Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP3757474B2 - Ion exchange resin regeneration method - Google Patents
[go: Go Back, main page]

JP3757474B2 - Ion exchange resin regeneration method - Google Patents

Ion exchange resin regeneration method Download PDF

Info

Publication number
JP3757474B2
JP3757474B2 JP19224096A JP19224096A JP3757474B2 JP 3757474 B2 JP3757474 B2 JP 3757474B2 JP 19224096 A JP19224096 A JP 19224096A JP 19224096 A JP19224096 A JP 19224096A JP 3757474 B2 JP3757474 B2 JP 3757474B2
Authority
JP
Japan
Prior art keywords
exchange resin
ion exchange
regenerating
polar solvent
aqueous solution
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 - Fee Related
Application number
JP19224096A
Other languages
Japanese (ja)
Other versions
JPH1033993A (en
Inventor
正二 森田
治良 山元
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.)
Toray Industries Inc
Original Assignee
Toray Industries Inc
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toray Industries Inc filed Critical Toray Industries Inc
Priority to JP19224096A priority Critical patent/JP3757474B2/en
Publication of JPH1033993A publication Critical patent/JPH1033993A/en
Application granted granted Critical
Publication of JP3757474B2 publication Critical patent/JP3757474B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Treatment Of Liquids With Adsorbents In General (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は性能の低下したイオン交換樹脂を回生する方法に関する。イオン交換樹脂は長期間の使用により有機汚染などにより性能が低下する。この低下した性能をもとに戻す操作が回生である。
【0002】
【従来の技術】
含水ε−カプロラクタム等の極性液体に含まれるアニリン等の弱塩基性、あるいはフェノール等の弱酸性の微量有機成分をイオン交換樹脂で吸着除去する場合、長期間使用すると有機汚染等によりイオン交換樹脂の吸着能力が低下する。性能が低下したイオン交換樹脂の回生は温食塩水等で処理するのが一般的であるが、含水ε−カプロラクタム等の極性液体を処理して有機汚染されたイオン交換樹脂はこの方法で回生できないため新品樹脂と交換しなければならなかった。
【0003】
【発明が解決しようとする課題】
従って、有機汚染されたイオン交換樹脂を回生する簡便な方法が必要である。
【0004】
【課題を解決するための手段】
前記課題は、性能の低下したイオン交換樹脂を、食塩を溶解した含水極性溶媒に接触させることを特徴とする回生方法によって解決される。
【0005】
以下、本発明の構成について詳細に説明する。
【0006】
【発明の実施の形態】
性溶媒の具体例としてエタノール、イソプロパノールなどのアルコール類、酢酸、プロピオン酸などの有機酸、ジメチルスルホキシドに代表されるスルホキシド類、N,N−ジメチルホルムアミド、ε−カプロラクタムなどの鎖状あるいは環状アミド類が挙げられるが、本発明ではラクタム、ジメチルスルホキシド、またはジメチルホルムアミドを用いる。なかでも、ジメチルスルホキシド、N,N−ジメチルホルムアミド、ε−カプロラクタムが好ましく、特にε−カプロラクタムが好ましい。
【0007】
本発明において、含水極性溶媒に溶解した食塩の濃度は通常0.1重量%〜20 重量%であるが、含水極性溶媒に対する飽和溶解度以下で実施するのが望まし い。例えば、含水極性溶媒としてε-カプロラクタム水溶液を使用した場合、水 分率と飽和食塩濃度の関係は式(1)で示される。
【0008】
Y=5.09X+46.1X2 (1)
式(1)において、Yは飽和食塩濃度(溶液に対する食塩の重量%)、Xは水分率(ε-カプロラクタム水溶液中の水の重量分率)である。
【0009】
本発明において、イオン交換樹脂のイオン形はH形(陽イオン交換樹脂)あるいはOH形(陰イオン交換樹脂)でも良いが、あらかじめ食塩水溶液に接触させてNa形(陽イオン交換樹脂)あるいはCl形(陰イオン交換樹脂)に変えた後、食塩を溶解した含水極性溶媒に接触させて回生することもできる。
【0010】
本発明において、含水極性溶媒中の水分濃度は通常10重量%〜90重量%の範囲で実施するのが望ましい。
【0011】
本発明で実施する回生の温度は、陽イオン交換樹脂の場合通常30℃〜120℃の範囲であるが、陰イオン交換樹脂単独または陽イオン交換樹脂と混合の場合は30℃〜80℃で実施するのが望ましい。
【0012】
本発明において、一度に接触させる食塩を溶解した含水極性溶媒の量は通常イオン交換樹脂に対して0.5〜20容量部で実施するのが望ましい。
【0013】
本発明で用いられるイオン交換樹脂は、強酸性陽イオン交換樹脂、弱酸性陽イオン交換樹脂、強塩基性陰イオン交換樹脂、弱塩基性陰イオン交換樹脂の何れでもよく、またゲル型、ポーラス型の何れでも良い。回生操作は、陽イオン交換樹 脂、陰イオン交換樹脂それぞれ単独、あるいは両者を混合して実施しても良く、樹脂と回生液の接触はカラム流通方式でも撹拌槽混合方式でも実施可能である。また、回生操作は一段、あるいは液を入替えて繰返し多段で実施することができる。
【0014】
【実施例】
次に、本発明を実施例によりさらに詳しく説明するが、本発明は以下の実施例に限定されるものではない。
【0015】
本実施例においてイオン交換樹脂の性能評価は、陽、陰イオン交換樹脂をそれぞれ10mlを温水ジャケット付イオン交換カラム(内径1cm)に均一に混合して充填し、アニリン50ppmを含有するε−カプロラクタム水溶液(水分濃度12.5重量%)を通液温度40℃、空塔通液速度SV=3で通液したとき、5 時間通液後の流出液中残存アニリン濃度で行った。
【0016】
本実施例においてアニリンの検出はガスクロマトグラフ(固定相液体:Thermon-3000、担体:Chromosorb W(AW−DMCS)、カラ ム:2mガラス、検出器:水素炎、アニリンの検出限界=0.3ppm)で行っ た。
