JP3128249B2 - Wash water treatment method - Google Patents
Wash water treatment methodInfo
- Publication number
- JP3128249B2 JP3128249B2 JP03008738A JP873891A JP3128249B2 JP 3128249 B2 JP3128249 B2 JP 3128249B2 JP 03008738 A JP03008738 A JP 03008738A JP 873891 A JP873891 A JP 873891A JP 3128249 B2 JP3128249 B2 JP 3128249B2
- Authority
- JP
- Japan
- Prior art keywords
- washing
- washing water
- activated carbon
- water
- hollow fiber
- 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
Links
Classifications
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- 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
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/444—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
Landscapes
- Treatment Of Water By Ion Exchange (AREA)
- Water Treatment By Sorption (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Description
【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION
【0001】[0001]
【産業上の利用分野】本発明は、界面活性剤水溶液、エ
マルジョン洗浄剤、アルカリ洗浄剤等の水系洗浄剤や水
すすぎを必要とする有機溶剤を主体として準水系洗浄剤
による、金属、ガラス、プラスチック、セラミックス等
の脱脂洗浄やプリント基板のはんだフラックス洗浄の水
洗工程の水洗水を処理して水洗工程に戻し、水洗水とし
て循環使用する方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an aqueous detergent such as an aqueous solution of a surfactant, an emulsion detergent, an alkaline detergent, or a semi-aqueous detergent mainly composed of an organic solvent which requires water rinsing, for metal, glass, or the like. The present invention relates to a method for treating rinsing water in a rinsing step of a degreasing cleaning of plastics, ceramics, etc. and a soldering flux of a printed circuit board, returning the rinsing water to the rinsing step, and using the circulating water as the rinsing water.
【0002】[0002]
【従来の技術】水系洗浄剤または準水系洗浄剤による脱
脂洗浄やフラックス洗浄の水洗工程から排出される水洗
水には、洗浄剤や汚れに由来する界面活性剤、有機溶
剤、油、ロジン、アルカリ金属塩、乳化物等が多量に混
入してくる。この水洗水を循環使用するためには、循環
機構の中で、これらの混入物を除去処理する必要があ
る。2. Description of the Related Art Rinsing water discharged from a degreasing or flux cleaning process using an aqueous or semi-aqueous detergent includes surfactants derived from detergents and stains, organic solvents, oils, rosins, and alkalis. A large amount of metal salts, emulsions and the like are mixed. In order to use this washing water in circulation, it is necessary to remove these contaminants in a circulation mechanism.
【0003】その処理方法として、界面活性剤、油、有
機溶剤、ロジン等の有機成分に対しては、活性炭、活性
汚泥、逆浸透、凝集沈殿等があり、金属イオン、アルカ
リ金属塩等のイオン成分に対しては、イオン交換樹脂、
電気透析、逆浸透等がある。これらのうち、脱脂用洗浄
やフラックス洗浄の水洗工程における水洗水の循環使用
の処理方法を考えた場合、短時間のうちに高度の処理を
行い、水洗水として使用可能なまでに上記混入成分を除
去できること、さらに、処理装置がコンパクトで、洗浄
機の附属設備として簡単に設置可能なことが望まれる。
この観点から活性炭とイオン交換樹脂を組合せた方法が
用いられている。この場合、通常、水洗水を、活性炭を
充填したカラムに通して有機物を除去した後に、イオン
交換樹脂を充填したカラムに通してイオンを除去する方
法が取られる。As a treatment method, there are activated carbon, activated sludge, reverse osmosis, coagulation sedimentation, etc. for organic components such as surfactants, oils, organic solvents and rosin, and ions such as metal ions and alkali metal salts. For the components, ion exchange resin,
There are electrodialysis and reverse osmosis. Among these, when considering a treatment method of circulating use of washing water in the washing process of degreasing washing or flux washing, a high-level treatment is performed in a short time, and the above-mentioned mixed components are used until they can be used as washing water. It is desired that the treatment apparatus can be removed and that the treatment apparatus is compact and can be easily installed as an auxiliary equipment of the washing machine.
From this viewpoint, a method using a combination of activated carbon and an ion exchange resin is used. In this case, a method is generally employed in which the washing water is passed through a column filled with activated carbon to remove organic substances, and then passed through a column filled with an ion exchange resin to remove ions.
