JPH0818039B2 - Method and apparatus for recycling pure water or ultrapure water - Google Patents
Method and apparatus for recycling pure water or ultrapure waterInfo
- Publication number
- JPH0818039B2 JPH0818039B2 JP3195118A JP19511891A JPH0818039B2 JP H0818039 B2 JPH0818039 B2 JP H0818039B2 JP 3195118 A JP3195118 A JP 3195118A JP 19511891 A JP19511891 A JP 19511891A JP H0818039 B2 JPH0818039 B2 JP H0818039B2
- Authority
- JP
- Japan
- Prior art keywords
- water
- exchange resin
- cleaning
- pure water
- ion exchange
- 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
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 90
- 238000000034 method Methods 0.000 title claims description 28
- 238000004064 recycling Methods 0.000 title claims description 17
- 229910021642 ultra pure water Inorganic materials 0.000 title claims description 12
- 239000012498 ultrapure water Substances 0.000 title claims description 12
- 238000004140 cleaning Methods 0.000 claims description 43
- 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 claims description 30
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 28
- 239000003456 ion exchange resin Substances 0.000 claims description 24
- 229920003303 ion-exchange polymer Polymers 0.000 claims description 24
- 239000007789 gas Substances 0.000 claims description 21
- 239000012528 membrane Substances 0.000 claims description 21
- 239000002351 wastewater Substances 0.000 claims description 19
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 16
- 239000001257 hydrogen Substances 0.000 claims description 15
- 229910052739 hydrogen Inorganic materials 0.000 claims description 15
- 229910052763 palladium Inorganic materials 0.000 claims description 14
- 238000000108 ultra-filtration Methods 0.000 claims description 11
- 230000002378 acidificating effect Effects 0.000 claims description 8
- 239000003729 cation exchange resin Substances 0.000 claims description 8
- 239000003957 anion exchange resin Substances 0.000 claims description 7
- 230000008929 regeneration Effects 0.000 claims description 6
- 238000011069 regeneration method Methods 0.000 claims description 6
- 238000012545 processing Methods 0.000 claims description 5
- 239000007788 liquid Substances 0.000 claims description 4
- 238000002156 mixing Methods 0.000 claims description 4
- 238000005342 ion exchange Methods 0.000 claims description 3
- 230000001678 irradiating effect Effects 0.000 claims description 2
- 238000012958 reprocessing Methods 0.000 claims 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 14
- 239000001301 oxygen Substances 0.000 description 14
- 229910052760 oxygen Inorganic materials 0.000 description 14
- 239000000126 substance Substances 0.000 description 9
- 241000894006 Bacteria Species 0.000 description 6
- 150000002500 ions Chemical class 0.000 description 6
- 238000005406 washing Methods 0.000 description 6
- 238000011084 recovery Methods 0.000 description 5
- 239000011347 resin Substances 0.000 description 5
- 229920005989 resin Polymers 0.000 description 5
- 230000001954 sterilising effect Effects 0.000 description 4
- 238000004659 sterilization and disinfection Methods 0.000 description 4
- 238000007872 degassing Methods 0.000 description 3
- 239000010419 fine particle Substances 0.000 description 3
- 239000012510 hollow fiber Substances 0.000 description 3
- 238000012546 transfer Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 239000003638 chemical reducing agent Substances 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 2
- 229910052753 mercury Inorganic materials 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000010453 quartz Substances 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 238000005349 anion exchange Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 239000012459 cleaning agent Substances 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000007772 electroless plating Methods 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 230000002070 germicidal effect Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910001410 inorganic ion Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- -1 palladium Chemical class 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 238000007747 plating Methods 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229920002635 polyurethane Polymers 0.000 description 1
- 239000004814 polyurethane Substances 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 238000004381 surface treatment Methods 0.000 description 1
- 238000009281 ultraviolet germicidal irradiation Methods 0.000 description 1
- 238000009849 vacuum degassing Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Treatment Of Water By Ion Exchange (AREA)
- Physical Water Treatments (AREA)
- Removal Of Specific Substances (AREA)
- Cleaning By Liquid Or Steam (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、純水又は超純水の再生
利用方法に係り、特に、電子工業、精密機械産業等の純
水又は超純水を用いて洗浄する工程における洗浄水の、
回収再利用方法及び装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for recycling pure water or ultrapure water, and more particularly to cleaning water in a step of cleaning with pure water or ultrapure water in the electronics industry, precision machinery industry and the like. ,
The present invention relates to a recovery reuse method and device.
