JP2000288578A - Method and apparatus for treating water containing trace of organic matter - Google Patents

Method and apparatus for treating water containing trace of organic matter

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Publication number
JP2000288578A
JP2000288578A JP11096547A JP9654799A JP2000288578A JP 2000288578 A JP2000288578 A JP 2000288578A JP 11096547 A JP11096547 A JP 11096547A JP 9654799 A JP9654799 A JP 9654799A JP 2000288578 A JP2000288578 A JP 2000288578A
Authority
JP
Japan
Prior art keywords
water
ppm
membrane
dissolved oxygen
tank
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.)
Granted
Application number
JP11096547A
Other languages
Japanese (ja)
Other versions
JP3651306B2 (en
Inventor
Satoshi Yamada
聡 山田
Katsura Kitatsuji
桂 北辻
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP09654799A priority Critical patent/JP3651306B2/en
Publication of JP2000288578A publication Critical patent/JP2000288578A/en
Application granted granted Critical
Publication of JP3651306B2 publication Critical patent/JP3651306B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

PROBLEM TO BE SOLVED: To ensure stable and efficient treatment over a long period of time by holding the concn. of dissolved oxygen of a biological treatment tank to a specific value in a method for the biological treatment by oligotrophic bacteria and membrane separation treatment of water containing TOC in specific concn. and a trace of org. matter. SOLUTION: Water containing 5 ppb-50 ppm of TOC and a very small amt. of org. matter is introduced into a biological reaction tank 2 by a pump P1 through a raw water tank 1 and biologically treated with oligotrophic bacteria to decompose and remove the org. matter. A part of this biologically treated water is returned to the raw water tank 1 as circulating water and the remainder thereof is filtered by a strainer 4 through a biologically treated water tank 3 and subjected to membrane separation treatment in a UF membrane treatment device 5 to separate bacterial cells and membrane permeated water is taken out of the system as treated water and membrane conc. water is circulated to the biologically treated water tank 3. Herein, the concn. of dissolved oxygen is controlled so that the concn. of dissolved oxygen in the biological reaction tank 2 becomes 2 ppm or more.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、TOC5ppb〜
50ppmというような微量の有機物を含有する水を、
オリゴトロフィックバクテリアによる生物処理と膜分離
処理とで処理する方法及び装置に関する。
TECHNICAL FIELD [0001] The present invention relates to TOC5ppb ~
Water containing a trace amount of organic matter such as 50 ppm
The present invention relates to a method and an apparatus for performing a biological treatment with an oligotrophic bacterium and a membrane separation treatment.

【0002】[0002]

【従来の技術】半導体や液晶製造工場においては、理論
純水(H2Oのみからなる水)の比抵抗18.24MΩ
・cmに極めて近い、17〜18MΩ・cmの比抵抗を
有する超純水が洗浄用水として大量に用いられている。
2. Description of the Related Art In semiconductor and liquid crystal manufacturing factories, the specific resistance of theoretical pure water (water consisting only of H 2 O) is 18.24 MΩ.
Ultrapure water having a specific resistance of 17-18 MΩ · cm, which is very close to cm, is used in large quantities as cleaning water.

【0003】従来、この洗浄に用いられた洗浄排水は、
回収して処理された後、工水、井水等と共に更に処理さ
れて超純水の製造に再利用されている。しかして、この
洗浄排水(以下「回収水」と称す場合がある。)の処理
技術として、回収水中に低濃度で含まれるTOCを貧栄
養細菌であるオリゴトロフィックバクテリアで生物処理
することにより除去する方法がある(特許第21303
84号,特許第2887284号)。即ち、この回収水
は有機物含有量がTOCで5ppm以下であるような微
量有機物含有水であり、このような微量有機物含有水
は、一般的な活性汚泥法では処理することができない。
しかし、オリゴトロフィックバクテリアのような貧栄養
下でも生育する微生物を用いることにより、微量有機物
含有水を処理してTOCが著しく低減された処理水を得
ることができる。
Conventionally, washing wastewater used for this washing is:
After being collected and treated, it is further treated together with industrial water, well water, etc., and reused in the production of ultrapure water. As a treatment technique for the washing wastewater (hereinafter sometimes referred to as “recovered water”), TOC contained in the recovered water at a low concentration is removed by biological treatment with oligotrophic bacteria, which are oligotrophic bacteria. (Japanese Patent No. 21303)
No. 84, Patent No. 2887284). That is, the recovered water is water containing a trace amount of organic matter having an organic matter content of 5 ppm or less in TOC, and such trace amount of water containing organic matter cannot be treated by a general activated sludge method.
However, by using a microorganism that grows even under oligotrophic conditions, such as an oligotrophic bacterium, it is possible to treat a trace amount of organic substance-containing water to obtain treated water having a significantly reduced TOC.

