JPS6124479B2 - - Google Patents
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- JPS6124479B2 JPS6124479B2 JP52152440A JP15244077A JPS6124479B2 JP S6124479 B2 JPS6124479 B2 JP S6124479B2 JP 52152440 A JP52152440 A JP 52152440A JP 15244077 A JP15244077 A JP 15244077A JP S6124479 B2 JPS6124479 B2 JP S6124479B2
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- water
- ion exchange
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- Treatment Of Water By Ion Exchange (AREA)
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Description
本発明は電着塗装廃液の処理方法に関するもの
であり、さらに詳しく述べるならば電着塗装の塗
料廃液をイオン交換によつて精製して電着塗装液
を定められた性能に維持する方法に関するもので
ある。
従来の電着塗廃液処理法の代表例を図面に基づ
いて説明する。
第1図は廃液処理法の基本的処理系統をフロー
チヤートで示した図面である。表面処理ラインの
電着塗装槽(以下電着槽と呼ぶ)Aから溢れ出た
電着塗装液をサブタンクBに受け、これをポンプ
(図示せず)によつて実線に沿つて循環させる。
E及びFはそれぞれ陰イオン交換塔及び陽イオン
交換塔を示しており、前処理工程から持込まれる
硫酸イオン及び塩素イオンなどの陰イオン系不純
物を陰イオン交換塔でイオン交換し、ナトリウム
やアルミニウムなどの陽イオン系不純物を陽イオ
ン交換塔でイオン交換する。しかる後に熱交換器
(図示せず)を経て電着槽Aに戻す。また、必要
により、電着塗料の一部をフイルタDを具えたバ
イパスから電着槽Aに戻す。電着槽Aの液の組成
PH、液温を適当な手段によつて監視して、これら
が所定の限界内に入つた時にポンプの運転を中止
する。
イオン交換樹脂E,Fのイオン交換能力が低下
した時には、逆洗、再生、押出などの公知の再生
操作を行つてイオン交換能力を回復せしめる。逆
洗工程等においては純水タンクMから点線に沿つ
てイオン交換塔E,Fの中に多量の純水を流し廃
水タンクIに送る。出願人の操業例では第1図に
示した陰イオン交換塔Eの樹脂量が1350の場合
で、イオン交換処理を2時間行つた後毎時約14m3
の純水を15ないし30分間に亘つて流し続ける。イ
オン交換塔に残つている樹脂量は1350より少な
いから、回収、水洗、逆洗により樹脂濃度は希釈
されてしまう。また同様に陽イオン交換塔も希釈
される。したがつて、希釈された液は電着塗装に
使用するには塗料成分が低すぎ、さらに電着イオ
ン交換塔から完全に塗料成分を分離することがき
ないため、塗料が回収されずNで廃液処理されて
いるのが現状である。電着槽Aの浴液の塗料成分
の濃度は被処理材料から持込まれる水分によつて
希釈される。
また、塗料が塗膜として有効に利用され、ある
いは塗料が槽から汲出されたときにも、塗料成分
の浴中の濃度は稀釈されるため、電着槽Aの浴液
に補充する液の濃度はタンク内の規定濃度よりも
高くなければならない。よつて、多量の水性液で
押出して回収した液を電着槽Aに補充すると、電
着槽Aから浴液が溢れ出してしまう。したがつ
て、従来は塗料の回収は実際には行われていなか
つた。
従来のイオン交換精製方法の他の欠点は、逆
洗、押出及び第2水洗等の操作で廃水タンクIか
ら排出される廃液が公害問題を生じることにあ
る。すなわち廃液に含まれる塗料のために廃液の
BOD,COD,SS等が高く、したがつて通常量を
越える高分子凝集剤を使用して装置Nで廃水処理
を行つても凝集効果が少ない。したがつてイオン
交換樹脂の再生の都度白濁水が放流されて、
BOD,COD,SSや汚濁色などの公害問題を起し
ている。
第2図は逆浸透処理装置を使用した電着塗装廃
液処理法の最近のフローチヤートである。第2図
においてサブタンクBから塗装廃液を逆浸透処理
装置Gに送り、塗装廃液から分離された透過水を
水洗槽(電着塗装されたアルミニウムサツシなど
の水洗槽)Hに送る。透過水のほかに工水が水洗
槽に補給され、所定量とされる。塗装廃液から逆
浸透処理によつて分離された塗料成分を濃度調整
槽Jに溜め、所定濃度に調整した後に、電着槽A
に戻す。水洗水は廃水処理設備Nにかける必要が
ある。
本件特許出願人は特願昭52−64022号におい
て、電着イオン交換塔の交換能力が減退した時に
前記イオン交換塔に純水を流して、塗料成分を押
し出し塗料成分を含む水性液を得、次に水性液の
みに逆浸透圧処理を施して塗料成分を回収し、こ
の回収塗料成分を電導塗料槽に戻すことを要旨と
する電着塗装廃液の処理方法を提案した。この方
法によると、イオン交換塔の処理能力を回復する
段階でイオン交換塔から排出される含塗料水を閉
回路内で処理するととともに、塗料成分を含塗料
水から回収することができる。この方法の一つの
欠点は、塗料成分回収のために純水を必要とする
ため、純水精製装置を廃水処理設備に設けなけれ
ばならずコストが嵩むことにある。
本発明は、以上の事実に鑑み、上記特願出願の
利点を純水を使用せずに達成することを目的とす
る。
本発明は、被処理材を電着塗装槽で電着塗装
し、次にこの被処理材を水洗槽で水洗する、電着
塗装法を実施するに際し、電着塗装槽からの廃液
をイオン交換塔で処理することを含む電着塗装廃
液の処理方法において、イオン交換塔から排出さ
れる含塗料水性液に逆浸透処理を施して、電着塗
料の回収液及び透過水を得、イオン交換塔の交換
能力が減退した時にこのイオン交換塔に前記透過
水を流して、含塗料水性液を排出させ、また前記
電着塗料の回収液を前記電着塗装槽に戻すことを
特徴とする。ここで電着槽及びそのサブタンクを
電着塗装槽と総称している。
以下、本発明を図面に基づいて説明する。
第3図は第2図の従来の処理系統を改良した処