【0002】[0002]
【従来の技術】従来、洗浄排水の処理は、有害物質を除
去後系外へ排出する方法、洗浄排水をイオン除去、殺
菌、及びろ過後再利用する方法、等が行われていた。ま
た近年、工場全体で使用する水のクローズド化も行われ
てきている。この方法は、工場内の各種の工程の排水
を、それぞれ汚染物質濃度の高い1回目洗浄水と、2回
目以降の洗浄水とに分け、1回目の排水は蒸発等の手段
によってそれぞれ別に処理し、2回目以降の洗浄排水を
洗浄用の純水の原水として再利用するものである。2. Description of the Related Art Conventionally, the treatment of cleaning wastewater has been carried out by a method of removing harmful substances to the outside of the system, a method of removing the cleaning wastewater by ion removal, sterilization, and recycling after filtration. In recent years, the water used in the entire factory has been closed. This method divides the wastewater from various processes in the factory into the first wash water with high pollutant concentration and the second and subsequent wash water, and treats the first wastewater separately by means such as evaporation. The second and subsequent cleaning wastewater is reused as raw water of pure water for cleaning.
【0003】[0003]
【発明が解決しようとする課題】洗浄排水を系外へ排出
する方法は、重金属イオン、シアンなどの有害物質の除
去後であっても、工場の立地条件によっては、工場外へ
の放流が認められないこともある。また、水資源の有効
利用の点からも問題がある。また、従来の洗浄排水の再
生利用方法では、一般にイオン除去工程、殺菌工程及び
微粒子除去工程によって再生処理するため、表面処理設
備及び被表面処理物等からの溶出による洗浄水中の有機
物質の増加、洗浄時に空気開放になるために溶存酸素の
増加又は飽和、等の問題があった。特に溶存酸素につい
ては、従来の溶存酸素除去方法として、脱気塔を用いる
真空脱気、膜を介した真空膜脱気、窒素曝気、還元剤の
添加等があるが、装置が大規模になる、過剰の還元剤及
び反応生成物が残留する等の問題があり、小型でクロー
ズド化した装置に用いることは困難であった。According to the method of discharging the cleaning wastewater to the outside of the system, even after the removal of harmful substances such as heavy metal ions and cyan, the discharge to the outside of the factory is permitted depending on the location conditions of the factory. Sometimes you can't. There is also a problem in terms of effective use of water resources. Further, in the conventional method for recycling the cleaning waste water, since the ion removal step, the sterilization step and the fine particle removal step are generally recycled, an increase in organic substances in the cleaning water due to elution from the surface treatment equipment and the surface treated material, There was a problem such as increase or saturation of dissolved oxygen due to air release during cleaning. Particularly for dissolved oxygen, conventional methods for removing dissolved oxygen include vacuum degassing using a degassing tower, vacuum film degassing through a film, nitrogen aeration, addition of a reducing agent, etc., but the apparatus becomes large-scale. However, there is a problem that an excessive reducing agent and a reaction product remain, and it is difficult to use it in a small-sized closed apparatus.
【0004】また、工場全体のクローズド化を行う方法
では、洗浄工程とか、排水処理工程の事故等によって、
所定の性能が維持できない場合があり、純水製造装置へ
の過負荷を招き、最悪の場合工場全体に影響が及ぶ恐れ
がある。本発明は、上記従来技術の問題点を解決し、水
のクローズド化が行える小型で処理性能のよい純水又は
超純水の再生利用方法及び装置を提供することを課題と
する。In addition, in the method of closing the entire factory, due to an accident in the cleaning process or wastewater treatment process,
In some cases, the predetermined performance may not be maintained, which may cause an overload on the pure water production system, and in the worst case, may affect the entire factory. SUMMARY OF THE INVENTION It is an object of the present invention to solve the above-mentioned problems of the prior art, and to provide a small-sized, high-purity pure water or ultrapure water recycling method and device capable of closing water.
【0005】[0005]
【課題を解決するための手段】上記課題を解決するため
に、本発明では、純水又は超純水を用いた洗浄工程の洗
浄排水を再生処理して利用する再生利用方法において、
前記再生処理を、(イ)洗浄排水をイオン交換樹脂層に
通水する工程、(ロ)パラジウムを担持した気体透過膜
の接液側に(イ)の処理水を通水し、接ガス側に水素を
供給する工程、(ハ)(ロ)の処理水に紫外線を照射す
る工程、(ニ)H型強酸性カチオン交換樹脂とOH型ア
ニオン交換樹脂とを混合したイオン交換樹脂層に(ハ)
の処理水を通水する工程、(ホ)(ニ)の処理水を限外
ろ過する工程、の各工程を順次通すことにより行うこと
を特徴とする純水又は超純水の再生利用方法としたもの
である。上記再生処理方法において、再生処理は、さら
に熱交換処理工程に通して行うのがよい。In order to solve the above-mentioned problems, the present invention provides a recycling method in which cleaning waste water in a cleaning step using pure water or ultrapure water is recycled and used.
