JPH0470948B2 - - Google Patents
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- Publication number
- JPH0470948B2 JPH0470948B2 JP58131179A JP13117983A JPH0470948B2 JP H0470948 B2 JPH0470948 B2 JP H0470948B2 JP 58131179 A JP58131179 A JP 58131179A JP 13117983 A JP13117983 A JP 13117983A JP H0470948 B2 JPH0470948 B2 JP H0470948B2
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- boron
- resin
- solution
- adsorption
- treatment
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Description
【発明の詳細な説明】
本発明はスチレン系共重合体を樹脂母体とする
ホウ素選択吸着樹脂を用いて、硬度成分および/
又は重金属成分を含有する溶液中のホウ素の吸着
処理或は高温溶液中のホウ素の吸着処理などにお
いて、安定した処理操作を行うための該樹脂の再
生方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention uses a boron selective adsorption resin having a styrene copolymer as a resin base to absorb hardness components and/or
The present invention also relates to a method for regenerating the resin for stable treatment operations such as boron adsorption treatment in solutions containing heavy metal components or boron adsorption treatment in high-temperature solutions.
ホウ素は天然に広く分布し、植物の成育にとつ
て必須の元素であるが、これが過剰に存在すると
植物の成長に悪影響を及ぼすことが知られてい
る。従つてホウ素を含有する地下水や地熱水、石
炭火力発電所からの廃水等をかんがい用水として
利用する場合には極力ホウ素濃度を低く抑える必
要がある。また海水中に溶存するマグネシウムを
原料とするマグネシウム製錬分野においてもそこ
に存在するホウ素は製品に対し種々の悪影響を及
ぼすためマグネシウム溶液中のホウ素除去も必要
である。 Boron is widely distributed in nature and is an essential element for plant growth, but it is known that excessive presence of boron has a negative effect on plant growth. Therefore, when using boron-containing groundwater, geothermal water, wastewater from coal-fired power plants, etc. as irrigation water, it is necessary to keep the boron concentration as low as possible. Furthermore, in the field of magnesium smelting, which uses magnesium dissolved in seawater as a raw material, it is necessary to remove boron from the magnesium solution, since boron present therein has various adverse effects on the product.
これらの塩類が共存する溶液とかアルカリ性溶
液からのホウ素の吸着処理においては、一般に用
いられている強塩基性および弱塩基性のアニオン
交換樹脂ではホウ素に対する選択吸着能が乏しく
実用に耐え得ない。 In the adsorption treatment of boron from solutions in which these salts coexist or alkaline solutions, commonly used strong and weak basic anion exchange resins have poor selective adsorption ability for boron and cannot be put to practical use.
近年、これらの溶液からホウ素を選択的に吸着
処理する目的で、スチレン系共重合体の樹脂母体
に下記一般式()で表わされるアミンにより官
能基を導入したホウ素選択吸着樹脂が
式中、n=1〜6(整数)、Rは−CH2〔―CH
(OH)〕―nCH2OH又はアルキル基を表わす。但
し、m=0〜6(整数)である。 In recent years, for the purpose of selectively adsorbing boron from these solutions, boron selective adsorption resins have been developed in which a functional group is introduced into a styrene copolymer resin matrix using an amine represented by the following general formula (). In the formula, n = 1 to 6 (integer), R is -CH 2 [-CH
(OH)]— n Represents CH 2 OH or an alkyl group. However, m=0 to 6 (integer).
