JPS603082B2 - Manufacturing method of heavy metal adsorbent - Google Patents

Manufacturing method of heavy metal adsorbent

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Publication number
JPS603082B2
JPS603082B2 JP10179476A JP10179476A JPS603082B2 JP S603082 B2 JPS603082 B2 JP S603082B2 JP 10179476 A JP10179476 A JP 10179476A JP 10179476 A JP10179476 A JP 10179476A JP S603082 B2 JPS603082 B2 JP S603082B2
Authority
JP
Japan
Prior art keywords
copolymer
adsorbent
heavy metal
uranium
acid
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
JP10179476A
Other languages
Japanese (ja)
Other versions
JPS5326887A (en
Inventor
博 中山
裕子 谷口
久司 谷
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.)
Kanebo Ltd
Original Assignee
Kanebo Ltd
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Filing date
Publication date
Application filed by Kanebo Ltd filed Critical Kanebo Ltd
Priority to JP10179476A priority Critical patent/JPS603082B2/en
Publication of JPS5326887A publication Critical patent/JPS5326887A/en
Publication of JPS603082B2 publication Critical patent/JPS603082B2/en
Expired legal-status Critical Current

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  • Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Description

【発明の詳細な説明】 本発明は水中に陽イオン、鰭イオンとして溶解している
重金属イオンに対して選択的吸着館を有する重金属吸着
剤の製造方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing a heavy metal adsorbent having selective adsorption chambers for heavy metal ions dissolved in water as cations and fin ions.

従来、金属イオン吸着剤としてはカチオン又はアニオン
交換樹脂やポリァミン系、ィミ/酢酸系のキレート樹脂
等が知られている。
Conventionally, as metal ion adsorbents, cation or anion exchange resins, polyamine-based, imi/acetic acid-based chelate resins, and the like are known.

これ等の樹脂は多種類の金属を無差別に吸着して特定の
有用金属に対する選択吸着性に乏しく、例えば海水中に
溶存するウランを吸着採取する場合、吸着館を全く有し
ていない。
These resins adsorb many types of metals indiscriminately and have poor selective adsorption properties for specific useful metals. For example, when collecting uranium dissolved in seawater by adsorption, they do not have any adsorption chambers.

近時、該ウランに対して吸着能を有するものとしてチタ
ン酸、レゾルシンヒ酸樹脂、トリアミノフェノールグリ
オキサゾール樹脂等が提案されているが吸着館は小さく
又水中での形状保持が不安定である等の理由により実用
化されていない。
Recently, titanic acid, resorcinol arsenic acid resin, triaminophenol glyoxazole resin, etc. have been proposed as having adsorption ability for uranium, but the adsorption capacity is small and the shape retention in water is unstable. It has not been put into practical use for several reasons.

本発明者は上記せる問題点を解消すべく、鋭意広範囲に
系統的研究を行ない本発明を完成したものであり、その
目的とするところは水中に溶存する重金属イオンに対し
て高吸着館を有し、特にウランに対して優れた選択性と
吸着館を有する重金属吸着剤の製造方法を提供するにあ
る。即ち本発明はボリアミノスチレン系共重合体をジア
ゾ化した後−般式01(式中RはH又はOHであり×は
S、0、NHのいずれかを示す)で表わされる4ーヒド
ロキシベンゾィミダゾ−ル、4−ヒドロキシベンゾオキ
サゾール、4−ヒドロキシベンゾチアゾール又は該誘導
体とカップリング反応せしめることを特徴とする重金属
吸着剤の製造方法である。
In order to solve the above-mentioned problems, the present inventor conducted extensive systematic research and completed the present invention. Another object of the present invention is to provide a method for producing a heavy metal adsorbent having excellent selectivity and adsorption capacity, especially for uranium. That is, the present invention diazotizes a polyaminostyrene copolymer and then converts it into a 4-hydroxybenzo compound represented by the general formula 01 (wherein R is H or OH and x represents either S, 0, or NH). This is a method for producing a heavy metal adsorbent, which is characterized by carrying out a coupling reaction with imidazole, 4-hydroxybenzoxazole, 4-hydroxybenzothiazole, or a derivative thereof.

本発明に用いるポリアミノスチレン系共重合体とはポリ
スチレン系共重合体例えばスチレンージビニルベンゼン
共重合体、スチレンーピニルピリジン共重合体、スチレ
ンークロルメチルスチレン共重合体をアミン類により努
稀海せしめたもの等をニトロ化して還元することにより
得られる。
The polyaminostyrene copolymer used in the present invention is a polystyrene copolymer, such as styrene-divinylbenzene copolymer, styrene-pinylpyridine copolymer, or styrene-chloromethylstyrene copolymer, which is prepared by mixing with amines. It can be obtained by nitration and reduction of such substances.

ポリスチレン系共重合体のニトロ化は常法により濃硝酸
−濃硫酸混合系で50〜100℃の温度下でニトロ化す
ることが望ましい。温度が50℃より低いと反応速度が
遅くなり、長時間を要し、又100℃より高いと基体が
損傷したり酸化を受けやすくなる。
It is desirable to nitrate the polystyrene copolymer using a conventional method using a mixed system of concentrated nitric acid and concentrated sulfuric acid at a temperature of 50 to 100°C. If the temperature is lower than 50°C, the reaction rate will be slow and it will take a long time, and if the temperature is higher than 100°C, the substrate will be damaged or susceptible to oxidation.

