JPH0432717B2 - - Google Patents

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Publication number
JPH0432717B2
JPH0432717B2 JP58214812A JP21481283A JPH0432717B2 JP H0432717 B2 JPH0432717 B2 JP H0432717B2 JP 58214812 A JP58214812 A JP 58214812A JP 21481283 A JP21481283 A JP 21481283A JP H0432717 B2 JPH0432717 B2 JP H0432717B2
Authority
JP
Japan
Prior art keywords
sodium
acid
salt
heavy metal
wastewater
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP58214812A
Other languages
Japanese (ja)
Other versions
JPS60106585A (en
Inventor
Masafumi Morya
Kazuo Hosoda
Tomio Imachi
Makoto Takai
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.)
Myoshi Oil and Fat Co Ltd
Original Assignee
Myoshi Oil and Fat 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 Myoshi Oil and Fat Co Ltd filed Critical Myoshi Oil and Fat Co Ltd
Priority to JP21481283A priority Critical patent/JPS60106585A/en
Publication of JPS60106585A publication Critical patent/JPS60106585A/en
Publication of JPH0432717B2 publication Critical patent/JPH0432717B2/ja
Granted legal-status Critical Current

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Description

【発明の詳細な説明】 本発明は、エチレンジアミン四酢酸(以下
EDTAと略記す)とキレート結合している重金
属イオン、たとえば、銅、ニツケル、水銀、マン
ガン、カドミウム、亜鉛、鉛等の重金属イオンを
含む廃水から高分子系金属捕集剤を使用して重金
属イオンを捕集除去する方法に関するものであ
る。
DETAILED DESCRIPTION OF THE INVENTION The present invention provides ethylenediaminetetraacetic acid (hereinafter referred to as
Heavy metal ions such as copper, nickel, mercury, manganese, cadmium, zinc, and lead are extracted using a polymeric metal scavenger from wastewater containing heavy metal ions chelated with EDTA (abbreviated as EDTA). This relates to a method for collecting and removing.

従来よりEDTAと結合している重金属イオン
はEDTAの持つ強いキレート形成能により、そ
の処理は非常に困難であるといわれている。
It has been said that it is extremely difficult to treat heavy metal ions that have been bound to EDTA due to EDTA's strong chelate-forming ability.

今日までEDTAと結合している金属イオンの
処理方法として、第一にEDTAを酸化分解した
後、重金属イオンを中和凝集沈澱方などにより処
理する方法、第二にEDTAと結合した重金属イ
オンを含む廃水のPH値を3以下とし、鉄塩を水中
の重金属イオンの当量あるいは当量より過剰に添
加し、次にPH値を急速に上昇させて重金属イオン
を難溶性の沈澱物として分離除去する方法(特開
昭50−161056)、第三にEDTAと結合した重金属
イオンを含む廃水に少なくとも反応当量の約1.2
倍量のカルシウム化合物を加え、前記重金属がそ
の水酸化物の沈澱を形成するに充分な少なくとも
PH12.6のアルカリ性領域において、前記重金属成
分を不溶性沈澱物として分離除去する方法(特開
昭51−10176)などが知られている。
To date, the methods for treating metal ions bound to EDTA include, firstly, oxidative decomposition of EDTA, and then treatment of heavy metal ions by neutralization, coagulation, and precipitation, and secondly, methods for treating heavy metal ions bound to EDTA. A method in which the PH value of wastewater is set to 3 or less, iron salt is added in an equivalent amount or in excess of the equivalent amount of heavy metal ions in the water, and then the PH value is rapidly increased to separate and remove the heavy metal ions as hardly soluble precipitates ( (Japanese Patent Application Laid-Open No. 161056), and thirdly, the wastewater containing heavy metal ions combined with EDTA should be treated with at least about 1.2 reaction equivalents.
Add twice the amount of calcium compound and add at least enough of the heavy metal to form a precipitate of its hydroxide.
In the alkaline region of pH 12.6, a method is known in which the heavy metal components are separated and removed as insoluble precipitates (Japanese Patent Laid-Open No. 10176/1983).

