JPH07213897A - Polymer heavy metal collecting agent, alkali metal dithiocarbramate polymer and their production - Google Patents

Polymer heavy metal collecting agent, alkali metal dithiocarbramate polymer and their production

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Publication number
JPH07213897A
JPH07213897A JP6025879A JP2587994A JPH07213897A JP H07213897 A JPH07213897 A JP H07213897A JP 6025879 A JP6025879 A JP 6025879A JP 2587994 A JP2587994 A JP 2587994A JP H07213897 A JPH07213897 A JP H07213897A
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JP
Japan
Prior art keywords
polymer
heavy metal
carbons
formula
degree
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.)
Granted
Application number
JP6025879A
Other languages
Japanese (ja)
Other versions
JP3264348B2 (en
Inventor
Tadashi Kato
加藤  正
Tadao Endo
忠雄 遠藤
Ryuichi Mukai
隆一 向井
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.)
Nitto Boseki Co Ltd
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Nitto Boseki Co Ltd
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Publication date
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Priority to JP02587994A priority Critical patent/JP3264348B2/en
Publication of JPH07213897A publication Critical patent/JPH07213897A/en
Application granted granted Critical
Publication of JP3264348B2 publication Critical patent/JP3264348B2/en
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Expired - Fee Related legal-status Critical Current

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Abstract

PURPOSE:To efficiently remove heavy metal ions by using such a specified polyallylamine polymer as a heavy metal collecting agent that a specified ratio of the total amt. of primary and secondary amino groups (NH) is changed into alkali metal dithiocarbamate. CONSTITUTION:This collecting agent contains such a polymer of polyallylamine polymer expressed by formula I or formula II that 70-100% of total of the primary and secondary amino groups (NH) of the polymer are changed into alkali metal dithiocarbamate expressed by N-C(=S)-SM wherein M is Li, Na, or K. In formula I, R<2> is a 1-6C alkyl group or a 5-7C cycloalkyl group, (m) is the polymn. degree, (j) is 0<=j<=1. In formula II, R<1> is H, a 1-6C alkyl group or a 5-7C cycloalkyl group, R<2> is H or methyl, (m) is the polymn. degree and (j) is 0<=j<=1. The polymer collecting agent for heavy metals has excellent sedimentation property of the produced collecting agent-heavy metal complex and has good removing performance for heavy metal ions. Even when an amt. of the collecting agent more than the equiv. of the heavy metal ions is used, the collecting effect is neary unchanged.

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、高分子重金属捕集剤、
ジチオカルバミン酸アルカリ金属塩化重合体、及びそれ
らの製造方法に関する。更に詳しくは、重金属イオンの
除去能がよく、かつ、形成した金属錯体の沈降分離性に
優れた高分子重金属捕集剤、ジチオカルバミン酸アルカ
リ金属塩化重合体、及びそれらの製造方法に関する。
TECHNICAL FIELD The present invention relates to a polymer heavy metal scavenger,
TECHNICAL FIELD The present invention relates to an alkali metal dithiocarbamate chlorinated polymer and a method for producing the same. More specifically, the present invention relates to a high molecular weight heavy metal scavenger, an alkali metal dithiocarbamate chlorinated polymer, which has a good ability to remove heavy metal ions and an excellent sedimentation / separation property of a formed metal complex, and a method for producing them.

【0002】[0002]

【従来の技術】重金属イオンは強い毒性を有するため、
メッキ工場の廃水処理やゴミ焼却場の廃水処理等には、
重金属イオンの効率的な除去方法が要求される。従来、
重金属イオンを含む廃水の処理方法としては、中和凝集
沈殿法、硫化ソーダ法、キレート樹脂による吸着法及び
高分子重金属捕集剤による方法等が知られている(ファ
インケミカル、1985年8月1日号、16頁)。
2. Description of the Related Art Heavy metal ions are highly toxic
For wastewater treatment at plating factories and wastewater treatment at garbage incinerators, etc.
An efficient method for removing heavy metal ions is required. Conventionally,
As a method for treating wastewater containing heavy metal ions, a neutralization coagulation sedimentation method, a sodium sulfide method, an adsorption method with a chelate resin, a method with a high molecular weight heavy metal scavenger, etc. are known (Fine Chemical, August 1, 1985). No., p. 16).

【0003】中和凝集沈殿法はランニングコストが安
い。しかし、生成する不溶性の金属水酸化物がアルカリ
側では安定であるが、酸性側で再溶出するという欠点が
ある。また、硫化ソーダ法は、硫化水素を発生するた
め、二次公害の問題がある。一方、キレート樹脂による
吸着法は、有機物も吸着するため、重金属イオンの捕集
効率の低下が起こる。
The neutralization coagulation sedimentation method has a low running cost. However, although the insoluble metal hydroxide produced is stable on the alkaline side, it has the drawback of being re-eluted on the acidic side. Further, the sodium sulfide method has a problem of secondary pollution because it produces hydrogen sulfide. On the other hand, in the adsorption method using a chelate resin, since organic substances are also adsorbed, the efficiency of collecting heavy metal ions is reduced.

【0004】これに対し、高分子重金属捕集剤による方
法は、酸性側で再溶出せず、二次公害がなく、かつ、有
機物との吸着もない。また、処理操作も簡単である(特
開昭60−193585)。そのため、優れた処理効果
が認められる(ファインケミカル、1985年8月1日
号、16頁)。この高分子重金属捕集剤としては、ポリ
エチレンイミンのジチオカルバミン酸ナトリウム化重合
体、ポリビニルアミンのジチオカルバミン酸ナトリウム
化重合体、セルロースキサントゲン酸ナトリウム、ポリ
グルタミン酸ナトリウム等が知られている。
On the other hand, the method using a polymer heavy metal scavenger does not cause re-elution on the acidic side, does not cause secondary pollution, and does not adsorb with organic substances. Also, the processing operation is simple (Japanese Patent Laid-Open No. 60-193585). Therefore, an excellent treatment effect is recognized (Fine Chemical, August 1, 1985, p. 16). Known examples of the heavy metal heavy metal scavenger include polyethyleneimine sodium dithiocarbamate polymer, polyvinylamine sodium dithiocarbamate polymer, sodium cellulose xanthate, and sodium polyglutamate.

【0005】これら高分子重金属捕集剤の中で、ポリエ
チレンイミンのジチオカルバミン酸ナトリウム化重合体
が、製造しやすいので実用的に使用されている。しか
し、ポリエチレンイミンのジチオカルバミン酸ナトリウ
ム化重合体にはいくつかの問題がある。すなわち、この
重合体は、重金属イオンとの反応が不十分なため、重金
属イオンの除去能が悪い。また、形成する金属との錯体
の沈降分離性が良くないため,重金属イオンの除去に長
い時間を必要とする。更に、通常、重金属の除去には存
在する重金属イオンに比べやや過剰当量の重合体を使用
するが、過剰にこの重合体を使用すると、形成した沈殿
が溶け出して再分散がおこる。そのため、沈降分離性が
ますます悪くなる。その結果、重金属イオンの除去が不
十分で、しかも、時間がかかる。
Among these high molecular weight heavy metal scavengers, a sodium dithiocarbamate polymer of polyethyleneimine is practically used because it is easy to produce. However, the sodium dithiocarbamate polymer of polyethyleneimine has some problems. That is, this polymer has a poor ability to remove heavy metal ions because of insufficient reaction with heavy metal ions. In addition, since the complex formed with the metal is not well precipitated and separated, it takes a long time to remove heavy metal ions. Further, usually, a slight excess of the amount of the polymer is used for the removal of the heavy metal as compared with the heavy metal ions present. However, if this polymer is used in an excessive amount, the formed precipitate is dissolved and redispersion occurs. Therefore, the sedimentation and separability becomes worse. As a result, the removal of heavy metal ions is insufficient and it takes time.

【0006】[0006]

【発明が解決しようとする課題】本発明が解決しようと
する課題は、形成した金属錯体の沈降分離性に優れ、か
つ、重金属イオンの除去能がよい高分子重金属捕集剤、
ジチオカルバミン酸アルカリ金属化重合体、及びそれら
の製造方法を提供することである。特に、存在する重金
属イオンに比べやや過剰の捕集剤を使用しても、重金属
イオンの除去能が低下せず、再分散がおこらず、かつ、
沈降分離性に優れた高分子重金属捕集剤、ジチオカルバ
ミン酸アルカリ金属化重合体、及びそれらの製造方法を
提供することである。
The problem to be solved by the present invention is to provide a polymer heavy metal scavenger which is excellent in the sedimentation / separation property of the formed metal complex and has a good ability to remove heavy metal ions.
An object is to provide an alkali metal dithiocarbamate polymer and a method for producing the same. In particular, even when using a slight excess of the scavenger compared to the existing heavy metal ions, the ability to remove heavy metal ions does not decrease, redispersion does not occur, and
It is an object of the present invention to provide a high molecular weight heavy metal scavenger excellent in sedimentation / separation property, an alkali metal dithiocarbamate polymer, and a method for producing the same.