【0017】
本実施例において使用したイオン交換樹脂の未使用樹脂および長期使用により性能が低下した樹脂の再生品(陽イオン交換樹脂は10重量%塩酸水溶液を空塔通液速度SV=3で1時間通液してH形に、陰イオン交換樹脂は5重量%の苛性ソーダ水溶液を空塔通液速度SV=3で1時間通液してOH形に再生し、さらにイオン交換水を空塔通液速度SV=10で1時間通液して洗浄した)の5時間通液後の流出液中アニリン濃度はそれぞれ検出限界以下(≦0.3ppm)および1 2.5ppmであった。
【0018】
実施例1
長期使用によって吸着能力が低下したマクロポーラス型強酸性陽イオン交換樹脂(レバチット SP112;三井東圧ファイン株式会社)およびポーラス型強塩 基性陰イオン交換樹脂(ダイヤイオン PA 308;三菱化学株式会社)それぞれ30mlを内径1cmのカラムに別々に詰め、10重量%の食塩水を空塔通液速度SV=3で1時間通液し陽イオン交換樹脂はNa形、陰イオン交換樹脂はCl形に変換した。還流冷却器付の内容積200mlのナス型フラスコに水切した上記イオン交換樹脂15mlを採取し、ε−カプロラクタム:水:食塩の組成が70:27:3重量部である回生液75mlを加え80℃で8時間加熱処理し た。
【0019】
樹脂を水洗後、内径1cmのガラスカラムに詰め、陽イオン交換樹脂は10重量%塩酸水溶液でH形に、陰イオン交換樹脂は5重量%の苛性ソーダ水溶液を空塔通液速度SV=3で1時間通液してOH形に再生し、さらにイオン交換水を空塔通液速度SV=10で1時間通液して洗浄した。
【0020】
回生、再生した陽、陰イオン交換樹脂をそれぞれ10ml採取し、温水ジャケット付イオン交換カラム(内径1cm)に均一に混合して充填し、アニリン50ppmを含有するε−カプロラクタム水溶液(水分濃度12.5重量%)を通液温 度40℃、空塔通液速度SV=3で通液した。5時間通液後の流出液中アニリン濃度は0.9ppmであった。
【0021】
比較例1
回生液を食塩を含まないε−カプロラクタム水溶液(水分濃度30重量%)に変更した以外実施例1と全く同様に処理した。5時間通液後の流出液中アニリン濃度は12ppmであった。
【0022】
比較例2
回生液をε−カプロラクタムを含まない10重量%の食塩水に変更した以外実施例1と全く同様に処理した。5時間通液後の流出液中アニリン濃度は12.5p pmであった。
【0023】
【発明の効果】
本発明によれば、従来回生不可能であった有機汚染されたイオン交換樹脂を、食塩を溶解した含水極性溶媒と接触させるという簡便な方法で回生可能であり、イオン交換樹脂の交換に伴う交換費用および産業廃棄物の発生を低減できる。
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for regenerating an ion exchange resin with reduced performance. The performance of ion exchange resins deteriorates due to organic contamination due to long-term use. The operation to restore this reduced performance is regeneration.
[0002]
[Prior art]
When adsorbing and removing weakly basic organic substances such as aniline or weakly acidic organic substances such as phenol contained in polar liquids such as hydrous ε-caprolactam with ion exchange resins, ion exchange resin Adsorption capacity decreases. Regeneration of ion-exchange resins with reduced performance is generally treated with warm saline, but ion-exchange resins contaminated with organic liquids by treating polar liquids such as hydrous ε-caprolactam cannot be regenerated by this method. Therefore, it had to be replaced with a new resin.
[0003]
[Problems to be solved by the invention]
Therefore, there is a need for a simple method for regenerating an organic contaminated ion exchange resin.
[0004]
[Means for Solving the Problems]
The above-mentioned problem is solved by a regenerative method characterized in that an ion exchange resin having a reduced performance is brought into contact with a hydrous polar solvent in which sodium chloride is dissolved.
[0005]
Hereinafter, the configuration of the present invention will be described in detail.
[0006]
DETAILED DESCRIPTION OF THE INVENTION
Alcohols such as ethanol, isopropanol Specific examples of polar solvents, acetic acid, organic acids such as propionic acid, sulfoxides represented by dimethyl sulfoxide, N, N- dimethylformamide, chain or cyclic amides such as ε- caprolactam Although class is Ru and the like, lactams in the present invention, dimethyl sulfoxide or dimethylformamide, is used. Of these, dimethyl sulfoxide, N, N-dimethylformamide, and ε-caprolactam are preferable, and ε-caprolactam is particularly preferable.
[0007]