更に該ニトロ基をアミノ基に還元するに際しては例えば
エタノール中でニトロ化ポリスチレン系共重合体を濃塩
酸と塩化第一錫と共に加熱還流する方法により達成出来
る。
Further, the reduction of the nitro group to an amino group can be achieved, for example, by heating and refluxing the nitrated polystyrene copolymer with concentrated hydrochloric acid and stannous chloride in ethanol.

ニトロ化の際ポリスチレン系共重合体の架橋度が低い場
合、ポリマーが融解又は豚着を生じるため長時間を要し
て反応させる必要が生ずる。
If the degree of crosslinking of the polystyrene copolymer is low during nitration, the polymer may melt or become sticky, making it necessary to carry out the reaction over a long period of time.

この場合ニトロイG鞠ま低下する鏡向がある。又、架橋
度が高過ぎる場合、ニトロTG率が低下する倭向を示し
、これが最終的にペンゾヒドロキサム酸誘導体との反応
率にも影響を与える為適宜条件を選択することが好まし
く、例えばスチレンとジビニルベンゼンとを乳化重合又
は懸濁重合により共重合するに際し、ジビニルベンゼン
の仕込み比率をスチレンに対し、0.5〜30モル%、
特に好ましくは、0.5〜5モル%とすることにより、
ニトロ化の際上記難点を克服することが出釆る。この場
合のニトロイG率‘ま全ベンゼン核の80〜95%であ
る。又スチレンとクロルメチルスチレンを共重合せしめ
るに際し、クロルメチルスチレンの仕込み比率がスチレ
ンに対して5〜100モル%が好ましく、得られた共重
合体を粉末とするか又は繊維状にしてアミン類例えばエ
チレンジアミン、ジェチレントリアミン、トリエチレン
テトラミン、ピベラジン、キシリレンジアミンの如き少
なくとも二官能性を有するアミンと水又はメタノール、
エタノール、プロパノール、ブタノールの如きアルコー
ル類或いはアセトン、メチルエチルケトンの如きケトン
類、更にはアセトニトリル、ニトロメタン、ジメチルホ
ルムアミド、ジメチルアセトアミド、ジメチルスルホキ
シド等の溶媒中で室温から50〜9ぴ0の温度に1〜l
q寺間で徐々に昇溢して処理し架橋せしめる。
In this case, there is a mirror direction in which the nitro G ball decreases. In addition, if the degree of crosslinking is too high, the nitroTG rate tends to decrease, which ultimately affects the reaction rate with the penzohydroxamic acid derivative, so it is preferable to select conditions appropriately. When copolymerizing and divinylbenzene by emulsion polymerization or suspension polymerization, the charging ratio of divinylbenzene to styrene is 0.5 to 30 mol%,
Particularly preferably, by setting it to 0.5 to 5 mol%,
It is possible to overcome the above-mentioned difficulties during nitration. In this case, the nitro G ratio is 80 to 95% of the total benzene nuclei. Further, when copolymerizing styrene and chloromethylstyrene, the charging ratio of chloromethylstyrene to styrene is preferably 5 to 100% by mole, and the resulting copolymer is made into powder or fibers and mixed with amines such as an amine having at least difunctionality such as ethylenediamine, jethylenetriamine, triethylenetetramine, piperazine, xylylenediamine and water or methanol;
Alcohols such as ethanol, propanol, butanol, ketones such as acetone, methyl ethyl ketone, and solvents such as acetonitrile, nitromethane, dimethylformamide, dimethylacetamide, dimethyl sulfoxide, etc., at a temperature of 50 to 90°C from room temperature for 1 to 1 liters.
q Gradually rise and overflow in Terama, process and crosslink.

この場合昇溢速度が上記条件より大きい場合、粉末、或
いは繊維状物質の表面が融解し、互いに豚着してガム状
となる。
In this case, if the overflow rate is higher than the above conditions, the surfaces of the powder or fibrous material melt and adhere to each other, forming a gum-like state.

この方法により得られる粉末状或いは繊維状物質は、不
溶不融性が高くニトロ化の条件にも耐えることが出釆、
又ニトロ化率は全ベンゼン核の75〜95%である。上
記方法により得られるポリアミ/スチレン系共重合体は
次にジアゾ化する。
The powdered or fibrous material obtained by this method is highly insoluble and infusible and can withstand nitration conditions.
Further, the nitration rate is 75 to 95% of all benzene nuclei. The polyamide/styrenic copolymer obtained by the above method is then diazotized.

この際該共重合体の形状は粉末状或は繊維状が好ましい
。ボリアミ/スチレン系共重合体を該共重合体のアミ/
基塁に対して3倍モル量の塩酸を含有する水溶液に浸濃
し0〜1ぴ0の温度下で縄拝しながら亜硝酸ソーダ水溶
液を滴下する。
In this case, the shape of the copolymer is preferably powder or fiber. Polyamide/styrenic copolymer
It is immersed in an aqueous solution containing 3 times the molar amount of hydrochloric acid as the base base, and a sodium nitrite aqueous solution is added dropwise at a temperature of 0 to 1 0.