【0007】[0007]

【課題を解決するための手段】本発明者らは、高分子重
金属捕集剤及びその製造方法について鋭意研究を重ね
た。その結果、驚くべきことに、ある種のポリアリルア
ミン系重合体の、第1級及び第2級アミノ基(NH)の
総和の70−100%が、ジチオカルバミン酸アルカリ
金属塩化(N−C(=S)−SM、ただし、Mはアルカ
リ金属を示す)された重合体を、重金属捕集剤として用
いると、重金属イオンを効率良く除去できることを見い
だした。本発明は、かかる知見により達成できたもので
ある。
[Means for Solving the Problems] The inventors of the present invention have conducted extensive studies on a polymeric heavy metal scavenger and a method for producing the same. As a result, surprisingly, 70 to 100% of the total amount of primary and secondary amino groups (NH) of a certain polyallylamine-based polymer is dithiocarbamate alkali metal chloride (NC (= It was found that heavy metal ions can be efficiently removed by using a polymer obtained by S) -SM, where M represents an alkali metal) as a heavy metal scavenger. The present invention has been achieved by such knowledge.

【0008】本発明の高分子重金属捕集剤は、一般式The polymeric heavy metal scavenger of the present invention has the general formula

【化13】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、mは重合度を示し、jは
0≦j≦1を示す)又は一般式
[Chemical 13] (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of m, m represents the degree of polymerization, and j represents 0 ≦ j ≦ 1) or the general formula

【化14】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、R2 は水素、メチ
ルより選ばれ、mは重合度を示し、jは0<j≦1を示
す)で表されるポリアリルアミン系重合体において、第
1級及び第2級アミノ基(NH)の総和の70−100
%が、ジチオカルバミン酸アルカリ金属塩化(N−C
(=S)−SM、ただし、MはLi、Na、Kのアルカ
リ金属から選ばれる)された重合体(以下、本発明重合
体と記載することもある)を含むことに特徴がある。す
なわち、本発明重合体は、ポリアリルアミン系重合体に
組み込まれた単量体を単位として、70−100モル%
N−ジチオカルバミン酸アルカリ金属塩化されたもので
ある。
[Chemical 14] (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, R 2 is selected from hydrogen and methyl, m is the degree of polymerization, and j is 0 < In the polyallylamine-based polymer represented by j ≦ 1), the total of primary and secondary amino groups (NH) is 70-100.
% Is an alkali metal dithiocarbamate chloride (NC)
(= S) -SM, where M is a polymer selected from alkali metals such as Li, Na, and K) (hereinafter sometimes referred to as the polymer of the present invention). That is, the polymer of the present invention is 70-100 mol% based on the monomer incorporated in the polyallylamine polymer.
N-dithiocarbamate alkali metal chloride.

【0009】本発明高分子重金属捕集剤又は本発明重合
体は、一般式
The polymer heavy metal scavenger of the present invention or the polymer of the present invention has the general formula

【化15】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、mは重合度を示し、jは
0≦j≦1を示す)又は一般式
[Chemical 15] (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of m, m represents the degree of polymerization, and j represents 0 ≦ j ≦ 1) or the general formula

【化16】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、R2 は水素、メチ
ルより選ばれ、mは重合度を示し、jは0<j≦1を示
す)で表されるポリアリルアミン系重合体を出発原料と
して合成できる。
[Chemical 16] (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, R 2 is selected from hydrogen and methyl, m is the degree of polymerization, and j is 0 < A polyallylamine-based polymer represented by j ≦ 1) can be synthesized as a starting material.

【0010】通常、原料のポリアリルアミン系重合体の
塩は、1又は2種類の適当なアリルアミン系単量体の塩
をラジカル重合させる既知の方法で製造できる。原料の
フリーのポリアリルアミン系重合体は、ポリアリルアミ
ン系重合体の塩を水酸化ナトリウム等のアルカリで中和
した後、透析処理で生成する塩を除去して入手すること
ができる。例えば、原料のポリアリルアミン系重合体及
びその塩は、特公平2−14364、特公平2−056
361、特公平2−052362、特公昭63−043
402、特公平2−056365、特公平2−0570
84、特公平4−041686及び特開昭63−286
405に記載の方法により製造できる。また、日東紡績
(株)より市販されているものを用いても良い。塩は、
特に限定されないが、塩酸塩、リン酸塩又は酢酸塩等が
使用可能である。
Usually, the salt of the raw material polyallylamine-based polymer can be produced by a known method in which a salt of one or two suitable allylamine-based monomers is radically polymerized. The free polyallylamine-based polymer as a raw material can be obtained by neutralizing the salt of the polyallylamine-based polymer with an alkali such as sodium hydroxide and then removing the salt produced by the dialysis treatment. For example, starting polyallylamine polymers and salts thereof are disclosed in Japanese Patent Publication No. 2-14364 and Japanese Patent Publication No. 2-056.
361, Japanese Patent Publication No. 2-052362, Japanese Patent Publication No. 63-043
402, Japanese Patent Publication 2-056365, Japanese Patent Publication 2-0570
84, JP-B-4-041686 and JP-A-63-286.
It can be manufactured by the method described in 405. Alternatively, a commercially available product from Nitto Boseki Co., Ltd. may be used. Salt is
Although not particularly limited, hydrochloride, phosphate, acetate or the like can be used.

【0011】本発明の高分子重金属捕集剤又は本発明重
合体は,原料のポリアリルアミン系重合体又はその塩
を、二硫化炭素(CS2 )とアルカリの存在下、N−ジ
チオカルバミン酸アルカリ金属塩化(N−C(=S)−
SM、ただし、MはLi、Na、Kのアルカリ金属より
選ばれる)させて製造できる。その製造方法は、第1級
又は第2級アミノ基が、アルカリ存在下、二硫化炭素と
反応して、N−ジチオカルバミン酸アルカリ金属塩化さ
れることを応用している。
The heavy metal heavy metal scavenger of the present invention or the polymer of the present invention is obtained by adding the polyallylamine polymer or its salt as a raw material to an alkali metal N-dithiocarbamate in the presence of carbon disulfide (CS 2 ) and an alkali. Chloride (N-C (= S)-
SM, provided that M is selected from the alkali metals Li, Na and K). The production method applies that the primary or secondary amino group reacts with carbon disulfide in the presence of an alkali to form an N-dithiocarbamic acid alkali metal salt.

【化17】 ただし、Xはアルキル、Yは水素、アルキルより選ばれ
る。
[Chemical 17] However, X is selected from alkyl and Y is selected from hydrogen and alkyl.

【0012】本発明の製造方法では、原料のポリアリル
アミン系重合体を、適当な溶媒で溶解または懸濁して反
応させる。その溶媒は、原料のアルカリの溶解性から、
水が好ましい。また、溶媒の量は、特に制限はないが、
通常、原料のポリアリルアミン系重合体が5−70重量
%、好ましくは10−50重量%になるような濃度範囲
で使用する。原料として、ポリアリルアミン系重合体の
塩を用いるときは、更に、高濃度で使用できる。
In the production method of the present invention, the raw material polyallylamine-based polymer is dissolved or suspended in a suitable solvent and reacted. The solvent is the solubility of the raw material alkali,
Water is preferred. The amount of solvent is not particularly limited,
Usually, it is used in a concentration range such that the starting polyallylamine polymer is 5-70% by weight, preferably 10-50% by weight. When a salt of a polyallylamine polymer is used as a raw material, it can be used at a higher concentration.

