JP3993370B2 - Method for recovering Cr (V1) from anion exchange resin tower - Google Patents
Method for recovering Cr (V1) from anion exchange resin tower Download PDFInfo
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- JP3993370B2 JP3993370B2 JP2000268913A JP2000268913A JP3993370B2 JP 3993370 B2 JP3993370 B2 JP 3993370B2 JP 2000268913 A JP2000268913 A JP 2000268913A JP 2000268913 A JP2000268913 A JP 2000268913A JP 3993370 B2 JP3993370 B2 JP 3993370B2
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- 238000000034 method Methods 0.000 title claims description 26
- 239000003957 anion exchange resin Substances 0.000 title description 19
- 239000007788 liquid Substances 0.000 claims description 59
- 238000011069 regeneration method Methods 0.000 claims description 27
- 230000008929 regeneration Effects 0.000 claims description 21
- 238000005342 ion exchange Methods 0.000 claims description 15
- 229920006395 saturated elastomer Polymers 0.000 claims description 9
- 230000001172 regenerating effect Effects 0.000 claims description 5
- 238000001125 extrusion Methods 0.000 claims description 4
- 239000011651 chromium Substances 0.000 description 59
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 14
- 239000012141 concentrate Substances 0.000 description 8
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 7
- 229910052804 chromium Inorganic materials 0.000 description 7
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 6
- 150000002500 ions Chemical class 0.000 description 6
- 239000011347 resin Substances 0.000 description 6
- 229920005989 resin Polymers 0.000 description 6
- 239000012535 impurity Substances 0.000 description 5
- 239000003456 ion exchange resin Substances 0.000 description 5
- 229920003303 ion-exchange polymer Polymers 0.000 description 5
- 238000001179 sorption measurement Methods 0.000 description 5
- 238000005349 anion exchange Methods 0.000 description 4
- 150000001450 anions Chemical class 0.000 description 4
- 239000002994 raw material Substances 0.000 description 4
- WGLPBDUCMAPZCE-UHFFFAOYSA-N chromium trioxide Inorganic materials O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- 238000001514 detection method Methods 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000003729 cation exchange resin Substances 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- ZCDOYSPFYFSLEW-UHFFFAOYSA-N chromate(2-) Chemical compound [O-][Cr]([O-])(=O)=O ZCDOYSPFYFSLEW-UHFFFAOYSA-N 0.000 description 1