この際晒硝酸ソーダの飽和量は沃素デンプン試験紙を用
いて知ることが出来る。
At this time, the saturated amount of bleached sodium nitrate can be determined using iodine starch test paper.

即ち沃素デンプン紙が青色を示し、且数分以上退色しな
い点を以つて、飽和量とする。これに従って、核ポリア
ミノスチレン系共重合体のジアゾ化を受けるアミノ基の
量が解る。ジアゾ化を完了した該共重合体は炉8Uし、
4ーヒドロキシベンゾイミダゾール、4ーヒドロキシベ
ンゾオキサゾール、4ーヒドロキシベンゾチアゾール又
は談議導体を徐々にアミノ基量の1〜10倍モル溶解し
た10%苛性ソーダ水溶液に加え−5〜1ぴ○で窒素雰
囲気中1〜2独特間燈拝してカップリングを完了する。
本発明で使用される前記一般式‘11で示される化合物
は例えば4−ヒドロキシベンゾィミダゾール、4ーヒド
ロキシベンゾオキサゾール、4ーヒドロキシベンゾチア
ゾール、4・6−ジヒドロキシベンゾイミダゾール、4
・6−ジヒドロキシベンゾオキサゾール、4・6ージヒ
ドロキシベンゾチアゾール等が挙げられる。
That is, the saturation amount is defined as the point at which the iodine starch paper shows a blue color and does not fade for more than a few minutes. According to this, the amount of amino groups that undergo diazotization in the core polyaminostyrene copolymer can be determined. The copolymer that has undergone diazotization is heated in a furnace of 8U,
4-Hydroxybenzimidazole, 4-hydroxybenzoxazole, 4-hydroxybenzothiazole, or a discussion conductor was gradually added to a 10% caustic soda aqueous solution containing 1 to 10 times the molar amount of amino groups dissolved in a nitrogen atmosphere at -5 to 1 pi○. During the 1st and 2nd year of junior high school, complete the coupling by performing a unique tokuhai.
The compounds represented by the general formula '11 used in the present invention are, for example, 4-hydroxybenzimidazole, 4-hydroxybenzoxazole, 4-hydroxybenzothiazole, 4,6-dihydroxybenzimidazole, 4
-6-dihydroxybenzoxazole, 4,6-dihydroxybenzothiazole, etc.

本発明の吸着剤の製造過程に於ける反応の確認及び分析
は次の方法により行なった。
Confirmation and analysis of reactions in the manufacturing process of the adsorbent of the present invention were performed by the following method.

即ち、ポリスチレン系共重合体のニトロ化反応に於いて
反応率はケルダール窒素分析法により窒素を測定し、こ
れからニトロ基の量を決定した。
That is, in the nitration reaction of a polystyrene copolymer, the reaction rate was determined by measuring nitrogen by Kjeldahl nitrogen analysis method, and the amount of nitro groups was determined from this.

又、ニトロ化されたポリスチレン系共重合体の赤外吸収
スペクトルは1520仇‐1、1340肌‐1にニトロ
基に由来する吸収を有する。又、ジアゾ化の際の亜硝酸
ソーダの飽和量からジアゾ化を受けるアミ/基の塁を測
定した。
In addition, the infrared absorption spectrum of the nitrated polystyrene copolymer has absorptions derived from nitro groups at 1520-1 and 1340-1. In addition, the number of amino groups/groups undergoing diazotization was determined from the saturation amount of sodium nitrite during diazotization.

これによりニトロ基の95〜100%がアミノ基に還元
されていることを確認した。更に前記ジアゾ化ポリアミ
ノスチレン系共重合体と前記一般式‘1に示す化合物の
カップリングの反応率は反応前後のカップリング成分含
有水溶液の吸光度を測定して決めることが出来る。
This confirmed that 95 to 100% of the nitro groups were reduced to amino groups. Further, the reaction rate of the coupling between the diazotized polyaminostyrene copolymer and the compound represented by the general formula '1' can be determined by measuring the absorbance of the aqueous solution containing the coupling component before and after the reaction.

吸光度の測定は350〜23仇仇の間で行い、極大吸収
を用いた方が正確である。
Absorbance measurements are made between 350 and 23 degrees, and it is more accurate to use the maximum absorption.

これから決められた反応率は、ジアゾ化を受けたアミノ
基量の25〜即%であった。本発明方法により得られる
吸着剤をケルダール法により窒素分析を行ない、この値
より推定したカップリング反応率は吸光度測定より求め
た反応率の10%誤差の範囲にあった。本発明方法によ
り得られる重金属吸着剤は水溶液中の鉄、ウラン、亜鉛
、銅、ニッケル、カドミウム、鉛、クロム、マンガン等
の重金属を吸着し、とりわけウラニルィオンに対し選択
性を示す。
The reaction rate determined from this was 25 to immediate % of the amount of diazotized amino groups. The adsorbent obtained by the method of the present invention was subjected to nitrogen analysis using the Kjeldahl method, and the coupling reaction rate estimated from this value was within a 10% error of the reaction rate determined from absorbance measurement. The heavy metal adsorbent obtained by the method of the present invention adsorbs heavy metals such as iron, uranium, zinc, copper, nickel, cadmium, lead, chromium, and manganese in an aqueous solution, and exhibits selectivity for uranylion in particular.