【0013】二硫化炭素の量は、原料のポリアリルアミ
ン系重合体に組み込まれた単量体を単位として、通常7
0−1000モル%、好ましくは70−120モル%、
より好ましくは80−110モル%使用する。二硫化炭
素の量は、生成する高分子重金属捕集剤のN−ジチオカ
ルバミン酸アルカリ金属塩化(N−C(=S)−SM、
ただし、MはLi、Na、Kのアルカリ金属より選ばれ
る)される割合に影響する。二硫化炭素の量が少ない
と、N−ジチオカルバミン酸アルカリ金属塩化される割
合の少ない高分子重金属捕集剤が生成する。多すぎる
と、アミノ基が実質上100%、N−ジチオカルバミン
酸アルカリ金属塩化できるが、二硫化炭素が無駄である
と同時に後処理がやりにくい。ポリアリルアミン系重合
体のアミノ基が実質上100%N−ジチオカルバミン酸
アルカリ金属塩化された高分子重金属捕集剤を、製造す
る場合、二硫化炭素は、原料のポリアリルアミン系重合
体に組み込まれた単量体を単位として、通常100−1
20モル%、好ましくは100−110モル%使用す
る。
The amount of carbon disulfide is usually 7 based on the monomer incorporated in the raw material polyallylamine polymer.
0-1000 mol%, preferably 70-120 mol%,
More preferably, 80-110 mol% is used. The amount of carbon disulfide is determined by using a polymer heavy metal scavenger N-dithiocarbamate alkali metal chloride (N-C (= S) -SM,
However, M affects the ratio of Li, Na, and K selected from alkali metals. When the amount of carbon disulfide is small, a polymer heavy metal scavenger with a low proportion of alkali metal N-dithiocarbamate is formed. If the amount is too large, substantially 100% of amino groups can be chlorinated by alkali metal N-dithiocarbamate, but carbon disulfide is wasted and at the same time post-treatment is difficult. When producing a high molecular weight heavy metal scavenger in which the amino group of the polyallylamine-based polymer is substantially 100% alkali metal N-dithiocarbamate, carbon disulfide is incorporated into the raw material polyallylamine-based polymer. Normally, 100-1
20 mol%, preferably 100-110 mol% is used.

【0014】アルカリとしては、通常、水酸化ナトリウ
ム、水酸化カリウム、水酸化リチウム、炭酸ナトリウ
ム、炭酸カリウムが使用できる。好ましくは、水酸化ナ
トリウムが用いられる。アルカリの量は、通常、二硫化
炭素に対し、等モル当量使用する。アルカリを溶かす溶
媒は、通常、水である。溶媒の量は、使用するアルカリ
により違う。水酸化ナトリウムの場合、アルカリ濃度が
5−50重量%、好ましくは、10−50重量%になる
ように水に溶かして使用する。また、原料の重合体が塩
のときは、塩をフリーにするだけ、余計に加える。
As the alkali, usually sodium hydroxide, potassium hydroxide, lithium hydroxide, sodium carbonate, potassium carbonate can be used. Preferably sodium hydroxide is used. The amount of alkali is usually equimolar equivalent to carbon disulfide. The solvent that dissolves the alkali is usually water. The amount of solvent depends on the alkali used. In the case of sodium hydroxide, it is used by dissolving it in water so that the alkali concentration becomes 5 to 50% by weight, preferably 10 to 50% by weight. When the raw material polymer is a salt, the salt is freed and added in excess.

【0015】反応時間と反応温度は、入手したい高分子
重金属捕集剤により、適宜変えることができる。しか
し、反応温度は、二硫化炭素の沸点が低いので、通常、
反応系の温度は60℃以下、好ましくは10−55℃、
さらに好ましくは20−50℃が好ましい。反応時間
は、通常、10時間以下で終了できる。
The reaction time and reaction temperature can be appropriately changed depending on the polymer heavy metal scavenger to be obtained. However, the reaction temperature is usually because the boiling point of carbon disulfide is low.
The temperature of the reaction system is 60 ° C or lower, preferably 10-55 ° C,
More preferably, the temperature is 20-50 ° C. The reaction time is usually 10 hours or less.

【0016】試薬を加える順序は、特に制限はないが、
発熱反応に注意して行う。例えば、次ぎの操作で、高分
子重金属捕集剤を製造できる。原料のポリアリルアミン
系重合体の水溶液又は水懸濁液に二硫化炭素を加える。
次いで、内温20−50℃の温度でかき混ぜながら、ア
ルカリ水溶液を加え反応させる。この時、発熱に注意し
ながら、反応系の温度が50℃を超えないように調節し
て加える。滴下終了後、20−50℃で2−5時間反応
を続ける。この時、25−40℃に温度設定しておく
と、反応効率と安全性から更に好ましい。この製造操作
で、二硫化炭素を加える前に、アルカリを加え、20−
45℃に維持しながら、発熱に注意して、二硫化炭素を
加えても良い。また、反応系を20−45℃に維持しな
がら、二硫化炭素とアルカリを別々の滴下口から同時に
滴下しても良い。更に、少量のスケールの場合、二硫化
炭素とアルカリを30℃以下で一度に加え、冷却して温
度を25−40℃に維持して、2−7時間反応を行うこ
とができる。
The order of adding the reagents is not particularly limited,
Be careful of exothermic reactions. For example, the polymer heavy metal scavenger can be produced by the following procedure. Carbon disulfide is added to an aqueous solution or suspension of a polyallylamine-based polymer as a raw material.
Next, while stirring at an internal temperature of 20 to 50 ° C., an alkaline aqueous solution is added and reacted. At this time, paying attention to heat generation, the temperature of the reaction system is adjusted so that the temperature does not exceed 50 ° C. After completion of the dropping, the reaction is continued at 20-50 ° C for 2-5 hours. At this time, it is more preferable to set the temperature to 25-40 ° C. from the viewpoint of reaction efficiency and safety. In this manufacturing operation, alkali was added before adding carbon disulfide,
While maintaining the temperature at 45 ° C, carbon disulfide may be added while paying attention to heat generation. Further, while maintaining the reaction system at 20 to 45 ° C., carbon disulfide and alkali may be dropped simultaneously from separate dropping ports. Further, in the case of a small scale, carbon disulfide and alkali can be added all at once at 30 ° C. or lower, cooled to maintain the temperature at 25-40 ° C., and the reaction can be carried out for 2-7 hours.

【0017】反応終了後の溶液は、通常、そのまま、高
分子重金属捕集剤として使用できる。その溶液を多量の
アセトン中に加えて沈殿させ、濾取し、乾燥させると、
本発明重合体を得ることができる。本発明重合体は、通
常、黄色の粉末として得られる。
The solution after completion of the reaction can be used as it is as a high molecular weight heavy metal scavenger. The solution was added to a large amount of acetone to cause precipitation, which was collected by filtration and dried,
The polymer of the present invention can be obtained. The polymer of the present invention is usually obtained as a yellow powder.

【0018】本発明重合体の重量平均分子量は、原料の
ポリアリルアミン系重合体又はその塩の重量平均分子
量、及び二硫化炭素の量に依存する。本発明重合体の重
量平均分子量は、特に制限されないが、通常1000−
10,000,000、好ましくは1500−5,00
0,000,より好ましくは2000−2,000,0
00である。重量平均分子量が小さすぎると、重金属捕
集剤として沈降分離性が悪い。大きすぎると、溶解しず
らく、作業性が低下する。
The weight average molecular weight of the polymer of the present invention depends on the weight average molecular weight of the raw material polyallylamine polymer or its salt and the amount of carbon disulfide. The weight average molecular weight of the polymer of the present invention is not particularly limited, but is usually 1000-
10,000,000, preferably 1500-5,00
10,000, more preferably 2000-2,000,0
00. If the weight average molecular weight is too small, the heavy metal scavenger has poor sedimentation and separation properties. If it is too large, it is difficult to dissolve and the workability deteriorates.

【0019】本発明重合体の繰り返し単位は、原料のポ
リアリルアミン系重合体の繰り返し単位に依存する。ま
た、本発明重合体のN−ジチオカルバミン酸アルカリ金
属塩化された割合は、通常70−100%、好ましくは
80−100%、より好ましくは90−100%であ
る。その割合は、通常、元素分析値より決めることがで
きる。また、その割合は、本発明重合体を希硫酸で分解
し、定量的に発生する二硫化炭素をザンテートとし、ヨ
ウ素で滴定する方法(工業化学雑誌、69巻、766
頁、1966年)でも、決めることができる。本発明重
合体の赤外スペクトルには、通常、C=S結合に基づく
960cm-1付近に強い吸収とN−C=SのN−C結合
に基づく1375cm-1付近に強い吸収がみられる。
The repeating unit of the polymer of the present invention depends on the repeating unit of the raw material polyallylamine polymer. Further, the proportion of the polymer of the present invention salified with an alkali metal N-dithiocarbamate is usually 70-100%, preferably 80-100%, more preferably 90-100%. The ratio can usually be determined from elemental analysis values. The ratio is determined by decomposing the polymer of the present invention with dilute sulfuric acid, quantitatively generating carbon disulfide as xanthate, and titrating with iodine (Industrial Chemistry Magazine, Vol. 69, 766).
Page, 1966). In the infrared spectrum of the polymer of the present invention, a strong absorption is usually observed near 960 cm −1 based on the C═S bond and a strong absorption near 1375 cm −1 based on the N—C═S N—C bond.