In the regeneration treatment, (a) a step of passing cleaning wastewater through the ion-exchange resin layer, (b) passing treated water of (a) to the liquid contact side of the gas permeable membrane supporting palladium, and contacting the gas contact side. The step of supplying hydrogen to (a), (b) the step of irradiating the treated water with ultraviolet rays, and (d) the ion exchange resin layer obtained by mixing the H-type strongly acidic cation exchange resin and the OH-type anion exchange resin ( )
The method for recycling pure water or ultrapure water, which is characterized in that it is carried out by sequentially passing through each step of the step of passing the treated water of (4) and the step of (e) ultrafiltration of the treated water. It was done. In the above-mentioned regeneration treatment method, it is preferable that the regeneration treatment is further conducted through a heat exchange treatment step.
【0006】また、本発明では、上記純水の再生利用方
法に使用する装置であって、前記再生処理装置が、
(イ)イオン交換樹脂塔と、(ロ)パラジウムを担持し
た気体透過膜と、(ハ)紫外線照射塔と、(ニ)H型強
酸性カチオン交換樹脂とOH型アニオン交換樹脂とを混
合したイオン交換樹脂層を有するイオン交換装置と、
(ホ)限外ろ過装置とを備え、(ヘ)前記(イ)から
(ホ)までの装置相互間を順次接続する配管、ポンプ、
及びタンクとからなり、前記(ホ)からの再生処理水を
洗浄装置に供給する配管、及び洗浄装置からの排水を前
記再生処理装置に供給する配管を有することを特徴とす
る純水又は超純水の再生利用装置としたものである。ま
た、上記再生利用装置において、前記再生処理装置、再
生処理水の供給路、又は洗浄排水の供給路のいずれかに
熱交換設備を設けるのがよい。According to the present invention, there is provided an apparatus used in the above-mentioned method for recycling pure water, wherein the recycling processing apparatus is
(A) Ion exchange resin tower, (b) Palladium-supported gas permeable membrane, (c) UV irradiation tower, (d) Ion in which H-type strongly acidic cation exchange resin and OH-type anion exchange resin are mixed An ion exchange device having an exchange resin layer,
(E) An ultrafiltration device, and (f) a pipe and a pump for sequentially connecting the devices (a) to (e) to each other.
And pure water, or a tank, and a pipe for supplying reclaimed treated water from (e) to the cleaning device, and a pipe for supplying wastewater from the cleaning device to the regenerating device. This is a water recycling device. Further, in the above recycling apparatus, it is preferable to provide a heat exchange facility in any of the recycling processing device, the recycled treated water supply path, or the cleaning drainage supply path.
【0007】以下に本発明を詳細に説明する。図1は、
本発明の実施態様の一例を示すフローの説明図である。
図1を用いて、本発明の再生利用方法と装置をさらに詳
しく説明する。図1において、洗浄装置12で使用され
た水は、洗浄装置内の洗浄排水タンク14から、洗浄排
水ライン15、ポンプ16を介してイオン交換樹脂塔1
へ導入する。ついで該処理水をパラジウムを担持した気
体透過膜3を有する溶存酸素除去装置2の接液側に導入
する。このとき該装置の接ガス側には、水素水封管4の
水頭差を0〜100cmAqになるように水素ガスを供
給する。ついで該処理水をタンク6へ供給する。タンク
6からは、洗浄水供給流量の1〜3倍に相当する流量の
被処理水を、ポンプ7を介して、紫外線照射塔8に導入
する。ついで該紫外線処理水をイオン交換樹詣塔9へ導
入し、ついで限外ろ過装置10へ導入する。ついで該処
理水は洗浄装置12を含む循環ライン11へ供給され、
未使用水は熱交換装置13を介してタンク6へ戻る。The present invention will be described in detail below. Figure 1
It is explanatory drawing of the flow which shows an example of the embodiment of this invention.
The recycling method and apparatus of the present invention will be described in more detail with reference to FIG. In FIG. 1, the water used in the cleaning device 12 is supplied from the cleaning drainage tank 14 in the cleaning device via the cleaning drainage line 15 and the pump 16 to the ion exchange resin tower 1
Introduce to. Then, the treated water is introduced to the liquid contact side of the dissolved oxygen removing device 2 having the gas permeable membrane 3 supporting palladium. The gas contacting side of this time the device for supplying hydrogen gas to the water head difference hydrogen water sealed tube 4 so that the 0 to 100 c MAQ. Then, the treated water is supplied to the tank 6. From the tank 6, water to be treated having a flow rate corresponding to 1 to 3 times the flow rate of washing water is introduced into the ultraviolet irradiation tower 8 via the pump 7. Then, the ultraviolet-treated water is introduced into the ion-exchange tree tower 9, and then into the ultrafiltration device 10. Then, the treated water is supplied to a circulation line 11 including a cleaning device 12,
The unused water returns to the tank 6 via the heat exchange device 13.