本発明方法により得られる吸着剤を使用して金属イオン
を吸着するに際しては、該イオン吸着剤をカラムに充填
して、又は繊維状、薄膜状等の形状で重金属イオン含有
水と適当時間接触せしめる。
When adsorbing metal ions using the adsorbent obtained by the method of the present invention, the ion adsorbent is packed in a column or in the form of a fiber, a thin film, etc. and brought into contact with heavy metal ion-containing water for an appropriate period of time. .

・また重金属イオン含有水が多量の
アルカリ、酸を含有する場合は賄4〜軸9.5に調整し
てから使用することが望ましい。
- Also, if the heavy metal ion-containing water contains a large amount of alkali or acid, it is desirable to adjust it to a value of 4 to 9.5 before use.

例えば産業廃水中の重金属を除去回収する場合は、水不
落怪物費を除去してからpHを5〜9に調整して使用す
ることが好ましい。重金属イオン含有水と接触せしめた
イオン吸着剤は酸(例えば硫酸、硝酸、塩酸等の滋酸)
又、金属によってはアルカリ(例えば苛性ソーダ、アン
モニア水等)、水溶性炭酸塩(例えば、炭酸ナトリウム
、炭酸アンモン等)、水溶性重炭酸塩(例えば重炭酸ナ
トリウム)等を含有する水溶液中に浸潰して吸着重金属
を脱離溶解して回収することができる。
For example, when removing and recovering heavy metals from industrial wastewater, it is preferable to adjust the pH to 5 to 9 after removing water from the water. The ion adsorbent that has been brought into contact with water containing heavy metal ions is an acid (e.g. sulfuric acid, nitric acid, hydrochloric acid, etc.)
Also, depending on the metal, it may be immersed in an aqueous solution containing alkali (e.g., caustic soda, aqueous ammonia, etc.), water-soluble carbonate (e.g., sodium carbonate, ammonium carbonate, etc.), water-soluble bicarbonate (e.g., sodium bicarbonate), etc. The adsorbed heavy metals can be desorbed, dissolved and recovered.

本発明方法により得られる重金属吸着剤は廃水処理或は
海水からの有用金属特にウランの回収等工業的利用価値
は極めて大きいのである。
The heavy metal adsorbent obtained by the method of the present invention has extremely high industrial utility value, such as wastewater treatment or recovery of useful metals, especially uranium, from seawater.

以下実施例について説明する。Examples will be described below.

実施例 1 1モル%のジビニルベンゼンを含有するスチレン1Mに
界面活性剤2夕(花王アトラス社製ェマール10を1夕
、共栄社油脂製/ニオラィトPN−12を1夕)を加え
て、250ccの水に乳化させ、窒素気流中過硫酸カリ
0.1夕を加えて80℃で激しく櫨拝する。
Example 1 To 1 M of styrene containing 1 mol % of divinylbenzene, add 2 parts of surfactant (1 night of Kao Atlas's EMAR 10, 1 night of Kyoeisha Yushi Co., Ltd./Niolite PN-12), and add 250 cc of water. Emulsify the mixture, add 0.1 tsp of potassium persulfate in a nitrogen stream, and heat vigorously at 80°C.

3世分後、1モル%のジピニルベンゼンを含むスチレン
70夕を1時間要して滴下し、更に、この系を5時間、
80℃で櫨梓する。
After 3 hours, 70 g of styrene containing 1 mol% dipinylbenzene was added dropwise over 1 hour, and the system was further heated for 5 hours.
Rinse at 80℃.

生じたラテツクスを濃塩酸を加えて破壊し、ポリスチレ
ン系共重合体を炉別、洗浄する。このポリスチレン系共
重合体粉末を乾燥し、7夕を濃硝酸15cc、濃硫酸4
0cc中に7ぴ○で燈拝しながら、2時間掛けて加え、
更に70午0で3の分、反応させた後砕氷に注ぐ。
The resulting latex is destroyed by adding concentrated hydrochloric acid, and the polystyrene copolymer is separated from the furnace and washed. This polystyrene-based copolymer powder was dried, and then mixed with 15 cc of concentrated nitric acid and 4 ml of concentrated sulfuric acid.
While worshiping the light with 7 pi○ in 0cc, add it for 2 hours,
After reacting for another 3 minutes at 70:00, pour over crushed ice.

この様にして得たニトロ化ポリスチレン系共重合体は十
分洗浄した後乾燥した。得られた共重合体中の全窒素量
をケルダール法により測定したところ10偽りサンプル
中0.65mMの窒素を含有していた。
The nitrated polystyrene copolymer thus obtained was thoroughly washed and then dried. The total amount of nitrogen in the obtained copolymer was measured by the Kjeldahl method, and it was found that the copolymer contained 0.65 mM of nitrogen in 10 false samples.