In the present invention, the concentration of sodium chloride dissolved in the hydrous polar solvent is usually from 0.1% by weight to 20% by weight, but it is desirable that the concentration be less than the saturation solubility in the hydrous polar solvent. For example, when an ε-caprolactam aqueous solution is used as the hydrous polar solvent, the relationship between the water fraction and the saturated salt concentration is expressed by the formula (1).
[0008]
Y = 5.09X + 46.1X 2 (1)
In the formula (1), Y is a saturated salt concentration (% by weight of salt with respect to the solution), and X is a moisture content (weight fraction of water in the ε-caprolactam aqueous solution).
[0009]
In the present invention, the ion form of the ion exchange resin may be H form (cation exchange resin) or OH form (anion exchange resin), but it is previously contacted with a saline solution to form Na form (cation exchange resin) or Cl form. After changing to (anion exchange resin), it can be regenerated by contacting with a hydrous polar solvent in which sodium chloride is dissolved.
[0010]
In the present invention, the water concentration in the hydrated polar solvent is preferably 10 to 90% by weight.
[0011]
The temperature of regeneration carried out in the present invention is usually in the range of 30 ° C. to 120 ° C. in the case of a cation exchange resin, but is carried out at 30 ° C. to 80 ° C. in the case of an anion exchange resin alone or mixed with a cation exchange resin. It is desirable to do.
[0012]
In the present invention, the amount of the hydrous polar solvent in which the salt to be contacted at one time is usually preferably 0.5 to 20 parts by volume with respect to the ion exchange resin.
[0013]
The ion exchange resin used in the present invention may be any of strong acid cation exchange resin, weak acid cation exchange resin, strong base anion exchange resin, weak base anion exchange resin, and gel type and porous type. Any of these may be used. The regenerative operation may be carried out by cation exchange resin and anion exchange resin alone or by mixing both, and the contact between the resin and the regenerative liquid can be carried out by a column flow system or a stirring tank mixing system. Further, the regenerative operation can be carried out in one stage or repeatedly in multiple stages by changing the liquid.
[0014]
【Example】
EXAMPLES Next, although an Example demonstrates this invention further in detail, this invention is not limited to a following example.
[0015]
In this example, the performance evaluation of the ion exchange resin was carried out by uniformly mixing 10 ml of cation and anion exchange resin into an ion exchange column (inner diameter 1 cm) with a warm water jacket, and an ε-caprolactam aqueous solution containing 50 ppm of aniline. (Water concentration 12.5% by weight) When passing through at a passing temperature of 40 ° C. and a superficial flow rate SV = 3, the remaining aniline concentration in the effluent after passing through for 5 hours was used.
[0016]
In this example, aniline was detected by gas chromatography (stationary phase liquid: Thermon-3000, carrier: Chromosorb W (AW-DMCS), column: 2 m glass, detector: hydrogen flame, detection limit of aniline = 0.3 ppm). I went there.
[0017]