理系統図である。常時は電着槽Aからサブタンク
Bにオーバーフローした含塗料水をイオン交換塔
E,Fにかけ、不純物を交換除去された含塗料水
を電着槽Aに戻す。電着槽Aの上流に配置され
た、被処理材のアルマイト封孔処理装置又は湯洗
槽(図示せず)から電着槽Aに水分が持込まれる
電着塗料液を稀釈する。この稀釈を防ぐ含塗料水
を逆浸透処理装置Gにかける。逆浸透処理装置G
によつて含塗料水(サブタンクBの廃液)から分
離された透過水を、通常は実線に沿つて水洗槽H
に送り水洗水として再使用する。イオン交換塔
E,Fから塗料成分を回収する時には、透過水の
一部を点線に沿つて受槽Kに溜め、イオン交換能
力が減退した時にイオン交換塔E,Fに送り、塔
内の塗料を回収するために押出水として使用す
る。回収された含塗料水を受液槽Lに溜め、濃度
調整槽Jにて電着槽Aで使用するに適した濃度に
調整する。受槽Kに貯められた透過水を必要なら
ば濃度調整槽Jに送つて、電着塗料液の濃度調整
を行つてもよい。
装置Gにおける逆浸透圧処理に使用する逆浸膜
としては、塗料の溶剤に耐えるものでなければな
らない。このような逆浸膜としては溶剤による膨
潤、収縮に耐える化学的又は機械的処理をモジユ
ールとモジユールの継ぎ目に施したものが好まし
い。塗料の溶剤はかなりの部分が透過水に、樹脂
固形分は99%以上が回収液に分離される。電着塗
料液の諸成分が透過水に混入する割合の一例を示
すと次のとおりである。
樹脂固形分: 0.0003〜0.07%
ブチルセロソルブ: 50〜56.5%
メタノール:99〜100%
イソプロピルセロソルブ: 68〜75%
アミン(トリエチルアミン及びジメチルアミン
の合計: 70〜77%
上記百分率は電着塗装廃液に含まれる当該成分
の重量に基づいて重量百分率で透過水への混入率
を比較した数値である。
上記割合で混入した溶剤は透過水に対して50%
以上の重量を占めることがある。イオン交換塔
E,Fから塗料分を回収するために逆浸透処理に
かけられて得られた透過水は、溶剤を含んでいる
ために、純水を使用する先願の方法に比較して、
次の点で好都合である。すなわち、イオン交換塔
に滞留する樹脂固形分は純水と接触するとゲル化
して回収困難になる。しかし本発明によると高濃
度の溶剤成分が透過水中に存在するのでゲル化は
起らない。またイオン交換樹脂が空気にさらされ
たのち純水と接触すると、イオン交換樹脂の表面
に樹脂固形分が付着して再生不能となる。しか
し、本発明によると高濃度の溶剤部分が透過水中
に存在するため、イオン交換樹脂の表面でゲル化
しない。
イオン交換樹脂が硫酸根、鉄、塩素、アルミニ
ウムなどのイオンを交換し除去する能力を回復す
るために、陰イオン交換塔では、水洗、逆洗、再
生、押出、水洗、置換の公知の諸段階が行われ
る。本発明によると、前記水洗を行う前に透過水
で塗料成分を回収することができることが必要で
ある。前記水洗は純水でも透過水でもよい。逆洗
は透過水で行つてもよいが純水で行う方が好まし
い。押出及び水洗は純水で行う。次に、陽イオン
交換塔でも水洗を行う前に透過水で塗料成分を回
収することが必要である。諸水洗は透過水でも純
水でも実施できる。
逆浸透処理前に含塗料水にろ過処理を施して、
ごみ又はほこりなどを除去することが有益であ
る。
受液槽Lで含塗料水のPH、比抵抗又は樹脂固形
分濃度を測定することによつて、イオン交換樹脂
内に現存する塗料濃度を推定する。そして塗料が
イオン交換樹脂内に現存している限りは、逆浸透
装置に含塗料水を通過せしめて塗料を回収するこ
とが好ましい。逆浸透圧処理によつて得られ受槽
Kから送られた透過水を濃度調整槽Jで電着に必
要な成分を調整した後、電着槽Aに戻す。
イオン交換塔の交換能力が減退した時には、再
び、上記一連の操作を繰返して行う。よつて、本
発明によると、完全クローズドシステムで塗料成
分を極めて効果的に回収することができる。
本発明に係る方法を実施する装置は、電着槽
と、水洗槽と、電解槽及び/又は水洗槽と連通し
ている逆浸透処理装置と、この装置と底部に設け
られたバルブを介して連通しているイオン交換塔
と、を含んでなるものである。
上記装置のイオン交換塔の具体例が第4図に参
照符号E(F)として図示されている。このイオン交
換塔の本体は円筒状タンクであつて内部にイオン
交換樹脂を収納している。本体1の外壁には数個
ののぞき窓2が設けられ内部の浴液の状態を観察
できるように配慮されている。本体の上部には水
又はイオン交換樹脂用薬液を注入するためのノズ
ル3が取付けられている。同様に塗料を注入する
ためのノズル4も取付けられている。これらのノ
ズル3,4はタンクの壁面を貫いて伸び、散水管
5と連結されている。タンクの下部においてタン
ク内を仕切る床部6がタンクの内壁に連結されて
いる。この床部6はイオン交換樹脂(図示せず)
を支持するとともに、浴液を流下させるものであ
る。したがつて床部6は水平方向において相互に
隔てられた複数の板が上下に一組づつ配列された
ものからなるものである。この支持床とほぼ同一
レベルにおいて薬液出口7が設けられ、同様に再
生の際の液出口8が設けられている。この出口8
は再生バルブ(図示せず)によつて開閉される。
支持床8より下方に、回収バルブ9と空気吹込み
用バルブ10が取付けられた出口管11が固着さ
れている。回収バルブ9は逆浸透処理装置への塗
料廃液の導入及び遮断を行う。この出口管11に
異物が流入するおを妨げている網状囲い蓋12が
タンクの底部に設けられている。
上述の如きイオン交換塔において浴液その他の
材料のレベルは次の如く定められている。イオン
交換樹脂は支持板6からh1なるタンクの高さの約
半分程度に充填されている。そしてイオン交換精
製の最中にタンク内に入つている含塗料水の高さ
は該塗料水の入口までに相当するh2である。次
に、塗料の回収を行うために含塗料水の一部が抜
かれた後の塗料高さは、樹脂高さh1より例えば5
cm高いh3に定められている。この高さより浴液面
が低下しないようにこれを監視する液検知管13
が設けられている。塗料の回収を行う際に透過水
が補給された時の浴液面のレベルh4であり、また
逆洗展開用液高さはh5であり、それぞれのレベル
を監視するために適当な液検知管を設ける。
上記イオン交換塔の運転は次のようにして行わ