開発され、これまでにこの種のものとしてダイヤ
イオンCRB−02(三菱化成工業(株)製、商品名)、
アンバーライトIRA−743(ロームアンドハース社
製、商品名)等が市販されている。これらは何れ
もホウ素に対し、極めて秀れた選択吸着能を示す
樹脂であるが、石炭火力発電所の廃水や海水から
採取した塩化マグネシウム溶液中に含まれるホウ
素除去のように、溶液中に共存塩としてカルシウ
ムやマグネシウム等の硬度成分および/又は鉄、
ニツケル等の重金属成分が存在する場合に、これ
らの樹脂をアルカリ溶液で再生して遊離アミン形
として用いると、硬度成分等の水酸化物の沈澱を
生じ、樹脂性能を低下させたり、樹脂層がブロツ
キングして固まるという問題がある。更にこれら
の樹脂を用いて、地熱発電所排水の如き、高温の
ホウ素含有液を処理すると官能基の熱劣化が起
り、吸着性能が経時的に低下するという問題もあ
る。Diaion CRB-02 (manufactured by Mitsubishi Chemical Industries, Ltd., product name),
Amberlite IRA-743 (manufactured by Rohm and Haas, trade name) and the like are commercially available. All of these are resins that exhibit extremely excellent selective adsorption ability for boron, but they coexist in solutions such as the removal of boron contained in magnesium chloride solutions collected from coal-fired power plant wastewater and seawater. Hardness components such as calcium and magnesium and/or iron as salt,
When heavy metal components such as nickel are present, if these resins are regenerated with an alkaline solution and used in the free amine form, hydroxides such as hardness components will precipitate, reducing resin performance and causing the resin layer to deteriorate. There is a problem with blocking and hardening. Furthermore, when these resins are used to treat high-temperature boron-containing liquids such as wastewater from geothermal power plants, there is a problem that thermal deterioration of the functional groups occurs and the adsorption performance deteriorates over time.
本発明者等は、このようなスチレン系共重合体
の樹脂母体に上記の一般式()で表わされるア
ミンにより官能基アミンを導入して得られるホウ
素選択吸着樹脂を用いて溶液中のホウ素を吸着処
理する際に生ずるこれらの問題を解決すべく鋭意
検討した結果、上記ホウ素選択吸着樹脂の官能基
アミンの中に、樹脂母体にアミンを反応させる過
程で生ずる塩基度の高い、中性塩分解能を示す部
分が存在し、これが硬度成分および/又は重金属
成分を含む溶液中のホウ素吸着処理の際にこれら
の水酸化物沈澱生成に関与していることを見い出
した。すなわち該樹脂を用いて溶液中のホウ素吸
着処理を行うに際し、アルカリ溶液で再生して樹
脂の官能基アミンを遊離形とし、次いで塩化ナト
リウム等の中性塩溶液を該樹脂と接触させて、該
樹脂の官能基アミン中の塩基度の高い中性塩分解
能を示す部分を塩負荷形としてから、硬度成分お
よび/又は重金属成分を含有する溶液中のホウ素
吸着処理に供するならば、硬度成分等の水酸化物
の生成がなく安定したホウ素吸着処理が行なえる
ことが判明した。更に該樹脂中の官能基アミン中
の塩基度の高い中性塩分解能を示す部分と塩基度
の低い酸吸着能しか示さない部分は、遊離アミン
形に於て熱安定性に差があり、塩基度の高い部分
は40℃以上で実質的に熱分解が起こる一方、塩基
度の低い部分は100℃以上でも安定である。とこ
ろが塩基度の高い部分を塩化ナトリウム等の中性
塩溶液と接触させて塩負荷形とすると熱安定性が
向上し、100℃以上でも実質的に使用に耐えるこ
とも判明した。 The present inventors used a boron selective adsorption resin obtained by introducing a functional amine represented by the above general formula () into the resin base of such a styrene-based copolymer to remove boron in a solution. As a result of intensive studies to solve these problems that occur during adsorption treatment, we found that the functional amine in the boron selective adsorption resin has the ability to decompose neutral salts with high basicity that are generated during the process of reacting the amine to the resin matrix. It has been found that there exists a portion exhibiting the following, and that this portion is involved in the formation of these hydroxide precipitates during boron adsorption treatment in a solution containing hardness components and/or heavy metal components. That is, when performing boron adsorption treatment in a solution using this resin, the functional amine of the resin is regenerated with an alkaline solution to make it into a free form, and then a neutral salt solution such as sodium chloride is brought into contact with the resin. If the part of the resin functional group amine that shows neutral salt decomposition ability with high basicity is made into a salt-loaded form and then subjected to boron adsorption treatment in a solution containing hardness components and/or heavy metal components, hardness components, etc. It was found that stable boron adsorption treatment could be performed without the generation of hydroxide. Furthermore, in the functional amine in the resin, there is a difference in thermal stability in the free amine form between the part with high basicity that shows neutral salt decomposition ability and the part with low basicity that shows only acid adsorption ability. The part with high basicity undergoes substantial thermal decomposition at temperatures above 40°C, while the part with low basicity remains stable even above 100°C. However, it has been found that when the highly basic part is brought into contact with a neutral salt solution such as sodium chloride to create a salt-loaded form, the thermal stability is improved and it can be practically used even at temperatures above 100°C.
