore, according to the present invention, high-purity barium chloride or the like can be produced from the mother liquor, and it can also contribute to the recycling of copper resources using copper sulfide as a smelting raw material.

【0034】[0034]

【実施例】【Example】

実施例1(連続反応) バライト鉱石の還元焙焼及び浸出処理により得られた硫
化バリウム溶液(BaS:12.44%)1361重量部
と銅板エッチング廃液(CuCl2:22.52%、F−
HCl:1.57%、Zn2+80.5ppm、Mn2+:0.2
1ppm、Ni2+:54.4ppm、Cr3+:0.15ppm、
-:27ppm、COD:78ppm)597重量部とを反応
容器に同時に添加して撹拌しながら混合処理した。
Example 1 (continuous reaction) 1361 parts by weight of a barium sulfide solution (BaS: 12.44%) obtained by reduction roasting and leaching of barite ore, copper plate etching waste liquid (CuCl 2 : 22.52%, F-).
HCl: 1.57%, Zn 2+ 80.5ppm, Mn 2+ : 0.2
1 ppm, Ni 2+ : 54.4 ppm, Cr 3+ : 0.15 ppm,
F : 27 ppm, COD: 78 ppm) (597 parts by weight) were simultaneously added to the reaction vessel and mixed with stirring.

【0035】この場合による反応は室温にて系の酸化還
元電位を0〜100mVに維持してpHを所定の範囲内
に保持しながら行ったが反応終了までH2Sガスの発生
は認められず安全に操作できた。次いで30分間熟成さ
せた後、処理液を炭酸バリウムでpH6.5に中和して
濾過分離した(反応終了液中のBa収率は97%であっ
た)。分離用液には重金属イオンおよび還元性物質は検
出されなかったので、これを濃縮後晶析処理を施してB
aCl2・2H2Oの結晶物として回収した。この結晶物
を分析したところ次の表1の結果が得られた。一方、黒
色沈殿物は洗浄後乾燥して硫化銅粉末として回収し、こ
れを銅製錬原料として送ることができた。
The reaction in this case was carried out at room temperature while maintaining the redox potential of the system at 0 to 100 mV and keeping the pH within a predetermined range, but no H 2 S gas was generated until the reaction was completed. I was able to operate it safely. Then, after aging for 30 minutes, the treated solution was neutralized to pH 6.5 with barium carbonate and separated by filtration (Ba yield in the reaction completed solution was 97%). Heavy metal ions and reducing substances were not detected in the separation liquid, so they were concentrated and crystallized to give B.
It was recovered as a crystalline product of aCl 2 .2H 2 O. When this crystal product was analyzed, the results shown in Table 1 below were obtained. On the other hand, the black precipitate was washed and dried to recover as copper sulfide powder, which could be sent as a copper smelting raw material.

【0036】実施例2(バッチ反応) 実施例1と同様の銅板エッチング廃液(CuCl2:2
2.52%)299重量部を反応容器に入れ、撹拌しつつ
室温にて硫化バリウム溶液(BaS:12.44%)68
2重量部を徐々に添加した。反応終了時のpHは0.
5、酸化還元電位は50mVであり、H2Sガスの発生
は認められず安全に操作できた。次いで30分間熟成さ
せた後、処理液を水酸化バリウムで、pH6.5中和し
て濾過分離した(反応終了液中のBa収率は98.1%で
あった)。分離母液には重金属イオンと還元性物質はほ
とんど検出されなかったので、これを濃縮後、晶析処理
を施して、BaCl2・2H2Oの結晶物として回収し
た。この結晶を分析して次の表1の結果が得られた。一
方、黒色沈殿物は洗浄後乾燥して硫化銅粉末として回収
し、これを銅製錬原料として送ることができた。
Example 2 (batch reaction) The same copper plate etching waste liquid (CuCl 2 : 2) as in Example 1 was used.
2.52%) 299 parts by weight was placed in a reaction vessel, and barium sulfide solution (BaS: 12.44%) 68 was added at room temperature while stirring.
2 parts by weight were gradually added. The pH at the end of the reaction is 0.
5. The oxidation-reduction potential was 50 mV, and the generation of H 2 S gas was not observed, and the operation was safe. Then, after aging for 30 minutes, the treated solution was neutralized with barium hydroxide to pH 6.5 and separated by filtration (Ba yield in the reaction completed solution was 98.1%). Almost no heavy metal ions and reducing substances were detected in the separated mother liquor. Therefore, the concentrated mother liquor was concentrated and crystallized to recover BaCl 2 .2H 2 O crystals. The crystals were analyzed and the results shown in Table 1 below were obtained. On the other hand, the black precipitate was washed and dried to recover as copper sulfide powder, which could be sent as a copper smelting raw material.