【0020】本発明の高分子金属捕集剤は、かかる本発
明重合体を必須成分として含むものである。本発明の高
分子金属捕集剤は、好ましくは0.05−10%、より
好ましくは1−5%の水溶液として単独でも使用でき
る。その添加量は、廃水中の重金属イオン含有量に依存
し、次式により算出できる。 添加量=(Mw x 廃水の重金属イオンの量g)/金
属イオンの1当量g。 ただし、金属イオンの1当量=原子量/電荷数、Mw=
本発明重合体の重量平均分子量/(本発明重合体の重合
度 x N−ジチオカルバミン酸アルカリ金属塩化の割
合)、である。
The polymeric metal scavenger of the present invention contains the polymer of the present invention as an essential component. The polymeric metal scavenger of the present invention can be used alone as an aqueous solution of preferably 0.05-10%, more preferably 1-5%. The amount added depends on the content of heavy metal ions in the waste water and can be calculated by the following formula. Addition amount = (Mw x amount g of heavy metal ion of waste water) / equivalent g of metal ion. However, 1 equivalent of metal ion = atomic weight / charge number, Mw =
The weight average molecular weight of the polymer of the present invention / (degree of polymerization of the polymer of the present invention x ratio of N-dithiocarbamic acid alkali metal chloride).

【0021】本発明高分子重金属捕集剤は、必要に応じ
て、通常、捕集剤に添加される物質を含むこともでき
る。例えば、硫化ナトリウム、多硫化ナトリウム、水硫
化ナトリウムと併用しても良い。また、従来公知のアニ
オン性、ノニオン性及びカチオン性の高分子凝集剤と併
用することもできる。一方、廃水中の重金属イオン濃度
は、変動するので、本発明重合体は、多少、多めに加え
ることもできる。この過剰分の本発明重合体による不溶
化には、塩化第二鉄等を用いることもできる。本発明の
高分子重金属捕集剤は、従来の捕集剤、例えば、ポリエ
チレンイミンのジチオカルバミン酸ナトリウム化重合体
に比べ、重金属イオンの除去率が高く、生成する錯体の
沈降分離性も極めて良好である。
The polymeric heavy metal scavenger of the present invention may contain a substance which is usually added to the scavenger, if necessary. For example, you may use together with sodium sulfide, sodium polysulfide, and sodium hydrosulfide. It is also possible to use together with conventionally known anionic, nonionic and cationic polymer flocculants. On the other hand, the heavy metal ion concentration in the waste water varies, so the polymer of the present invention can be added in a slightly larger amount. Ferric chloride or the like can also be used for insolubilization with this excess amount of the polymer of the present invention. The polymeric heavy metal scavenger of the present invention has a higher removal rate of heavy metal ions than the conventional scavengers, for example, a sodium dithiocarbamate polymer of polyethyleneimine, and has a very good sedimentation / separation property of the resulting complex. is there.

【0022】[0022]

【作用】本発明重合体は、従来の高分子重金属捕集剤と
同様(ファインケミカル、1985年8月1日号、16
頁)、重金属イオンと1:1の錯体を形成すると考えら
れる。1:1錯体であることは、実施例7の表2に示す
ように、本発明重合体の添加量が、重金属イオンに対
し、1当量を使用すると、ほとんど金属が除去されるこ
とから支持される。この錯体の構造は、本発明の良好な
重金属捕集能と関係があると考えられる。本発明重合体
のモノマー部位のアリルアミン系ユニットCH2 C(R
2 )CH2 N(ただし、R2 は水素、メチルより選ばれ
る)は、ポリエチレンイミンのジチオカルバミン酸ナト
リウム化重合体のエチレンイミンユニットCH2 CH2
Nに比べ、疎水性が高い構造である。したがって、本発
明重合体と重金属イオンとの反応により生成する錯体
も、従来の捕集剤・金属錯体に比べ、疎水性が高い。そ
のため、生成した錯体は、沈殿のまま保持しやすく、水
に溶け出さないと考えられる。更に、過剰の本発明重金
属捕集剤を用いて重金属の除去能が減少しないのも、錯
体がより難溶性となるためと考えられる。
The polymer of the present invention is similar to the conventional heavy metal heavy metal scavenger (Fine Chemical, August 1, 1985, 16).
Page), and is believed to form a 1: 1 complex with heavy metal ions. As shown in Table 2 of Example 7, the 1: 1 complex is supported because most of the metal is removed when the amount of the polymer of the present invention added is 1 equivalent to the heavy metal ion. It It is believed that the structure of this complex is related to the good heavy metal collecting ability of the present invention. Allylamine unit CH 2 C (R
2 ) CH 2 N (wherein R 2 is selected from hydrogen and methyl) is an ethyleneimine unit CH 2 CH 2 of a sodium dithiocarbamate polymer of polyethyleneimine.
The structure is more hydrophobic than N. Therefore, the complex formed by the reaction between the polymer of the present invention and the heavy metal ion is also more hydrophobic than the conventional scavenger-metal complex. Therefore, it is considered that the produced complex is easy to hold as a precipitate and does not dissolve in water. Furthermore, the reason why the heavy metal scavenging ability is not decreased by using the excess heavy metal scavenger of the present invention is considered to be because the complex becomes more insoluble.

【0023】本発明重金属捕集剤は、70−100%
と、ジチオカルバミン酸アルカリ金属化の割合(以下、
置換化率と記すこともある)が高い。これが、重金属の
除去能が高い1つの原因と考えられる。一方、ポリエチ
レンイミンのジチオカルバミン酸ナトリウム化重合体の
場合、置換化率は低い。この原因として、原料のポリエ
チレンイミンのアミノ基の相当部分が、分岐している構
造、すなわち、第3級アミノ基であり、二硫化炭素と反
応しないことが挙げられる。また、原料のポリエチレン
イミンの第2級アミノ基部分も、重合体の主鎖を形成す
る部分であるため、反応性が悪いので、二硫化炭素と反
応しない第2級アミノ基も捕集剤に存在してくる可能性
もあると考えられる。いずれにしろ、ポリエチレンイミ
ンのジチオカルバミン酸ナトリウム化重合体は、ジチオ
カルバミン酸ナトリウム化されないフリーのアミンの割
合が高い。そのため、形成する重金属との錯体は、親水
性が高く、水に溶けやすくなる。したがって、ポリエチ
レンイミンのジチオカルバミン酸ナトリウム化重合体
は、本発明重合体とは異なり、疎水性に起因する高い重
金属除去能を、持たないものと考察できる。以上のよう
に、本発明重金属捕集剤の優れた重金属除去能は、本発
明重合体特有の構造に起因すると考えられる。
The heavy metal scavenger of the present invention is 70-100%
And the ratio of alkali metal dithiocarbamate (hereinafter,
(Also referred to as the substitution rate) is high. This is considered to be one of the reasons for the high ability to remove heavy metals. On the other hand, in the case of a sodium dithiocarbamate polymer of polyethyleneimine, the substitution rate is low. The reason for this is that a considerable part of the amino group of polyethyleneimine as a raw material has a branched structure, that is, a tertiary amino group and does not react with carbon disulfide. Also, the secondary amino group part of the raw material polyethyleneimine is a part that forms the main chain of the polymer, so the reactivity is poor, so the secondary amino group that does not react with carbon disulfide also acts as a scavenger. It is possible that they will exist. In any case, the polyethyleneimine sodium dithiocarbamate polymer has a high proportion of free amine that is not sodium dithiocarbamate. Therefore, the formed complex with a heavy metal has high hydrophilicity and is easily dissolved in water. Therefore, it can be considered that the sodium dithiocarbamate polymer of polyethyleneimine does not have a high heavy metal removing ability due to the hydrophobicity, unlike the polymer of the present invention. As described above, the excellent heavy metal removing ability of the heavy metal scavenger of the present invention is considered to be due to the structure peculiar to the polymer of the present invention.

【0024】[0024]

【実施例】以下に、本発明の高分子重金属捕集剤、本発
明の重合体、及びそれらの製造方法を実施例で示す。本
発明はこれらの実施例によって限定されるものではない
ことはもちろんである。
EXAMPLES The polymer heavy metal scavenger of the present invention, the polymers of the present invention, and the methods for producing them will be shown below in Examples. Of course, the invention is not limited to these examples.