【0004】なお、生物処理と膜分離処理とを組み合せ
た処理方法において、生物処理水に残留塩素濃度が0.
3〜1.5ppmとなるように塩素剤を添加することに
より後段の膜分離装置の膜濾過効率を向上させる方法が
提案されている(特開平5−329477号公報)。ま
た、生物処理槽の溶存酸素濃度を1.0mg/L以上に
維持することで、後段の膜分離装置の透過流束を高く維
持する方法も提案されている(特開平4−330993
号公報)。
[0004] In a treatment method in which biological treatment and membrane separation treatment are combined, the concentration of residual chlorine in the biological treatment water is set to 0.1.
A method of improving the membrane filtration efficiency of a subsequent membrane separation device by adding a chlorine agent so as to be 3 to 1.5 ppm has been proposed (JP-A-5-329777). Also, a method has been proposed in which the concentration of dissolved oxygen in the biological treatment tank is maintained at 1.0 mg / L or more to maintain the permeation flux of the subsequent membrane separation device high (Japanese Patent Application Laid-Open No. 4-330993).
No.).

【0005】また、微生物を保持した担体を保有する流
動床式生物反応槽において、担体に担持された微生物に
酸素を補給するために、過酸化水素の供給手段を設けた
ものも提案されている(特開平9−271793号公
報)。
[0005] Further, there has been proposed a fluidized-bed biological reaction tank having a carrier holding microorganisms, which is provided with a hydrogen peroxide supply means in order to replenish the microorganisms carried on the carrier with oxygen. (JP-A-9-271793).

【0006】[0006]

【発明が解決しようとする課題】本発明者らの研究によ
り、回収水をオリゴトロフィックバクテリアで生物処理
し、この生物処理水を膜分離処理すると、経時により膜
の透過流束が低下することが判明した。
According to the study of the present inventors, when the recovered water is biologically treated with oligotrophic bacteria, and the biologically treated water is subjected to membrane separation, the permeation flux of the membrane decreases with time. There was found.

【0007】前述の如く、生物処理と膜分離処理とを組
み合せた処理において、膜分離装置での処理効率の向上
のために、塩素剤を添加する方法や溶存酸素を維持する
方法が提案されている。このうち、特開平5−3294
77号公報に記載される塩素剤を添加する方法は、塩素
により、膜に付着した菌体やその代謝物などを剥離させ
て膜濾過効率を向上させるものであるが、この方法では
遊離塩素の酸化力により膜が劣化するという問題があ
り、また、高濃度で塩素を添加するために膜処理水に塩
素が多く残留するという欠点がある。
As described above, in a treatment combining biological treatment and membrane separation treatment, a method of adding a chlorine agent and a method of maintaining dissolved oxygen have been proposed in order to improve the treatment efficiency in a membrane separation device. I have. Of these, Japanese Unexamined Patent Publication No.
The method of adding a chlorinating agent described in JP-A No. 77 is to remove bacteria and their metabolites attached to the membrane by chlorine to improve membrane filtration efficiency, but this method removes free chlorine. There is a problem that the membrane is deteriorated by the oxidizing power, and there is a disadvantage that a large amount of chlorine remains in the membrane treatment water because chlorine is added at a high concentration.

【0008】さらに、特開平4−330993号公報に
は、生物処理槽の溶存酸素濃度を1.0ppm以上に維
持することにより生物処理水を膜処理する際の膜の濾過
性が向上することが明らかにされているが、この方法
は、BODが1000ppm程度の一般的な排水に適用
されるものであり、この方法で用いられている菌相、即
ち、BOD1000ppm程度の水中に生息して有機物
を資化する活性汚泥の菌相と、TOC濃度が10ppm
程度の水中に生息するオリゴトロフィックバクテリアの
菌相とは全く異なり、また、生物処理水に含まれる菌体
濃度も2〜3のオーダーで異なるため、生物処理水を膜
処理する膜分離装置の構造や運転方法に違いがある。そ
れゆえ、両者の違いを考慮して微量有機物含有水を生物
処理した後の処理水の膜濾過性を改善させる方法が求め
られていた。
Further, Japanese Patent Application Laid-Open No. Hei 4-330993 discloses that maintaining the dissolved oxygen concentration in a biological treatment tank at 1.0 ppm or more improves the filterability of the membrane when membrane-treating biologically treated water. It has been clarified that this method is applied to general wastewater having a BOD of about 1000 ppm, and the microflora used in this method, that is, inhabiting water having a BOD of about 1000 ppm to remove organic matter. Activated sludge flora assimilated and TOC concentration 10ppm
It is completely different from the bacterial flora of oligotrophic bacteria inhabiting water of a degree, and the concentration of cells contained in biologically treated water also differs in the order of two to three. There are differences in structure and driving method. Therefore, there has been a demand for a method of improving the membrane filtration property of treated water after biological treatment of trace organic substance-containing water in consideration of the difference between the two.