- KRVSOGSZCMJSLX-UHFFFAOYSA-L chromic acid Chemical class O[Cr](O)(=O)=O KRVSOGSZCMJSLX-UHFFFAOYSA-L 0.000 description 1
- 150000001844 chromium Chemical class 0.000 description 1
- 150000001845 chromium compounds Chemical class 0.000 description 1
- -1 chromium salts Chemical class 0.000 description 1
- 229940117975 chromium trioxide Drugs 0.000 description 1
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 description 1
- GAMDZJFZMJECOS-UHFFFAOYSA-N chromium(6+);oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[Cr+6] GAMDZJFZMJECOS-UHFFFAOYSA-N 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000007747 plating Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000012492 regenerant Substances 0.000 description 1
- 238000004904 shortening Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
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Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/10—Selective adsorption, e.g. chromatography characterised by constructional or operational features
- B01D15/20—Selective adsorption, e.g. chromatography characterised by constructional or operational features relating to the conditioning of the sorbent material
- B01D15/203—Equilibration or regeneration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction, e.g. ion-exchange, ion-pair, ion-suppression or ion-exclusion
- B01D15/361—Ion-exchange
- B01D15/363—Anion-exchange
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B34/00—Obtaining refractory metals
- C22B34/30—Obtaining chromium, molybdenum or tungsten
- C22B34/32—Obtaining chromium
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Organic Chemistry (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Life Sciences & Earth Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Treatment Of Liquids With Adsorbents In General (AREA)
- Manufacture And Refinement Of Metals (AREA)
Description
【0001】
【発明の属する技術分野】
本発明は、Cr(VI)、SO4 2- 、Cl-イオン等を吸着して吸着飽和したイオン交換樹脂から、Cr(VI)を高濃度で効率よく回収する方法及び回収装置に関する。
【0002】
【従来の技術】
クロメートあるいはクロムメッキ工場において発生する6価クロム含有水洗水の可搬式イオン交換塔による処理法として、陰イオン交換樹脂を充填したイオン交換塔にて有害なCr(VI)のみを吸着除去する方法、あるいは陽イオン交換樹脂と陰イオン交換樹脂とでカチオン、アニオン(Cr(VI)以外のアニオンも含む)を全て吸着除去し、処理水は純水として系内で再利用する方法がある。
【0003】
いずれの方法も、需要家で吸着飽和したイオン交換塔は、専用の車で集中再生場まで運び再生作業を行なう必要があった。集中再生場における再生方法は、通常、需要家で吸着飽和したイオン交換樹脂を充填したイオン交換塔を再生スタンドに並列に並べ、向流多段再生するという方法が採用されている。なお、需要家には代わりの再生済みのイオン交換塔が設置され、連続使用されることになる。
【0004】
回収したCr(VI)液は、三酸化クロム又はクロム化合物の製造原料として有効利用するのが環境保全の意味からも最も望ましい方法である。しかし、従来の向流多段再生法の場合、上述したように需要家で使用済みの吸着飽和した陰イオン交換樹脂には、Cr(VI)以外にSO4 2- 、Cl- イオン等も吸着している。このため、これらのイオンも回収Cr(VI)液中に混入してくるため、更に精製処理を施す必要が生じるという問題があった。
【0005】