【0008】ここで、イオン交換樹脂塔1は、洗浄排水
中に含有するイオンを除去できるものであれば良く、洗
浄対象物質、洗浄薬剤等によって異なるが、弱塩基性又
は強塩基性のアニオン交換樹脂と、強酸性カチオン交換
樹脂との混合樹脂等を用いることができる。いずれの樹
脂を用いる場合でも、使用前に高度に再生し、十分に水
洗しておくことが望ましい。溶存酸素除去装置2は、パ
ラジウムを担持した気体透過膜3を有したものである。
該気体透過膜3は、水素は透過させ、液体は透過しない
膜にパラジウムを担持させたものであれば良く、接ガス
側には水素を供給5する。気体透過膜3へのパラジウム
の担持は、本発明者らが既に提案しているが、プラスチ
ックへのメッキ方法又はイオン交換樹脂等への担持方法
に準じて行うことができる。接ガス側への水素供給5
は、該溶存酸素除去装置2への流入水中に溶解している
酸素の等量から等量の3倍程度を供給することが好まし
い。Here, the ion exchange resin tower 1 may be any one capable of removing the ions contained in the cleaning wastewater, and it varies depending on the substance to be cleaned, the cleaning agent, etc., but is a weakly basic or strongly basic anion exchange. A mixed resin of a resin and a strongly acidic cation exchange resin can be used. Whichever resin is used, it is desirable that it be highly regenerated and thoroughly washed with water before use. The dissolved oxygen removing device 2 has a gas permeable membrane 3 supporting palladium.
The gas permeable film 3 may be any film that is permeable to hydrogen but impermeable to liquid and has palladium supported thereon, and hydrogen is supplied 5 to the gas contact side. The loading of palladium on the gas permeable membrane 3 has been already proposed by the present inventors, but it can be carried out according to a plating method on plastics or a loading method on ion exchange resins or the like. Hydrogen supply to gas contact side 5
Is preferably supplied from an equivalent amount to about 3 times the equivalent amount of oxygen dissolved in the inflowing water to the dissolved oxygen removing device 2.
【0009】タンク6は、洗浄水の使用量及びその変動
に対応するものであり、使用水量又はその変動が大きい
場合にはタンク6を大きくする必要がある。紫外線照射
塔8での光源は、波長400nm以下の紫外線を照射す
るものであれば良く、殺菌線とされる波長260nm付
近、及び有機物質に効果があるとされる波長200nm
以下の紫外線が照射できるものが特に望ましい。ランプ
及び保護管に人工石英を用いた低圧水銀ランプを好まし
く用いることが出来る。混床式イオン交換樹脂塔9は、
H型強酸性カチオン交換樹脂とOH型強塩基性アニオン
交換樹脂との混合樹脂であり、混合前に高度に再生し、
十分に水洗しておくことが望ましい。ここで水洗は、4
0℃程度に加温した超純水又は純水を用いて行うことが
望ましい。限外ろ過装置10としては、外圧型中空糸限
外ろ過膜を用いることが望ましい。熱交換装置13は、
ポンプ及び紫外線ランプ等によって供給される熱量によ
る水温の上昇を防止する装置であり、多重管型、プレー
ト型等を用いることができる。The tank 6 corresponds to the amount of cleaning water used and its fluctuation, and when the amount of water used or its fluctuation is large, the tank 6 needs to be enlarged. The light source in the ultraviolet irradiation tower 8 may be any one that irradiates ultraviolet rays having a wavelength of 400 nm or less, and has a wavelength of about 260 nm which is a germicidal ray and a wavelength of 200 nm which is considered to be effective for organic substances.
Those which can be irradiated with the following ultraviolet rays are particularly desirable. A low pressure mercury lamp using artificial quartz for the lamp and the protective tube can be preferably used. The mixed bed type ion exchange resin tower 9 is
It is a mixed resin of H type strongly acidic cation exchange resin and OH type strongly basic anion exchange resin, which is highly regenerated before mixing,
It is desirable to wash thoroughly with water. Wash with water here is 4
It is desirable to use ultrapure water or pure water heated to about 0 ° C. As the ultrafiltration device 10, it is desirable to use an external pressure type hollow fiber ultrafiltration membrane. The heat exchange device 13
It is a device that prevents the rise in water temperature due to the amount of heat supplied by a pump, an ultraviolet lamp, or the like, and may be a multi-tube type, a plate type, or the like.