れる。底部回収バルブ9を開放して液を高さh3ま
で抜き、終点を液検知室13で検知する。次に、
水導入ノズル3から透過水を高さh4まで入れ、液
検知管(図示せず)によつて導入を停止する。続
いて、空気導入バルブ10を開放して、空気によ
りイオン交換樹脂をほぐし、塗料が樹脂から除か
れるようにする。そして再び最初の操作に戻つて
含塗料水を抜きこれを逆浸透処理する。
上述のようなイオン交換塔によると、イオン交
換樹脂高さより上方までイオン交換塔内で含塗料
水を圧空押出す必要がない。すなわち、透過水を
イオン交換塔内に流し、次にこの透過水の圧力に
よつて、その底部からバルブを介して含塗料水を
押出し、この押出された水性液を再び逆浸透処理
して塗料が回収される。
逆浸透装置としてはスパイラル型、フオローフ
アイバー型及びチユーブラー型(管圧型)を使用
することができる。但し、塗料成分の回収時に23
〜28Kg/cm2程度の圧力に耐えることが必要である
ため、伸縮し難いという特色があるフオローフア
イバー型が好ましい。また逆浸透装置の管内に乱
流を流すことができるために、その半透膜上に汚
物が付着し難いという利点がある。また、付着し
てもスポンジホールなどを用いて機械的に洗浄で
きるために、含塗料液中に不純物が多く混入して
もその使用効果が低下しないという利点がある。
以下、本発明の実施例を説明する。
実施例
この実施例における電着塗料廃水の処理系統は
第3図の如きものであつた。
陰イオン交換塔の運転操作条件を次表に示す。
The present invention relates to a method for treating electrocoating waste liquid, and more specifically, to a method for purifying electrocoating paint waste liquid by ion exchange to maintain the electrocoating liquid at a specified performance. It is. A typical example of a conventional electrodeposition coating waste liquid treatment method will be explained based on the drawings. FIG. 1 is a flowchart showing the basic treatment system of the waste liquid treatment method. The electrodeposition coating liquid overflowing from the electrodeposition coating tank (hereinafter referred to as electrodeposition tank) A of the surface treatment line is received in a sub-tank B, and is circulated along the solid line by a pump (not shown).
E and F indicate an anion exchange tower and a cation exchange tower, respectively, and the anion exchange tower exchanges anionic impurities such as sulfate ions and chloride ions brought in from the pretreatment process, and converts them into sodium, aluminum, etc. The cationic impurities are ion-exchanged in a cation exchange tower. Thereafter, it is returned to the electrodeposition tank A via a heat exchanger (not shown). Further, if necessary, a portion of the electrodeposition paint is returned to the electrodeposition tank A from a bypass provided with a filter D. Composition of the liquid in electrodeposition tank A
The pH and liquid temperature are monitored by appropriate means and the pump is shut down when these fall within predetermined limits. When the ion exchange ability of the ion exchange resins E and F decreases, known regeneration operations such as backwashing, regeneration, and extrusion are performed to restore the ion exchange ability. In the backwashing process, etc., a large amount of pure water flows from the pure water tank M into the ion exchange towers E and F along the dotted line and is sent to the waste water tank I. In the applicant's operation example, the amount of resin in the anion exchange tower E shown in Fig. 1 is 1350, and after 2 hours of ion exchange treatment, the amount of resin is approximately 14 m 3 per hour.