【0025】実施例1 原料の既知ポリアリルアミンは、ポリアリルアミン塩酸
塩(日東紡績社製、コードPAA−HCl−10L、重
量平均分子量100,000)を、特開昭63−286
405号に記載する方法により水酸化ナトリウムで中和
した後、透析して、副成する食塩を除いたものを用い
た。ポリアリルアミンの15%水溶液380.64gと
蒸留水378.00gを撹拌機、滴下濾斗、温度計およ
び還流冷却器を備えた2リットルの反応器に入れる。こ
れに水酸化ナトリウムの20%水溶液200gを加え
た。次に、撹拌下に温度を30℃に保ちながら、二硫化
炭素76.14gを徐々に滴下した。滴下終了後、40
℃で4時間反応を続けると透明で淡黄色の溶液が得られ
た。この溶液は、そのまま、高分子重金属捕集剤として
も使用できる。この溶液を多量のアセトン中に加え、沈
殿した生成物を濾別した。減圧下室温で乾燥すると、1
49.6g(96%)のポリアリルアミンのジチオカル
バミン酸ナトリウム化重合体を得た。元素分析結果は、
C=30.64%、H=3.95%、N=9.05%、
S=41.07%であった。これらの値は、計算値C4
6 NS2 Naに基づく値、C=30.95%、H=
3.90%、N=9.02%、S=41.32%と一致
した。この結果は、得られたジチオカルバミン酸ナトリ
ウム化重合体が、実質上、100%ジチオカルバミン酸
ナトリウム化されていることを示している。
Example 1 Known polyallylamine as a raw material was polyallylamine hydrochloride (manufactured by Nitto Boseki Co., Ltd., code PAA-HCl-10L, weight average molecular weight 100,000) as disclosed in JP-A-63-286.
After neutralizing with sodium hydroxide by the method described in No. 405, it was dialyzed to remove salt by-product and used. 380.64 g of a 15% aqueous solution of polyallylamine and 378.00 g of distilled water are placed in a 2 liter reactor equipped with stirrer, dropping funnel, thermometer and reflux condenser. To this was added 200 g of a 20% aqueous solution of sodium hydroxide. Next, while maintaining the temperature at 30 ° C. under stirring, 76.14 g of carbon disulfide was gradually added dropwise. 40 after the dropping
When the reaction was continued at 4 ° C for 4 hours, a transparent and pale yellow solution was obtained. This solution can be used as it is as a polymer heavy metal scavenger. This solution was added to a large amount of acetone, and the precipitated product was filtered off. When dried at room temperature under reduced pressure, 1
49.6 g (96%) of polyallylamine sodium dithiocarbamate polymer was obtained. The elemental analysis results are
C = 30.64%, H = 3.95%, N = 9.05%,
It was S = 41.07%. These values are calculated values C 4
Value based on H 6 NS 2 Na, C = 30.95%, H =
It was in agreement with 3.90%, N = 9.02%, and S = 41.32%. This result shows that the obtained sodium dithiocarbamate polymer is substantially 100% sodium dithiocarbamate.

【0026】実施例2 原料のアリルアミンとジアリルアミンとの共重合体(モ
ル比4:1)は、アリルアミン塩酸塩とジアリルアミン
塩酸塩との共重合体(モル比4:1、特公平2−563
65に記載した方法により製造された重量平均分子量1
0,000のもの)を、特開昭63−286405に記
載した方法により、中和し透析したものを用いた。アリ
ルアミンとジアリルアミンとの共重合体(モル比4:
1)の15%水溶液434.06gと蒸留水378.0
0gを、実施例1と同じ反応容器中に入れ、これに水酸
化ナトリウムの20%水溶液200gを加えた。次に、
撹拌下に温度を30℃に保ちながら、二硫化炭素76.
14gを徐々に滴下した。滴下終了後、40℃で4時間
反応を続けると、透明で淡黄色の高分子重金属捕集剤溶
液が得られた。この溶液を実施例1と同じ方法で後処理
し、158.4g(97%)のアリルアミンとジアリル
アミンとの共重合体(モル比4:1)のジチオカルバミ
ン酸ナトリウム化重合体を得た。元素分析結果は、C=
33.81%、H=4.25%、N=8.55%、S=
39.15%であった。これらの値は、100%ジチオ
カルバミン酸ナトリウム化された重合体の計算値C23
345 10Na5 に基づく値、C=33.85%、H=
4.20%、N=8.58%、S=39.29%と一致
した。
Example 2 A raw material copolymer of allylamine and diallylamine (molar ratio 4: 1) was a copolymer of allylamine hydrochloride and diallylamine hydrochloride (molar ratio 4: 1, Japanese Patent Publication No. 2-563).
Weight average molecular weight 1 produced by the method described in 65.
50,000) was neutralized and dialyzed by the method described in JP-A-63-286405. Copolymer of allylamine and diallylamine (molar ratio 4:
43% of a 15% aqueous solution of 1) and distilled water of 378.0
0 g was placed in the same reaction vessel as in Example 1, and 200 g of a 20% aqueous solution of sodium hydroxide was added thereto. next,
While maintaining the temperature at 30 ° C. under stirring, carbon disulfide 76.
14 g was gradually added dropwise. After the dropping was completed, the reaction was continued at 40 ° C. for 4 hours to obtain a transparent, pale yellow polymer heavy metal scavenger solution. This solution was post-treated in the same manner as in Example 1 to obtain 158.4 g (97%) of a copolymer of allylamine and diallylamine (molar ratio 4: 1) of sodium dithiocarbamate polymer. Elemental analysis result is C =
33.81%, H = 4.25%, N = 8.55%, S =
It was 39.15%. These values are the calculated values of C 23 H of the polymer converted to 100% sodium dithiocarbamate.
Value based on 34 N 5 S 10 Na 5 , C = 33.85%, H =
It was in agreement with 4.20%, N = 8.58%, and S = 39.29%.

【0027】実施例3 原料の、アリルアミンとジアリルアミンとの共重合体
(モル比1:2)は、アリルアミン塩酸塩とジアリルア
ミン塩酸塩との共重合体(モル比1:2、特公平2−5
6365に記載した方法により製造した重量平均分子量
80,000の重合体)を、特開昭63−286405
に記載した方法により中和した後、透析したものを用い
た。アリルアミンとジアリルアミンとの共重合体(モル
比1:2)の15%水溶液558.71gと蒸留水37
8.00gを、実施例1と同じ反応容器中に入れ、これ
に水酸化ナトリウムの20%水溶液200gを加えた。
次に、撹拌下に温度を30℃に保ちながら、二硫化炭素
76.14gを徐々に滴下した。滴下終了後、40℃で
4時間反応を続けると、透明で淡黄色の高分子重金属捕
集剤溶液が得られた。この溶液を実施例1と同じ方法で
後処理して、アリルアミンとジアリルアミンとの共重合
体(モル比1:2)のジチオカルバミン酸ナトリウム化
重合体を得た。元素分析結果は、C=39.56%、H
=4.84%、N=7.65%、S=35.19%であ
った。これらの値は、100%ジチオカルバミン酸ナト
リウム化された重合体の計算値のC18263 6 Na
3 に基づく値、C=39.61%、H=4.80%、N
=7.70%、S=35.25%と一致した。図1に、
得られたアリルアミンとジアリルアミンとの共重合体
(モル比1:2)のジチオカルバミン酸ナトリウム化重
合体の赤外吸収スペクトルを示した。スペクトルには、
第1級アミンと第2級アミンに起因する特性吸収は認め
られず、C=S結合に起因する960cm-1、N−C=
SのN−C結合に起因する1375cm-1の吸収があ
る。
Example 3 As a raw material, a copolymer of allylamine and diallylamine (molar ratio 1: 2) was a copolymer of allylamine hydrochloride and diallylamine hydrochloride (molar ratio 1: 2, Japanese Patent Publication No. 2-5).
A polymer having a weight average molecular weight of 80,000 produced by the method described in JP-A No. 63-286405.
After being neutralized by the method described in 1., the dialyzed product was used. 558.71 g of a 15% aqueous solution of a copolymer of allylamine and diallylamine (molar ratio 1: 2) and distilled water 37
8.00 g was put in the same reaction vessel as in Example 1, and 200 g of a 20% aqueous solution of sodium hydroxide was added thereto.
Next, while maintaining the temperature at 30 ° C. under stirring, 76.14 g of carbon disulfide was gradually added dropwise. After the dropping was completed, the reaction was continued at 40 ° C. for 4 hours to obtain a transparent, pale yellow polymer heavy metal scavenger solution. This solution was post-treated in the same manner as in Example 1 to obtain a copolymer of allylamine and diallylamine (molar ratio 1: 2), a sodium dithiocarbamate polymer. Elemental analysis result is C = 39.56%, H
= 4.84%, N = 7.65%, S = 35.19%. These values are the calculated values of C 18 H 26 N 3 S 6 Na of the polymer polymerized with 100% sodium dithiocarbamate.
Value based on 3 , C = 39.61%, H = 4.80%, N
= 7.70% and S = 35.25%. In Figure 1,
The infrared absorption spectrum of the obtained sodium dithiocarbamate polymer of the copolymer of allylamine and diallylamine (molar ratio 1: 2) is shown. In the spectrum,
No characteristic absorption due to primary amines and secondary amines was observed, and 960 cm −1 due to C = S bond, N—C =
There is an absorption at 1375 cm −1 due to the S—N—C bond.