Reused product of the ion exchange resin used in this example and a resin whose performance deteriorated due to long-term use (a cation exchange resin was passed through a 10% by weight hydrochloric acid aqueous solution for 1 hour at a superficial flow rate of SV = 3). Then, the anion exchange resin is regenerated to the OH form by passing 5% by weight of caustic soda aqueous solution at the superficial flow rate SV = 3 for 1 hour, and the deionized water is fed to the superficial flow rate SV. The concentration of aniline in the effluent after 5 hours of passing through (= 10 for 1 hour and washing) was below the detection limit (≦ 0.3 ppm) and 12.5 ppm, respectively.
[0018]
Example 1
Macroporous strongly acidic cation exchange resin (Lebatit SP112; Mitsui Toatsu Fine Co., Ltd.) and porous strong salt-based anion exchange resin (Diaion PA 308; Mitsubishi Chemical Co., Ltd.) whose adsorptive capacity has been reduced by long-term use 30 ml each is packed separately in a 1 cm inner diameter column and 10% by weight saline is passed for 1 hour at a superficial flow rate of SV = 3 to convert the cation exchange resin into Na form and the anion exchange resin into Cl form. did. 15 ml of the above ion-exchange resin drained into a 200-ml eggplant type flask equipped with a reflux condenser was collected, and 75 ml of regenerative liquid having a composition of ε-caprolactam: water: sodium salt of 70: 27: 3 parts by weight was added to 80 ° C. For 8 hours.
[0019]
After washing the resin with water, it is packed in a glass column having an inner diameter of 1 cm. The cation exchange resin is 10% by weight hydrochloric acid aqueous solution in H form, and the anion exchange resin is 5% by weight caustic soda aqueous solution at a superficial flow rate SV = 3. The solution was passed through for a period of time to regenerate the OH form, and the ion-exchanged water was further passed through at a superficial flow rate SV = 10 for 1 hour for washing.
[0020]
10 ml each of regenerated, regenerated cation and anion exchange resins are collected, uniformly mixed and packed in an ion exchange column with a warm water jacket (inner diameter 1 cm), and an ε-caprolactam aqueous solution (moisture concentration of 12.5) containing 50 ppm of aniline. (Weight%) was passed through at a liquid passing temperature of 40 ° C. and an empty liquid passing speed SV = 3. The aniline concentration in the effluent after passing through for 5 hours was 0.9 ppm.
[0021]
Comparative Example 1
The regenerated solution was treated in the same manner as in Example 1 except that the aqueous solution was changed to an ε-caprolactam aqueous solution (water concentration 30% by weight) containing no salt. The aniline concentration in the effluent after passing through for 5 hours was 12 ppm.
[0022]
Comparative Example 2
The regenerated solution was treated in the same manner as in Example 1 except that the regenerated solution was changed to 10% by weight saline without ε-caprolactam. The aniline concentration in the effluent after passing through for 5 hours was 12.5 ppm.
[0023]
【The invention's effect】
According to the present invention, an organic-contaminated ion exchange resin that cannot be regenerated in the past can be regenerated by a simple method of contacting with a polar hydrous solvent in which sodium chloride is dissolved. Costs and industrial waste generation can be reduced.