本発明は、かゝる新規な知見に基づいて達成さ
れたものであり、スチレン系共重合体を樹脂母体
とするホウ素選択吸着樹脂による溶液中のホウ素
の吸着処理の安定した処理操作を行う方法を提供
するものである。 The present invention has been achieved based on such novel findings, and provides a method for stably adsorbing boron in a solution using a boron selective adsorption resin using a styrene copolymer as a resin base. It provides:
本発明について詳細に説明する。 The present invention will be explained in detail.
本発明で用いられるホウ素選択吸着樹脂とは、
スチレンをジビニルベンゼン等の架橋剤で共重合
させたものをクロロメチルメチルエーテル等でハ
ロメチル化した樹脂母体を、下記一般式()で
示される二級アミンでアミノ化して得られるもの
である。かゝる二級アミンとしては、N−メチル
−D−グルカミン、N−エチル−D−グルカミ
ン、N−メチル−D−ガラクタミン、N−メチル
−D−マンノサミン、ジ−l−アラビチルアミン
等が挙げられる。 The boron selective adsorption resin used in the present invention is
It is obtained by aminating a resin base obtained by copolymerizing styrene with a crosslinking agent such as divinylbenzene and halomethylating it with chloromethyl methyl ether or the like with a secondary amine represented by the following general formula (). Such secondary amines include N-methyl-D-glucamine, N-ethyl-D-glucamine, N-methyl-D-galactamine, N-methyl-D-mannosamine, di-l-arabitylamine, etc. can be mentioned.
n=1〜6(整数)、Rは−CH2〔―CH(OH)〕―n
CH2OH又はアルキル基を表わす。但し、m=0
〜6(整数)
アミノ反応は、通常実施されている方法により
行われる。例えば、ハロメチル化した樹脂母体を
ジオキサン、アセトン、メチルエチルケトン、ク
ロロホルム、ジクロルエタン等の適当な溶媒の存
在下20〜100℃の温度で2〜20時間アミンと反応
させれば良い。又スチレン系共重合体から成る樹
脂母体はいわゆるゲル型でもハイポーラス型でも
良い。 n = 1 to 6 (integer), R is -CH 2 [-CH(OH)] - n
Represents CH 2 OH or an alkyl group. However, m=0
~6 (integer) The amino reaction is performed by a commonly used method. For example, a halomethylated resin base may be reacted with an amine at a temperature of 20 to 100°C for 2 to 20 hours in the presence of a suitable solvent such as dioxane, acetone, methyl ethyl ketone, chloroform, dichloroethane, etc. Further, the resin matrix made of a styrene copolymer may be of a so-called gel type or a highly porous type.