これからニトロ化率を計算すると、全ベンゼン核の鱗%
がニトロ化を受けていることになる。続いて該共重合体
をエタノール80cc、濃塩酸70cc中で塩化第一錫
2水塩10夕とに1■時間加熱還流した後口遇し、水洗
が苛性ソーダ洗浄後水洗して次にジアゾ化を行なう。
Calculating the nitration rate from this, the scale% of all benzene nuclei is
is undergoing nitration. Subsequently, the copolymer was heated under reflux for 1 hour in 80 cc of ethanol and 70 cc of concentrated hydrochloric acid over 10 minutes of stannous chloride dihydrate, washed with water, washed with caustic soda, washed with water, and diazotized. Let's do it.

全窒素量をケルダール法により測定した結果100Mサ
ンプル中、0.80mMの窒素を含有していた。
As a result of measuring the total nitrogen amount by Kjeldahl method, it was found that the 100M sample contained 0.80mM nitrogen.

従って、この値から計算すると、ニトロ基はほぼ完全に
アミノ基に還元されたと考えられる。このアミノ化ポリ
スチレン系共重合体1夕を水25cc、INの塩酸25
ccに懸濁し氷冷し5℃以下に保った儀、激しく蝿拝し
ながら、亜硝酸ソーダの1モル溶液を徐々に滴下し、7
.8ccでヨウ素デンプン試験紙は明瞭な青紫色を呈し
た。従ってこの値から全ニトロ基の殆んど全てが還元さ
れ、又アミ/基の97〜99%がジアゾ化を受けたと考
えられる。ジアゾ化を行なった共重合体は素遠くロ別し
氷水で洗浄する。
Therefore, when calculated from this value, it is considered that the nitro group is almost completely reduced to an amino group. This aminated polystyrene copolymer was mixed with 25 cc of water and 25 mL of hydrochloric acid.
Suspended in cc, cooled on ice and kept below 5℃, while stirring vigorously, a 1 molar solution of sodium nitrite was gradually added dropwise.
.. At 8 cc, the iodine starch test paper exhibited a clear blue-purple color. Therefore, it is considered from this value that almost all of the nitro groups were reduced and that 97 to 99% of the amide/groups were diazotized. The diazotized copolymer is thoroughly filtered and washed with ice water.

4ーヒドロキシベンズイミダゾ−ル3.4夕を10%苛
性ソーダ50ccに溶解し窒素雰囲気中で0〜3℃に保
った状態で、該ジアゾ化共重合体を少量ずつ加え、後0
℃で2錨時間燭拝し、カップリング反応を行なった。
4-Hydroxybenzimidazole was dissolved in 50 cc of 10% caustic soda, and the diazotized copolymer was added little by little while keeping the temperature at 0 to 3°C in a nitrogen atmosphere.
The coupling reaction was carried out by heating at ℃ for 2 hours.

反応終了後、粉末状樹脂をロ別し、水洗した後、風乾し
て吸着剤を得た。カップリング反応率は、反応前後の溶
媒中の4ーヒドロキシベンズィミダゾールの吸光度測定
から求めた。
After the reaction was completed, the powdered resin was filtered, washed with water, and air-dried to obtain an adsorbent. The coupling reaction rate was determined by measuring the absorbance of 4-hydroxybenzimidazole in the solvent before and after the reaction.

反応液lccをサンプリングし2%苛性ソーダで2.5
そとする。この吸光度を島津製作所製UV一200を用
いて25仇のに於いて測定した。これから計算すると3
0mMの4ーヒドロキシベンズィミダゾールが反応した
ことになる。従って、ジアゾ化を受けたアミノ基の滋%
がカップリング反応を行なったと考えられる。この様に
して得られた吸着剤に就いて、ウラン吸着テストを行な
った。
Sample the reaction solution LCC and add 2.5% caustic soda to
That's it. This absorbance was measured using UV-200 manufactured by Shimadzu Corporation at 25 meters. Calculating from this, 3
This means that 0mM of 4-hydroxybenzimidazole has reacted. Therefore, the percentage of diazotized amino groups
is thought to have performed the coupling reaction. A uranium adsorption test was conducted on the adsorbent thus obtained.

ウラン500山夕を硝酸ゥラニルとして添加した天然海
水5〆中に吸着剤100奴を入れ、30℃で24時間燈
梓後、吸着剤を炉3Uし乾燥した謎料を理学電機製ガイ
ガーフレックスSX蟹光X線分析菱贋によりウランを定
基した。
100 ml of adsorbent was added to 50 ml of natural seawater to which 500 uranium was added as uranyl nitrate, heated at 30°C for 24 hours, and the adsorbent was dried in a 3U oven using Geigerflex SX crab manufactured by Rigaku Denki. Uranium was determined by optical X-ray analysis.