しかしながら第一の方法では酸化分解を必要と
するため、多量の酸化剤を使用し、さらに処理工
程が多くなる欠点がある。また第二の方法はPHを
3以下にする工程、さらにPHを11以上にする工程
等、工程が多くなり、経済性に欠ける。また第三
の方法は廃水に対して1.2倍量のカルシウム化合
物を加え、さらに水酸化物の沈澱を形成するに充
分な少なくともPH12.6のアルカリ性領域にするた
め、使用する薬剤量が膨大となり不経済である。
さらにこれら第一〜第三の方法では重金属イオン
の除去下限もよくない欠点がある。
However, since the first method requires oxidative decomposition, it has the disadvantage of using a large amount of oxidizing agent and requiring a large number of processing steps. In addition, the second method requires many steps, such as the step of reducing the pH to 3 or less and the step of increasing the pH to 11 or more, and is therefore uneconomical. In the third method, 1.2 times the amount of calcium compound is added to the wastewater to make it at least alkaline at pH 12.6, which is sufficient to form hydroxide precipitates, which results in a huge amount of chemicals being used. It's the economy.
Furthermore, these first to third methods have the drawback that the lower limit of removal of heavy metal ions is not good.

本発明者らは、これらの欠点を解決すべく鋭意
研究を行つたところ、EDTAと結合した重金属
イオンを含む廃水を、官能基としてジチオカルバ
ミン酸またはその塩、ヂチオ酸またはその塩、チ
オールまたはその塩、およびチオ尿素から選ばれ
たる少なくとも一種を有する高分子系金属捕集剤
で処理するか、あるいは上記の高分子系金属捕集
と硫化ソーダ、多硫化ソーダ、水硫化ソーダより
選ばれたる少なくとも一種とを併用して処理する
ことにより、EDTAと結合した重金属イオンを
効率よく、しかも低濃度まで捕集除去できること
を見いだした。硫化ソーダ類を添加すると、それ
を添加しないのに比べて重金属類の捕集率が上昇
すると共に、短時間で効率の良い廃水処理を行う
ことができる。さらに濾過後のスラツジの容量が
小さくなり、その処理が容易になると言う長所が
有る。
The present inventors conducted intensive research to solve these drawbacks and found that wastewater containing heavy metal ions combined with EDTA can be treated with dithiocarbamic acid or its salt, dithioic acid or its salt, thiol or its salt as a functional group. , and thiourea, or the above-mentioned polymeric metal trapping agent and at least one selected from sodium sulfide, sodium polysulfide, and sodium hydrogen sulfide. We have discovered that heavy metal ions bound to EDTA can be efficiently collected and removed down to a low concentration by treatment in combination with EDTA. When soda sulfides are added, the collection rate of heavy metals increases compared to not adding them, and wastewater treatment can be performed efficiently in a short time. Furthermore, there is an advantage that the volume of the sludge after filtration is reduced, making it easier to process.

本発明によればEDTAと結合した重金属イオ
ン含有廃水に、特定の高分子系金属捕集剤をその
まま添加し処理するだけでよく、その後生成した
不溶性沈澱物を固液分離すれば、含有した重金属
イオンは、EDTAと結合したまま捕集除去され
る。したがつて処理工程も簡単であり、経済的に
優れている。
According to the present invention, it is sufficient to simply add a specific polymeric metal scavenger to wastewater containing heavy metal ions combined with EDTA and treat the wastewater, and if the insoluble precipitate formed is then subjected to solid-liquid separation, the heavy metals contained in the wastewater can be treated. Ions are collected and removed while remaining bound to EDTA. Therefore, the treatment process is simple and economically advantageous.

さらにまた、EDTAと結合した重金属イオン
を除去した後、PHを3以下にすることにより、
EDTAを不溶性物質とし、回収することもでき
る利点がある。
Furthermore, after removing heavy metal ions combined with EDTA, by reducing the pH to 3 or less,
It has the advantage that EDTA is an insoluble substance and can be recovered.

本発明の金属捕集方法としては、高分子系金属
捕集剤単独または高分子系金属捕集剤と硫化ソー
ダ、多硫化ソーダ、水硫化ソーダより選ばれたる
少なくとも1種を併用した捕集剤を廃水に添加
し、バツチ法等により処理することができる。こ
れら捕集剤の添加量は廃水中の重金属含有量に依
存するが、重金属含有量の0.3〜1.2倍モル当量好
ましくは0.5〜1.0倍モル当量の捕集剤を添加すれ
ば良い。多硫化ソーダとしては、二硫化ソーダ、
三硫化ソーダ、四硫化ソーダ、五硫化ソーダが挙
げられる。
The metal collecting method of the present invention includes a polymeric metal trapping agent alone or a polymeric metal trapping agent combined with at least one selected from sodium sulfide, sodium polysulfide, and sodium hydrogen sulfide. can be added to wastewater and treated by a batch method or the like. The amount of these scavengers to be added depends on the heavy metal content in the wastewater, but the scavenger may be added in an amount of 0.3 to 1.2 times the molar equivalent, preferably 0.5 to 1.0 times the molar equivalent of the heavy metal content. Sodium polysulfide includes sodium disulfide,
Examples include sodium trisulfide, sodium tetrasulfide, and sodium pentasulfide.