【0004】[0004]
【発明が解決しようとする課題】しかしながら、水系洗
浄剤または準水系洗浄剤による脱脂洗浄やフラックス洗
浄から出る水洗水中には、洗浄剤中の界面活性剤やアル
カリによる、油、ロジン等の乳化物が含まれ、活性炭に
対する有機物の負荷が非常に高い。このため、吸着容量
の限られた活性炭の有機物除去能力が早期に低下し、活
性炭を新しい活性炭と交換する頻度が高くなる。活性炭
の交換頻度が高いと、活性炭の再生維持費用がかかるだ
けでなく、生産にも支障をきたすという問題が起きる。However, in washing water discharged from degreasing washing or flux washing with an aqueous detergent or semi-aqueous detergent, an emulsion of oil, rosin or the like due to a surfactant or alkali in the detergent is contained. And the organic matter load on the activated carbon is very high. For this reason, the ability of the activated carbon having a limited adsorption capacity to remove organic substances is reduced at an early stage, and the frequency of replacing the activated carbon with new activated carbon is increased. If the frequency of replacement of the activated carbon is high, the cost of regeneration and maintenance of the activated carbon is high, and the production is hindered.
【0005】また、活性炭が処理する排水中の界面活性
剤、油分、有機溶剤、乳化物等の有機成分の濃度が高い
と、処理後の排水中の有機成分濃度も高くなり,乳化物
が完全には除去できず、続いてイオン交換樹脂による処
理を行う場合、イオン交換樹脂が有機汚染され、イオン
交換能力が低下するという問題も起きる。これらの見地
から、水洗水中の乳化物を除去し、活性炭への有機物負
荷をできる限り減らすことが望まれる。[0005] If the concentration of organic components such as surfactants, oils, organic solvents, and emulsions in the wastewater treated by activated carbon is high, the concentration of the organic components in the wastewater after the treatment is also high, and the emulsified product is completely removed. When the treatment with the ion exchange resin is subsequently performed, there is also a problem that the ion exchange resin is organically contaminated and the ion exchange capacity is reduced. From these viewpoints, it is desired to remove the emulsified product in the washing water and reduce the organic substance load on the activated carbon as much as possible.
【0006】[0006]
【課題を解決するための手段】本発明者らは、鋭意検討
した結果、中空繊維状の限外濾過膜で限外濾過すること
により、簡単かつコンパクトな装置を用いる方法で、水
洗水中に含まれる乳化物を除去し、活性炭への有機物負
荷を大幅に軽減することを見いだし、本発明を完成する
に至った。Means for Solving the Problems As a result of intensive studies, the present inventors have found that ultrafiltration with a hollow fiber ultrafiltration membrane allows simple and compact equipment to be used in washing water. It has been found that the emulsified product is removed and the load of organic substances on the activated carbon is significantly reduced, and the present invention has been completed.
【0007】すなわち、本発明は、脱脂洗浄またはフラ
ックス洗浄の水洗工程の、界面活性剤および/またはア
ルカリによる乳化物を含む水洗水を処理して水洗工程に
戻し、循環再使用する方法において、この水洗水を、中
空繊維状の限外濾過膜で限外濾過した後に、活性炭処理
し、水洗工程に戻すことを特徴とする水洗水の処理方
法、及び上記方法により活性炭処理した水洗水をイオン
交換樹脂処理し、水洗工程に戻すことを特徴とする水洗
水の処理方法である。That is, the present invention relates to a method for treating a washing water containing a surfactant and / or an alkali emulsified substance in a washing step of a degreasing washing or a flux washing, returning the washing water to the washing step, and recycling and using the same. The washing water is subjected to activated carbon treatment after ultrafiltration with a hollow fiber ultrafiltration membrane, and then returned to the washing step, and the washing water treated with activated carbon by the above method is subjected to ion exchange. This is a method for treating washing water, which comprises subjecting the resin to a resin treatment and returning to a washing step.