【0037】実施例3(HClとの混合使用) 実施例1と同様の銅板エッチング廃液(CuCl2:2
2.52%、F−HCl:1.57%)90重量部と塩酸
(試薬1級HCl:35%)73重量部を混合し調整した
溶液を反応容器に入れ、撹拌しつつ室温にて硫化バリウ
ム溶液(BaS:12.44)706重量部を徐々に添加
した。このバッチによる添加は室温にて行い反応終了時
のpHは4、酸化還元電位は−400mVであり、H2
Sガスは酸化還元電位の変曲点以降で発生し始め、反応
終了に至るまで発生した。溶存H2Sガスをエアレーシ
ョンで脱気した後、30分間熟成させ処理液を水酸化バ
リウムでpH7.0に中和して濾過分離した。
Example 3 (mixed use with HCl) The same copper plate etching waste solution as in Example 1 (CuCl 2 : 2)
2.52%, F-HCl: 1.57%) 90 parts by weight and hydrochloric acid
A solution prepared by mixing 73 parts by weight of reagent first-grade HCl: 35% was placed in a reaction vessel, and 706 parts by weight of a barium sulfide solution (BaS: 12.44) was gradually added with stirring at room temperature. This batch was added at room temperature, the pH at the end of the reaction was 4, the redox potential was -400 mV, and H 2
The S gas started to be generated after the inflection point of the redox potential, and was generated until the end of the reaction. After the dissolved H 2 S gas was degassed by aeration, it was aged for 30 minutes, the treated liquid was neutralized to pH 7.0 with barium hydroxide, and separated by filtration.

【0038】分離母液には、微量の鉄イオンと還元性性
質が検出されたため酸化処理後pHを7.0として生成
した沈殿物を濾過分離した。この濾液を濃縮後、晶析処
理を施してBaCl2・2H2Oの結晶物を回収した。こ
の結晶を分析して次の表1の結果が得られた。一方、黒
色沈殿物は洗浄後乾燥して硫化銅粉末として回収し、こ
れを銅製錬として送ることができた。
In the separated mother liquor, a trace amount of iron ions and a reducing property were detected, and thus the precipitate formed after the oxidation treatment was adjusted to pH 7.0 and separated by filtration. The filtrate was concentrated and then crystallized to recover BaCl 2 .2H 2 O crystals. The crystals were analyzed and the results shown in Table 1 below were obtained. On the other hand, the black precipitate was washed and dried to recover as copper sulfide powder, which could be sent as copper smelting.

【0039】[0039]

【表1】 品質特性 実施例1 実施例2 実施例3 BaCl2・2H2O(%) 99.5 99.3 99.4 水不溶分(%) 0.0010 0.0008 0.0027 よう素還元性物質(%) 0.0001以下 0.0001以下 0.0001 Fe(%) 0.00002 0.00004 0.00004 Cu(%) 0.0001以下 0.0001以下 0.0001以下 いずれの方法によってもJIS−K−1414塩化バリウム規格
に十分に合格している。
[Table 1] Quality characteristics Example 1 Example 2 Example 3 BaCl 2 .2H 2 O (%) 99.5 99.3 99.4 Water insoluble matter (%) 0.0010 0.0008 0.0027 Iodine reducing substance (%) 0.0001 or less 0.0001 or less 0.0001 Fe (%) 0.00002 0.00004 0.00004 Cu (%) 0.0001 or less 0.0001 or less 0.0001 or less The JIS-K-1414 barium chloride standard is sufficiently passed by any method.