上記硫化ソーダ類を併用する場合には、高分子
系金属捕集剤と硫化ソーダ類との比が重量にて、
各々99:1〜20:80の範囲で用いられが、90:10
〜40:60の範囲が好ましい。
When using the above sodium sulfides together, the ratio of the polymeric metal scavenger to the soda sulfides by weight is
Each is used in the range of 99:1 to 20:80, but 90:10
A range of ~40:60 is preferred.

また捕集剤の添加量を調節する目的か、あるい
は捕集剤の捕集効率をあげる目的で、鉄イオンお
よびアルミニウムイオン水溶液を併用して使用す
ることも可能である。
Further, it is also possible to use an aqueous solution of iron ions and aluminum ions in combination for the purpose of adjusting the amount of the scavenger added or increasing the collection efficiency of the scavenger.

本発明における高分子系金属捕集剤とは、官能
基として、ジチオカルバミン酸またはその塩類、
ジチオ酸またはその塩、チオールまたはその塩お
よびチオ尿素基から成る群より選ばれたる少なく
とも一種を有し、ポリスチレン、ポリアクリル
酸、塩化ビニル、エポキシ樹脂、ポリエチレンイ
ミンより選ばれたる少なくとも一種を主鎖とする
高分子系金属捕集剤であり、常法により製造した
ものを用いることができる。例えば、ポリスチレ
ンを主鎖とする高分子系金属捕集剤としては、そ
の芳香核をクロロメチル化後、モンモニアまたは
ポリアルキレンポアミンを反応し、次いで水酸化
ナトリウムの存在下に二硫化炭素を反応してジチ
オカルバミン酸基を導入した化合物、およびポリ
スチレンをクロロメチル化後、チオ尿素を反応し
てチオール基を導入した化合物、チオール基を導
入した後チオホスゲンを反応し、水酸化ナトリウ
ムで処理してジチオ酸基を導入した化合物が挙げ
られる。またポリアクリル酸を主鎖とする高分子
系金属捕集剤としては、ポリアクリル酸の低級ア
ルコールエステルにチオ尿素を反応して、チオ尿
素基を導入した化合物、ポリアクリル酸の低級ア
ルコールエステルにアンモニアまたはポリアルキ
レンポアミンを反応し、次いで水酸化ナトリウム
の存在下に二硫化炭素を反応してジチオカルバミ
ン酸基を導入した化合物が挙げられる。ポリ塩化
ビニルを主鎖とする高分子系金属捕集剤として
は、ポリ塩化ビニルに水硫化ソーダを反応してチ
オール基を導入した化合物、ポリ塩化ビニルにア
ンモニアまたはポリアルキレンポアミンを反応
し、次いで水酸化ナトリウムの存在下に二硫化炭
素を反応してジチオカルバミン酸基を導入した化
合物が挙げられる。エポキシ樹脂を主鎖とする高
分子系金属捕集剤としては、ポリアルキレンポリ
アミンに活性水素を2ケ残すように水酸化ナトリ
ウムの存在下に二硫化炭素を反応し、次いでビス
エポキシド化合物で架橋したヂチオカルバミン酸
基を有する化合物が挙げられる。ポリエチレンイ
ミン主鎖とする高分子系金属捕集剤としては、ポ
リエチレンイミンに水酸化ナトリウムの存在下、
二硫化炭素を反応して得られる化合物が挙げられ
る。
The polymeric metal scavenger in the present invention includes dithiocarbamic acid or a salt thereof as a functional group,
It has at least one selected from the group consisting of dithioic acid or its salt, thiol or its salt, and thiourea group, and has at least one selected from polystyrene, polyacrylic acid, vinyl chloride, epoxy resin, and polyethyleneimine in its main chain. It is a polymeric metal scavenger, which can be produced by a conventional method. For example, as a polymeric metal scavenger with polystyrene as the main chain, its aromatic nucleus is chloromethylated, then reacted with monmonium or polyalkylenepoamine, and then reacted with carbon disulfide in the presence of sodium hydroxide. A compound in which a dithiocarbamate group is introduced by chloromethylating polystyrene, a compound in which a thiol group is introduced by reacting with thiourea, and a compound in which a thiol group is introduced and then reacted with thiophosgene, and then treated with sodium hydroxide to form a dithiocarbamate. Examples include compounds into which acid groups have been introduced. In addition, as polymeric metal scavengers with polyacrylic acid as the main chain, there are compounds in which thiourea groups are introduced by reacting lower alcohol esters of polyacrylic acid with thiourea, and compounds in which thiourea groups are introduced into lower alcohol esters of polyacrylic acid. Examples include compounds in which dithiocarbamate groups are introduced by reacting ammonia or polyalkylenepoamine and then reacting with carbon disulfide in the presence of sodium hydroxide. Polymeric metal scavengers with polyvinyl chloride as the main chain include compounds in which thiol groups are introduced by reacting polyvinyl chloride with sodium hydrogen sulfide, and compounds in which thiol groups are introduced by reacting polyvinyl chloride with ammonia or polyalkylenepoamine. Examples include compounds in which a dithiocarbamate group is introduced by reacting carbon disulfide in the presence of sodium hydroxide. As a polymeric metal scavenger with an epoxy resin as the main chain, polyalkylene polyamine is reacted with carbon disulfide in the presence of sodium hydroxide so as to leave two active hydrogen atoms, and then cross-linked with a bisepoxide compound. Examples include compounds having a dithiocarbamic acid group. As a polymeric metal scavenger with a polyethyleneimine main chain, polyethyleneimine in the presence of sodium hydroxide,
Examples include compounds obtained by reacting carbon disulfide.