【0010】[0010]
【作用】本発明の作用を各処理工程に従って説明する。
イオン交換樹脂によって、洗浄排水中の金属イオン、シ
アン等の無機イオンが除去される。また、有機酸等のイ
オン性有機物質も除去される。次に、パラジウムを担持
した気体透過膜を有し、接ガス側に水素を供給した溶存
酸素除去装置では、パラジウムの存在下で、式 O2 + 2H2 → 2H2 O で表される反応が行われ、酸素が除去される。このとき
水素はパラジウムに溶解した形で酸素と接触するため効
率的に反応し、また生成物が水であるため、不純物の増
加がない。なお、この処理工程によって残留する水素は
わずかであるが、必要であれば膜脱気装置等によって除
去することも可能である。The operation of the present invention will be described according to each processing step.
The ion exchange resin removes metal ions and inorganic ions such as cyanide in the cleaning waste water. In addition, ionic organic substances such as organic acids are also removed. Next, in a dissolved oxygen removing apparatus having a gas permeable membrane supporting palladium and supplying hydrogen to the gas contact side, in the presence of palladium, the reaction represented by the formula O 2 + 2H 2 → 2H 2 O Done to remove oxygen. At this time, hydrogen comes into contact with oxygen in the form of being dissolved in palladium, so that hydrogen reacts efficiently, and since the product is water, impurities do not increase. Although a small amount of hydrogen remains in this treatment step, it can be removed by a membrane degassing device or the like if necessary.
【0011】ついで紫外線照射装置では、200nm以
下の波長を含む紫外線によって、被処理水中に残存する
有機物質、及び洗浄装置自体及び本再生利用装置から溶
出する有機物質が分解される。又殺菌線と言われる波長
260nm付近の紫外線によって殺菌も行われる。次に
イオン交換樹脂塔9では、紫外線分解によるイオン性の
分解生成物、及びパラジウムを担持した気体透過膜から
極微量溶出するパラジウム等のイオンを除去する。次に
限外ろ過装置によって微粒子を除去する。この微粒子は
被処理水中に含まれるものの他、バクテリアの死菌、ポ
ンプの発塵、イオン交換樹脂及び気体透過膜等から漏出
したものを含む。次に処理水は循環ライン11を介して
洗浄装置12に送られ、未使用水はタンク6へ還流され
る。Next, in the ultraviolet irradiation device, the organic substances remaining in the water to be treated and the organic substances eluted from the cleaning device itself and the recycling device are decomposed by the ultraviolet rays having a wavelength of 200 nm or less. In addition, sterilization is also performed by ultraviolet rays having a wavelength of around 260 nm, which is called sterilization line. Next, in the ion-exchange resin tower 9, ionic decomposition products due to ultraviolet decomposition and ions such as palladium, which are eluted in a very small amount from the gas permeable membrane supporting palladium, are removed. Next, fine particles are removed by an ultrafiltration device. The fine particles include not only those contained in the water to be treated but also bacteria killed by bacteria, dust generated by the pump, leaked from the ion exchange resin, the gas permeable membrane and the like. Next, the treated water is sent to the cleaning device 12 through the circulation line 11, and the unused water is returned to the tank 6.
【0012】さらに、洗浄水を使用する洗浄設備内の、
少なくとも給水バルブの直近の分岐点までを含めて、洗
浄用水を循環させることによって、配管内のいわゆる死
に水を最小限に抑えることが出来、バクテリアの繁殖等
を防止することが出来る。ここで、紫外線ランプ、循環
ポンプ等は、水に対してエネルギーを与えるため、水温
の上昇を招くものである。通常の純水装置等では、使用
された水は排出され、常温の補給水が供給されるため、
水温の上昇は顕著にはならない。しかし、水の排出及び
補給がほとんど無い状態でクローズド化を図る場合に
は、水温上昇は無視できない。ここで、洗浄用水として
は水温が高いことは洗浄効果が上がり、むしろ望ましい
が、現在実用化されているイオン交換樹脂等は耐熱性に
欠け、概略40℃を超えると性能が低下する。従って水
温の上昇を抑える必要があり、再生利用設備に用いたエ
ネルギーに相当する冷却能力の冷却設備が必要となる。Further, in a cleaning facility using cleaning water,
By circulating the cleaning water at least up to the branch point closest to the water supply valve, it is possible to minimize the water so-called dead in the pipe and prevent the propagation of bacteria and the like. Here, since the ultraviolet lamp, the circulation pump, and the like give energy to water, the water temperature rises. In a normal water purifier, etc., the used water is discharged and makeup water at room temperature is supplied,
The rise in water temperature is not significant. However, the rise in water temperature cannot be ignored when the system is closed with almost no water being discharged or replenished. Here, it is preferable that the washing water has a high water temperature because the washing effect is improved, but the ion-exchange resins and the like currently put into practical use lack heat resistance, and the performance deteriorates when the temperature exceeds about 40 ° C. Therefore, it is necessary to suppress the rise in water temperature, and a cooling facility having a cooling capacity equivalent to the energy used for the recycling facility is required.