【発明が解決しようとする課題】
本発明は、かかる事情に鑑みてなされたものであり、その課題とするところは回収したCr(VI)液中の不純物を容易に低減でき、クロム塩類の製造原料として使用可能となる方法及び装置を提供する。
【0006】
【課題を解決するための手段】
この課題を解決するために、本発明は、少なくともCr(VI)、SO4 2- 、及びCl- イオンを飽和吸着した陰イオン交換樹脂塔に、Cr( VI )濃度10g/L〜100g/LのCr(VI)濃厚液をpH6.5〜7.0に調整した後、通液してSO4 2- 、Cl-イオンを押し出す工程と、この工程の後、向流多段再生法を行なってCr(VI)のみを高濃度で回収する工程とを有する方法であって、前記押し出し工程は、Cr(VI)濃厚液として向流多段再生法で回収したCr(VI)高濃度液の一部を通液するCr(VI)の回収方法である。
【0009】
【発明の実施の形態】
以下、本発明を詳細に説明する。
本発明方法では、向流多段再生を行なう前に、需要家で吸着飽和した陰イオン交換樹脂塔に不純物の少ないCr(VI)濃厚液を通液し、吸着しているSO4 2- 、Cl- イオン等の押し出しを行なった後に、引き続き、向流多段再生を行なう。そして、使用するCr(VI)濃厚液は、一度、向流多段再生を行って得られたCr(VI)液を再使用することにより、新たな無水クロム酸等の購入が不要になる。また、向流多段再生はイオン交換塔を複数塔並べて同時再生を行うことにより、濃縮効率の向上、作業時間の短縮につながる。
【0010】
通液するCr(VI)濃厚液は、全ての使用済み陰イオン交換樹脂塔に同量通液する必要はなく、個々に通液量も異なるので個々に監視する必要がある。その理由は、需要家にて通液する液種、通液条件等によって、陰イオン交換樹脂へのCr(VI)吸着度合は様々であるからである。Cr(VI)イオンは有色イオンであるため、吸着すると、イオン交換樹脂の色が黄色あるいはオレンジ色に呈してくるので、Cr(VI)イオンが多く吸着して飽和したイオン交換塔の場合、通液するCr(VI)量は少なくてすみ、逆にCr(VI)イオンが少なく吸着しているような場合、通液量は多く必要となる。従って、樹脂の着色状況を容易に目視で確認できるようにイオン交換塔の側面には覗窓が上方及び下方に最低2箇所設けられていることが望ましい。なお、必要通液量を自動的に検知し、検知信号に基づいて通液の停止を行うことも可能である。
【0011】
Cr(VI)濃度は濃いほど、SO4 2- 、Cl- イオン等の不純物陰イオンを押出すのに効果がある。Cr(VI)濃度としては、できれば10g/L以上で濃いほどよいが、あまり濃すぎるとイオン交換樹脂は劣化する。又、イオン交換樹脂は有機物であるため、安全性の点から上限は100g/L以下が望ましい。
【0012】
また、Cr(VI)を吸着させるために通液するCr(VI)濃厚液のpHは酸性側に調整しておく必要がある。しかし、得られた回収液をクロム酸類の原料として使用する場合、回収液中のCl−,SO4 2−濃度を極力少なくするため、6.5〜7.0位が望ましい。pH調整用の酸としては、硫酸、又は塩酸が望ましい。その他、通液するCr(VI)濃厚液のCr(VI)濃度が低い場合、濃縮器で濃縮して使用するという方法も可能である。
【0013】
なお、通液するCr(VI) 濃厚液に懸濁物が含まれている場合、あらかじめフィルタープレスなどのろ過機にて除去しておく必要がある。
【0014】
【実施例】
本発明のCr(VI)の高濃度回収法について図1に示す実施例に基づき説明する。なお、図1は向流3段法での場合で、陰イオン交換樹脂塔には弱塩基性陰イオン交換樹脂が充填されている。
【0015】
(押出し工程)
まず、需要家で吸着飽和した陰イオン交換樹脂塔5を集中再生場に持ち込み、樹脂に付着した夾雑物を除去するため水洗浄を行なった後(ただし、図1には記載されていない)、再生スタンド17に配置接続する。再生スタンド17には他の需要家で使用済みのイオン交換塔6〜8も同様に所定の位置に配置接続する。
【0016】
Cr(VI)濃厚液タンク4には、硫酸溶液15でpH6.5に調整したCr(VI)濃厚液が入っており、この液をバルブ4a,ポンプ14を介してバルブ5a,5b,6a,6b,7a,7b,8a,8bを経由して所定位置に設置した4塔の陰イオン交換樹脂塔5〜8に同時に通液し、処理水はバルブ5c,5d,6c,6d,7c,7d,8c,8dを通り、さらにバルブ16aを介して排水16に流す(以後、クロム再吸着工程と称する。また、バルブの開閉については、特に指定しない限り、イオン交換塔上部及び下部接続用バルブ5a〜5d、7a〜7d、8a〜8dは、常時開いている状態とし、それ以外は記述した場合のみ開いている状態を示すものとする。)
通液終了の目安は、それぞれのイオン交換塔の処理水にCr(VI)濃厚液同様の色が目視で認められた時点で個々のイオン交換塔入口のバルブを閉め、全ての通液が終了した時点とする。以上でクロム再吸着工程は終了となり、次の向流多段再生工程へと移行する。
【0017】
ここで、クロム再吸着工程を行うために設置する陰イオン交換塔にCr(VI)液が多量に吸着していれば、Cr(VI)濃厚タンク4からの通液量が少なくてすみ、Cr(VI)濃厚タンク4の液量はあまり減ることがない。逆に、設置した陰イオン交換塔の樹脂にCr(VI)がほとんど吸着していなければ、クロム再吸着工程でCr(VI)濃厚タンク4から多量の液を通液する必要がある。
【0018】
(向流多段再生工程)