Continue to flow pure water for 15 to 30 minutes. Since the amount of resin remaining in the ion exchange tower is less than 1350, the resin concentration will be diluted by recovery, water washing, and backwashing. Similarly, the cation exchange column is also diluted. Therefore, the diluted solution has too low a paint component to be used for electrodeposition coating, and furthermore, the paint component cannot be completely separated from the electrodeposition ion exchange tower, so the paint is not recovered and is drained with N. The current situation is that it is being processed. The concentration of paint components in the bath solution in electrodeposition tank A is diluted by moisture brought in from the material to be treated. Also, when the paint is used effectively as a coating film or when the paint is pumped out from the tank, the concentration of paint components in the bath is diluted, so the concentration of the solution replenished to the bath solution in electrodeposition tank A is also diluted. must be higher than the specified concentration in the tank. Therefore, when the electrodeposition tank A is replenished with the liquid recovered by extrusion with a large amount of aqueous liquid, the bath liquid overflows from the electrodeposition tank A. Therefore, in the past, paint was not actually collected. Another drawback of the conventional ion exchange purification method is that the waste liquid discharged from the waste water tank I during operations such as backwashing, extrusion and second water washing creates a pollution problem. In other words, due to the paint contained in the waste liquid,
The BOD, COD, SS, etc. are high, so even if wastewater is treated with apparatus N using a polymer flocculant exceeding the normal amount, the flocculation effect is small. Therefore, cloudy water is discharged every time the ion exchange resin is regenerated.
It causes pollution problems such as BOD, COD, SS and dirty color. Figure 2 is a recent flowchart of a method for treating electrocoating waste liquid using a reverse osmosis treatment device. In FIG. 2, the coating waste liquid is sent from the sub-tank B to the reverse osmosis treatment device G, and the permeated water separated from the coating waste liquid is sent to the washing tank (washing tank for electrocoated aluminum sash, etc.). In addition to the permeated water, industrial water is supplied to the washing tank to maintain a predetermined amount. The paint components separated from the paint waste liquid by reverse osmosis treatment are collected in a concentration adjustment tank J, and after being adjusted to a predetermined concentration, the paint components are transferred to an electrodeposition tank A.