【0009】また、特開平9−271793号公報に記
載される方法は、有機物の分解に必要な酸素を過酸化水
素の添加により供給するに過ぎず、過酸化水素の添加に
より生じた酸素のほとんどが有機物の分解に消費され、
生物処理水の溶存酸素濃度が2ppm以上に維持されな
い恐れがあり、このような場合、膜濾過性は悪化する。
Further, the method described in Japanese Patent Application Laid-Open No. 9-271793 only supplies oxygen necessary for decomposing organic substances by adding hydrogen peroxide. Is consumed in the decomposition of organic matter,
The dissolved oxygen concentration of the biological treatment water may not be maintained at 2 ppm or more, and in such a case, the membrane filtration property is deteriorated.

【0010】本発明は上記従来の実情に鑑みてなされた
ものであって、TOC5ppb〜50ppmというよう
な微量の有機物を含有する水を、オリゴトロフィックバ
クテリアによる生物処理と膜分離処理とで処理するに当
り、膜の透過流束の低下を防止して長期に亘り安定かつ
効率的な処理を行う方法及び装置を提供することを目的
とする。
The present invention has been made in view of the above-mentioned conventional circumstances, and treats water containing a trace amount of organic matter, such as 5 ppb to 50 ppm of TOC, by biological treatment with oligotrophic bacteria and membrane separation treatment. In view of the above, an object of the present invention is to provide a method and an apparatus for performing a stable and efficient treatment for a long period of time by preventing a decrease in permeation flux of a membrane.

【0011】[0011]

【課題を解決するための手段】本発明の微量有機物含有
水の処理方法は、TOCを5ppb〜50ppmの濃度
で含む微量有機物含有水を、オリゴトロフィックバクテ
リアによる生物処理と膜分離処理とにより処理する方法
において、該生物処理槽の溶存酸素濃度を2ppm以上
に維持することを特徴とする。
According to the present invention, there is provided a method for treating trace organic matter-containing water, which comprises treating trace organic matter-containing water containing TOC at a concentration of 5 ppb to 50 ppm by biological treatment with oligotrophic bacteria and membrane separation treatment. The method is characterized in that the concentration of dissolved oxygen in the biological treatment tank is maintained at 2 ppm or more.

【0012】本発明の微量有機物含有水の処理装置は、
TOCを5ppb〜50ppmの濃度で含む微量有機物
含有水が導入され、オリゴトロフィックバクテリアによ
り該水中の汚染物質を分解する生物処理槽と、該生物処
理槽の処理水を膜分離する膜分離装置とを備えてなる微
量有機物含有水の処理装置において、該生物処理槽が溶
存酸素濃度2ppm以上に維持されることを特徴とす
る。
[0012] The apparatus for treating trace organic matter-containing water of the present invention comprises:
A biological treatment tank for introducing water containing trace amounts of organic matter containing TOC at a concentration of 5 ppb to 50 ppm and decomposing contaminants in the water by oligotrophic bacteria, and a membrane separation device for membrane-separating the treated water in the biological treatment tank. Wherein the biological treatment tank is maintained at a dissolved oxygen concentration of 2 ppm or more.

【0013】即ち、本発明者らは、TOC5ppb〜5
0ppmというような微量の有機物を含有する水を、オ
リゴトロフィックバクテリアによる生物処理と膜分離処
理とで処理するに当り、膜の透過流速が低下する原因に
ついて鋭意検討を重ねた結果、次のような知見を得た。
That is, the present inventors have proposed that TOC5ppb-5
When water containing a trace amount of organic matter such as 0 ppm is treated by the biological treatment with oligotrophic bacteria and the membrane separation treatment, as a result of intensive studies on the cause of a decrease in the permeation flow rate of the membrane, the following results are obtained. Knowledge was obtained.