第1の再生液タンク1の液の一定量をバルブ1a,ポンプ13、バルブ13aを介してバルブ5a,5b,6a,6b,7a,7b,8a,8bを経由して所定位置に設置した4塔の陰イオン交換樹脂塔5〜8に同時通液した後、処理水はバルブ5c,5d,6c,6d,7c,7d,8c,8dを通り更にバルブ4bを通してCr(VI)濃厚液タンク4に入れる。この場合、Cr(VI)濃厚液タンク4には、クロム再吸着工程で減った液量だけ入り、補充されるので、クロム再吸着工程を行うために設置する陰イオン交換塔にCr(VI)液が多量に吸着している場合と、少量しか吸着していない場合とで、第1の再生液タンク1からの液補充量は異なることとなる。そして、第1の再生液タンク1の残存液は、バルブ1a,ポンプ13、バルブ13aを介してバルブ5a,5b,6a,6b,7a,7b,8a,8bを経由して所定位置に設置した4塔の陰イオン交換樹脂塔5〜8に同時通液した後、処理水はバルブ5c,5d,6c,6d,7c,7d,8c,8dを通り更にバルブ12aを通して回収液タンク12に入れる(これが、クロム塩類の原料用として利用されることとなる)。そして、第1の再生液タンク1は実質的に空になる。
【0019】
引き続き、第2の再生液タンク2の液は、バルブ2a,ポンプ13、バルブ13aを介してバルブ5a,5b,6a,6b,7a,7b,8a,8bを経由して4塔の陰イオン交換樹脂塔5〜8に通液した後、処理水はバルブ5c,5d,6c,6d,7c,7d,8c,8dを通り更にバルブ1bを介して空の第1の再生液タンク1に入る。この時、第2の再生液タンク2は実質的に空になる。
【0020】
同様に、第3の再生液タンク3の液は、バルブ3a,ポンプ13、バルブ13aを介してバルブ5a,5b,6a,6b,7a,7b,8a,8bを経由して4塔の陰イオン交換樹脂塔5〜8に通液した後、処理水はバルブ5c,5d,6c,6d,7c,7d,8c,8dを通り更にバルブ2bを介して空の第2の再生液タンク2に入る。ここでも第3の再生液タンク3は実質的に空になる。
【0021】
そして、エアー10のバルブ10aが開き、バルブ5a,5b,6a,6b,7a,7b,8a,8bを経由して4塔の陰イオン交換樹脂塔5〜8内のCr(VI)含有残液はバルブ5c,5d,6c,6d,7c,7d,8c,8dを通り更にバルブ3bを介して空の第3の再生液タンク3に入る。
【0022】
更に水11のバルブ11aが開き、バルブ5a,5b,6a,6b,7a,7b,8a,8bを経由して4塔の陰イオン交換樹脂塔5〜8内の陰イオン交換樹脂の表面に付着したCr(VI)液をバルブ5c,5d,6c,6d,7c,7d,8c,8dを通り更にバルブ3bを介して第3の再生液タンク3に入る。その後第3の再生液タンク3には苛性ソーダ溶液9がバルブ9aを介して所定量添加され濃度調整される。これまでの作業で向流多段再生工程は終了となり、以後は例えば、その位置で水洗を行うか、或いはイオン交換塔上部、下部のバルブ5b,5c,6b,6c,7b,7c,8b,8cを脱着して別の場所で水洗をおこなうことになる。
【0023】
なお、すでに述べたように、第1の再生タンク1の液をCr(VI)濃厚液タンク4に入れるか、回収液タンク12に回収するか、その液量をどのように調節するかは、陰イオン交換塔の樹脂に吸着したCr(VI)に依存し、ケースバイケースとなる。また、その切り替えは、Cr(VI)濃厚液タンク4内のCr(VI)濃厚液をどの程度使用したか(イオン交換塔にどの程度の量を通液したか)を検知手段で検知し、記憶しておき、この量だけ第1の再生タンク1の液をCr(VI)濃厚液タンク4に入れ、その後バルブなどのオンオフを切り替えて、回収液タンク12似いれるという操作を自動的に行うようにしても良い。
【0024】
参考までに本発明方法により得られた回収液タンク12の組成及び濃度の一例を従来法と共に下記表1に示す。
【0025】
【表1】
【0026】
【発明の効果】
本発明を実施することにより、需要家で使用済みの陰イオン交換樹脂塔からCr(VI)を高濃度でかつ不純物の少ない状態で回収することが可能になる。
【図面の簡単な説明】
【図1】本発明に係るCr(VI)の高濃度回収法の説明図。
【符号の説明】
1〜3…第1〜第3の再生液タンク
1a,1b,2a,2b,3a,3b,4a,4b,5a〜5d,6a〜6d,7a〜7d,8a〜8d,9a,10a,11a,12a,13a,16a...バルブ
4…Cr(VI)濃厚液タンク、
5〜8…陰イオン交換樹脂塔、
9…苛性ソーダ溶液、
10…エアー、
11…水、
12…回収液タンク、
13,14…ポンプ
15...硫酸溶液
16...排水
17...再生スタンド[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method and an apparatus for efficiently recovering Cr (VI) at a high concentration from an ion exchange resin adsorbed and saturated by adsorbing Cr (VI), SO 4 2− , Cl − ions, and the like.
[0002]
[Prior art]
A method of removing only harmful Cr (VI) with an ion exchange column filled with an anion exchange resin as a treatment method using a portable ion exchange column containing hexavalent chromium-containing flush water generated in a chromate or chrome plating plant, Alternatively, there is a method in which all cations and anions (including anions other than Cr (VI)) are adsorbed and removed with a cation exchange resin and an anion exchange resin, and treated water is reused as pure water in the system.