【0008】本発明で用いる中空繊維状の限外濾過膜の
素材は、ポリアクリロニトリル、酢酸セルロース、ポリ
スルホン等の従来の限外濾過に用いられているものを用
いることができる。中空繊維状の限外濾過膜を用いるに
あたっては、大きな濾過膜面積を得るために、この中空
繊維を円筒形の容器の中に多数充填し、中空繊維の両端
が、開口した状態でエポキシ樹脂やポリウレタン樹脂等
のシール材でシールされたものとして用いるのが好まし
い。[0008] As the material of the hollow fiber ultrafiltration membrane used in the present invention, polyacrylonitrile, cellulose acetate, polysulfone and the like used in conventional ultrafiltration can be used. When using a hollow fiber ultrafiltration membrane, in order to obtain a large filtration membrane area, a large number of the hollow fibers are filled in a cylindrical container, and epoxy resin or the like is opened in a state where both ends of the hollow fibers are open. It is preferably used as a material sealed with a sealing material such as a polyurethane resin.
【0009】本発明で用いる中空繊維状の限外濾過膜の
膜厚は10〜400μmが好ましく、20〜100μm
がさらに好ましい。また、中空繊維状の限外濾過膜の内
径は100〜1000μmが好ましく、100〜400
μmがさらに好ましい。また、中空繊維状の限外濾過膜
の分画分子量は、5,000〜15,000が好まし
く、6,000〜13,000がさらに好ましい。さら
に、中空繊維状の限外濾過膜の水の濾過速度は、膜面積
1m2 あたり10l/h以上あるのが好ましく、100
l/h以上あるのがさらに好ましい。The thickness of the hollow fiber ultrafiltration membrane used in the present invention is preferably from 10 to 400 μm, preferably from 20 to 100 μm.
Is more preferred. Further, the inner diameter of the hollow fiber ultrafiltration membrane is preferably 100 to 1000 μm, and 100 to 400 μm.
μm is more preferred. The molecular weight cut-off of the hollow fiber ultrafiltration membrane is preferably from 5,000 to 15,000, more preferably from 6,000 to 13,000. Further, the filtration rate of water of the hollow fiber ultrafiltration membrane is preferably 10 l / h or more per 1 m 2 of membrane area.
More preferably, it is 1 / h or more.
【0010】なお、限外濾過の前に、ゴミを除くため
の、膜状、わた状、ワインド型等のプレフィルターを置
くことが好ましい。本発明で用いる中空繊維状の限外濾
過膜については、特開昭47−50398号公報、特開
昭57−136903号公報に開示された方法によって
製造したものを用いることができる。[0010] Before ultrafiltration, it is preferable to place a pre-filter such as a film, a cotton, or a wind type for removing dust. As the hollow fiber ultrafiltration membrane used in the present invention, those manufactured by the methods disclosed in JP-A-47-50398 and JP-A-57-136903 can be used.
【0011】上記特定の中空繊維状の限外濾過膜によっ
て限外濾過された水洗水は、次いで活性炭処理される。
通常、これには活性炭カラムが用いられる。活性炭カラ
ムに充填される活性炭としては、水処理粒状活性炭を用
いるのが一般的である。活性炭の量は、個々の場合によ
り、処理水量、設置スペース、交換頻度等により決めら
れる。The washing water ultrafiltered by the specific hollow fiber ultrafiltration membrane is then treated with activated carbon.
Usually, an activated carbon column is used for this. As the activated carbon filled in the activated carbon column, water-treated granular activated carbon is generally used. The amount of activated carbon is determined by the amount of treated water, installation space, replacement frequency, and the like, depending on the individual case.
【0012】このようにして活性炭処理された水洗水中
に多量のイオンが含まれている場合は、イオン交換樹脂
等でイオン成分を除去してから水洗工程に戻し、水洗水
として循環使用することができる。イオン成分の除去
は、この他、電気透析や、逆浸透によって可能である。When a large amount of ions are contained in the washing water thus treated with activated carbon, it is possible to remove the ionic components with an ion-exchange resin or the like, and then return to the washing step to recycle the washing water. it can. Removal of the ionic component is also possible by electrodialysis or reverse osmosis.
【0013】[0013]
【実施例】以下、実施例により、本発明を具体的に説明
する。The present invention will be described below in detail with reference to examples.