【0014】生物処理と膜分離処理とで処理する場合に
おける膜の透過流束は、生物処理槽内での微生物の活動
状態に依存し、生物処理槽の溶存酸素濃度が2ppmを
下回る状態が長時間発生すると菌体分離のための膜の透
過流束が低下する。この原因は生物処理槽の溶存酸素濃
度が2ppm未満の運転では、生物相又は生物代謝物
が、膜に付着し易く、膜分離処理に不適当なものへ変化
するためである。
[0014] The permeation flux of the membrane in the biological treatment and the membrane separation treatment depends on the activity state of the microorganisms in the biological treatment tank, and the dissolved oxygen concentration in the biological treatment tank is less than 2 ppm. As time elapses, the permeation flux of the membrane for separating cells decreases. This is because in the operation of the biological treatment tank where the dissolved oxygen concentration is less than 2 ppm, the biological phase or the biological metabolite easily adheres to the membrane and changes to an unsuitable one for the membrane separation treatment.

【0015】従って、本発明では生物処理槽の溶存酸素
濃度を2ppm以上となるように維持することにより、
膜の透過流束の低下の原因となる膜に付着し易い物質の
生成を抑制して、膜の透過流束の低下を防止し、長期に
亘り、安定かつ効率的な処理を行うことを可能とする。
しかも、この方法であれば、塩素剤を高濃度で用いる特
開平5-329477号公報に記載される方法に比し
て、膜の劣化を引き起こす恐れが小さい。
Therefore, in the present invention, by maintaining the dissolved oxygen concentration in the biological treatment tank at 2 ppm or more,
Suppresses the generation of substances that easily adhere to the membrane, which causes a decrease in the permeation flux of the membrane, prevents the permeation flux of the membrane from lowering, and enables stable and efficient processing over a long period of time. And
Moreover, according to this method, the risk of causing deterioration of the film is small as compared with the method described in Japanese Patent Application Laid-Open No. 5-329777, which uses a chlorine agent at a high concentration.

【0016】なお、従来において、オリゴトロフィック
バクテリアのような貧栄養細菌を用いた生物処理槽の運
転では溶存酸素濃度は管理されておらず、通常の状態で
の溶存酸素濃度は1ppm程度であった。これは、生物
処理槽の溶存酸素濃度が1ppm程度であれば低濃度で
含まれるTOCを分解するに十分と考えられ、溶存酸素
濃度をこれ以上高く維持しても処理水水質の向上は期待
できず、これ以上に溶存酸素濃度を高めることは無駄で
あると考えられていたためである。
Conventionally, in the operation of a biological treatment tank using an oligotrophic bacterium such as an oligotrophic bacterium, the dissolved oxygen concentration is not controlled, and the dissolved oxygen concentration in a normal state is about 1 ppm. Was. This is considered to be sufficient for decomposing TOC contained at a low concentration if the dissolved oxygen concentration in the biological treatment tank is about 1 ppm. Even if the dissolved oxygen concentration is maintained at a higher level, an improvement in the quality of treated water can be expected. This is because it was considered that increasing the dissolved oxygen concentration further than this was useless.

【0017】なお、本発明において、原水となる微量有
機物含有水のTOCが5ppb未満でも50ppmを超
えてもオリゴトロフィックバクテリアによる生物処理が
困難である。
In the present invention, biological treatment with oligotrophic bacteria is difficult even if the TOC of the trace organic substance-containing water as raw water is less than 5 ppb or more than 50 ppm.

【0018】ところで、通常の場合、オリゴトロフィッ
クバクテリアのような貧栄養細菌を用いる生物処理槽で
は、担体を使用した流動床生物処理槽が用いられてい
る。この方式の生物処理槽では下からの曝気を行うと菌
体(担体)が流出するため、酸素の吹き込みで溶存酸素
濃度を上げるためには、生物処理水を循環させて循環系
路で水に酸素を吹き込むことにより酸素の供給を行うこ
ととなる。しかし、この方式では溶存酸素濃度を高くす
ることが困難であるため、請求項2,4に従って過酸化
水素を添加することにより溶存酸素濃度を2ppm以上
に維持するのが好ましい。
By the way, usually, in a biological treatment tank using oligotrophic bacteria such as oligotrophic bacteria, a fluidized bed biological treatment tank using a carrier is used. In this type of biological treatment tank, bacteria (carriers) flow out when aeration is performed from below. To increase the dissolved oxygen concentration by blowing oxygen, the biological treatment water is circulated and the water is circulated through the circulation system. Oxygen is supplied by blowing oxygen. However, it is difficult to increase the concentration of dissolved oxygen in this method, so it is preferable to maintain the concentration of dissolved oxygen at 2 ppm or more by adding hydrogen peroxide according to claims 2 and 4.