Claims (8)

極性溶媒に含まれる微量有機成分を吸着除去して有機汚染されたイオン交換樹脂を回生する際に、イオン交換樹脂を食塩を溶解した含水極性溶媒に接触させるイオン交換樹脂の回生方法であって、含水極性溶媒がラクタム水溶液、ジメチルスルホキシド水溶液、またはジメチルホルムアミド水溶液であることを特徴とするイオン交換樹脂の回生方法。When regenerating an organic-contaminated ion exchange resin by adsorbing and removing trace organic components contained in a polar solvent, the ion exchange resin is regenerated by contacting the ion exchange resin with a hydrous polar solvent in which sodium chloride is dissolved , A method for regenerating an ion exchange resin, wherein the hydrous polar solvent is a lactam aqueous solution, a dimethyl sulfoxide aqueous solution, or a dimethylformamide aqueous solution . あらかじめイオン交換樹脂を食塩水溶液に接触させた後、食塩を溶解した含水極性溶媒に接触させることを特徴とする請求項1記載のイオン交換樹脂の回生方法。2. The method for regenerating an ion exchange resin according to claim 1, wherein the ion exchange resin is previously brought into contact with a saline solution and then brought into contact with a hydrous polar solvent in which the salt is dissolved. イオン交換樹脂がε−カプロラクタム水溶液に含まれるアニリンを吸着除去して有機汚染されたものであることを特徴とする請求項1または2記載のイオン交換樹脂の回生方法。 The method for regenerating an ion exchange resin according to claim 1 or 2, wherein the ion exchange resin is organically contaminated by adsorbing and removing aniline contained in the ε-caprolactam aqueous solution . 含水極性溶媒に溶解した食塩の濃度が0.1重量%〜20重量%である請求項1〜3のいずれか1項記載のイオン交換樹脂の回生方法。The method for regenerating an ion exchange resin according to any one of claims 1 to 3, wherein the concentration of sodium chloride dissolved in the hydrous polar solvent is 0.1 wt% to 20 wt%. 含水極性溶媒の水分濃度が10重量%〜90重量%である請求項1〜4のいずれか1項記載のイオン交換樹脂の回生方法。The method for regenerating an ion exchange resin according to any one of claims 1 to 4, wherein the moisture concentration of the hydrous polar solvent is 10 wt% to 90 wt%. 接触させる温度が、陽イオン交換樹脂を回生する場合30℃〜120℃、陰イオン交換樹脂を回生する場合30℃〜80℃、陽イオン交換樹脂と陰イオ ン交換樹脂との混合物を回生する場合30℃〜80℃である請求項1〜5のいずれか1項記載のイオン交換樹脂の回生方法。When regenerating the cation exchange resin, the contact temperature is 30 ° C to 120 ° C. When regenerating the anion exchange resin, 30 ° C to 80 ° C. When regenerating the mixture of the cation exchange resin and the anion exchange resin. It is 30 degreeC-80 degreeC, The regeneration method of the ion exchange resin of any one of Claims 1-5. 接触させる食塩を溶解した含水極性溶媒の量がイオン交換樹脂に対して0.5〜20容量部である請求項1〜6のいずれか1項記載のイオン交換樹脂の回生方法。The method for regenerating an ion exchange resin according to any one of claims 1 to 6, wherein the amount of the hydrous polar solvent in which the salt to be contacted is 0.5 to 20 parts by volume with respect to the ion exchange resin. 含水極性溶媒がε−カプロラクタム水溶液である請求項1〜7のいずれか1項記載のイオン交換樹脂の回生方法。The method for regenerating an ion exchange resin according to any one of claims 1 to 7, wherein the hydrous polar solvent is an aqueous ε-caprolactam solution.
JP19224096A 1996-07-22 1996-07-22 Ion exchange resin regeneration method Expired - Fee Related JP3757474B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP19224096A JP3757474B2 (en) 1996-07-22 1996-07-22 Ion exchange resin regeneration method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP19224096A JP3757474B2 (en) 1996-07-22 1996-07-22 Ion exchange resin regeneration method