以下実施例によつて具体的に説明するが以下の
実施例によつて限定されるものではない。
The present invention will be specifically explained below using examples, but is not limited to the following examples.

実施例 1 エチレンジアミン四酢酸(2Na)1000ppm、銅
イオン10ppmを含むPH7の水溶液1に、ポリエ
チレンイミンを母体とし、ジチオカルバミン酸基
を官能基として有する金属捕集剤の1%水溶液を
5ml添加し、10分間撹拌処理した。固液分離後、
残存イオン(Cu2+)濃度を測定したところ
0.1ppmであり、除去率は99%であつた。
Example 1 To aqueous solution 1 of pH 7 containing 1000 ppm of ethylenediaminetetraacetic acid (2Na) and 10 ppm of copper ions, 5 ml of a 1% aqueous solution of a metal scavenger having polyethyleneimine as a base and a dithiocarbamate group as a functional group was added. The mixture was stirred for a minute. After solid-liquid separation,
Measurement of residual ion (Cu 2+ ) concentration
It was 0.1 ppm, and the removal rate was 99%.

実施例 2 エチレンジアミン四酢酸(2Na)1%、銅イオ
ン2ppm、ニツケルイオン2ppm、水銀イオン
2ppmを含むPH7.5の水溶液1に、ポリエチレン
イミンにチオ尿素を官能基として結合させた金属
捕集剤の1%水溶液10ml及び3%硫化ソーダ水溶
液2mlを添加し、30分間撹拌処理した。生成した
不溶物を固液分離した後、残存金属イオン濃度を
測定したところ、Cu2+:0.01ppm、Ni2+
0.05ppm、Hg2+:0.005ppmであつた。
Example 2 Ethylenediaminetetraacetic acid (2Na) 1%, copper ion 2ppm, nickel ion 2ppm, mercury ion
10 ml of a 1% aqueous solution of a metal scavenger in which thiourea is bonded to polyethyleneimine as a functional group and 2 ml of a 3% aqueous sodium sulfide solution were added to aqueous solution 1 containing 2 ppm and having a pH of 7.5, and the mixture was stirred for 30 minutes. After solid-liquid separation of the generated insoluble matter, the remaining metal ion concentration was measured; Cu 2+ : 0.01 ppm, Ni 2+ :
0.05ppm, Hg 2+ : 0.005ppm.