その結果吸着剤10触り当り415r夕のウランを吸着
していた。これは吸着剤1夕当りに換算して4.15奴
を吸着したことになり又全ウランの斑%を回収したこと
になる。比較例として既知吸着剤であるチタン酸、レゾ
ルシンーヒ酸樹脂、2・4・6ートリアミノフェノール
ーグリオキザール樹脂の各々粉末10仇夕を吸着剤とし
て前記方法と同様に吸着テストを行なった結果をあわせ
て第1表に示す。但しチタン酸は四塩化チタン塩酸溶液
を苛性ソーダで中和して得られたものである。又、レゾ
ルシンーヒ酸樹脂はしゾルシンーヒ酸を通常の方法でホ
ルマリン重合して得られたものである。又、2・4・6
−トリアミノフェノールーグリオキザール樹脂は2・4
・6−トリアミノフェ/ールとグリオキザールを酸舷媒
で縮合重合して得られたものである。第1表 次に蟹光X線測定を行なった吸着剤をとり出し、IN塩
酸10ccに70℃で浸渡し、更にもう一度同様の処理
を行って、ウランを溶出させ液中のウランをフツ化ナト
リウム球法により紫外姿光を測定した結果溶出液中ウラ
ンは410ムタであった。
As a result, 415 r of uranium was adsorbed per 10 touches of adsorbent. This means that 4.15 tons of uranium were adsorbed per night of adsorbent, and that % of the total uranium was recovered. As a comparative example, we conducted an adsorption test in the same manner as in the above method using 10 powders of each of known adsorbents titanic acid, resorcinol-arsenic acid resin, and 2,4,6-triaminophenol-glyoxal resin as adsorbents. are shown in Table 1. However, titanic acid is obtained by neutralizing titanium tetrachloride hydrochloric acid solution with caustic soda. Further, resorcinol-arsenic acid resin is obtained by formalin polymerization of resorcinol-arsenic acid in a conventional manner. Also, 2, 4, 6
-Triaminophenol-glyoxal resin is 2.4
- Obtained by condensation polymerization of 6-triaminophenol and glyoxal in an acidic medium. Table 1 Next, the adsorbent subjected to crab light X-ray measurement was taken out and immersed in 10 cc of IN hydrochloric acid at 70°C, and the same treatment was performed once again to elute the uranium and remove the uranium from the solution using sodium fluoride. As a result of measuring ultraviolet light using a sphere method, the amount of uranium in the eluate was 410 Muta.

従って、この4−ヒドロキシベンズイミダゾールーァゾ
ースチレン樹脂に吸着されたウラン容易にほぼ完全に脱
着される。上記せる如く本発明による吸着剤は優れたウ
ラン吸着館をもち、その吸着速度、選択性の点でも非常
に良好であることが解る。
Therefore, the uranium adsorbed on the 4-hydroxybenzimidazole-azostyrene resin is easily and almost completely desorbed. As mentioned above, it can be seen that the adsorbent according to the present invention has an excellent uranium adsorption capacity and is also very good in terms of adsorption rate and selectivity.

実施例 2 スチレンージビニルベンゼン共重合体をジビニルベンゼ
ンのスチレンに対する仕込み比率を0〜.・40モル%
の間で変えて乳化重合せしめて共重合体を得た。
Example 2 A styrene-divinylbenzene copolymer was prepared at a charging ratio of divinylbenzene to styrene of 0 to .・40 mol%
A copolymer was obtained by emulsion polymerization while changing between

乳化重合は実施例1と同様に行い得られた共重合体のニ
トロ化、還元、ジアゾカップリングに就いても、実施例
1と同じ方法で行い、吸着剤を得た。ジアゾカップリン
グを行うに際して、4・6ージヒドロキシベンゾオキサ
ゾールを用いポリアミノスチレン系共重合体1夕に対し
、&0夕を反応させ、反応率は2技ぬ仇の吸光度で測定
した。縛られた吸着剤10仇9を鉛濃度1脚になる様に
硝酸鉛を添加した水溶液2そ中に入れ、室温で24時間
縄拝し、樹脂中の鉛を実施例1と同じく蟹光X線法によ
り定草した。この結果を第2表に示す。
Emulsion polymerization was carried out in the same manner as in Example 1, and nitration, reduction, and diazo coupling of the obtained copolymer were carried out in the same manner as in Example 1 to obtain an adsorbent. When carrying out the diazo coupling, 4,6-dihydroxybenzoxazole was used to react 100% of the polyaminostyrene copolymer with 100% of the polyaminostyrene copolymer, and the reaction rate was measured by the absorbance of 200% of the polyaminostyrene copolymer. The bound adsorbents 10 and 9 were placed in an aqueous solution containing lead nitrate so that the lead concentration was 1 foot, and the mixture was kept at room temperature for 24 hours. It was drawn up using the line method. The results are shown in Table 2.

第2表 第2表から藤る様にジピニルベンゼンの共重合比率が3
0モル%を超えるとジアゾ化当量は著しく低下し、実用
に適さなくなる。
Table 2 From Table 2, the copolymerization ratio of dipinylbenzene is 3.
If it exceeds 0 mol%, the diazotization equivalent decreases significantly, making it unsuitable for practical use.

又、同時に鉛の吸着量も相乗的に低下する倭向が見られ
る。又ジビニルベンゼンを含有しないポリスチレンは、
ニトロ化条件を緩和せざるを得ない為ポリマー中の官能
基は減少したと考えられる。即ち、ジビニルベンゼンの
共重合比率はスチレンに対し0.5〜30モル%の範囲
、更には0.5〜5モル%が袴に好ましいことがわかる
。実施例 3 スチレン85部に対し、クロルメチルスチレン25部を
混合し、窒素置換した封管中で過酸化ペンゾィルを開始
剤とし、80℃で魂重合を行ない得られたポリマーを1
80℃で溶融抜糸し、径10リの繊維とする。
At the same time, the amount of lead adsorbed also appears to be decreasing synergistically. Polystyrene that does not contain divinylbenzene is
It is thought that the number of functional groups in the polymer decreased because the nitration conditions had to be relaxed. That is, it can be seen that the copolymerization ratio of divinylbenzene to styrene is preferably in the range of 0.5 to 30 mol%, more preferably 0.5 to 5 mol% for the hakama. Example 3 85 parts of styrene was mixed with 25 parts of chloromethylstyrene, and polymerization was carried out at 80°C using penzoyl peroxide as an initiator in a sealed tube purged with nitrogen.
The fibers are melted and removed at 80°C to obtain fibers with a diameter of 10 liters.