Publications (2)

Publication Number Publication Date
JPH1033993A JPH1033993A (en) 1998-02-10
JP3757474B2 true JP3757474B2 (en) 2006-03-22

Family

ID=16287996

Family Applications (1)

Application Number Title Priority Date Filing Date
JP19224096A Expired - Fee Related JP3757474B2 (en) 1996-07-22 1996-07-22 Ion exchange resin regeneration method

Country Status (1)

Country Link
JP (1) JP3757474B2 (en)

Also Published As

Publication number Publication date
JPH1033993A (en) 1998-02-10

Similar Documents

Publication Publication Date Title
EP0196173B1 (en) Removal of iodide compounds from non-aqueous organic media
KR100231623B1 (en) Process for removing iodide compounds from carboxylic acids and carboxylic acid anhydrides
JP4302201B2 (en) Method for purification of substantially anhydrous organic liquids
CN105849038B (en) The refining methd of the production method and aqueous hydrogen peroxide solution of anion exchanger and cation exchange column mixture and mixed bed
JP2004181351A (en) Method for refining non-aqueous liquid material
JP3757474B2 (en) Ion exchange resin regeneration method
JP2003048716A (en) Method for recovering molybdate
US4828810A (en) Removal of low level ethylene oxide contaminants by treatment of contaminated gases with cationic exchange resins at gas-solid interface reaction conditions
US5484511A (en) Process for the removal of impurities from hydrazine hydrate
JP2000202442A (en) Method for separating and recovering boron in boron-containing water
CN101928048A (en) A method for purifying humic acid pollutants in water by using polyaniline
JPH07206804A (en) Taurine purification method
Sargent et al. Reversible sorbents for organic acids and amines
SU1143694A1 (en) Method of cleaning waste water from organic compounds
SU829128A1 (en) Method of cleaning saline solutions and sewage from organic compounds
CA2159183C (en) Resin regeneration process
JPS621307B2 (en)
JP2664495B2 (en) Method for purification or regeneration of contaminated or used process sulfolane
SU159512A1 (en)
JPS5924663B2 (en) Solution processing method
JPH02295499A (en) Device for desalting and purifying sucrose solution
JPS6352018B2 (en)
JPS583639A (en) Fluorine disposing agent
JPH01119344A (en) Method for reducing eluates from strongly acidic cation exchange resins
JP2002059002A (en) Regeneration method of synthetic adsorbent

Legal Events

Date Code Title Description
A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20050815

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20050906

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20051102

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20051206

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20051219

LAPS Cancellation because of no payment of annual fees