実施例 3 エチレンジアミン四酢酸(2Na)5000ppm、
Cd2+3ppm、Zn2+5ppm、Ca500ppm、NaCl2%を
含むPH6.5の水溶液1に、ポリスチレンにジチ
オカルバミン酸基を官能基として有する金属捕集
剤の5%水溶液3mlを添加し、20分間撹拌処理し
た。固液分離後、残存金属イオン濃度を測定した
ところ、Cd2+:0.05ppm、Zn2+:0.05ppmであつ
た。
Example 3 Ethylenediaminetetraacetic acid (2Na) 5000ppm,
To aqueous solution 1 of pH 6.5 containing 3ppm of Cd 2+ , 5ppm of Zn 2+ , 500ppm of Ca, and 2% of NaCl, 3 ml of a 5% aqueous solution of a metal scavenger having polystyrene with a dithiocarbamate group as a functional group was added and stirred for 20 minutes. Processed. After solid-liquid separation, the remaining metal ion concentrations were measured and found to be 0.05 ppm for Cd 2+ and 0.05 ppm for Zn 2+ .

実施例 4 エチレンジアミン四酢酸(2Na)1600ppm、
Cu2+4ppm、Zn2+6ppmを含むPH4.2の水溶液1
に、ポリアクリル酸を主鎖としチオ尿素基を官能
基として有する金属捕集剤の6%水溶液2mlを添
加し、30分間撹拌処理した。固液分離後、残存金
属イオン濃度を測定したところ、Cu2+
0.01ppm、Zn2+:0.04ppmであつた。
Example 4 Ethylenediaminetetraacetic acid (2Na) 1600ppm,
Aqueous solution 1 of PH4.2 containing Cu 2+ 4ppm and Zn 2+ 6ppm
To the mixture, 2 ml of a 6% aqueous solution of a metal scavenger having polyacrylic acid as a main chain and a thiourea group as a functional group was added, and the mixture was stirred for 30 minutes. After solid-liquid separation, the remaining metal ion concentration was measured and found that Cu 2+ :
It was 0.01ppm, Zn 2+ : 0.04ppm.

実施例 5 エチレンジアミン四酢酸(2Na)400ppm、
Pb2+10ppm、Cd2+2ppmを含むPH5.2の水溶液1
に、塩化ビニルにチオール基導入した金属捕集剤
の0.5%水溶液4mlを添加し、10分間撹拌処理し
た。固液分離後、残存金属イオン濃度を測定した
ところ、Pb2+:0.01ppm、Cd2+:0.01ppmであつ
た。
Example 5 Ethylenediaminetetraacetic acid (2Na) 400ppm,
Aqueous solution 1 of PH5.2 containing 10ppm Pb 2+ and 2ppm Cd 2+
4 ml of a 0.5% aqueous solution of a metal scavenger in which a thiol group was introduced into vinyl chloride was added to the mixture, and the mixture was stirred for 10 minutes. After solid-liquid separation, the remaining metal ion concentrations were measured and found to be 0.01 ppm for Pb 2+ and 0.01 ppm for Cd 2+ .

実施例 6 エチレンジアミン四酢酸(2Na)6000ppm、
Ni2+3ppm、Cu2+5ppmを含むPH6.1の水溶液1
に、エポキシ樹脂を主鎖としたジチオ酸基を官能
基として有する金属捕集剤の2%水溶液0.5mlを
添加し、40分間撹拌処理した。固液分離後、残存
金属イオン濃度を測定したところ、Ni2+
0.1ppm、Cu2+:0.01ppmであつた。
Example 6 Ethylenediaminetetraacetic acid (2Na) 6000ppm,
Aqueous solution 1 of PH6.1 containing 3ppm Ni 2+ and 5ppm Cu 2+
To this was added 0.5 ml of a 2% aqueous solution of a metal scavenger having an epoxy resin main chain and a dithioic acid group as a functional group, and the mixture was stirred for 40 minutes. After solid-liquid separation, the remaining metal ion concentration was measured and found that Ni 2+ :
0.1ppm, Cu 2+ : 0.01ppm.

