JPS5915710B2 - Method for removing heavy metals from aqueous solution - Google Patents

Method for removing heavy metals from aqueous solution

Info

Publication number
JPS5915710B2
JPS5915710B2 JP51095035A JP9503576A JPS5915710B2 JP S5915710 B2 JPS5915710 B2 JP S5915710B2 JP 51095035 A JP51095035 A JP 51095035A JP 9503576 A JP9503576 A JP 9503576A JP S5915710 B2 JPS5915710 B2 JP S5915710B2
Authority
JP
Japan
Prior art keywords
aqueous solution
resin
heavy metals
heavy metal
polyalkylene polyamine
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
JP51095035A
Other languages
Japanese (ja)
Other versions
JPS5320661A (en
Inventor
孝治 板垣
義雄 梅沢
明弘 志村
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.)
Mitsubishi Kasei Corp
Original Assignee
Mitsubishi Kasei Corp
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 Mitsubishi Kasei Corp filed Critical Mitsubishi Kasei Corp
Priority to JP51095035A priority Critical patent/JPS5915710B2/en
Publication of JPS5320661A publication Critical patent/JPS5320661A/en
Publication of JPS5915710B2 publication Critical patent/JPS5915710B2/en
Expired legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Removal Of Specific Substances (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Treatment Of Water By Ion Exchange (AREA)

Description

【発明の詳細な説明】 本発明は重金属イオンを含む水溶液をポリアルキレンポ
リアミン型のキレート形成基を有する樹脂で処理して該
水溶液より、重金属を除去する方法に関するものである
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing heavy metals from an aqueous solution containing heavy metal ions by treating the aqueous solution with a resin having a polyalkylene polyamine type chelate forming group.

詳しくは、ポリアルキレンポリアミン型のキレート形成
基を有する樹脂(以下ポリアルキレンポリアミン型キレ
ート樹脂と記す。
Specifically, the resin has a polyalkylene polyamine type chelate forming group (hereinafter referred to as polyalkylene polyamine type chelate resin).

)で重金属イオンを含む水溶液を処理する際に、NaC
l 、CaC12、Na2 SO4等のアルカリ金属塩
、アルカリ土類金属塩な、該水溶液に存在させることに
より、樹脂の金属吸着容量を増加させる方法に関するも
のである。
) when treating aqueous solutions containing heavy metal ions, NaC
The present invention relates to a method for increasing the metal adsorption capacity of a resin by allowing an alkali metal salt or alkaline earth metal salt such as 1, CaC12, Na2SO4, etc. to be present in the aqueous solution.

最近、公害問題、資源の回収に関係して、鉱山や工場廃
水中の重金属の捕捉の問題が重視されており、この対策
として各種の金属吸着剤が研究開発されている。
Recently, in connection with pollution problems and resource recovery, the problem of capturing heavy metals in mine and factory wastewater has been emphasized, and various metal adsorbents have been researched and developed as a countermeasure.

これらの金属吸着剤は、活性炭或いはシリカゲル等の担
体にジチゾン、2−メルカプトベンゾチアゾール等のい
わゆるキレート剤を担持させたものや、合成樹脂に各種
のキレート形成基を固定させたいわゆるキレート樹脂と
称せられるものであるが、重金属を吸着した吸着剤の再
生の容易性、即ち、(り返し使用の可能性或いは製造の
難易性等の面でそれぞれ一長一短がある。
These metal adsorbents include those in which so-called chelating agents such as dithizone and 2-mercaptobenzothiazole are supported on carriers such as activated carbon or silica gel, and so-called chelate resins in which various chelate-forming groups are immobilized on synthetic resins. However, each has advantages and disadvantages in terms of the ease of regenerating the adsorbent that has adsorbed heavy metals, that is, the possibility of repeated use, and the difficulty of manufacturing.

これらのうち、ポリアルキレンポリアミン型キレート樹
脂は、塩酸、硫酸等の酸水溶液で処理することによって
容易に再生できるので、(り返し使用が可能であること
、比較的安価、容易に製造できること、等から実用上優
れた吸着剤である。
Among these, polyalkylene polyamine type chelate resins can be easily regenerated by treatment with an aqueous acid solution such as hydrochloric acid or sulfuric acid (reusable, relatively inexpensive, easy to manufacture, etc.). Therefore, it is an excellent adsorbent in practical use.

本発明者等は、ポリアルキレンポリアミン型キレート樹
脂による重金属含有水溶液の処理法を検討している間に
、ポリアルキレンポリアミン型のキレート樹脂で重金属
含有水溶液を処理する際に、NaC1,、CaCl2、
Ca S 04等のアルカリ金属塩、アルカリ土類金属
塩を、重金属含有水溶液中に共存させることにより、樹
脂の金属吸着容量が増大するという新事実を見出して本
発明に到達した。
While investigating a method for treating a heavy metal-containing aqueous solution using a polyalkylene polyamine type chelate resin, the present inventors found that when treating a heavy metal-containing aqueous solution with a polyalkylene polyamine type chelate resin, NaCl, CaCl2,
The present invention was achieved by discovering a new fact that the metal adsorption capacity of a resin is increased by coexisting an alkali metal salt or alkaline earth metal salt such as Ca S 04 in an aqueous solution containing heavy metals.