【0028】実施例4 ポリ(N−イソプロピルアリルアミン塩酸塩)(特公平
2−57084に記載した方法により製造した重量平均
分子量5,000の重合体)の60%水溶液226.0
6g、及び蒸留水613.12gを、実施例1と同じ反
応容器中に入れて、撹拌下に温度を30℃に保ちなが
ら、水酸化ナトリウムの20%水溶液400gと二硫化
炭素76.14gを、同時に徐々に滴下した。滴下終了
後、40℃で4時間反応を続けると、透明で淡黄色の高
分子重金属捕集剤溶液が得られた。この溶液中には、副
生した食塩が含まれるので、それを除去した。この溶液
の一部を透析チューブ(スペクトラム社製スペクトラ/
ポア6、No.132590、カットオフ分子量3,5
00)に入れ、蒸留水中で透析した。透析液を濃縮した
後、アセトン中に加え、実施例1と同じ方法で後処理し
てポリ(N−イソプロピルアリルアミン)のジチオカル
バミン酸ナトリウム化重合体を得た。元素分析結果は、
C=42.54%、H=6.19%、N=7.05%、
S=32.43%であった。これらの値は、100%ジ
チオカルバミン酸ナトリウム化された重合体の計算値C
7 12NS2 Naに基づく値、C=42.61%、H=
6.13%、N=7.10%、S=32.50%と一致
した。
Example 4 226.0 60% aqueous solution of poly (N-isopropylallylamine hydrochloride) (polymer having a weight average molecular weight of 5,000 produced by the method described in JP-B-2-57084)
6 g and 613.12 g of distilled water were placed in the same reaction vessel as in Example 1, 400 g of a 20% aqueous solution of sodium hydroxide and 76.14 g of carbon disulfide were added while keeping the temperature at 30 ° C. under stirring. At the same time, it was dripped slowly. After the dropping was completed, the reaction was continued at 40 ° C. for 4 hours to obtain a transparent, pale yellow polymer heavy metal scavenger solution. Since this solution contained salt as a by-product, it was removed. A part of this solution is used as a dialysis tube (Spectra / Spectra /
Pore 6, No. 132590, cutoff molecular weight 3,5
00) and dialyzed in distilled water. The dialysate was concentrated, added to acetone, and post-treated in the same manner as in Example 1 to obtain a poly (N-isopropylallylamine) sodium dithiocarbamate polymer. The elemental analysis results are
C = 42.54%, H = 6.19%, N = 7.05%,
It was S = 32.43%. These values are calculated values C of the polymer converted to 100% sodium dithiocarbamate.
Value based on 7 H 12 NS 2 Na, C = 42.61%, H =
It was in agreement with 6.13%, N = 7.10%, and S = 32.50%.

【0029】実施例5 ポリ(N−シクロヘキシルアリルアミン塩酸塩)(特公
平2−57084に記載した方法により製造した重量平
均分子量4,000の重合体)の60%水溶液292.
84gと蒸留水813.44gとを、実施例1と同じ反
応容器に入れて、撹拌下に温度を30℃に保ちながら、
水酸化ナトリウムの20%水溶液400gと二硫化炭素
76.14gを、同時に徐々に滴下した。滴下終了後、
40℃で4時間反応を続けると、透明で淡黄色の高分子
重金属捕集剤溶液が得られた。この溶液中には、副生し
た食塩が含まれるので、それを除去した。すなわち、こ
の溶液の一部を透析チューブ(スペクトラム社製スペク
トラ/ポア6、No.132590、カットオフ分子量
3,500)に入れ、蒸留水中で透析した。透析液を濃
縮した後、アセトン中に加え、実施例1と同じ方法で後
処理してポリ(N−シクロヘキシルアリルアミン)のジ
チオカルバミン酸ナトリウム化重合体を得た。元素分析
結果は、C=50.54%、H=6.84%、N=5.
86%、S=26.96%であった。これらの値は、1
00%ジチオカルバミン酸ナトリウム化された重合体の
計算値C1016NS2 Naに基づく値、C=50.60
%、H=6.79%、N=5.90%、S=27.00
%と一致した。
Example 5 A 60% aqueous solution of poly (N-cyclohexylallylamine hydrochloride) (polymer having a weight average molecular weight of 4,000 produced by the method described in JP-B-2-57084) 292.
84 g and 813.44 g of distilled water were placed in the same reaction vessel as in Example 1, and the temperature was kept at 30 ° C. under stirring,
400 g of a 20% aqueous solution of sodium hydroxide and 76.14 g of carbon disulfide were gradually added dropwise at the same time. After the dropping is completed,
When the reaction was continued at 40 ° C. for 4 hours, a transparent light yellow polymer heavy metal scavenger solution was obtained. Since this solution contained salt as a by-product, it was removed. That is, a part of this solution was put into a dialysis tube (Spectra / Pore 6, No. 132590, cutoff molecular weight 3,500 manufactured by Spectrum Co.) and dialyzed in distilled water. The dialysate was concentrated, added to acetone, and post-treated in the same manner as in Example 1 to obtain a poly (N-cyclohexylallylamine) sodium dithiocarbamate polymer. Elemental analysis results show that C = 50.54%, H = 6.84%, N = 5.
It was 86% and S = 26.96%. These values are 1
Calculated value for polymer polymerized with 00% sodium dithiocarbamate C 10 H 16 NS 2 Na, C = 50.60
%, H = 6.79%, N = 5.90%, S = 27.00
Coincided with%.

【0030】比較例 ポリエチレンイミン(日本触媒株式会社製、エポミンP
−1000、重量平均分子量70,000)の30%水
溶液143.56gと蒸留水427.07gを実施例1
と同じ反応容器に入れて、これに、水酸化ナトリウムの
20%水溶液150gを加えた。次に、撹拌下に温度を
30℃に保ちながら、二硫化炭素57.10gを徐々に
滴下した。滴下終了後、40℃で4時間反応を続けると
透明で淡黄色の溶液が得られた。この溶液を実施例1と
同じ方法で後処理してポリエチレンイミンのジチオカル
バミン酸ナトリウム化重合体を得た。元素分析結果は、
C=28.00%、H=3.81%、N=11.66
%、S=40.75%であった。これらの値は、計算値
11174 6 Na3 に基づく値、C=28.31
%、H=3.67%、N=12.01%、S=41.2
3%とほぼ一致し、ポリエチレンイミンの全アミノ基数
の75%がジチオカルバミン酸ナトリウム化された。
Comparative Example Polyethyleneimine (Epomin P manufactured by Nippon Shokubai Co., Ltd.)
Example 1 was prepared by adding 143.56 g of a 30% aqueous solution of -1000 and a weight average molecular weight of 70,000) and 427.07 g of distilled water.
Into the same reaction vessel as above, 150 g of a 20% aqueous solution of sodium hydroxide was added. Next, while maintaining the temperature at 30 ° C. under stirring, 57.10 g of carbon disulfide was gradually added dropwise. After the dropping was completed, the reaction was continued at 40 ° C. for 4 hours to obtain a transparent and pale yellow solution. This solution was post-treated in the same manner as in Example 1 to obtain a sodium dithiocarbamate polymer of polyethyleneimine. The elemental analysis results are
C = 28.00%, H = 3.81%, N = 11.66
%, S = 40.75%. These values are based on the calculated value C 11 H 17 N 4 S 6 Na 3 , C = 28.31.
%, H = 3.67%, N = 12.01%, S = 41.2
Consistent with 3%, 75% of the total number of amino groups of polyethyleneimine was converted to sodium dithiocarbamate.