Return to The washing water needs to be applied to the wastewater treatment facility N. In Japanese Patent Application No. 52-64022, the applicant of this patent discloses that when the exchange capacity of the electrodeposited ion exchange tower decreases, pure water is flowed through the ion exchange tower to extrude the paint components and obtain an aqueous liquid containing the paint components. Next, we proposed a method for treating electrocoating waste liquid, which consists of subjecting only the aqueous liquid to reverse osmosis treatment to recover paint components, and returning the recovered paint components to the conductive paint tank. According to this method, the paint-containing water discharged from the ion-exchange tower can be treated in a closed circuit at the stage of restoring the processing capacity of the ion-exchange tower, and paint components can be recovered from the paint-containing water. One drawback of this method is that since pure water is required to recover paint components, a pure water purification device must be installed in the wastewater treatment facility, which increases costs. In view of the above facts, the present invention aims to achieve the advantages of the above patent application without using pure water. The present invention applies ion exchange to the waste liquid from the electrodeposition coating tank when carrying out the electrodeposition coating method in which the treated material is electrocoated in an electrodeposition coating tank and then the treated material is washed with water in a water washing tank. In a method for treating electrocoating waste liquid that includes treatment in a tower, reverse osmosis treatment is applied to the paint-containing aqueous liquid discharged from the ion exchange tower to obtain a recovered electrocoat liquid and permeated water, When the exchange capacity of the ion exchange tower decreases, the permeated water is passed through the ion exchange tower to discharge the paint-containing aqueous liquid, and the recovered liquid of the electrodeposition paint is returned to the electrodeposition coating tank. Here, the electrodeposition tank and its sub-tank are collectively referred to as the electrodeposition coating tank. Hereinafter, the present invention will be explained based on the drawings. FIG. 3 is a processing system diagram that is an improved version of the conventional processing system shown in FIG. Normally, the paint-containing water overflowing from the electrodeposition tank A into the sub-tank B is passed through ion exchange towers E and F, and the paint-containing water from which impurities have been exchanged and removed is returned to the electrodeposition tank A. The electrodeposition coating liquid, in which water is brought into the electrodeposition tank A from an alumite sealing treatment device for the material to be treated or a hot water washing tank (not shown) disposed upstream of the electrodeposition tank A, is diluted. Water containing paint to prevent this dilution is applied to the reverse osmosis treatment device G. Reverse osmosis treatment equipment G
The permeated water separated from the paint-containing water (waste liquid from sub-tank B) by
The water is sent to the tank and reused as washing water. When recovering paint components from ion exchange towers E and F, part of the permeated water is collected in a receiver tank K along the dotted line, and when the ion exchange capacity decreases, it is sent to ion exchange towers E and F to remove the paint in the tower. Use as extrusion water to recover. The recovered paint-containing water is stored in a liquid receiving tank L, and adjusted in a concentration adjusting tank J to a concentration suitable for use in the electrodeposition tank A. If necessary, the permeated water stored in the receiving tank K may be sent to a concentration adjusting tank J to adjust the concentration of the electrodeposition coating liquid. The reverse osmosis membrane used in the reverse osmosis treatment in device G must be resistant to paint solvents. Such a reverse immersion membrane is preferably one in which the joints between the modules are chemically or mechanically treated to resist swelling and shrinkage caused by solvents. A considerable portion of the paint solvent is separated into permeate water, and more than 99% of the resin solids are separated into the recovered liquid. An example of the ratio of various components of the electrodeposition coating liquid mixed into permeated water is as follows. Resin solid content: 0.0003-0.07% Butyl cellosolve: 50-56.5% Methanol: 99-100% Isopropyl cellosolve: 68-75% Amine (total of triethylamine and dimethylamine: 70-77% The above percentages are included in the electrocoating waste liquid This is a value that compares the rate of mixing into permeated water by weight percentage based on the weight of the component.The solvent mixed at the above ratio is 50% of the permeated water.