【0040】実施例4 セレスタイト鉱石の還元焙焼および浸出処理により得ら
れた硫化ストロンチウム溶液(SrS:4.60%)26
02重量部と実施例1と同じ銅板エッチング廃液(Cu
Cl2:22.52%)597重量部とを反応容器に同時
に撹拌しながら混合処理した。この混合による反応は室
温にて系の酸化還元電位を0〜100mVに維持してp
Hを所定の範囲内に保持しながら行ったが、反応終了ま
でH2Sの発生は認められず安全に操作できた。
Example 4 A strontium sulfide solution (SrS: 4.60%) obtained by reducing roasting and leaching treatment of Celestite ore 26
02 parts by weight and the same copper plate etching waste liquid (Cu as in Example 1)
Cl 2 : 22.52%) (597 parts by weight) was mixed into the reaction vessel while stirring at the same time. The reaction by this mixing is performed at room temperature while maintaining the redox potential of the system at 0 to 100 mV.
Although H was maintained within a predetermined range, H 2 S was not generated until the reaction was completed, and safe operation was possible.

【0041】次いで、30分間熟成させた後処理液を炭
酸ストロンチウムでpH6.5に中和して濾過分離した
(反応終了液中のSr収率は96.5%)。分離母液に
は、重金属イオンおよび還元性物質は殆ど検出されなか
ったので、これを濃縮後晶析処理を施し、SrCl2
6H2Oの結晶物を回収した。この結晶物を分析したと
ころ表2の結果が得られた。一方、黒色沈殿物は洗浄後
乾燥して硫化銅粉末として回収し、これを銅製錬原料と
して送ることができた。
Next, the post-treatment liquid which had been aged for 30 minutes was neutralized to pH 6.5 with strontium carbonate and separated by filtration.
(The Sr yield in the reaction completed liquid is 96.5%). Almost no heavy metal ions and reducing substances were detected in the separated mother liquor. Therefore, the concentrated mother liquor was subjected to crystallization treatment after concentration, and SrCl 2
6H 2 O crystals were recovered. When this crystal product was analyzed, the results shown in Table 2 were obtained. On the other hand, the black precipitate was washed and dried to recover as copper sulfide powder, which could be sent as a copper smelting raw material.

【0042】[0042]

【表2】 [Table 2]

【0043】[0043]