これをジヱチレントリアミンの20%エタノール溶媒中
に浸簿し、3ぴ0で3時間燈拝した後、3時間掛けて7
ぴ0迄徐々に昇溢し、その後更に7ぴC2時間処理する
。この様にして得られた繊維を、実施例1と同様に、ニ
トロ化還元ジアゾカップリング反応を行なった。
This was immersed in a 20% ethanol solvent of diethylenetriamine, heated for 3 hours at 3-0, and then heated for 3 hours to 7
Gradually raise the temperature to 0 and then treat for 7 more hours for 2 hours. The fiber thus obtained was subjected to a nitration-reduction diazo coupling reaction in the same manner as in Example 1.

ジアゾカップリングを行なうに際して4−ヒドロキシベ
ンゾチアゾールを用い、繊維1のこ対し、30夕を反応
させ、反応率を26触れの吸光度により決定した。各反
応はニトロ化が全ベンゼン核の約90%でありジアゾ化
を受けたアミ/基は7.1wM/夕4ーヒドロキシベン
ゾチアゾールの反応量は2.8mMであった。
When carrying out the diazo coupling, 4-hydroxybenzothiazole was used to react 1 piece of fiber with 30 pieces of fiber, and the reaction rate was determined by absorbance at 26 pieces. In each reaction, about 90% of the total benzene nuclei were nitrated, and the diazotized amino/group was 7.1 wM/2.8 mM of the reacted amount of 4-hydroxybenzothiazole.

この繊維状吸着剤300雌を蓬1仇のカラムに5奴の長
さに充填した。
300 pieces of this fibrous adsorbent were packed into a 1 piece column to a length of 5 pieces.

硝酸第二鋼、塩化第二鉄、硝酸カドミウム、硝酸ウラニ
ル、塩化亜鉛、硝酸鉛、酢酸ニッケル、酢酸第二クロム
、硝酸マンガン(ロ)を用いて各重金属濃度が全て0.
1脚である水溶液を調整し、この5そを、上記カラムに
、2q寿間掛けて通液し、繊維に吸着した重金属を蟹光
X線分析法により定さした。
Ferric nitrate, ferric chloride, cadmium nitrate, uranyl nitrate, zinc chloride, lead nitrate, nickel acetate, chromic acetate, and manganese (b) nitrate were used to reduce the concentration of each heavy metal to 0.
An aqueous solution was prepared, and this solution was passed through the above column for 2 q of life, and the heavy metals adsorbed on the fibers were determined by crab light X-ray analysis.

その結果を第3表に示す。The results are shown in Table 3.

第3表 第3表から明らかな様に、該繊維の重金属吸着館は優れ
て居り、特にウラニルィオンはほぼ全;吸着したと考え
られる。
As is clear from Table 3, the heavy metal adsorption capacity of the fiber was excellent, and in particular, it is thought that almost all of the uranylion was adsorbed.

又重金属を吸着させた繊維から、重金属を脱着するに際
し、塩酸、硫酸、硝酸、苛性ソーダ、重炭酸ソーダ、炭
酸ソーダ、炭酸アンモニウムを用い各々に就いて脱着館
を検討した。
In addition, when desorbing heavy metals from fibers on which heavy metals have been adsorbed, desorption chambers were investigated using hydrochloric acid, sulfuric acid, nitric acid, caustic soda, bicarbonate of soda, soda carbonate, and ammonium carbonate.

脱着方法としては各0.9Y溶液25cc中に繊維吸着
剤100の夕を50℃、3の片穣綾し、この操作を2度
繰り返し、その後繊維中の重金属量を姿光X線分析によ
り測定した。その結果、塩酸、硫酸、硝酸を用いた場合
脱着率は各金属共96〜100%の間にあるが、塩酸を
用いた場合、鉛の脱着率は54%であった。実施例 4
実施例1で用いたポリアミノスチレン系共重合体を同様
の方法により凶4ーヒドロキシベンズィミダゾール、脚
4−ヒドロキシベンゾオキサゾ−ル、‘C14ーヒドロ
キシベンゾチアゾールを各々ジアゾカップリングさせ吸
着剤(A、B、C)を製造した。
As a desorption method, 100% of the fiber adsorbent was mixed in 25 cc of each 0.9Y solution at 50°C for 3 cycles, and this operation was repeated twice.Then, the amount of heavy metals in the fibers was measured by optical X-ray analysis. did. As a result, when hydrochloric acid, sulfuric acid, and nitric acid were used, the desorption rate for each metal was between 96 and 100%, but when hydrochloric acid was used, the desorption rate for lead was 54%. Example 4
The polyaminostyrene copolymer used in Example 1 was diazo-coupled with 4-hydroxybenzimidazole, 4-hydroxybenzoxazole, and 'C14-hydroxybenzothiazole in the same manner to form an adsorbent. (A, B, C) were produced.