It may weigh more than Since the permeated water obtained by reverse osmosis treatment to recover paint from ion exchange towers E and F contains a solvent, compared to the method of the previous application which uses pure water,
It is advantageous in the following respects. That is, when the resin solid content remaining in the ion exchange tower comes into contact with pure water, it gels and becomes difficult to recover. However, according to the present invention, gelation does not occur because a high concentration of solvent components is present in the permeate water. Furthermore, when the ion exchange resin is exposed to air and then comes into contact with pure water, resin solids adhere to the surface of the ion exchange resin, making it impossible to regenerate it. However, according to the present invention, since a highly concentrated solvent portion is present in the permeate water, gelation does not occur on the surface of the ion exchange resin. In order to restore the ability of the ion exchange resin to exchange and remove ions such as sulfate radicals, iron, chlorine, aluminum, etc., the anion exchange tower undergoes the known steps of water washing, backwashing, regeneration, extrusion, water washing, and displacement. will be held. According to the present invention, it is necessary to be able to recover paint components with permeated water before performing the water washing. The water washing may be performed with pure water or permeated water. Backwashing may be performed using permeated water, but it is preferable to use pure water. Extrusion and washing are performed with pure water. Next, in the cation exchange tower, it is necessary to recover paint components using permeated water before washing with water. Washing with water can be performed with permeated water or pure water. The paint-containing water is filtered before reverse osmosis treatment.
It is beneficial to remove dirt, dust, etc. By measuring the pH, specific resistance, or resin solid content concentration of the paint-containing water in the liquid receiving tank L, the paint concentration currently present in the ion exchange resin is estimated. As long as the paint is present in the ion exchange resin, it is preferable to collect the paint by passing the paint-containing water through a reverse osmosis device. The permeated water obtained by reverse osmosis treatment and sent from the receiving tank K is returned to the electrodeposition tank A after adjusting the components necessary for electrodeposition in a concentration adjustment tank J. When the exchange capacity of the ion exchange column decreases, the above series of operations is repeated again. Therefore, according to the present invention, paint components can be recovered very effectively in a completely closed system. An apparatus for carrying out the method according to the present invention includes an electrodeposition bath, a washing bath, a reverse osmosis treatment device that communicates with the electrolytic bath and/or the washing bath, and a valve provided at the bottom of the device. and an ion exchange tower in communication with each other. A specific example of the ion exchange column of the above apparatus is illustrated in FIG. 4 as reference numeral E(F). The main body of this ion exchange tower is a cylindrical tank that contains an ion exchange resin. Several viewing windows 2 are provided on the outer wall of the main body 1 so that the state of the bath liquid inside can be observed. A nozzle 3 for injecting water or a chemical solution for ion exchange resin is attached to the upper part of the main body. Similarly, a nozzle 4 for injecting paint is also installed. These nozzles 3 and 4 extend through the wall of the tank and are connected to a water sprinkler pipe 5. At the bottom of the tank, a floor section 6 that partitions the inside of the tank is connected to the inner wall of the tank. This floor part 6 is made of ion exchange resin (not shown)
It supports the bath and allows the bath liquid to flow down. Therefore, the floor section 6 is made up of a plurality of plates arranged one above the other and separated from each other in the horizontal direction. A chemical solution outlet 7 is provided at approximately the same level as this support bed, and a solution outlet 8 for regeneration is similarly provided. This exit 8
is opened and closed by a regeneration valve (not shown).
An outlet pipe 11 to which a recovery valve 9 and an air blowing valve 10 are attached is fixed below the support bed 8. The recovery valve 9 introduces and shuts off paint waste liquid to the reverse osmosis treatment device. A mesh enclosure cover 12 is provided at the bottom of the tank to prevent foreign matter from entering the outlet pipe 11. In the above-mentioned ion exchange tower, the levels of bath liquid and other materials are determined as follows. The ion exchange resin is filled to about half the height of the tank h1 from the support plate 6. The height of the paint-containing water entering the tank during ion exchange purification is h2 , which corresponds to the inlet of the paint water. Next, the height of the paint after some of the paint water is removed to recover the paint is, for example, 5 from the resin height h1 .
Set at cm high h 3 . Liquid detection tube 13 that monitors the bath liquid level so that it does not fall below this height.