これらのホウ素選択吸着樹脂の塩基度の高いア
ミン部分を部分的に塩負荷形にすることが必要で
あるが、部分的塩負荷方法としては、ホウ素吸着
処理を終了した樹脂に塩酸、硫酸等の酸溶液を接
触させて、樹脂に吸着しているホウ素を溶離した
後、苛性ソーダ、アンモニア等のアルカリ性溶液
で再生して樹脂の官能基アミンを遊離形とし、次
いで塩化ナトリウム、塩化カリ、硫酸ナトリウ
ム、硫酸カリウム等のアルカリ金属のハロゲン化
物もしくは硫酸塩から選ばれる中性塩溶液を樹脂
と接触させて、樹脂の官能基アミン中の塩基度の
高い中性塩分解能を有する部分に塩負荷を行な
う。塩負荷を行なう際に用いられる中性塩溶液の
濃度は、1〜10重量%の範囲で選定されれば良
く、また使用する量は樹脂官能基アミンの中性塩
分解容量を予め測定し、その量の1〜10倍量の範
囲で、ホウ素含有溶液中に共存する他の硬度成分
等の濃度、処理流速、処理温度等を考慮して適宜
選定される。このようにして部分塩負荷を施した
樹脂は、次いで原液中のホウ素の吸着処理に用い
られる。 It is necessary to partially salt-load the highly basic amine part of these boron selective adsorption resins, but as a partial salt-loading method, hydrochloric acid, sulfuric acid, etc. are added to the resin after boron adsorption treatment. After contacting with an acid solution to elute boron adsorbed on the resin, it is regenerated with an alkaline solution such as caustic soda or ammonia to free the functional amine of the resin, and then sodium chloride, potassium chloride, sodium sulfate, etc. A solution of a neutral salt selected from halides or sulfates of alkali metals such as potassium sulfate is brought into contact with the resin to load the salt into a portion of the functional amine of the resin that has a high basicity and has the ability to decompose a neutral salt. The concentration of the neutral salt solution used for salt loading may be selected within the range of 1 to 10% by weight, and the amount to be used should be determined by measuring the neutral salt decomposition capacity of the resin functional amine in advance. The amount is appropriately selected within the range of 1 to 10 times that amount, taking into consideration the concentration of other hardness components coexisting in the boron-containing solution, processing flow rate, processing temperature, etc. The resin thus partially salt-loaded is then used for adsorption treatment of boron in the stock solution.
本発明方法により部分的に塩負荷処理を施した
樹脂によりホウ素含有溶液を処理すれば、溶液中
に共存する硬度成分や重金属成分の水酸化物生成
によるブロツキングとか、処理液のPH上昇などを
生ずることなく安定した操作を行うことが出来、
しかも比較的高い温度の溶液も処理出来るのであ
る。更に又、本発明方法で処理すれば、吸着した
ホウ素の溶離に使用する酸の量を低減することが
出来、また、再生速度も早められるので、樹脂を
繰返し使用することを考慮すれば本発明方法は工
業的に極めて有用な方法である。 If a boron-containing solution is treated with a partially salt-loaded resin using the method of the present invention, blocking due to the formation of hydroxides of hardness components and heavy metal components coexisting in the solution, and an increase in the pH of the treatment solution will occur. You can perform stable operation without any trouble,
Furthermore, it is possible to process solutions at relatively high temperatures. Furthermore, if the method of the present invention is used, the amount of acid used to elute the adsorbed boron can be reduced and the regeneration rate can be accelerated. The method is industrially extremely useful.
次に、本発明方法を実施例により更に詳細に説
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。 Next, the method of the present invention will be explained in more detail with reference to Examples, but the present invention is not limited to the following Examples unless the gist thereof is exceeded.
実施例 1
ホウ素選択吸着樹脂ダイヤイオンCRB02〔スチ
レン−ジビニルベンゼン共重合体をハロメチル化
した樹脂母体に前記一般式()で示される二級
アミンにより官能基を導入した樹脂〕(三菱化成
工業(株)製、商品名)を遊離形で150ml採り、これ
を内径20mmφ長さ500mmφのジヤケツト付ガラス
製カラムに充填し、これに5%塩酸150mlをSV2
で流し、次いで脱塩水で押出水洗後、5%苛性ソ
ーダ150mlをSV2で流して再生する。次いで、脱
塩水で押出水洗を行なつた後、5wt%塩化ナトリ
ウム水溶液200mlをSV2で流し脱塩水で水洗し、
次いでカラムジヤケツトに60℃の温水を循環して
カラム内温度を60℃に保つた。これにホウ酸1.29
g/(225ppm:B換算)塩化ナトリウム1.3
g/、硫酸ナトリウム0.9g/、フツ化ナト
リウム0.03g/、硫酸マグネシウム0.3g/、
塩化カルシウム5.3g/を含むPH6.0の溶液を流
速SV15で通液してホウ素の吸着処理を行なつた。
この時カラムから流出する処理液中のホウ素濃度
をカーミン酸比色法で測定した所、処理液量
17Bed Volume(以下BVと略す)までは処理液
中のホウ素濃度は0.1ppm(B換算)以下でその後
徐々にホウ素の漏出が起こり、処理液中のホウ素
濃度が1ppm(B換算)までの処理液量は18BVで
あつた。この時の処理液のPHとホウ素の破過曲線
を図1に示す。処理液のPHは9前後に保たれ、硬
度成分の水酸化物による沈澱はみられなかつた。
処理液中のホウ素濃度10ppm(B換算)に達した
時点で通液を停止し、吸着したホウ素の溶離、再
生;塩負荷を行なつて再び原液を流してホウ素の
吸着処理を行なつた。以上の工程を合計10回繰り
返しても処理液中および樹脂層内での硬度成分の
水酸化物沈澱は見られず、安定した処理ができ
た。Example 1 Boron selective adsorption resin Diaion CRB02 [resin in which a functional group is introduced into a resin base obtained by halomethylating a styrene-divinylbenzene copolymer with a secondary amine represented by the general formula ()] (Mitsubishi Chemical Industries, Ltd.) Take 150ml of free form of 200ml (manufactured by ), trade name), fill it into a jacketed glass column with an inner diameter of 20mmφ and a length of 500mmφ, and add 150ml of 5% hydrochloric acid to it in SV2
After extruding and washing with demineralized water, 150 ml of 5% caustic soda was poured in with SV2 to regenerate. Next, after extrusion washing with demineralized water, 200ml of a 5wt% sodium chloride aqueous solution was poured through SV2, and the product was washed with demineralized water.