【0019】[0019]

【発明の実施の形態】以下に図面を参照して本発明の実
施の形態を詳細に説明する。
Embodiments of the present invention will be described below in detail with reference to the drawings.

【0020】図1は本発明の実施の形態を示す系統図で
ある。
FIG. 1 is a system diagram showing an embodiment of the present invention.

【0021】図1において、1は原水槽、2は生物反応
槽であり、槽内には、支持床2A上に微生物を担持した
粒状又はペレット状の活性炭等の担体による流動床2B
が形成されている。3は生物処理水タンク、4はストレ
ーナ、5はUF膜分離装置、P1,P2はポンプである。
In FIG. 1, reference numeral 1 denotes a raw water tank, and 2 denotes a biological reaction tank. Inside the tank, a fluidized bed 2B made of a carrier such as granular or pelletized activated carbon carrying microorganisms on a support bed 2A.
Are formed. Reference numeral 3 is a biological treatment water tank, 4 is a strainer, 5 is a UF membrane separation device, and P 1 and P 2 are pumps.

【0022】原水(回収水等の、TOCを5ppb〜5
0ppmで含む微量有機物含有水)は、原水槽1を経て
ポンプP1により生物反応槽2に導入されてオリゴトロ
フィックバクテリアにより生物処理され、含有される有
機物が分解除去される。この生物処理水の一部は循環水
として原水槽1に返送され、残部は生物処理水タンク3
を経てポンプP2によりストレーナ4で濾過された後、
UF膜分離装置5で膜分離処理されることにより菌体が
分離され、膜透過水は処理水として系外へ取り出され
る。また、膜濃縮水は生物処理水タンク3に循環され
る。この循環水は一部が廃水として系外へ排出される。
Raw water (TOC of recovered water etc. is 5 ppb to 5 ppb)
Trace organic substance-containing water) containing at 0ppm is introduced into the bioreactor 2 by pump P 1 through the raw water tank 1 is biologically treated by oligo Toro Fick bacteria, organic material contained is decomposed and removed. A part of this biologically treated water is returned to the raw water tank 1 as circulating water, and
After being filtered by the strainer 4 by the pump P 2
The cells are separated by the membrane separation treatment in the UF membrane separation device 5, and the permeated water is taken out of the system as treated water. The membrane concentrated water is circulated to the biological treatment water tank 3. Part of this circulating water is discharged out of the system as wastewater.

【0023】本発明においては、このような処理におい
て、生物反応槽2内の溶存酸素濃度が2ppm以上とな
るように溶存酸素濃度を制御する。この溶存酸素濃度が
2ppmを下回り、特に、12時間以上も溶存酸素濃度
2ppm未満の状態が継続すると膜処理に不適当な粘着
性の菌体代謝物等が生成し、膜の透過流束が著しく低下
することとなる。
In the present invention, in such treatment, the dissolved oxygen concentration is controlled so that the dissolved oxygen concentration in the biological reaction tank 2 becomes 2 ppm or more. When the dissolved oxygen concentration is lower than 2 ppm, and particularly when the dissolved oxygen concentration is lower than 2 ppm for more than 12 hours, viscous bacterial metabolites and the like unsuitable for membrane treatment are generated, and the permeation flux of the membrane is remarkably increased. Will decrease.

【0024】生物反応槽2の溶存酸素濃度は2ppm以
上となるよう、被処理水のTOC濃度や酸素の溶存量を
調整する。過度に溶存酸素濃度を高くすることは、その
ためのコストが嵩む上に、後工程に脱気処理を施す場
合、その負荷が増大することから好ましくない。生物反
応槽2の溶存酸素濃度は、特に2〜8ppmの範囲に維
持するのが好ましく、2.0〜3.5ppmの範囲に維
持するのが特に好ましい。
The TOC concentration of the water to be treated and the dissolved amount of oxygen are adjusted so that the dissolved oxygen concentration in the biological reaction tank 2 becomes 2 ppm or more. An excessively high dissolved oxygen concentration is not preferable because the cost is increased and, when degassing is performed in a subsequent step, the load increases. The dissolved oxygen concentration in the biological reaction tank 2 is particularly preferably maintained in the range of 2 to 8 ppm, and particularly preferably in the range of 2.0 to 3.5 ppm.

【0025】ところで、通常、溶存酸素濃度を高めるた
めには、酸素の曝気が考えられるが、前述の如く曝気に
より菌体(担体)が流出する恐れがある場合、好ましく
ない。
In general, oxygen aeration can be considered to increase the dissolved oxygen concentration. However, it is not preferable when the aeration may cause bacterial cells (carriers) to flow out.