【0014】[0014]
【実施例1〜5および比較例】炭酸ソーダ、ケイ酸ソー
ダ、界面活性剤、油、ロジンを含む水洗水モデル液(透
過率44%、COD640ppm)を、表2に示す中空
繊維状の限外濾過膜A〜Eで限外濾過し、ついで、水処
理用の粒状活性炭(クラレ(株)製、商品名:クラレコ
ールKW10〜30メッシュ)を充填したカラムに通し
た。限外濾過後の水洗水の透過率およびCOD、活性炭
カラム通過後の水洗水の透過率及びCODを測定した。
その結果を表1に示す。EXAMPLES 1-5 AND COMPARATIVE EXAMPLE A washing water model liquid (permeability: 44%, COD: 640 ppm) containing sodium carbonate, sodium silicate, surfactant, oil, and rosin was used as a hollow fiber ultra-thin powder as shown in Table 2. Ultrafiltration was performed using filtration membranes A to E, and then the mixture was passed through a column filled with granular activated carbon for water treatment (manufactured by Kuraray Co., Ltd., trade name: Kuraray Coal KW10 to 30 mesh). The transmittance and COD of the washing water after ultrafiltration, and the transmittance and COD of the washing water after passing through the activated carbon column were measured.
Table 1 shows the results.
【0015】上記方法で乳化物および有機物を除去した
水洗水中には、まだアルカリ塩が含まれ、導電率1,6
70μS/cmという高い値を示し、水洗水として再使
用できなかったため、この水洗水をカチオン交換樹脂カ
ラムおよびアニオン交換樹脂カラムに通したところ、導
電率10μS/cmの水洗水が得られ、再使用可能な水
洗水とすることができた。The washing water from which emulsions and organic substances have been removed by the above method still contains an alkali salt and has a conductivity of 1,6.
Since it showed a high value of 70 μS / cm and could not be reused as washing water, when this washing water was passed through a cation exchange resin column and an anion exchange resin column, washing water having a conductivity of 10 μS / cm was obtained. Possible washing water was obtained.
【0016】比較のため限外濾過しない場合についても
実施した。その結果を表1に示す。なお、上記透過率
は、可視吸光計で550nmにて測定した値で、この数
値が大きいほど乳化物の量が少ないことを示し、透過率
100%は乳化物が見られないことを示す。また、CO
Dは、JIS−K0102(1986)に記載の方法に
より測定した値で、この数値が小さいほど有機物の量が
少ないことを示す。さらに、導電率は、電気化学計器製
導電率計AOL−40で測定した値である。[0016] For comparison, a case where ultrafiltration was not performed was also performed. Table 1 shows the results. In addition, the said transmittance | permeability is a value measured at 550 nm with a visible absorption spectrometer, and this numerical value is so large that the quantity of an emulsion is small, and 100% of transmittance | permeability shows that an emulsion is not seen. Also, CO
D is a value measured by the method described in JIS-K0102 (1986), and a smaller value indicates a smaller amount of organic matter. Further, the conductivity is a value measured by a conductivity meter AOL-40 manufactured by Electrochemical Instruments.
【0017】以上の水洗水循環フローの1形態を図1に
示した。FIG. 1 shows one embodiment of the above-mentioned circulating flow of washing water.
【0018】[0018]
【表1】 [Table 1]
【0019】[0019]
【表2】 [Table 2]
【0020】[0020]
【発明の効果】本発明は、簡単な方法で、活性炭への有
機物負荷を大幅に低減することができ、活性炭の寿命を
伸ばし、活性炭の交換頻度を減らすと共に、活性炭処理
後の水洗水の有機物レベルをも低減し、良質な水洗水を
再生利用できる。According to the present invention, the organic matter load on the activated carbon can be greatly reduced by a simple method, the life of the activated carbon is extended, the frequency of replacement of the activated carbon is reduced, and the organic matter of the washing water after the activated carbon treatment is reduced. The level can be reduced, and high-quality washing water can be recycled.
【図1】図1は、本発明の水洗水処理方法の1実施態様
を示したものである。FIG. 1 shows an embodiment of a washing water treatment method of the present invention.