Next, 60°C hot water was circulated through the column jacket to maintain the column internal temperature at 60°C. This includes boric acid 1.29
g/(225ppm: B conversion) Sodium chloride 1.3
g/, sodium sulfate 0.9g/, sodium fluoride 0.03g/, magnesium sulfate 0.3g/,
Boron adsorption treatment was carried out by passing a pH 6.0 solution containing 5.3 g of calcium chloride at a flow rate of SV15.
At this time, when the boron concentration in the treated liquid flowing out from the column was measured using the carminic acid colorimetric method, the amount of treated liquid was
Up to 17Bed Volume (hereinafter abbreviated as BV), the boron concentration in the processing solution is below 0.1ppm (B conversion), after which boron leakage gradually occurs until the boron concentration in the processing solution reaches 1ppm (B conversion). The amount was 18 BV. Figure 1 shows the pH of the treatment solution and the breakthrough curve of boron at this time. The pH of the treatment solution was maintained at around 9, and no precipitation due to hydroxide, a hardness component, was observed.
When the boron concentration in the treatment solution reached 10 ppm (in terms of B), the flow of the solution was stopped, and the adsorbed boron was eluted and regenerated; salt loading was carried out, and the stock solution was passed again to perform the boron adsorption treatment. Even when the above steps were repeated a total of 10 times, no hydroxide precipitation of hardness components was observed in the treatment solution or in the resin layer, and stable treatment was achieved.
実施例 2
実施例1の試験が終了した樹脂とカラムをその
まま用いて、実施例1と同様の方法で樹脂を部分
塩負荷形とし、カラムジヤケツトに80℃の温水を
通してカラム内温度を80℃に保ち、これにホウ酸
0.57g/(100ppm;B換算)、塩化ナトリウム
0.2g/、硫酸ナトリウム0.3g/を含むPH5.0
の溶液を流速SV20で通液してホウ素の吸着処理
を行なつた。この時カラムから流出する処理液中
のホウ素の分析は実施例1と同様の方法で行なつ
た所、処理液量23.2BVまでは処理液中のホウ素
濃度は0.1ppm(B換算)以下でその後徐々にホウ
素の漏出が起こり、処理液中のホウ素濃度が
1ppm(B換算)までの処理液量26.0BVであつた。
処理液中のホウ素濃度が10ppm(B換算)に達し
た時点で通液を停止し、吸着したホウ素の酸によ
る溶離、アルカリによる再生、中性塩溶液による
部分塩負荷を行なつた後、再び原液を流してホウ
素の吸着処理を行なつた。この工程を50回繰り返
しても樹脂のホウ素の吸着能力に何らの変化もな
く安定して処理ができた。Example 2 Using the resin and column for which the test in Example 1 was completed, the resin was made into a partially salt-loaded form in the same manner as in Example 1, and the temperature inside the column was maintained at 80°C by passing 80°C hot water through the column jacket. , to which boric acid
0.57g/(100ppm; B conversion), sodium chloride
PH5.0 containing 0.2g/, sodium sulfate 0.3g/
The boron adsorption treatment was carried out by passing a solution of the above at a flow rate of SV20. At this time, analysis of boron in the treated liquid flowing out from the column was carried out in the same manner as in Example 1, and the boron concentration in the treated liquid was 0.1 ppm (B conversion) or less until the treated liquid amount was 23.2 BV. Boron gradually leaks out, and the boron concentration in the processing liquid increases.