この際、カップリング反応軍鰍ま実施例1と同様に測定
し、各々風41%、‘B}40%、‘C’39%であっ
た。実施例3で使用した重金属−塩を用い、各金属濃度
共0.5rM溶液とした水溶液5Z中に核吸着剤10仇
2を加え、2鴎時間、麹拝し、吸着金属土を姿光X線に
より求めた。結果を第4表に示す。
At this time, the coupling reaction was measured in the same manner as in Example 1, and the wind was 41%, 'B' was 40%, and 'C' was 39%, respectively. Using the heavy metal salts used in Example 3, 10 2 nuclear adsorbents were added to an aqueous solution 5Z in which each metal concentration was 0.5 rM, and the adsorbent was mixed for 2 hours. It was determined by the line. The results are shown in Table 4.

第4表 第4表に示した結果より明らかな様に、本発明方法によ
る吸着剤は重金属イオンの吸着に優れ特に鉄及びウラニ
ルィオンに対して選択性が大きい。
Table 4 As is clear from the results shown in Table 4, the adsorbent produced by the method of the present invention has excellent adsorption of heavy metal ions and particularly high selectivity for iron and uranyl ions.

Claims (1)

【特許請求の範囲】 1 ポリアミノスチレン系共重合体をジアゾ化した後
一般式(1) ▲数式、化学式、表等があります▼ (式中、RはH又はOHであり、XはS、O、又はNH
を示す)で表わされる4−ヒドロキシベンゾイミダゾー
ル、4−ヒドロキシベンゾオキサゾール、4−ヒドロキ
シベンゾチアゾール又は該誘導体をカツプリング反応せ
しめることを特徴とする重金属吸着剤の製造方法。
[Claims] 1. After diazotizing the polyaminostyrene copolymer
General formula (1) ▲There are mathematical formulas, chemical formulas, tables, etc.▼ (In the formula, R is H or OH, and X is S, O, or NH
A method for producing a heavy metal adsorbent, which comprises subjecting 4-hydroxybenzimidazole, 4-hydroxybenzoxazole, 4-hydroxybenzothiazole, or a derivative thereof to a coupling reaction.
JP10179476A 1976-08-25 1976-08-25 Manufacturing method of heavy metal adsorbent Expired JPS603082B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
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Publication Number Publication Date
JPS5326887A JPS5326887A (en) 1978-03-13
JPS603082B2 true JPS603082B2 (en) 1985-01-25

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Country Link
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Families Citing this family (22)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5530733Y2 (en) * 1974-06-28 1980-07-22
JPS5187213A (en) * 1975-01-25 1976-07-30 Iseki Agricult Mach TORAKUTAANIOKERUSOKOSOCHI
JPS5193527U (en) * 1975-01-25 1976-07-27
US4341281A (en) * 1980-03-03 1982-07-27 General Motors Corporation Split axle drive mechanism
JPS57202938U (en) * 1981-06-22 1982-12-24
JPS58422A (en) * 1981-06-22 1983-01-05 Kubota Ltd Car for riding and serving
JPS57204271U (en) * 1981-06-23 1982-12-25
JPS5833529A (en) * 1981-08-22 1983-02-26 Kubota Ltd Passenger service car
JPS5843864A (en) * 1981-09-10 1983-03-14 Kubota Ltd agricultural vehicle
JPS58171723U (en) * 1982-05-13 1983-11-16 ヤンマー農機株式会社 Traveling device of riding rice transplanter
JPS5935122U (en) * 1982-08-30 1984-03-05 株式会社クボタ Transmission device for mobile agricultural machinery
JPS5967174A (en) * 1982-10-07 1984-04-16 Kubota Ltd Movable agricutural machine
JPS5967173A (en) * 1982-10-08 1984-04-16 Kubota Ltd mobile agricultural machinery
JPS5978171U (en) * 1982-11-17 1984-05-26 株式会社クボタ Operating structure for running agricultural vehicles
JPS5992032U (en) * 1982-12-15 1984-06-22 ヤンマー農機株式会社 four wheel drive agricultural vehicle
JPS59167333A (en) * 1983-03-11 1984-09-20 Honda Motor Co Ltd Front and rear wheel drive four-wheel vehicle
JPS59145424U (en) * 1983-03-18 1984-09-28 株式会社クボタ Riding rice transplanter
JPS59145423U (en) * 1983-03-18 1984-09-28 株式会社クボタ Riding rice transplanter
JPS59216730A (en) * 1983-05-24 1984-12-06 Mitsubishi Agricult Mach Co Ltd Four-wheel-drive vehicle
JPS60169327A (en) * 1984-02-14 1985-09-02 Iseki & Co Ltd Running device of four wheel drive service car
JPS60183629U (en) * 1984-05-17 1985-12-05 ヤンマー農機株式会社 Wheel drive device for riding rice transplanter
CN110127762B (en) * 2019-05-17 2021-11-02 扬州大学 A method for recovering uranium oxide from uranium-containing wastewater

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Publication number Publication date
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