本発明のポリアルキレンポリアミン型キレート樹脂には
、例えば次のような物が含まれる。
The polyalkylene polyamine type chelate resin of the present invention includes, for example, the following.

即ち、ポリアルキレンポリアミンをエピハロヒドリン又
はアルキレンジブロマイドと反応させて得られる架橋結
合を有する樹脂や、スチレンとジビニルベンゼンの架橋
共重合物の如き芳香環を有する架橋共重合体をメチルク
ロロメチルエーテル等でハロメチル化した後、更にポリ
アルキレンポリアミンを反応させて得られる樹脂等であ
る。
That is, a resin having a crosslinked bond obtained by reacting a polyalkylene polyamine with epihalohydrin or alkylene dibromide, or a crosslinked copolymer having an aromatic ring, such as a crosslinked copolymer of styrene and divinylbenzene, is reacted with methyl chloromethyl ether or the like. These are resins obtained by further reacting polyalkylene polyamine after halomethylation.

本発明で処理される重金属イオンとしては、亜鉛、カド
ミウム、水銀、銅及びマンガン等の重金属のイオンが掲
げられる。
Examples of the heavy metal ions treated in the present invention include ions of heavy metals such as zinc, cadmium, mercury, copper, and manganese.

また、本発明で重金属含有水溶液をポリアルキレンポリ
アミン型のキレート樹脂で処理する際に、重金属含有水
溶液中に共存させる塩類はNa、K、Ca、Mg等のア
ルカリ金属、アルカリ土類金属の塩酸塩、硫酸塩、硝酸
塩等であり、共存させる量は、共存させる塩及び対象重
金属によっても異なるが、10ppm以上、好ましくは
40ppm以上である。
In addition, in the present invention, when a heavy metal-containing aqueous solution is treated with a polyalkylene polyamine type chelate resin, the salts coexisting in the heavy metal-containing aqueous solution are hydrochlorides of alkali metals such as Na, K, Ca, Mg, and alkaline earth metals. , sulfates, nitrates, etc., and the amount of coexisting salts varies depending on the salts coexisting and the target heavy metal, but is 10 ppm or more, preferably 40 ppm or more.

これらの塩類を共存させることにより、樹脂の金属吸着
容量が増大する理由は目下のところ不明であるが、何ら
かの作用でポリアルキレンポリアミン型キレート樹脂の
キレート形成反応速度を増大している為と推察される。
The reason why the metal adsorption capacity of the resin increases due to the coexistence of these salts is currently unknown, but it is presumed that the chelate formation reaction rate of the polyalkylene polyamine type chelate resin increases due to some effect. Ru.

重金属含有水溶液の処理法は、キレート樹脂をカラムに
充填してこれに重金属含有水溶液を通液する方法や、重
金属含有水溶液と樹脂を攪拌混合接触させた後、傾斜或
いは濾過等で樹脂と液を分離させる方法等、通常のイオ
ン交換単位操作で採用される方法が適用可能である。
Treatment methods for heavy metal-containing aqueous solutions include filling a column with chelate resin and passing the heavy metal-containing aqueous solution through the column, or stirring and mixing the heavy metal-containing aqueous solution and the resin, and then separating the resin and liquid by decanting or filtration. Methods employed in normal ion exchange unit operations, such as separation methods, are applicable.

カラムへの通液方法は特に限定されることなく通常の方
法で行うことができ、上向流方式あるいは下向流方式等
適宜、任意に決定することができる。
The method for passing the liquid through the column is not particularly limited, and can be carried out by a conventional method, and can be arbitrarily determined as appropriate, such as an upward flow method or a downward flow method.

被処理液のpHは通常2〜12、好ましくは3.5〜7
に調整する。
The pH of the liquid to be treated is usually 2 to 12, preferably 3.5 to 7.
Adjust to.

pH値が小さ過ぎると樹脂の金属吸着能が低下し、逆に
pH値が太き過ぎると金属水酸化物が析出し、操作に支
障をきたす場合がある。
If the pH value is too low, the metal adsorption ability of the resin will decrease, and if the pH value is too high, metal hydroxides will precipitate, which may impede the operation.

重金属を吸着した樹脂は1〜6規定の硫酸等の酸水溶液
で処理することにより、吸着されていた重金属を酸の塩
として容易に回収することができる。
By treating the resin that has adsorbed heavy metals with an aqueous acid solution such as 1 to 6 N sulfuric acid, the adsorbed heavy metals can be easily recovered as acid salts.

酸水溶液で処理した樹脂は、水洗を充分に施した後、更
に1〜6規定のNaOHやKOH等のアルカリで処理し
て、樹脂を遊離形にした後、再度水洗し、再び重金属除
去に使用することができる。
The resin treated with an acid aqueous solution is thoroughly washed with water, and then further treated with an alkali such as 1 to 6N NaOH or KOH to make the resin into a free form, washed with water again, and used again to remove heavy metals. can do.