【0026】従って、本発明においては、過酸化水素を
生物反応槽2に注入して過酸化水素の分解で生成する酸
素により溶存酸素濃度を高めることが好ましい。
Therefore, in the present invention, it is preferable to inject hydrogen peroxide into the biological reaction tank 2 to increase the concentration of dissolved oxygen by oxygen generated by the decomposition of hydrogen peroxide.

【0027】この場合、過酸化水素の添加濃度は1〜2
0ppmとするのが好ましく、4〜10ppmがより好
ましい。即ち、過酸化水素は通常は殺菌のために用いら
れるが、菌体は過酸化水素の突発的混入に対しては10
ppm程度であれば耐え、常時混入の場合は抗体が形成
されて数十ppmまで耐え得るものとなる。特に、活性
炭を微生物担持担体として使用する場合は、過酸化水素
は容易に分解されるため20ppm程度であれば殺菌作
用を示すことなく溶存酸素濃度を効率的に増加させるこ
とができる。
In this case, the concentration of hydrogen peroxide added is 1-2.
The content is preferably 0 ppm, more preferably 4 to 10 ppm. In other words, hydrogen peroxide is usually used for sterilization, but the cells are less than 10% against sudden contamination of hydrogen peroxide.
In the case of constant contamination, antibodies are formed and can withstand up to several tens of ppm. In particular, when activated carbon is used as a microorganism-carrying carrier, hydrogen peroxide is easily decomposed, so that the concentration of dissolved oxygen can be increased efficiently without a bactericidal action at about 20 ppm.

【0028】図1において過酸化水素の注入手段は記載
されていないが、過酸化水素は、生物反応槽2に直接混
入しても良く、また、回収水を原水槽1に導入する系
路、原水槽1から生物反応槽2に原水を導入する系路、
生物反応槽2から原水槽1へ循環水を返送する系路のい
ずれに注入しても良い。過酸化水素の注入手段は、生物
反応槽2又は生物処理水タンク等に設けた溶存酸素計と
連動させて自動制御で注入するようにすることもでき
る。また、この過酸化水素の注入は連続注入であっても
間欠注入であっても良い。
Although the means for injecting hydrogen peroxide is not shown in FIG. 1, the hydrogen peroxide may be directly mixed into the biological reaction tank 2, or a system for introducing recovered water into the raw water tank 1. A system for introducing raw water from the raw water tank 1 to the biological reaction tank 2;
It may be injected into any of the systems for returning the circulating water from the biological reaction tank 2 to the raw water tank 1. The means for injecting hydrogen peroxide may be automatically controlled and injected in conjunction with a dissolved oxygen meter provided in the biological reaction tank 2 or the biologically treated water tank. The injection of hydrogen peroxide may be continuous injection or intermittent injection.

【0029】なお、本発明において、膜分離装置の型式
や膜の種類等には特に制限はなく、膜の種類は、MF
(精密濾過)膜、UF(限外濾過)膜、RO(逆浸透)
膜等のいずれであっても良いが、オリゴトロフィックバ
クテリアによる生物処理水を処理するのに適したもの、
例えば波板状スパイラルのUF膜などを用いる。また、
膜材質にも特に制限はなく、特に、本発明では、セルロ
ースアセテートなどの塩素に弱い親水性有機膜も使用可
能である。
In the present invention, there is no particular limitation on the type of the membrane separation device, the type of the membrane, and the like.
(Microfiltration) membrane, UF (ultrafiltration) membrane, RO (reverse osmosis)
Any of membranes and the like may be used, but those suitable for treating biologically treated water by oligotrophic bacteria,
For example, a corrugated spiral UF film or the like is used. Also,
There is no particular limitation on the material of the film, and in particular, in the present invention, a hydrophilic organic film such as cellulose acetate, which is weak against chlorine, can be used.

【0030】この膜分離処理に供する生物処理水のpH
には特に制限はないが、中性付近であることが好まし
い。
The pH of the biologically treated water used for this membrane separation treatment
Is not particularly limited, but preferably around neutral.

【0031】このような本発明の方法及び装置は、特
に、超純水の製造システムに組み込まれる回収水の処理
工程に有効に適用される。
The method and apparatus of the present invention are particularly effectively applied to a process for treating recovered water incorporated in a system for producing ultrapure water.

【0032】[0032]

【実施例】以下に実施例及び比較例を挙げて本発明をよ
り具体的に説明する。
The present invention will be described more specifically below with reference to examples and comparative examples.

【0033】実施例1図1に示す処理装置を用いて、下
記処理条件により微量有機物含有水中の有機物の除去を
行った。
Example 1 Using the processing apparatus shown in FIG. 1, organic substances in trace amounts of organic substance-containing water were removed under the following processing conditions.