The amount of processing liquid up to 1 ppm (B conversion) was 26.0 BV.
When the boron concentration in the treatment solution reached 10 ppm (B conversion), the flow was stopped, and the adsorbed boron was eluted with an acid, regenerated with an alkali, and partially salted with a neutral salt solution, and then the solution was poured again. Boron adsorption treatment was performed by flowing the stock solution. Even after repeating this process 50 times, there was no change in the resin's ability to adsorb boron, and the process was stable.
比較例 1
実施例2でホウ素の吸着処理を終えた樹脂をそ
のまま用いて同一カラム内で、5%塩酸150mlを
SV2で流し吸着しているホウ素を溶離し、次いで
脱塩水で押出水洗を行なつてから5%苛性ソーダ
150mlをSV2で流し再生し、脱塩水で押出水洗を
行なつた。Comparative Example 1 Using the resin that had been subjected to boron adsorption treatment in Example 2, 150 ml of 5% hydrochloric acid was added in the same column.
The adsorbed boron was eluted by flowing with SV2, then extrusion was washed with demineralized water, and then 5% caustic soda was added.
150 ml was regenerated by flowing through SV2, and the extrusion was washed with demineralized water.
次いで、実施例1と同一のホウ素含有溶液を60
℃で、SV15でカラムに供給し、ホウ素の吸着処
理をした。この時の処理液のPHとホウ素破過の様
子を図1に破線で示す。この場合通液開始当初処
理液PHが12となり、原液の硬度成分に由来する水
酸化物の白色沈澱が処理液中にみられた。次いで
吸着処理を終了した後、カラム内の樹脂を取り出
した所、樹脂に同様の水酸化物の沈澱が付着し、
樹脂がこれによつてブロツキングして固まつてい
た。 Next, the same boron-containing solution as in Example 1 was added to 60
It was supplied to a column at SV15 at ℃ and subjected to boron adsorption treatment. The pH of the treatment solution and the state of boron breakthrough at this time are shown in broken lines in Figure 1. In this case, the pH of the treatment solution was 12 at the beginning of the flow, and a white precipitate of hydroxide derived from the hardness component of the stock solution was observed in the treatment solution. After the adsorption treatment was completed, when the resin in the column was taken out, similar hydroxide precipitates were found on the resin.
This caused the resin to block and harden.
比較例 2
実施例1で用いたカラムにダイヤイオン
CRB02(三菱化成工業(株)製、商品名)を遊離形で
150ml充填し、これに5%塩酸150mlをSV2で流
し、次いで脱塩水で押出水洗し、次に5%苛性ソ
ーダ150mlをSV2で流し脱塩水で押出・水洗をし
て実施例2と同一のホウ素含有原液を80℃で
SV20で通液してホウ素吸着処理をした。カラム
からの処理液中のホウ素濃度が10ppm(B換算)
となつた時点で、通液を停止し、酸によるホウ酸
の溶離とアルカリによる再生を行なつて再び原液
を通してホウ素の吸着処理を行なうという工程を
50回繰り返して行なつた。この方法では樹脂中の
アミンの塩基度の高い熱安定性に乏しい部分がア
ルカリ溶液で完全に再生されて遊離形となるため
に繰り返しの回数が増すにつれて徐々にホウ素吸
着能力の低下が見られ、処理液中のホウ素の漏出
量が1ppm(B換算)となるまでの処理液量で比較
すると50回目のそれは1回目と比較して10.2%の
低下であつた。Comparative Example 2 Diamond ion was added to the column used in Example 1.