【0013】[0013]
【実施例】以下に本発明を実施例にしたがって具体的に
説明するが、本発明はこの実施例に限定されるものでは
ない。 実施例1 図1に、本実施例に用いた装置の概略フロー図を示す。
洗浄装置からの排水は、洗浄排水ライン15、排水移送
ポンプ16を介して、イオン交換樹脂塔1に導入し、つ
いでパラジウムを担持した気体透過膜3を有する溶存酸
素除去装置2で処理した後タンク6へ供給する。タンク
6からは、ポンプ7によって5m3/hで、紫外線照射
装置8、カートリッジ型イオン交換樹脂塔9、限外ろ過
膜10へ供給し、循環処理を行った。ここで、イオン交
換樹脂1としては、強塩基性アニオン交換樹脂60リッ
トルと強酸性カチオン交換樹脂60リットルとを混合し
たカートリッジ型イオン交換樹脂塔を用いた。ついで、
溶存酸素除去装置2は、内側に無電解メッキ法に準じて
パラジウムによる触媒化、活性化までを行ったポリオレ
フィン−ポリウレタン系の中空糸複合膜を有する気体透
過膜モジュールであり、膜面積12m2 のモジュールを
用いた。このガス透過膜の内側に被処理水を通水し、外
側に水素ガスを0.1kgf/cm2 、100ml/m
inで供給した。EXAMPLES The present invention will be specifically described below with reference to examples, but the present invention is not limited to these examples. Example 1 FIG. 1 shows a schematic flow chart of the apparatus used in this example.
Wastewater from the cleaning device is introduced into the ion exchange resin tower 1 through the cleaning drainage line 15 and the drainage transfer pump 16, and then treated by the dissolved oxygen removing device 2 having the gas permeable membrane 3 carrying palladium, and then the tank. Supply to 6. From the tank 6, a pump 7 was supplied at a rate of 5 m 3 / h to the ultraviolet irradiation device 8, the cartridge type ion exchange resin tower 9, and the ultrafiltration membrane 10 for circulation treatment. Here, as the ion exchange resin 1, a cartridge type ion exchange resin tower in which 60 liters of a strongly basic anion exchange resin and 60 liters of a strongly acidic cation exchange resin were mixed was used. Then,
The dissolved oxygen removing device 2 is a gas permeable membrane module having a polyolefin-polyurethane-based hollow fiber composite membrane inside which is catalyzed and activated by palladium according to an electroless plating method and has a membrane area of 12 m 2 . A module was used. Water to be treated is passed through the inside of this gas permeable membrane, and hydrogen gas of 0.1 kgf / cm 2 , 100 ml / m is passed outside.
Supplied in.
【0014】ついで紫外線照射装置8の有効容積は約3
0リットルであり、人工石英管を介して消費電力100
Wの低圧水銀ランプ7本を点灯させた。次に、カートリ
ッジ型イオン交換樹脂塔9には、十分洗浄したH型強酸
性カチオン交換樹脂10リットルと、OH型強塩基性ア
ニオン交換樹脂20リットルとを混合してFRP製容器
に充填したもの2本を用いた。次に、限外ろ過装置10
は、外圧型中空糸膜モジュール(旭化成OLT−302
6)を2本用いた。ついで処理水を洗浄装置内を含む純
水ライン11に供給し、未使用水は熱交換装置13を介
して、タンク6へ還流させて循環使用した。洗浄排水移
送ポンプ16は、洗浄排水量によって運転制御を行い、
水素用自動弁17を連動させて制御することによって水
素の過剰供給を防止した。その結果を表1に示す。Next, the effective volume of the ultraviolet irradiation device 8 is about 3
0 liters, 100 power consumption through artificial quartz tube
Seven W low-pressure mercury lamps were turned on. Next, the cartridge type ion exchange resin tower 9 was prepared by mixing 10 liters of sufficiently washed H-type strongly acidic cation exchange resin and 20 liters of OH type strongly basic anion exchange resin and filling it in a FRP container. I used a book. Next, the ultrafiltration device 10
Is an external pressure type hollow fiber membrane module (Asahi Kasei OLT-302
Two of 6) were used. Then, the treated water was supplied to the pure water line 11 including the inside of the cleaning device, and the unused water was circulated to the tank 6 via the heat exchange device 13 for circulation. The cleaning drainage transfer pump 16 performs operation control according to the amount of cleaning drainage,
Excessive supply of hydrogen was prevented by interlocking and controlling the automatic valve 17 for hydrogen. Table 1 shows the results.