[0003]
In both methods, it was necessary to carry out the regeneration work by transporting the ion-exchange tower adsorbed and saturated by the customer to the central regeneration station using a dedicated vehicle. As a regeneration method in the concentrated regeneration field, a method is generally adopted in which ion exchange columns filled with ion exchange resin adsorbed and saturated by a customer are arranged in parallel on a regeneration stand, and countercurrent multistage regeneration is performed. In addition, instead of a regenerated ion exchange tower, the consumer will be used continuously.
[0004]
It is the most desirable method from the viewpoint of environmental protection to effectively use the recovered Cr (VI) liquid as a raw material for producing chromium trioxide or chromium compound. However, in the case of the conventional countercurrent multistage regeneration method, as described above, the adsorption-saturated anion exchange resin used by the consumer adsorbs SO 4 2− , Cl 2 − ions, etc. in addition to Cr (VI). ing. For this reason, since these ions are also mixed into the recovered Cr (VI) solution, there is a problem that further purification treatment needs to be performed.
[0005]
[Problems to be solved by the invention]
The present invention has been made in view of such circumstances, and the problem is that the impurities in the recovered Cr (VI) liquid can be easily reduced and can be used as a raw material for producing chromium salts. I will provide a.
[0006]
[Means for Solving the Problems]
In order to solve this problem, the present invention provides an anion exchange resin tower in which at least Cr (VI), SO 4 2− , and Cl 2 − ions are adsorbed in a saturated manner, with a Cr ( VI ) concentration of 10 g / L to 100 g / L. After adjusting the Cr (VI) concentrate of pH 6.5 to 7.0, the solution was passed through to extrude SO 4 2− and Cl 2 − ions, and after this step, a countercurrent multistage regeneration method was performed. A step of recovering only Cr (VI) at a high concentration, wherein the extruding step is a part of a Cr (VI) high concentration liquid recovered by a countercurrent multistage regeneration method as a Cr (VI) concentrated liquid This is a method for recovering Cr (VI) that is passed through.
[0009]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the present invention will be described in detail.