【0034】〔処理条件〕 原水:半導体基板洗浄排水 TOC:1.5ppm 水温 :20℃ pH :8.0 生物処理法:生物膜濾過式処理 反応時間:20min 膜分離処理法: 膜の種類:コルゲートスパイラルUF膜(材質セルロー
スアセテート) 孔径 :0.02μm 操作圧 :2kgf/cm2 上記の条件による通水で、必要に応じて濃度35%の過
酸化水素を添加することにより、表1に示す通り生物反
応槽出口近傍の生物処理水の溶存酸素濃度が2ppm以
上となるように維持して、1ヶ月間運転を行った結果、
表1に示すように1ヶ月間膜の透過流束は約1.5(m
/day・kgf/cm2)を保つことが可能であっ
た。
[Treatment conditions] Raw water: Semiconductor substrate cleaning wastewater TOC: 1.5 ppm Water temperature: 20 ° C. pH: 8.0 Biological treatment method: Biofilm filtration treatment Reaction time: 20 min Membrane separation treatment method: Type of membrane: corrugated Spiral UF membrane (material: cellulose acetate) Pore size: 0.02 μm Operating pressure: 2 kgf / cm 2 By passing water under the above conditions and adding 35% hydrogen peroxide as required, as shown in Table 1. As a result of operating for one month while maintaining the dissolved oxygen concentration of the biological treatment water near the outlet of the biological reaction tank at 2 ppm or more,
As shown in Table 1, the permeation flux of the membrane for one month was about 1.5 (m
/ Day · kgf / cm 2 ).

【0035】比較例1 実施例1において、生物処理装置の溶存酸素濃度を調整
せずに運転したこと以外は同様にして処理を行ったとこ
ろ、生物処理槽の溶存酸素濃度は、表1に示す通り2p
pmを下回り、膜の透過流束も表1に示す通り低下し
た。
Comparative Example 1 The procedure of Example 1 was repeated except that the operation was performed without adjusting the dissolved oxygen concentration of the biological treatment apparatus. The dissolved oxygen concentration in the biological treatment tank is shown in Table 1. Street 2p
pm, and the permeation flux of the membrane also decreased as shown in Table 1.

【0036】[0036]

【表1】 [Table 1]

【0037】実施例2、比較例2,3 実施例1において、生物処理槽に過酸化水素の注入装置
を設け、濃度35%の過酸化水素水を表2に示す濃度と
なるように常時添加したこと以外は同様にして1ヶ月間
処理を行った(ただし、比較例2では過酸化水素水添加
せず)。その結果、生物処理槽出口近傍の生物処理水の
溶存酸素濃度、膜の透過流束は表2に示す通りとなり、
適量の過酸化水素の注入で生物処理槽の溶存酸素濃度を
2ppm以上に維持することができ、これにより、膜の
透過流束を長期に亘り高く維持することができることが
確認された。
Example 2, Comparative Examples 2 and 3 In Example 1, an apparatus for injecting hydrogen peroxide was provided in the biological treatment tank, and a hydrogen peroxide solution having a concentration of 35% was constantly added so as to have a concentration shown in Table 2. The treatment was performed for one month in the same manner except that the hydrogen peroxide solution was not added in Comparative Example 2. As a result, the dissolved oxygen concentration of the biological treatment water near the biological treatment tank outlet and the permeation flux of the membrane are as shown in Table 2,
It was confirmed that by injecting an appropriate amount of hydrogen peroxide, the dissolved oxygen concentration in the biological treatment tank could be maintained at 2 ppm or more, and as a result, the permeation flux of the membrane could be kept high for a long period of time.

【0038】[0038]

【表2】 [Table 2]

【0039】[0039]

【発明の効果】以上詳述した通り、本発明の微量有機物
含有水の処理方法及び処理装置によれば、TOC5pp
b〜50ppmというような微量の有機物を含有する水
を、オリゴトロフィックバクテリアによる生物処理と膜
分離処理とで処理するに当り、膜の劣化や煩雑な後処理
を必要とすることなく、膜の透過流束の低下を防止して
長期に亘り安定かつ効率的な処理を行うことができる。
As described in detail above, according to the method and apparatus for treating water containing trace organic substances according to the present invention, TOC 5pp
In treating water containing a trace amount of organic substances such as b to 50 ppm by biological treatment with oligotrophic bacteria and membrane separation treatment, the membrane can be treated without deterioration and complicated post-treatment. A stable and efficient treatment can be performed over a long period of time by preventing a decrease in the permeation flux.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の実施の形態を示す系統図である。FIG. 1 is a system diagram showing an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 原水槽 2 生物反応槽 3 生物処理水タンク 4 ストレーナ 5 UF膜分離装置 Reference Signs List 1 raw water tank 2 biological reaction tank 3 biological treatment water tank 4 strainer 5 UF membrane separation device