CRB02 (manufactured by Mitsubishi Chemical Industries, Ltd., trade name) in free form
Filled with 150 ml, poured 150 ml of 5% hydrochloric acid in SV2, then extruded and washed with demineralized water, then poured 150 ml of 5% caustic soda in SV2, extruded and washed with demineralized water to obtain the same boron-containing material as in Example 2. Stock solution at 80℃
Boron adsorption treatment was performed by passing liquid through SV20. Boron concentration in the treated liquid from the column is 10ppm (B conversion)
At this point, the flow of liquid is stopped, the boric acid is eluted with an acid, the boron is regenerated with an alkali, and the raw liquid is passed through again for boron adsorption treatment.
I did it 50 times. In this method, the part of the amine in the resin with high basicity and poor thermal stability is completely regenerated with an alkaline solution and becomes a free form, so as the number of repetitions increases, the boron adsorption capacity gradually decreases. Comparing the amount of processing solution until the leakage amount of boron in the processing solution reached 1 ppm (in terms of B), the amount at the 50th time was a decrease of 10.2% compared to the first time.
第1図は、ホウ素選択吸着樹脂によるホウ素吸
着処理における処理液のPH値とホウ素の破過曲線
を示すものであり、横軸は、処理液量(BV)
を、縦軸(右)は処理液のPH値を、同(左)は処
理液のホウ素濃度(ppm;B換算)を表わす。
Figure 1 shows the PH value of the treatment solution and the boron breakthrough curve in boron adsorption treatment using a boron selective adsorption resin, and the horizontal axis is the amount of treatment solution (BV).
The vertical axis (right) represents the PH value of the treatment liquid, and the vertical axis (left) represents the boron concentration (ppm; B conversion) of the treatment liquid.
Claims (1)
脂母体を下記一般式() 式中、n=1〜6(整数)、Rは −CH2〔―CH(OH)〕―nCH2OH 又はアルキル基を表わす。但し、m=0〜6(整
数)である。 で表わされるアミンでアミノ化して得られるホウ
素選択吸着樹脂を使用して溶液中のホウ素を吸着
処理するに際し、アルカリ溶液で再生して遊離ア
ミン形とした該樹脂を中性塩溶液と接触させ、該
樹脂の中性塩分解能を有するアミン部分を塩負荷
形として吸着処理に供することを特徴とするホウ
素選択吸着樹脂の再生方法。 2 ホウ素と硬度成分及び/又は重金属成分を含
む溶液からホウ素を吸着処理することを特徴とす
る特許請求の範囲第1項記載の方法。 3 ホウ素を含む溶液の温度が40℃以上であるこ
とを特徴とする特許請求の範囲第1項記載の方
法。[Scope of Claims] 1. A resin matrix obtained by haloalkylating a styrene copolymer according to the following general formula () In the formula, n=1 to 6 (integer), and R represents -CH2 [-CH(OH)]- nCH2OH or an alkyl group. However, m=0 to 6 (integer). When adsorbing boron in a solution using a boron selective adsorption resin obtained by amination with an amine represented by, the resin is regenerated into a free amine form with an alkaline solution and brought into contact with a neutral salt solution, A method for regenerating a selective boron adsorption resin, which comprises subjecting the resin to an adsorption treatment in the form of a salt-loaded amine portion having a neutral salt decomposition ability. 2. The method according to claim 1, wherein boron is adsorbed from a solution containing boron and a hardness component and/or a heavy metal component. 3. The method according to claim 1, wherein the temperature of the solution containing boron is 40°C or higher.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58131179A JPS6022934A (en) | 1983-07-19 | 1983-07-19 | Method for regenerating boron selective adsorption resin |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58131179A JPS6022934A (en) | 1983-07-19 | 1983-07-19 | Method for regenerating boron selective adsorption resin |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6022934A JPS6022934A (en) | 1985-02-05 |
| JPH0470948B2 true JPH0470948B2 (en) | 1992-11-12 |
Family
ID=15051851
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP58131179A Granted JPS6022934A (en) | 1983-07-19 | 1983-07-19 | Method for regenerating boron selective adsorption resin |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6022934A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2007106860A2 (en) * | 2006-03-15 | 2007-09-20 | Reaction Sciences, Inc. | Method for making silicon for solar cells and other applications |
-
1983
- 1983-07-19 JP JP58131179A patent/JPS6022934A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6022934A (en) | 1985-02-05 |
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