In the method of the present invention, before carrying out countercurrent multistage regeneration, a concentrated solution of Cr (VI) with a small amount of impurities is passed through an anion exchange resin tower adsorbed and saturated by a consumer, and adsorbed SO 4 2− , Cl - after performing the extrusion such as ions, subsequently, it performs the counter-current multi-stage regeneration. The Cr (VI) concentrate to be used does not require the purchase of new chromic anhydride or the like by reusing the Cr (VI) liquid obtained by once performing countercurrent multistage regeneration. Further, countercurrent multistage regeneration leads to improvement of concentration efficiency and shortening of working time by performing simultaneous regeneration by arranging a plurality of ion exchange columns.
[0010]
It is not necessary to pass the same amount of the Cr (VI) concentrate to be passed through all the used anion exchange resin towers, and it is necessary to monitor them individually because the flow rate is different. The reason is that the degree of adsorption of Cr (VI) on the anion exchange resin varies depending on the type of liquid that is passed through by the customer, the liquid passing conditions, and the like. Since Cr (VI) ions are colored ions, when adsorbed, the color of the ion exchange resin becomes yellow or orange. Therefore, in the case of an ion exchange column saturated with a large amount of Cr (VI) ions adsorbed, When the amount of Cr (VI) to be liquid is small, conversely, when a small amount of Cr (VI) ions are adsorbed, a large amount of liquid is required. Therefore, it is desirable that at least two viewing windows are provided on the side surface of the ion exchange tower at the upper side and the lower side so that the colored state of the resin can be easily visually confirmed. It is also possible to automatically detect the necessary flow rate and stop the flow based on the detection signal.
[0011]
The higher the Cr (VI) concentration, the more effective is the extrusion of impurity anions such as SO 4 2− and Cl 2 − ions. The Cr (VI) concentration is preferably as high as possible at 10 g / L or more, but if too high, the ion exchange resin deteriorates. Further, since the ion exchange resin is an organic substance, the upper limit is preferably 100 g / L or less from the viewpoint of safety.
[0012]
Moreover, it is necessary to adjust the pH of the concentrated Cr (VI) solution to be adsorbed for adsorbing Cr (VI) to the acidic side. However, when the recovered liquid obtained is used as a raw material for chromic acids, it is preferably about 6.5 to 7.0 in order to reduce the Cl − and SO 4 2− concentration in the recovered liquid as much as possible. As the acid for adjusting the pH, sulfuric acid or hydrochloric acid is desirable. In addition, when the Cr (VI) concentration of the concentrated Cr (VI) liquid is low, a method of concentrating it with a concentrator is also possible.
[0013]
In addition, when the suspended liquid is contained in the liquid Cr (VI) concentrated liquid, it is necessary to remove in advance with a filter such as a filter press.
[0014]
【Example】
The high concentration recovery method of Cr (VI) of the present invention will be described based on the embodiment shown in FIG. FIG. 1 shows the case of the countercurrent three-stage method, and the anion exchange resin tower is filled with a weakly basic anion exchange resin.
[0015]
(Extrusion process)
First, after bringing the anion
[0016]
The Cr (VI) concentrated liquid tank 4 contains Cr (VI) concentrated liquid adjusted to pH 6.5 with the
The standard for the end of the flow is to close the valves at the entrance of each ion exchange tower when the same color as the Cr (VI) concentrate is visually recognized in the treated water of each ion exchange tower, and all the liquid flow is completed. The time when The chromium re-adsorption process is thus completed, and the process proceeds to the next countercurrent multistage regeneration process.
[0017]
Here, if a large amount of Cr (VI) liquid is adsorbed on the anion exchange tower installed to perform the chromium re-adsorption step, the amount of liquid flowing from the Cr (VI) concentrated tank 4 can be reduced. (VI) The amount of liquid in the thick tank 4 does not decrease so much. On the contrary, if Cr (VI) is hardly adsorbed on the resin of the installed anion exchange tower, it is necessary to pass a large amount of liquid from the Cr (VI) rich tank 4 in the chromium re-adsorption step.