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 TOCを5ppb〜50ppmの濃度で
含む微量有機物含有水を、オリゴトロフィックバクテリ
アによる生物処理と膜分離処理とにより処理する方法に
おいて、 該生物処理槽の溶存酸素濃度を2ppm以上に維持する
ことを特徴とする微量有機物含有水の処理方法。
1. A method for treating water containing trace amounts of organic substances containing TOC at a concentration of 5 ppb to 50 ppm by biological treatment with oligotrophic bacteria and membrane separation treatment, wherein the dissolved oxygen concentration in the biological treatment tank is 2 ppm or more. A method for treating trace organic matter-containing water, characterized by maintaining.
【請求項2】 請求項1において、該生物処理槽に過酸
化水素を添加して、溶存酸素濃度を2ppm以上に維持
することを特徴とする微量有機物含有水の処理方法。
2. The method according to claim 1, wherein hydrogen peroxide is added to the biological treatment tank to maintain the dissolved oxygen concentration at 2 ppm or more.
【請求項3】 TOCを5ppb〜50ppmの濃度で
含む微量有機物含有水が導入され、オリゴトロフィック
バクテリアにより該水中の汚染物質を分解する生物処理
槽と、該生物処理槽の処理水を膜分離する膜分離装置と
を備えてなる微量有機物含有水の処理装置において、 該生物処理槽が溶存酸素濃度2ppm以上に維持される
ことを特徴とする微量有機物含有水の処理装置。
3. A biological treatment tank into which a trace amount of organic substance-containing water containing TOC at a concentration of 5 ppb to 50 ppm is introduced, and a contaminant in the water is decomposed by oligotrophic bacteria; An apparatus for treating trace organic matter-containing water, comprising: a membrane separation device that performs the treatment. The biological treatment tank is maintained at a dissolved oxygen concentration of 2 ppm or more.
【請求項4】 請求項3において、該生物処理槽に過酸
化水素を供給する手段を設けたことを特徴とする微量有
機物含有水の処理装置。
4. An apparatus for treating water containing a trace amount of organic matter according to claim 3, further comprising means for supplying hydrogen peroxide to said biological treatment tank.
JP09654799A 1999-04-02 1999-04-02 Method and apparatus for treating water containing trace organic matter Expired - Fee Related JP3651306B2 (en)

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JP2010158605A (en) * 2009-01-06 2010-07-22 Kurita Water Ind Ltd Method of producing ultrapure water and apparatus therefor
JP2011183273A (en) * 2010-03-05 2011-09-22 Kurita Water Ind Ltd Water treatment method and method for producing ultrapure water
JP2011183274A (en) * 2010-03-05 2011-09-22 Kurita Water Ind Ltd Water treatment method and process for producing ultrapure water
US8916048B2 (en) 2010-03-05 2014-12-23 Kurita Water Industries Ltd. Water treatment method and method for producing ultrapure water
JP2016172207A (en) * 2015-03-16 2016-09-29 栗田工業株式会社 Membrane treatment method and membrane treatment device of organic substance-containing water
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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002336887A (en) * 2001-05-11 2002-11-26 Kurita Water Ind Ltd Extrapure water making device and extrapure water making method
JP2002336886A (en) * 2001-05-11 2002-11-26 Kurita Water Ind Ltd Extrapure water making device and extrapure water making method
JP2010158605A (en) * 2009-01-06 2010-07-22 Kurita Water Ind Ltd Method of producing ultrapure water and apparatus therefor
JP2011183273A (en) * 2010-03-05 2011-09-22 Kurita Water Ind Ltd Water treatment method and method for producing ultrapure water
JP2011183274A (en) * 2010-03-05 2011-09-22 Kurita Water Ind Ltd Water treatment method and process for producing ultrapure water
US8916048B2 (en) 2010-03-05 2014-12-23 Kurita Water Industries Ltd. Water treatment method and method for producing ultrapure water
JP2016172207A (en) * 2015-03-16 2016-09-29 栗田工業株式会社 Membrane treatment method and membrane treatment device of organic substance-containing water
WO2022259599A1 (en) * 2021-06-07 2022-12-15 オルガノ株式会社 Pure water production method and pure water production apparatus

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