1 中空繊維状の限外濾過膜を用いた限外濾過器 2 活性炭カラム 3 イオン交換樹脂カラム 4 水洗槽 5 水洗水循環経路 Reference Signs List 1 Ultrafiltration device using hollow fiber ultrafiltration membrane 2 Activated carbon column 3 Ion exchange resin column 4 Rinse tank 5 Rinse water circulation path
Claims (2)
程の、界面活性剤および/またはアルカリによる乳化物
を含む水洗水を処理して水洗工程に戻し、循環再使用す
る方法において、この水洗水を、中空繊維状の限外濾過
膜で限外濾過した後に活性炭処理し、水洗工程に戻すこ
とを特徴とする水洗水の処理方法。In a method of treating a washing water containing an emulsified product with a surfactant and / or an alkali in a washing step of a degreasing washing or a flux washing, the washing water is returned to the washing step, and the washing water is recycled. A method for treating washing water, comprising performing ultrafiltration with a hollow fiber ultrafiltration membrane, treating with activated carbon, and returning to a washing step.
程の、界面活性剤および/またはアルカリによる乳化物
を含む水洗水を処理して水洗工程に戻し、循環再使用す
る方法において、この水洗水を、中空繊維状の限外濾過
膜で限外濾過した後に活性炭処理し、ついでイオン交換
樹脂処理し、水洗工程に戻すことを特徴とする水洗水の
処理方法。2. A method for treating a washing water containing a surfactant and / or an alkali emulsified product in a washing step of a degreasing washing or a flux washing, returning the washing water to the washing step, and circulating and reusing the washing water. A method for treating washing water, comprising ultrafiltration with a hollow fiber ultrafiltration membrane, treatment with activated carbon, treatment with an ion exchange resin, and returning to the washing step.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP03008738A JP3128249B2 (en) | 1991-01-28 | 1991-01-28 | Wash water treatment method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP03008738A JP3128249B2 (en) | 1991-01-28 | 1991-01-28 | Wash water treatment method |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH04244289A JPH04244289A (en) | 1992-09-01 |
JP3128249B2 true JP3128249B2 (en) | 2001-01-29 |
Family
ID=11701292
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP03008738A Expired - Fee Related JP3128249B2 (en) | 1991-01-28 | 1991-01-28 | Wash water treatment method |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3128249B2 (en) |
Cited By (4)
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---|---|---|---|---|
WO2018146308A1 (en) | 2017-02-13 | 2018-08-16 | Merck Patent Gmbh | A method for producing ultrapure water |
WO2018146309A1 (en) | 2017-02-13 | 2018-08-16 | Merck Patent Gmbh | A method for producing ultrapure water |
US11629071B2 (en) | 2017-02-13 | 2023-04-18 | Merck Patent Gmbh | Method for producing ultrapure water |
US11807556B2 (en) | 2017-02-13 | 2023-11-07 | Merck Patent Gmbh | Method for producing ultrapure water |
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JP3268876B2 (en) * | 1993-03-01 | 2002-03-25 | ダイセル化学工業株式会社 | How to purify river or lake water |
FR2711129B1 (en) * | 1993-10-12 | 1996-02-02 | Aerospatiale | Washing water treatment and recycling station for a washing machine. |
JP3070379B2 (en) * | 1994-01-24 | 2000-07-31 | 荒川化学工業株式会社 | Cleaning system |
CA2594316A1 (en) * | 2005-01-11 | 2006-07-20 | 3M Innovative Properties Company | Treatment of wastewater streams containing surfactants |
CN117361683B (en) * | 2023-12-07 | 2024-03-08 | 陕西金河洗涤有限公司 | Washing wastewater treatment device |
-
1991
- 1991-01-28 JP JP03008738A patent/JP3128249B2/en not_active Expired - Fee Related
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2018146308A1 (en) | 2017-02-13 | 2018-08-16 | Merck Patent Gmbh | A method for producing ultrapure water |
WO2018146309A1 (en) | 2017-02-13 | 2018-08-16 | Merck Patent Gmbh | A method for producing ultrapure water |
US11629071B2 (en) | 2017-02-13 | 2023-04-18 | Merck Patent Gmbh | Method for producing ultrapure water |
US11807556B2 (en) | 2017-02-13 | 2023-11-07 | Merck Patent Gmbh | Method for producing ultrapure water |
US11820676B2 (en) | 2017-02-13 | 2023-11-21 | Merck Patent Gmbh | Method for producing ultrapure water |
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