【0015】比較例1 循環配管を設けず、処理水を処理水タンクに貯留して使
用時のみ洗浄装置に供給する間欠運転をした他は、実施
例と同様の装置を用いて、水の回収再利用を行った。結
果を表1に示す。供給水の比抵抗の低下、有機物質の増
加、生菌の増加等が認められる。特に生菌については、
実施例1に比較して大きな増加が認められた。COMPARATIVE EXAMPLE 1 Recovery of water was carried out by using the same apparatus as in Example except that the circulating water was not provided and the treated water was stored in the treated water tank and intermittently supplied to the cleaning device only when in use. It was reused. The results are shown in Table 1. Decrease in resistivity of feed water, increase in organic substances, increase in viable bacteria, etc. are observed. Especially for live bacteria,
A large increase was observed as compared to Example 1.
【0016】比較例2 従来のイオン交換樹脂と限外ろ過膜による装置によっ
て、水の回収再利用を行った。概略フローを図2に、結
果を表1に示す。溶存酸素がほとんど飽和となり、又生
菌も実施例と比較して増加していた。Comparative Example 2 Water was recovered and reused by a conventional device using an ion exchange resin and an ultrafiltration membrane. A schematic flow chart is shown in FIG. 2, and the results are shown in Table 1. The dissolved oxygen was almost saturated, and the number of viable bacteria was also increased as compared with the examples.
【0017】[0017]
【表1】 [Table 1]
【0018】[0018]
【発明の効果】以上示したように、本発明による水の回
収再利用装置を用いることによって、 (1)洗浄廃水を放流する方法に比較して、水の使用量
が大幅に減少し、水資源の有効利用がはかれる。 (2)工場全体のクローズド化を行う方法に比較して、
1工程のみのクローズド化のため、万一の事故等で処理
設備の性能が低下しても、工場全体に対する影響はほと
んどない。 (3)イオン交換樹脂及びろ過による回収再利用方法に
比較して、水質の劣化がない。 等の効果がある。As described above, by using the water recovery / reuse apparatus according to the present invention, (1) the amount of water used is greatly reduced as compared with the method of discharging washing wastewater, Effective use of resources is promoted. (2) Compared to the method of closing the whole factory,
Since only one process is closed, even if the performance of the processing equipment deteriorates due to an accident or the like, there is almost no effect on the entire factory. (3) There is no deterioration of water quality as compared with the method of recovery and reuse by ion exchange resin and filtration. And so on.
【図1】本発明の実施態様の一例を示す模式図である。FIG. 1 is a schematic diagram showing an example of an embodiment of the present invention.
【図2】従来の回収再生利用装置の模式図である。FIG. 2 is a schematic diagram of a conventional recovery / reuse device.
1:イオン交換樹脂塔A、2:溶存酸素除去装置、3:
パラジウム担持気体透過膜、4:水素水封管、5:水素
供給ライン、6:タンク、7:ポンプ、8:紫外線照射
塔、9:イオン交換樹脂塔B、10:限外ろ過装置、1
1:循環ライン、12:洗浄装置、13:熱交換装置、
14:洗浄廃水タンク、15:洗浄排水ライン、16:
排水移送ポンプ、17:水素用自動弁1: Ion-exchange resin column A, 2: Dissolved oxygen removal device, 3:
Palladium-supported gas permeable membrane, 4: hydrogen water sealing tube, 5: hydrogen supply line, 6: tank, 7: pump, 8: ultraviolet irradiation tower, 9: ion exchange resin tower B, 10: ultrafiltration device, 1
1: circulation line, 12: cleaning device, 13: heat exchange device,
14: Washing waste water tank, 15: Washing drain line, 16:
Wastewater transfer pump, 17: Automatic valve for hydrogen
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 9/00 503 B 504 B B08B 3/14 2119−3B C02F 1/32 1/42 B 1/44 J 9538−4D 1/58 T (72)発明者 中島 健 神奈川県藤沢市本藤沢4丁目2番1号 株 式会社荏原総合研究所内 (72)発明者 辻村 学 東京都大田区羽田旭町11番1号 株式会社 荏原製作所内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Office reference number FI technical display location C02F 9/00 503 B 504 B B08B 3/14 2119-3B C02F 1/32 1/42 B 1 / 44 J 9538-4D 1/58 T (72) Inventor Ken Nakajima 4-2-1 Motofujisawa, Fujisawa City, Kanagawa Prefecture Ebara Research Institute Ltd. (72) Inventor Manabu Tsujimura 11 Haneda Asahi-cho, Ota-ku, Tokyo No. 1 in EBARA CORPORATION
Claims (4)
排水を再生処理して利用する再生利用方法において、前
記再生処理を、(イ)洗浄排水をイオン交換樹脂層に通
水する工程、(ロ)パラジウムを担持した気体透過膜の
接液側に(イ)の処理水を通水し、接ガス側に水素を供
給する工程、(ハ)(ロ)の処理水に紫外線を照射する
工程、(ニ)H型強酸性カチオン交換樹脂とOH型アニ
オン交換樹脂とを混合したイオン交換樹脂層に(ハ)の