【0031】実施例6 実施例1−5で得られた本発明の高分子重金属捕集剤及
び比較例で得られた高分子系重金属捕集剤の捕集剤・カ
ドミウム錯体の沈降分離性について比較実験を行った。
試験方法は次の通りである。100ppmのCd2+イオ
ンを含む硫酸カドミウム水溶液50mlに、実施例1−
5と比較例で得られた高分子重金属捕集剤のMw=(本
発明重合体の平均分子量)/(本発明重合体の重合度
x N−ジチオカルバミン酸アルカリ金属塩化の割合)
に基づいて調製した0.089モル/l水溶液をCd2+
イオンの当量の0.8、1.0及び1.2倍になるよう
に添加した。pHを7.0に調整し、10分間撹拌した
後、10分間静置した。これらの試験液の上澄の濁りの
程度を目視で判定した。その結果を表1に示す。
Example 6 Precipitation Separability of the Cadmium Complex Scavenger of the Polymer Heavy Metal Scavenger of the Present Invention Obtained in Examples 1-5 and the Polymer Heavy Metal Scavenger Obtained in Comparative Examples A comparative experiment was conducted.
The test method is as follows. Example 1 was added to 50 ml of an aqueous cadmium sulfate solution containing 100 ppm of Cd 2+ ions.
5 and Mw of the high molecular weight heavy metal scavengers obtained in Comparative Examples = (average molecular weight of the polymer of the present invention) / (degree of polymerization of the polymer of the present invention)
x Proportion of N-dithiocarbamate alkali metal chloride)
A 0.089 mol / l aqueous solution prepared on the basis of Cd 2+
It was added so that it would be 0.8, 1.0 and 1.2 times the equivalent of the ions. The pH was adjusted to 7.0, the mixture was stirred for 10 minutes, and then allowed to stand for 10 minutes. The degree of turbidity of the supernatant of these test solutions was visually determined. The results are shown in Table 1.

【0032】表中、沈降分離性は、 良い:錯体が完全に沈降して上澄が透明な状態; 普通:錯体が完全に沈降せず上澄に多少にごりがある状
態; 悪い:錯体が完全に沈降せず上澄ににごりが多い状態; を表す。実施例1−5で得られた本発明の高分子重金属
捕集剤は、添加量0.8、1.0、1.2当量で錯体の
沈降分離性が良いが、比較例の捕集剤は、1.2当量の
使用では、悪い結果となった。
In the table, the sedimentation separability is good: the complex is completely precipitated and the supernatant is transparent; Normal: the complex is not completely precipitated and the supernatant is slightly turbid; Bad: the complex is completely Represents a state in which the supernatant does not settle and the supernatant is heavily turbid. The polymeric heavy metal scavengers of the present invention obtained in Examples 1-5 have good sedimentation and separability of the complex at the addition amounts of 0.8, 1.0 and 1.2 equivalents, but the scavengers of Comparative Examples. Had poor results when used at 1.2 equivalents.

【化18】 [Chemical 18]

【0033】実施例7 実施例1−5で得られた本発明の高分子重金属捕集剤及
び比較例で得られた高分子系重金属捕集剤のCd2+イオ
ンの捕捉能について比較実験を行った。試験方法は次の
通りである。実施例6で形成させたカドミウム錯体の沈
降物を東洋濾紙No.5Aを用いて濾別し、濾液中に含
まれるCd2+イオン濃度を原子吸光法によって測定し
た。測定は、日立製作所製170−30形原子吸光光度
計を用いて、実施した。1−4ppmのCd2+イオンを
含む硫酸カドミウムの標準溶液の吸光度を測定し、吸光
度と濃度が直線関係にある検量線を得た。試料溶液が4
ppm以上のときは、1−4ppmになるように適当に
薄めることにより、試料を測定した。その結果より、高
分子系重金属捕集剤によるCd2+イオンの除去率を求
め、Cd2+イオンの捕捉能を比較した。その結果を表2
に示す。
Example 7 A comparative experiment was conducted on the ability of the polymeric heavy metal scavengers of the present invention obtained in Examples 1-5 and the polymeric heavy metal scavengers obtained in Comparative Examples to capture Cd 2+ ions. went. The test method is as follows. The precipitate of the cadmium complex formed in Example 6 was used as Toyo Filter Paper No. 5A was used for filtration, and the Cd 2+ ion concentration contained in the filtrate was measured by the atomic absorption method. The measurement was carried out using a Hitachi Model 170-30 atomic absorption spectrophotometer. The absorbance of a standard solution of cadmium sulfate containing 1-4 ppm of Cd 2+ ions was measured to obtain a calibration curve having a linear relationship between the absorbance and the concentration. 4 sample solutions
When it was above ppm, the sample was measured by appropriately diluting it to 1-4 ppm. From the results, the removal rate of Cd 2+ ions by the high molecular weight heavy metal scavenger was obtained, and the scavenging ability of Cd 2+ ions was compared. The results are shown in Table 2.
Shown in.

【化19】 実施例1−5で得られた本発明の高分子系重金属捕集剤
は、添加量1.0当量で100%のCd2+イオンを捕捉
し、1.2当量でも、97−100%捕捉した。一方、
比較例の高分子系重金属捕集剤は、添加量1.0当量で
98%のCd2+イオンを捕捉するが、1.2当量では、
87%の捕捉に減少した。
[Chemical 19] The polymeric heavy metal scavenger of the present invention obtained in Example 1-5 captures 100% of Cd 2+ ions at an addition amount of 1.0 equivalent, and even at 1.2 equivalents, captures 97-100%. did. on the other hand,
The high molecular weight heavy metal scavenger of the comparative example captures 98% of Cd 2+ ions with an addition amount of 1.0 equivalent, but with 1.2 equivalents,
Reduced to 87% capture.

【0034】[0034]

【発明の効果】本発明の高分子重金属捕集剤は、従来の
高分子重金属捕集剤に比べ、重金属イオンの捕捉能と形
成した金属錯体の沈降分離性に優れている。特に、重金
属イオンの当量より、捕集剤を過剰に使用しても、捕捉
能はほとんど変わらない。廃水中の重金属イオンの濃度
は、通常変動する。しかし、過剰の本発明の重金属捕集
剤を使用すれば、いつも同様に処理できる。また、未知
濃度の重金属イオンを除去するとき、重金属イオンを正
確に定量する必要はなく、おおまかに定量するだけで良
い。過剰に本発明の重金属捕集剤を使用すれば、重金属
イオンの除去率が減少しないからである。
The polymeric heavy metal scavenger of the present invention is superior to the conventional polymeric heavy metal scavengers in the ability to trap heavy metal ions and the sedimentation / separation property of the formed metal complex. In particular, even if the scavenger is used in excess of the equivalent amount of heavy metal ions, the scavenging ability remains almost unchanged. The concentration of heavy metal ions in wastewater usually fluctuates. However, if an excess of the heavy metal scavenger of the invention is used, it can always be treated in the same way. Further, when removing heavy metal ions of unknown concentration, it is not necessary to accurately quantify the heavy metal ions, but only roughly. This is because if the heavy metal scavenger of the present invention is used in excess, the removal rate of heavy metal ions will not decrease.

【0035】[0035]

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

【図1】 アリルアミンとジアリルアミンとの共重合体
(モル比1:2)のジチオカルバミン酸ナトリウム化重
合体(実施例3の重合体)のKBr法の赤外吸収スペク
トルを示す。横軸は波数(cm-1)、縦軸は透過率又は
吸光度を表す。
FIG. 1 shows an infrared absorption spectrum of a copolymer of allylamine and diallylamine (molar ratio 1: 2), a sodium dithiocarbamate polymer (polymer of Example 3) by a KBr method. The horizontal axis represents wave number (cm −1 ) and the vertical axis represents transmittance or absorbance.