is provided. The level of the bath liquid level when the permeated water is replenished during paint recovery is h4 , and the height of the backwashing liquid is h5 , and appropriate liquids are used to monitor each level. Install a detection tube. The above ion exchange tower is operated as follows. The bottom collection valve 9 is opened to drain the liquid to a height h3 , and the end point is detected in the liquid detection chamber 13. next,
Permeated water is introduced from the water introduction nozzle 3 to a height h 4 and the introduction is stopped by a liquid detection tube (not shown). Subsequently, the air introduction valve 10 is opened so that the air loosens the ion exchange resin and removes the paint from the resin. Then, the process returns to the beginning and the water contained in the paint is removed and subjected to reverse osmosis treatment. According to the ion exchange tower as described above, there is no need to pneumatically extrude paint-containing water within the ion exchange tower above the height of the ion exchange resin. That is, permeated water is passed through an ion exchange tower, and then the pressure of this permeated water pushes out paint-containing water from the bottom through a valve, and the extruded aqueous liquid is again subjected to reverse osmosis treatment to produce paint. is collected. As the reverse osmosis device, a spiral type, a fiber-like type, and a tubular type can be used. However, when collecting paint components, 23
Since it is necessary to withstand a pressure of about 28 Kg/cm 2 , a foliated fiber type is preferred because it is difficult to expand and contract. Furthermore, since turbulent flow can be caused in the tube of the reverse osmosis device, there is an advantage that dirt is less likely to adhere to the semipermeable membrane. Furthermore, even if the paint adheres, it can be cleaned mechanically using a sponge hole or the like, so there is an advantage that the effectiveness of its use does not deteriorate even if a large amount of impurities are mixed into the paint-containing liquid. Examples of the present invention will be described below. Example The treatment system for electrocoating paint wastewater in this example was as shown in FIG. The operating conditions for the anion exchange tower are shown in the table below.
【表】【table】
【表】 次表に陽イオン交換塔の運転操作を示す。【table】 The following table shows the operation of the cation exchange tower.
【表】
この実施例では、逆浸透膜としてはデユポン社
製B7型を使用し、電着塗料液としてはハニー化
成製AL−700(樹脂分13%)を使用した。逆浸透
装置を透過した透過水へ抜け出た塗料成分が、電
解液中の該成分を100部とした場合に、該成分に
対して占める割合(透過率)は次表のとうりであ
つた。なお透過水中の溶剤部分の濃度は約18%で
あつた(但し濃度は測定値である)。[Table] In this example, the reverse osmosis membrane used was Type B7 manufactured by DuPont, and the electrodeposition coating liquid used was AL-700 manufactured by Honey Kasei (resin content: 13%). The proportion (permeability) of the paint components that escaped into the permeated water that passed through the reverse osmosis device relative to the components in the electrolytic solution was 100 parts as shown in the table below. The concentration of the solvent portion in the permeated water was approximately 18% (however, the concentration is a measured value).
【表】【table】
【表】
この透過水を電着イオン交換塔内を貫流させた
ところ、塔内で塗料の樹脂分のゲル化が見られな
かつた。この結果、塗料の樹脂分が99.4%の高率
で回収され、しかもイオン交換樹脂の能力回復も
良好に行われた。
本発明により達成される効果は次の通りであ
る。
(1) 電着イオン交換精製装置の廃水から塗料成分
をなくすことにより、廃水中のBOD及びCOD
値が低下する。塗料分の廃水中への混入を完全
になくすることにより、塗料が再使用されその
損失が少なくなる。
(2) 逆浸透装置で得られた透過水をイオン交換樹
脂の再生に使用することにより、純水のみで再
生を行う方法に比べて純水の使用量が低下す
る。
(3) 上記(1)及び(2)の効果から廃水処理のクローズ
化が可能になる。
(4) イオン交換塔内で塗料の樹脂固形分がゲル化
しないために、塗料の回収効率が高くなるとと
もにイオン交換樹脂がいたまない。
(5) 本発明によると含塗料水は高分子凝集剤によ
らずして塗料成分が除かれるために、高分子凝
集剤の使用に伴う問題はなくなる。[Table] When this permeated water was allowed to flow through the electrodeposition ion exchange column, no gelation of the resin component of the paint was observed in the column. As a result, the resin content of the paint was recovered at a high rate of 99.4%, and the ability of the ion exchange resin was also well recovered. The effects achieved by the present invention are as follows. (1) By eliminating paint components from wastewater from electrodeposition ion exchange purification equipment, BOD and COD in wastewater can be reduced.
value decreases. By completely eliminating the contamination of paint components into wastewater, the paint can be reused and losses are reduced. (2) By using the permeate water obtained from the reverse osmosis device to regenerate the ion exchange resin, the amount of pure water used is reduced compared to a method in which regeneration is performed using only pure water. (3) The effects of (1) and (2) above enable closed wastewater treatment. (4) Since the resin solid content of the paint does not gel in the ion exchange tower, the paint recovery efficiency is increased and the ion exchange resin is not wasted. (5) According to the present invention, paint components are removed from paint water without using a polymer flocculant, so problems associated with the use of polymer flocculants are eliminated.