[0018]
(Countercurrent multistage regeneration process)
A fixed amount of the liquid in the first regenerative liquid tank 1 is installed at a predetermined position via a
[0019]
Subsequently, the liquid in the second regenerated liquid tank 2 is exchanged through four valves through the
[0020]
Similarly, the liquid in the third regenerating
[0021]
Then, the
[0022]
Further, the
[0023]
As already described, whether the liquid in the first regeneration tank 1 is put into the Cr (VI) concentrated liquid tank 4 or recovered in the recovered
[0024]
For reference, an example of the composition and concentration of the recovered
[0025]
[Table 1]
[0026]
【The invention's effect】
By carrying out the present invention, it is possible to recover Cr (VI) in a high concentration and low impurity state from an anion exchange resin tower that has been used by consumers.
[Brief description of the drawings]
FIG. 1 is an explanatory view of a high concentration recovery method of Cr (VI) according to the present invention.
[Explanation of symbols]
1-3 ... 1st-3rd regeneration liquid tank
1a, 1b, 2a, 2b, 3a, 3b, 4a, 4b, 5a-5d, 6a-6d, 7a-7d, 8a-8d, 9a, 10a, 11a, 12a, 13a, 16a. . . Valve 4 ... Cr (VI) concentrate tank,
5-8 ... anion exchange resin tower,
9 ... caustic soda solution,
10 ... Air,
11 ... water,
12 ... recovered liquid tank,
13, 14 ... pump 15. . .
Claims (2)
Priority Applications (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000268913A JP3993370B2 (en) | 2000-09-05 | 2000-09-05 | Method for recovering Cr (V1) from anion exchange resin tower |
| KR10-2001-0053918A KR100432132B1 (en) | 2000-09-05 | 2001-09-03 | Method Of Collecting Cr(Ⅵ) From Anion Exchange Resin and Collecting Apparatus |
| TW090121806A TW576753B (en) | 2000-09-05 | 2001-09-04 | Method of collection Cr(VI) from anion exchange resin column and collecting apparatus |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2000268913A JP3993370B2 (en) | 2000-09-05 | 2000-09-05 | Method for recovering Cr (V1) from anion exchange resin tower |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JP2002079115A JP2002079115A (en) | 2002-03-19 |
| JP3993370B2 true JP3993370B2 (en) | 2007-10-17 |
Family
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2000268913A Expired - Fee Related JP3993370B2 (en) | 2000-09-05 | 2000-09-05 | Method for recovering Cr (V1) from anion exchange resin tower |
Country Status (3)
| Country | Link |
|---|---|
| JP (1) | JP3993370B2 (en) |
| KR (1) | KR100432132B1 (en) |
| TW (1) | TW576753B (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100509250B1 (en) * | 2002-10-15 | 2005-08-23 | 삼원금속 주식회사 | Apparatus for recovering sexivalent chrome in chromium plating washing water and method thereof |
| JP2015174048A (en) * | 2014-03-17 | 2015-10-05 | 株式会社三進製作所 | Ion exchange resin tower and method for regenerating ion exchange resin |
| JP6247968B2 (en) * | 2014-03-17 | 2017-12-13 | 株式会社三進製作所 | Ion exchange resin regeneration device and ion exchange resin regeneration system |
-
2000
- 2000-09-05 JP JP2000268913A patent/JP3993370B2/en not_active Expired - Fee Related
-
2001
- 2001-09-03 KR KR10-2001-0053918A patent/KR100432132B1/en not_active Expired - Fee Related
- 2001-09-04 TW TW090121806A patent/TW576753B/en not_active IP Right Cessation
Also Published As
| Publication number | Publication date |
|---|---|
| KR100432132B1 (en) | 2004-05-17 |
| KR20020019396A (en) | 2002-03-12 |
| JP2002079115A (en) | 2002-03-19 |
| TW576753B (en) | 2004-02-21 |
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