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 一般式 【化1】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、mは重合度を示し、jは
0≦j≦1を示す)又は一般式 【化2】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、R2 は水素、メチ
ル基より選ばれ、mは重合度を示し、jは0<j≦1を
示す)で表されるポリアリルアミン系重合体の、第1級
及び第2級アミノ基(NH)の総和の70−100%
が、ジチオカルバミン酸アルカリ金属塩化(N−C(=
S)−SM、ただし、MはLi、Na、Kのアルカリ金
属より選ばれる)された重合体を含む高分子重金属捕集
剤。
1. A general formula: (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of m, m is the degree of polymerization, and j is 0 ≦ j ≦ 1) or the general formula: (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, R 2 is selected from hydrogen and a methyl group, m is the degree of polymerization, and j is 0. 70-100% of the total of the primary and secondary amino groups (NH) of the polyallylamine-based polymer represented by <indicating j ≦ 1)
However, dithiocarbamate alkali metal chloride (NC (=
S) -SM, where M is a polymer heavy metal scavenger containing a polymer selected from the alkali metals Li, Na, and K).
【請求項2】 一般式 【化3】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、mは重合度を示し、jは
0≦j≦1を示す)又は一般式 【化4】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、R2 は水素、メチ
ルより選ばれ、mは重合度を示し、jは0<j≦1を示
す)で表されるポリアリルアミン系重合体の、第1級及
び第2級アミノ基(NH)の総和の70−100%が、
ジチオカルバミン酸アルカリ金属塩化(N−C(=S)
−SM、ただし、MはLi、Na、Kのアルカリ金属よ
り選ばれる)された重合体。
2. A general formula: (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of m, m represents the degree of polymerization, and j represents 0 ≦ j ≦ 1) or the general formula: (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, R 2 is selected from hydrogen and methyl, m is the degree of polymerization, and j is 0 < 70-100% of the total of primary and secondary amino groups (NH) in the polyallylamine-based polymer represented by
Alkali metal chloride dithiocarbamate (NC (= S)
-SM, where M is selected from the alkali metals Li, Na and K).
【請求項3】 一般式 【化5】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、MはLi、Na、Kのア
ルカリ金属より選ばれ、mは重合度を示し、jは0≦j
≦1を示す)又は一般式 【化6】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、MはLi、Na、
Kのアルカリ金属より選ばれ、R2 は水素、メチルより
選ばれ、mは重合度を示し、jは0<j≦1を示す)で
表される重合体を含む高分子重金属捕集剤。
3. A general formula: (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of M, selected from alkali metals of Li, Na, and K, m represents a degree of polymerization, and j is 0 ≦ j.
≦ 1) or the general formula: (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, M is Li, Na,
A heavy polymer scavenger containing a polymer selected from the alkali metals of K, R 2 selected from hydrogen and methyl, m represents the degree of polymerization, and j represents 0 <j ≦ 1).
【請求項4】 一般式 【化7】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、MはLi、Na、Kのア
ルカリ金属より選ばれ、mは重合度を示し、jは0≦j
≦1を示す)又は一般式 【化8】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、MはLi、Na、
Kのアルカリ金属より選ばれ、R2 は水素、メチルより
選ばれ、mは重合度を示し、jは0<j≦1を示す)で
表されるジチオカルバミン酸アルカリ金属塩化重合体。
4. A general formula: (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of M, selected from alkali metals of Li, Na, and K, m represents a degree of polymerization, and j is 0 ≦ j.
≦ 1) or the general formula: (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, M is Li, Na,
Alkali metal chlorinated polymer of dithiocarbamate represented by the formula: K selected from alkali metals, R 2 selected from hydrogen and methyl, m represents the degree of polymerization, and j represents 0 <j ≦ 1.
【請求項5】 一般式 【化9】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、mは重合度を示し、jは
0≦j≦1を示す)若しくは一般式 【化10】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、R2 は水素、メチ
ルより選ばれ、mは重合度を示し、jは0<j≦1を示
す)で表されるポリアリルアミン系重合体、又はその塩
を、アルカリの存在下で二硫化炭素と反応させることを
特徴とする請求項1又は3記載の高分子重金属捕集剤の
製造方法。
5. A general formula: (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of m, m represents the degree of polymerization, and j represents 0 ≦ j ≦ 1) or the general formula: (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, R 2 is selected from hydrogen and methyl, m is the degree of polymerization, and j is 0 < The polymer heavy metal scavenger according to claim 1 or 3, wherein a polyallylamine-based polymer represented by j <1) or a salt thereof is reacted with carbon disulfide in the presence of an alkali. Manufacturing method.
【請求項6】 一般式 【化11】 (式中、R1 は炭素数1−6のアルキル、炭素数5−7
のシクロアルキルより選ばれ、mは重合度を示し、jは
0≦j≦1を示す)若しくは一般式 【化12】 (式中、R1 は水素、炭素数1−6のアルキル、炭素数
5−7のシクロアルキルより選ばれ、R2 は水素、メチ
ルより選ばれ、mは重合度を示し、jは0<j≦1を示
す)で表されるポリアリルアミン系重合体、又はその塩
を、アルカリの存在下で二硫化炭素と反応させることを
特徴とする請求項2又は4記載のジチオカルバミン酸ア
ルカリ金属塩化重合体の製造方法。
6. A general formula: (In the formula, R 1 is alkyl having 1 to 6 carbons and 5 to 7 carbons.
Selected from cycloalkyl of m, m represents the degree of polymerization, and j represents 0 ≦ j ≦ 1) or the general formula: (In the formula, R 1 is selected from hydrogen, alkyl having 1 to 6 carbons and cycloalkyl having 5 to 7 carbons, R 2 is selected from hydrogen and methyl, m is the degree of polymerization, and j is 0 < 5. The polyallylamine-based polymer represented by the formula (j ≦ 1) or a salt thereof is reacted with carbon disulfide in the presence of an alkali. Manufacturing method of coalescence.
JP02587994A 1994-01-31 1994-01-31 Polymer heavy metal scavenger, alkali metal dithiocarbamate chloride polymer, and methods for producing them Expired - Fee Related JP3264348B2 (en)

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Cited By (12)

* Cited by examiner, † Cited by third party
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JPH09122618A (en) * 1995-10-31 1997-05-13 Miyoshi Oil & Fat Co Ltd Treatment agent for solid waste
JPH10192870A (en) * 1997-01-09 1998-07-28 Unitika Ltd Arsenic fixation agent and treatment of arsenic-containing wastewater
JP2002534564A (en) * 1999-01-15 2002-10-15 ナルコ ケミカル カンパニー Compositions and methods for precipitating metal ions from semiconductor wastewater while improving microfilter operation
EP1609613A1 (en) 2004-06-22 2005-12-28 Fuji Photo Film Co., Ltd. Image recording medium manufacturing method
JP2007232563A (en) * 2006-03-01 2007-09-13 Dkk Toa Corp Electrode body
EP2436740A1 (en) 2003-09-29 2012-04-04 Fujifilm Corporation Ink for inkjet printing, ink set for inkjet printing, inkjet recording material and producing method for inkjet recording material, and inkjet recording method
WO2013009594A3 (en) * 2011-07-12 2013-08-15 General Electric Company Polymer and method for using the same
CN106315808A (en) * 2016-10-13 2017-01-11 仲恺农业工程学院 Heavy metal chelating agent and preparation method thereof
CN106946333A (en) * 2017-04-13 2017-07-14 兰州交通大学 A kind of heavy metal flocculant and preparation method thereof
JP2020082003A (en) * 2018-11-29 2020-06-04 国立研究開発法人量子科学技術研究開発機構 Metal adsorbent having dithiocarbamic acid group and method for producing the same and metal extraction method
CN114106238A (en) * 2021-12-14 2022-03-01 西南石油大学 Zwitterionic flocculant and preparation method thereof
CN115196780A (en) * 2022-06-09 2022-10-18 山鹰国际控股股份公司 Treatment process of pulping and papermaking wastewater

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Cited By (14)

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JPH09122618A (en) * 1995-10-31 1997-05-13 Miyoshi Oil & Fat Co Ltd Treatment agent for solid waste
JPH10192870A (en) * 1997-01-09 1998-07-28 Unitika Ltd Arsenic fixation agent and treatment of arsenic-containing wastewater
JP2011117000A (en) * 1999-01-15 2011-06-16 Nalco Chemical Co Composition and method for precipitating metal ion from semiconductor wastewater and simultaneously improving microfilter operation
JP2002534564A (en) * 1999-01-15 2002-10-15 ナルコ ケミカル カンパニー Compositions and methods for precipitating metal ions from semiconductor wastewater while improving microfilter operation
EP2436740A1 (en) 2003-09-29 2012-04-04 Fujifilm Corporation Ink for inkjet printing, ink set for inkjet printing, inkjet recording material and producing method for inkjet recording material, and inkjet recording method
EP1609613A1 (en) 2004-06-22 2005-12-28 Fuji Photo Film Co., Ltd. Image recording medium manufacturing method
JP2007232563A (en) * 2006-03-01 2007-09-13 Dkk Toa Corp Electrode body
WO2013009594A3 (en) * 2011-07-12 2013-08-15 General Electric Company Polymer and method for using the same
US9371408B2 (en) 2011-07-12 2016-06-21 General Electric Company Polymer and method for using the same
CN106315808A (en) * 2016-10-13 2017-01-11 仲恺农业工程学院 Heavy metal chelating agent and preparation method thereof
CN106946333A (en) * 2017-04-13 2017-07-14 兰州交通大学 A kind of heavy metal flocculant and preparation method thereof
JP2020082003A (en) * 2018-11-29 2020-06-04 国立研究開発法人量子科学技術研究開発機構 Metal adsorbent having dithiocarbamic acid group and method for producing the same and metal extraction method
CN114106238A (en) * 2021-12-14 2022-03-01 西南石油大学 Zwitterionic flocculant and preparation method thereof
CN115196780A (en) * 2022-06-09 2022-10-18 山鹰国际控股股份公司 Treatment process of pulping and papermaking wastewater

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