第1図および第2図は従来の電着塗料廃液の処
理方法を示す系統図、第3図は本発明の一具体例
に係る処理系統図、第4図はイオン交換塔の一具
体例を示す部分断面図である。
A……メインタンク(電着槽)、B……サブタ
ンク、C……ポンプ、D……フイルタ、E……陰
イオン交換塔、F……陽イオン交換塔、G……逆
浸透処理装置、H……水洗槽、I……廃水タン
ク、J……濃度調整槽、K……受槽、L……受液
槽、M……純水槽、N……廃水処理設備、3……
純水入口、4……含塗料水入口、5……散水管、
6……支持床、7……薬液出口、8……再生時の
出口、9……回収バルブ、10……空気導入バル
ブ。
Figures 1 and 2 are system diagrams showing a conventional method for treating electrocoating waste liquid, Figure 3 is a treatment system diagram according to a specific example of the present invention, and Figure 4 is a specific example of an ion exchange column. FIG. A...Main tank (electrodeposition tank), B...Sub tank, C...Pump, D...Filter, E...Anion exchange tower, F...Cation exchange tower, G...Reverse osmosis treatment device, H...Washing tank, I...Wastewater tank, J...Concentration adjustment tank, K...Receiving tank, L...Liquid receiving tank, M...Pure water tank, N...Wastewater treatment equipment, 3...
Pure water inlet, 4...Paint-containing water inlet, 5...Water pipe,
6... Support bed, 7... Chemical solution outlet, 8... Outlet during regeneration, 9... Recovery valve, 10... Air introduction valve.
Claims (1)
の被処理材を水洗槽で水洗する、電着塗装法を実
施するに際し、前記電着塗装槽からの廃液をイオ
ン交換塔で処理することを含む電着塗装廃液の処
理方法において、 前記イオン交換塔から排出される含塗料水性液
に逆浸透処理を施して、電着塗料の回収液及び透
過水を得、前記イオン交換塔の交換能力が減退し
た時にこのイオン交換塔に前記透過水を流して、
含塗料水性液を排出させ、また前記電着塗料の回
収液を前記電着塗装槽に戻すことを特徴とする電
着塗装廃液の処理方法。[Scope of Claims] 1. When carrying out an electrodeposition coating method in which a material to be treated is electrocoated in an electrodeposition coating tank and then the material to be treated is washed with water in a water washing tank, a method is adopted in which the In a method for treating electrocoating waste liquid that includes treating the waste liquid in an ion exchange tower, reverse osmosis treatment is performed on the paint-containing aqueous liquid discharged from the ion exchange tower to remove the recovered electrocoat liquid and permeated water. and flowing the permeated water through the ion exchange tower when the exchange capacity of the ion exchange tower decreases,
A method for treating electrocoating waste liquid, which comprises discharging an aqueous paint-containing liquid and returning the recovered electrocoat liquid to the electrocoating tank.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15244077A JPS5485229A (en) | 1977-12-20 | 1977-12-20 | Treatment of electrodepositing coating waste solution |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15244077A JPS5485229A (en) | 1977-12-20 | 1977-12-20 | Treatment of electrodepositing coating waste solution |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5485229A JPS5485229A (en) | 1979-07-06 |
| JPS6124479B2 true JPS6124479B2 (en) | 1986-06-11 |
Family
ID=15540570
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP15244077A Granted JPS5485229A (en) | 1977-12-20 | 1977-12-20 | Treatment of electrodepositing coating waste solution |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5485229A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104986900A (en) * | 2015-07-30 | 2015-10-21 | 深圳市深联发精密科技有限公司 | Water reuse treatment method and apparatus for nickel-containing electroplating wastewater |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS58113400A (en) * | 1981-12-28 | 1983-07-06 | Nippon Light Metal Co Ltd | Method for recovering active ingredients from aluminum electrolytically colored wastewater |
| JP6788334B2 (en) * | 2014-08-01 | 2020-11-25 | メルク パテント ゲゼルシャフト ミット ベシュレンクテル ハフツングMerck Patent Gesellschaft mit beschraenkter Haftung | Water purification system and method |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5831217B2 (en) * | 1974-02-18 | 1983-07-05 | 三菱レイヨン株式会社 | Aeon Kokanjiyushino Shiyorihouhou |
| JPS5510675B2 (en) * | 1974-02-28 | 1980-03-18 | ||
| JPS5149229A (en) * | 1974-10-25 | 1976-04-28 | Honey Kasei Kk | Denchakutoryono shorihoho |
| JPS5322546A (en) * | 1976-08-13 | 1978-03-02 | Nippon Giken Kk | Method of washing resin in apparatus for refining electrodeposition paint |
-
1977
- 1977-12-20 JP JP15244077A patent/JPS5485229A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104986900A (en) * | 2015-07-30 | 2015-10-21 | 深圳市深联发精密科技有限公司 | Water reuse treatment method and apparatus for nickel-containing electroplating wastewater |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5485229A (en) | 1979-07-06 |
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