処理水を通水する工程、(ホ)(ニ)の処理水を限外ろ
過する工程、の各工程を順次通すことにより行うことを
特徴とする純水又は超純水の再生利用方法。1. A recycling method in which cleaning wastewater in a cleaning step using pure water or ultrapure water is recycled and used, wherein (a) cleaning wastewater is passed through the ion-exchange resin layer. Step (b): Passing the treated water of (a) to the liquid contact side of the gas permeable membrane supporting palladium and supplying hydrogen to the gas contact side, (c) UV light to the treated water of (b) The step of irradiating, (d) the step of passing the treated water of (c) through the ion exchange resin layer obtained by mixing the H-type strongly acidic cation exchange resin and the OH type anion exchange resin, (e) the treated water of (d) The method for reusing pure water or ultrapure water, which comprises performing the steps of:
工程に通す請求項1記載の純水又は超純水の再生利用方
法。2. The method for recycling pure water or ultrapure water according to claim 1, wherein the recycled water is further passed through a heat exchange treatment step.
用する装置であって、前記再生処理装置が、(イ)イオ
ン交換樹脂塔と、(ロ)パラジウムを担持した気体透過
膜と、(ハ)紫外線照射塔と、(ニ)H型強酸性カチオ
ン交換樹脂とOH型アニオン交換樹脂とを混合したイオ
ン交換樹脂層を有するイオン交換装置と、(ホ)限外ろ
過装置とを備え、(ヘ)前記(イ)から(ホ)までの装
置相互間を順次接続する配管、ポンプ、及びタンクとか
らなり、前記(ホ)からの再生処理水を洗浄装置に供給
する配管、及び洗浄装置からの排水を前記再生処理装置
に供給する配管を有することを特徴とする純水又は超純
水の再生利用装置。3. An apparatus used in the method for reclaiming pure water according to claim 1, wherein the regeneration processing apparatus comprises (a) an ion exchange resin tower and (b) a gas permeable membrane supporting palladium. And (c) an ultraviolet irradiation tower, (d) an ion exchange device having an ion exchange resin layer in which an H-type strongly acidic cation exchange resin and an OH-type anion exchange resin are mixed, and (v) an ultrafiltration device. And (f) a pipe, a pump, and a tank that sequentially connect the devices from (a) to (e), and a pipe that supplies the reclaimed treated water from (e) to a cleaning device, and a cleaning process. An apparatus for reusing pure water or ultrapure water, comprising a pipe for supplying wastewater from the apparatus to the reprocessing apparatus.
路、又は洗浄排水の供給路のいずれかに熱交換設備を有
する請求項3記載の純水又は超純水の再生利用装置。4. The apparatus for reusing pure water or ultrapure water according to claim 3, wherein a heat exchange facility is provided in any one of the regeneration treatment apparatus, the regeneration treatment water supply passage, and the cleaning drainage supply passage.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3195118A JPH0818039B2 (en) | 1991-07-10 | 1991-07-10 | Method and apparatus for recycling pure water or ultrapure water |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3195118A JPH0818039B2 (en) | 1991-07-10 | 1991-07-10 | Method and apparatus for recycling pure water or ultrapure water |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH05138195A JPH05138195A (en) | 1993-06-01 |
| JPH0818039B2 true JPH0818039B2 (en) | 1996-02-28 |
Family
ID=16335798
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3195118A Expired - Fee Related JPH0818039B2 (en) | 1991-07-10 | 1991-07-10 | Method and apparatus for recycling pure water or ultrapure water |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0818039B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4623868B2 (en) * | 2001-06-20 | 2011-02-02 | Tdk株式会社 | Cleaning water treatment method and apparatus for plated parts |
| CN100359106C (en) * | 2005-12-02 | 2008-01-02 | 浙江沁园水处理科技股份有限公司 | A water-saving discharge system of a direct-drinking pure water machine |
-
1991
- 1991-07-10 JP JP3195118A patent/JPH0818039B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH05138195A (en) | 1993-06-01 |
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