次に実施例により本発明を具体的に説明するが、本発明
はその要旨を超えない限り以下の実施例に限定されるも
のではない。
EXAMPLES Next, the present invention will be specifically explained with reference to Examples, but the present invention is not limited to the following Examples unless it exceeds the gist thereof.

実施例 1 スチレン系ポリエチレンポリイミン型キレート樹脂CR
−20(三菱化成工業株式会社製、商品名)の遊離形の
樹脂100m1を直径15mmのガラスカラムに充填し
、表に示した組成の液を空間速度10/hrの流速で下
降流で通液した。
Example 1 Styrenic polyethylene polyimine type chelate resin CR
A glass column with a diameter of 15 mm was filled with 100 ml of free resin -20 (manufactured by Mitsubishi Chemical Industries, Ltd., trade name), and a liquid having the composition shown in the table was passed in a downward flow at a space velocity of 10/hr. did.

尚この時、被処理液及び樹脂塔の温度は18℃に保持し
た。
At this time, the temperatures of the liquid to be treated and the resin tower were maintained at 18°C.

樹脂塔より流出してくる液中のCu+Eの濃度がlpp
mになる迄の通液量及び樹脂の貫流交換容量を求めた。
The concentration of Cu+E in the liquid flowing out from the resin tower is lpp
The amount of liquid passed and the through-flow exchange capacity of the resin until it reached m were determined.

結果は次表のとおりであった。CaCl2が存在する場
合のCa廿の貫流交換容量は犬であった。
The results are shown in the table below. The through-flow exchange capacity of Ca 2 in the presence of CaCl 2 was dog.

実施例 2 ダイヤイオンCR−20の遊離形の樹脂100m1を直
径15mmのガラスカラムに充填し、表に示した組成の
液を空間速度10 /hrの流速で下降流で通液した。
Example 2 A glass column with a diameter of 15 mm was filled with 100 ml of Diaion CR-20 free resin, and a liquid having the composition shown in the table was passed through the column in a downward flow at a space velocity of 10/hr.

尚、この時被処理液及び樹脂塔の温度は18℃に保持し
た。
At this time, the temperatures of the liquid to be treated and the resin tower were maintained at 18°C.

樹脂塔より流出して(る液中のCu+の濃度が1 pp
mになる迄の通液量及び樹脂の貫流交換容量を求めた。
The concentration of Cu+ in the liquid flowing out from the resin tower is 1 pp
The amount of liquid passed and the through-flow exchange capacity of the resin until it reached m were determined.

結果は次表のとおりである。The results are shown in the table below.

実施例 3 処理液の組成を変えた他は、実施例1と同様な′試験を
おこない、次の表に記した結果を得た。
Example 3 The same test as in Example 1 was conducted except that the composition of the treatment liquid was changed, and the results shown in the following table were obtained.

硫酸カルシウムが共存することにより、樹脂のCu升貫
流交換容量が増加した。
The coexistence of calcium sulfate increased the Cu cubic cross-flow exchange capacity of the resin.

実施例 4 処理液の組成を変え、又終点なZn+t’−1ppmと
した他は実施例1と同様な試験をおこない、次の表に記
した結果を得た。
Example 4 The same test as in Example 1 was conducted except that the composition of the treatment solution was changed and the end point was set at Zn+t'-1 ppm, and the results shown in the following table were obtained.

塩化カルシウムが共存することにより、樹脂のZn+貫
流交換容量が増加した。
The coexistence of calcium chloride increased the Zn+ flow exchange capacity of the resin.

Claims (1)

【特許請求の範囲】[Claims] 1 重金属イオンを含有する水溶液を遊離型のポリアル
キレンポリアミン型キレート樹脂で処理して、水溶液中
の重金属イオンを除去するに当り、該水溶液中にアルカ
リ金属塩および、またはアルカリ土類金属塩を存在させ
ることを特徴とする水溶液中の重金属イオンの除去方法
1 When treating an aqueous solution containing heavy metal ions with a free polyalkylene polyamine type chelate resin to remove heavy metal ions from the aqueous solution, the presence of alkali metal salts and/or alkaline earth metal salts in the aqueous solution A method for removing heavy metal ions in an aqueous solution, the method comprising:
JP51095035A 1976-08-10 1976-08-10 Method for removing heavy metals from aqueous solution Expired JPS5915710B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51095035A JPS5915710B2 (en) 1976-08-10 1976-08-10 Method for removing heavy metals from aqueous solution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51095035A JPS5915710B2 (en) 1976-08-10 1976-08-10 Method for removing heavy metals from aqueous solution

Publications (2)

Publication Number Publication Date
JPS5320661A JPS5320661A (en) 1978-02-25
JPS5915710B2 true JPS5915710B2 (en) 1984-04-11

Family

ID=14126819

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51095035A Expired JPS5915710B2 (en) 1976-08-10 1976-08-10 Method for removing heavy metals from aqueous solution

Country Status (1)

Country Link
JP (1) JPS5915710B2 (en)

Also Published As

Publication number Publication date
JPS5320661A (en) 1978-02-25

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