【発明の効果】本発明に係る方法によれば、銅板エッチ
ング廃液の処理を図りながら、高純度の塩化バリウムを
製造することができる。特に、Cu2+などの重金属イオ
ンが溶存している限り硫化水素ガスの実質的な発生をみ
ることなく、硫化バリウムと銅板エッチング廃液とを任
意に合理的に反応処理することにより、塩化バリウムの
製造と併行して銅有価成分を回収できることである。こ
のことは、従来、バリウム塩製造工業で、硫化水素ガス
の発生をよぎなくされ、その処理の困難性と多大な費用
を鑑みるとき、本発明に係る方法の工業的意義は誠に大
きなものと言うことができよう。
According to the method of the present invention, high-purity barium chloride can be produced while treating the copper plate etching waste liquid. In particular, as long as heavy metal ions such as Cu 2+ are dissolved, hydrogen sulfide gas is not substantially generated, and barium sulfide and a copper plate etching waste liquid are arbitrarily and rationally reacted to produce barium chloride. It is possible to recover valuable copper components in parallel with manufacturing. This, conventionally, in the barium salt manufacturing industry, in the generation of hydrogen sulfide gas, when considering the difficulty and great cost of the treatment, the industrial significance of the method according to the present invention is said to be of great significance. I can do it.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 宇野 幸光 東京都江東区亀戸9丁目15番1号 日本化 学工業株式会社研究開発本部内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Komitsu Uno 9-15-1, Kameido, Koto-ku, Tokyo Nihon Kagaku Kogyo Co., Ltd.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 アルカリ土類金属硫化物溶液と銅板エッ
チング廃液とを反応させることを特徴とするアルカリ土
類金属塩化物の製造並びに銅有価成分の回収方法。
1. A method for producing an alkaline earth metal chloride and recovering a valuable copper component, which comprises reacting an alkaline earth metal sulfide solution with a copper plate etching waste liquid.
【請求項2】 アルカリ土類金属硫化物溶液と銅板エッ
チング廃液とを反応系にCuが存在する状態で反応させ
た後、固液分離した母液を晶析操作によりアルカリ土類
金属塩化物結晶として、他方、固形物を硫化銅として回
収することを特徴とするアルカリ土類金属塩化物の製造
並びに銅有価成分の回収方法。
2. The alkaline earth metal sulfide solution and the copper plate etching waste liquid are reacted in the presence of Cu in the reaction system, and the mother liquor separated by solid-liquid separation is converted into alkaline earth metal chloride crystals by a crystallization operation. On the other hand, a method for producing an alkaline earth metal chloride and recovering a valuable copper component, which comprises recovering a solid matter as copper sulfide.
【請求項3】 アルカリ土類金属硫化物はバライト鉱ま
たはセレスタイト鉱の還元焙焼物の浸出液である請求項
1または2記載のアルカリ土類金属塩化物の製造並びに
銅有価成分の回収方法。
3. The method for producing an alkaline earth metal chloride and recovering a valuable copper component according to claim 1 or 2, wherein the alkaline earth metal sulfide is a leachate of a reduced roasted product of barite or Celestite ore.
【請求項4】 銅板エッチング廃液はCuCl:0〜5
0g/リットル、CuCl2:30〜300g/リット
ル、遊離HCl:10〜200g/リットル、その他の
成分:0〜30g/リットルの化学組成を有する水溶液
である請求項1または2記載のアルカリ土類金属塩化物
の製造並びに銅有価成分の回収方法。
4. The copper plate etching waste liquid is CuCl: 0 to 5
The alkaline earth metal according to claim 1 or 2, which is an aqueous solution having a chemical composition of 0 g / liter, CuCl 2 : 30 to 300 g / liter, free HCl: 10 to 200 g / liter, and other components: 0 to 30 g / liter. Method for producing chloride and recovering valuable copper components.
JP10087891A 1991-05-02 1991-05-02 Production of alkaline earth metal chloride and method for recovering valuable copper component Pending JPH0625771A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10087891A JPH0625771A (en) 1991-05-02 1991-05-02 Production of alkaline earth metal chloride and method for recovering valuable copper component

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10087891A JPH0625771A (en) 1991-05-02 1991-05-02 Production of alkaline earth metal chloride and method for recovering valuable copper component

Publications (1)

Publication Number Publication Date
JPH0625771A true JPH0625771A (en) 1994-02-01

Family

ID=14285587

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JPH0625771A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003076671A1 (en) * 2002-03-04 2003-09-18 Cabot Corporation Methods to reduce hydrosulphide and arsine emissions during wet ore processing
CN100333912C (en) * 2001-02-06 2007-08-29 奥林巴斯光学工业株式会社 Image forming apparatus
CN103570339A (en) * 2012-07-19 2014-02-12 北大方正集团有限公司 Recycling method of vulcanic ash waste material, sintered lumps, and application of sintered lumps
JP2017514015A (en) * 2014-04-01 2017-06-01 シグマ エンジニアリング アクティエボラーグ Oxidation of copper in copper etching solution by using oxygen and / or air as oxidant

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100333912C (en) * 2001-02-06 2007-08-29 奥林巴斯光学工业株式会社 Image forming apparatus
WO2003076671A1 (en) * 2002-03-04 2003-09-18 Cabot Corporation Methods to reduce hydrosulphide and arsine emissions during wet ore processing
US6800259B2 (en) 2002-03-04 2004-10-05 Cabot Corporation Methods to control H2S and arsine emissions
CN100436614C (en) * 2002-03-04 2008-11-26 卡伯特公司 Methods to reduce hydrosulphide and arsine emissions during wet ore processing
CN103570339A (en) * 2012-07-19 2014-02-12 北大方正集团有限公司 Recycling method of vulcanic ash waste material, sintered lumps, and application of sintered lumps
JP2017514015A (en) * 2014-04-01 2017-06-01 シグマ エンジニアリング アクティエボラーグ Oxidation of copper in copper etching solution by using oxygen and / or air as oxidant

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