比較例 1 エチレンジアミン四酢酸(2Na)1000ppm、銅
イオン10ppmを含むPH7の水溶液1に、ジメチ
ルジチオカルバミン酸ナトリウム塩の1%水溶液
を5mlを添加し、10分間撹拌処理した。固液分離
後、残存金属イオン(Cu2+)濃度を測定したと
ころ3ppmであり、陰去率は70%であつた。
Comparative Example 1 To aqueous solution 1 of pH 7 containing 1000 ppm of ethylenediaminetetraacetic acid (2Na) and 10 ppm of copper ions, 5 ml of a 1% aqueous solution of sodium dimethyldithiocarbamate was added and stirred for 10 minutes. After solid-liquid separation, the residual metal ion (Cu 2+ ) concentration was measured to be 3 ppm, and the negative removal rate was 70%.

Claims (1)

【特許請求の範囲】 1 官能基として、ジチオカルバミン酸またはそ
の塩、ジチオ酸またはその塩、チオールまたはそ
の塩およびチオ尿素基から成る群より選ばれたる
少なくとも一種を有し、ポリスチレン、ポリアク
リル酸、塩化ビニル、エポキシ樹脂、ポリエチレ
ンイミンより選ばれたる少なくとも一種を主鎖と
する高分子系金属捕集剤を用いて、重金属イオン
と結合したエチレンジアミン四酢酸を含む廃水を
処理することを特徴とする廃水の処理方法。 2 特許請求の範囲第1項に記載の金属捕集剤
と、硫化ソーダ、多硫化ソーダ、水硫化ソーダよ
り選ばれたる少なくとも一種とを併用して、重金
属イオンと結合したエチレンジアミン四酢酸を含
む廃水を処理することを特徴とする廃水の処理方
法。
[Scope of Claims] 1. Has at least one functional group selected from the group consisting of dithiocarbamic acid or its salt, dithioic acid or its salt, thiol or its salt, and thiourea group, and has polystyrene, polyacrylic acid, Wastewater characterized by treating wastewater containing ethylenediaminetetraacetic acid combined with heavy metal ions using a polymeric metal scavenger whose main chain is at least one selected from vinyl chloride, epoxy resin, and polyethyleneimine. processing method. 2 Wastewater containing ethylenediaminetetraacetic acid combined with heavy metal ions by using the metal scavenger according to claim 1 in combination with at least one selected from sodium sulfide, sodium polysulfide, and sodium hydrogen sulfide. A wastewater treatment method characterized by treating.
JP21481283A 1983-11-15 1983-11-15 Treatment of waste water Granted JPS60106585A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP21481283A JPS60106585A (en) 1983-11-15 1983-11-15 Treatment of waste water

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Application Number Priority Date Filing Date Title
JP21481283A JPS60106585A (en) 1983-11-15 1983-11-15 Treatment of waste water

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JPS60106585A JPS60106585A (en) 1985-06-12
JPH0432717B2 true JPH0432717B2 (en) 1992-06-01

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Publication number Priority date Publication date Assignee Title
JPS6265788A (en) * 1985-09-17 1987-03-25 Miyoshi Oil & Fat Co Ltd Method for capturing metal
US4789475A (en) * 1987-06-23 1988-12-06 Environmental Concerns, Inc. Water purification material, process therefor, and device for the removal of heavy metal toxins
JPH0625655A (en) * 1992-03-09 1994-02-01 Showa Kk Method for regeneration of brine and equipment therefor
JP3172728B2 (en) * 1993-10-13 2001-06-04 栗田工業株式会社 Method for removing divalent manganese ions
DE102004032255A1 (en) * 2004-07-03 2006-01-19 Bergthaller, Peter, Dr. Method for removing dissolved heavy metals, transition metals and/or metalloids from aqueous solution comprises contacting the solution with a water-insoluble hydrophilic polymer complex structure unit present in particle form
JP6884986B2 (en) * 2015-08-07 2021-06-09 東ソー株式会社 How to purify zinc-containing aqueous solution
JP6862659B2 (en) * 2016-03-01 2021-04-21 東ソー株式会社 How to purify nickel-containing aqueous solution
JP7031176B2 (en) * 2016-09-08 2022-03-08 東ソー株式会社 Purifying agent for nickel-containing aqueous solution and purification method for nickel-containing aqueous solution
JP2018043232A (en) * 2016-09-08 2018-03-22 東ソー株式会社 Purification agent for mercury-containing aqueous solution, and method of purifying mercury-containing aqueous solution

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51111756A (en) * 1975-03-26 1976-10-02 Oriental Shashin Kogyo Kk Photographic waste liquid treating method

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS51111756A (en) * 1975-03-26 1976-10-02 Oriental Shashin Kogyo Kk Photographic waste liquid treating method

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