JP2002166139A - Membrane separator - Google Patents

Membrane separator

Info

Publication number
JP2002166139A
JP2002166139A JP2000368269A JP2000368269A JP2002166139A JP 2002166139 A JP2002166139 A JP 2002166139A JP 2000368269 A JP2000368269 A JP 2000368269A JP 2000368269 A JP2000368269 A JP 2000368269A JP 2002166139 A JP2002166139 A JP 2002166139A
Authority
JP
Japan
Prior art keywords
ozone
liquid
tank
treated
membrane
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
JP2000368269A
Other languages
Japanese (ja)
Other versions
JP3832232B2 (en
Inventor
Kiyokazu Takemura
清和 武村
Masato Onishi
真人 大西
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.)
Hitachi Plant Technologies Ltd
Original Assignee
Hitachi Plant Technologies 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 Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Technologies Ltd
Priority to JP2000368269A priority Critical patent/JP3832232B2/en
Publication of JP2002166139A publication Critical patent/JP2002166139A/en
Application granted granted Critical
Publication of JP3832232B2 publication Critical patent/JP3832232B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

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

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)
  • Activated Sludge Processes (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a membrane separator that needs to be less frequently washed with chemicals and is therefore excellent in the ability to treat sewage and the ability to treat living organisms. SOLUTION: The nitrification/denitrification apparatus 10 has an ozone generator 56 that supplies ozone, and the generator 56 is connected to a treatment water tank 38 and to a circulation line 24. Therefore, when ozone is supplied to the treatment liquid 42 in the tank 38 to remove the colorant components from the effluent 42, and ozone is supplied to a treated liquid 20 circulating between the nitrification tank 16 and the denitrification tank 14 to inhibit a gel-like matter from adhering to the filter membrane of the unit 28. The tank 38 is connected to the unit 28 through a pour line 44, and the filter membrane is back-washed with the effluent 42 containing residual ozone.

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】本発明は膜分離装置に係り、
特に、活性汚泥処理を用いた廃水処理施設における膜分
離装置に関する。
TECHNICAL FIELD The present invention relates to a membrane separation device,
In particular, it relates to a membrane separation device in a wastewater treatment facility using activated sludge treatment.

【0002】[0002]

【従来の技術】活性汚泥処理を用いた廃水処理施設にお
いては、最終沈殿池における「バルキング」及び「放線
菌による汚泥浮上」といった固液分離障害が非常に大き
な問題になっている。この問題を解決する手段として、
活性汚泥処理と膜分離を組み合わせた膜分離活性汚泥法
の開発が進められている。この方法は、固液分離の手法
として膜ろ過を採用しているため、処理液の濁質分の流
出を防ぐことができ、且つ、大腸菌も完全に除去できる
ことから、衛生的で、透明度の高い処理液を安定して得
ることができるという特徴を持っている。また、活性汚
泥の高濃度保持が可能であるため、処理時間の短縮、及
び処理施設のコンパクト化が図れる。
2. Description of the Related Art In a wastewater treatment facility using activated sludge treatment, solid-liquid separation obstacles such as "bulking" and "sludge floating by actinomycetes" in a final sedimentation basin are very serious problems. As a solution to this problem,
The development of a membrane separation activated sludge method combining activated sludge treatment and membrane separation has been promoted. Since this method employs membrane filtration as a solid-liquid separation technique, it can prevent outflow of turbid matter in the processing solution, and can completely remove Escherichia coli, which is hygienic and highly transparent. It has the feature that a processing solution can be obtained stably. Further, since the activated sludge can be maintained at a high concentration, the processing time can be reduced and the processing facility can be made compact.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、膜分離
活性汚泥処理を用いた従来の膜分離装置は、処理液に色
度成分が残留したり、膜の目詰まりが起こるという大き
な問題を抱えている。特に、汚泥の性状が悪い場合(即
ち、汚泥のフロックが細かい、生物の代謝物が非常に多
い等)には、処理液の色度が高くなるだけでなく、膜の
目詰まりを起こしやすく、頻繁に膜の薬液洗浄を必要と
し、汚泥性状の更なる悪化を招き、安定運転の妨げにな
っていた。
However, the conventional membrane separation apparatus using the membrane separation activated sludge treatment has a serious problem that a chromaticity component remains in the treatment liquid and membrane clogging occurs. . In particular, when the properties of the sludge are poor (that is, the sludge has a fine floc and a large amount of biological metabolites, etc.), not only the chromaticity of the treatment liquid is increased, but also the membrane is easily clogged, Frequently, chemical cleaning of the membrane was required, causing further deterioration of sludge properties, and hindering stable operation.

【0004】また、従来の膜分離装置は、固液分離手段
を膜のみに頼るため、生物分解しにくい難分解性物質
(生物代謝物)が系外に排出されず、槽内に蓄積されて
いき、膜表面に付着しゲル化して、膜の差圧を上昇させ
る大きな原因になっていた。
Further, in the conventional membrane separation apparatus, since the solid-liquid separation means relies solely on the membrane, the hardly decomposable substances (biometabolites) which are hardly biodegraded are not discharged out of the system, but are accumulated in the tank. It suddenly adhered to the film surface and gelled, which was a major cause of increasing the differential pressure of the film.

【0005】本発明はこのような事情に鑑みて成された
もので、薬品洗浄頻度を減少させ、膜処理性能、及び生
物処理性能の優れた膜分離装置を提供することを目的と
する。
The present invention has been made in view of such circumstances, and an object of the present invention is to provide a membrane separation apparatus which reduces the frequency of chemical cleaning and has excellent membrane treatment performance and biological treatment performance.

【0006】[0006]

【課題を解決するための手段】請求項1記載の発明は前
記目的を達成するために、反応槽に設けられ、該反応槽
に供給された被処理液を膜でろ過して処理液を得るろ過
ユニットと、該ろ過ユニットで得られた処理液を前記ろ
過ユニットに逆流させて前記膜を逆洗する逆洗手段と、
を備えた膜分離装置において、前記反応槽に接続された
循環ラインを介して、前記被処理液を循環させる循環手
段と、該循環手段によって循環する前記循環ライン内の
被処理液と、前記ろ過ユニットで得られた処理液とに、
オゾンを供給するオゾン供給手段を備えたことを特徴と
している。
According to the first aspect of the present invention, in order to achieve the above object, a treatment liquid is provided in a reaction tank, and a liquid to be treated supplied to the reaction tank is filtered through a membrane to obtain a treatment liquid. Filtration unit, backwash means for backwashing the membrane by backflowing the treatment liquid obtained in the filtration unit to the filtration unit,
A circulating means for circulating the liquid to be treated via a circulating line connected to the reaction tank; a liquid to be treated in the circulating line circulated by the circulating means; With the processing solution obtained in the unit,
Ozone supply means for supplying ozone is provided.

【0007】請求項1記載の発明によれば、ろ過ユニッ
トで得られた処理液にオゾンを供給するので、処理液の
色度除去を行うことができるとともに、この処理液によ
って膜を逆洗するので、膜の高い洗浄効果を得ることが
でき、さらには、循環ライン内の被処理液にオゾンを供
給するので、オゾンを効率良く添加して膜にゲル状物質
が付着することを抑制できる。
According to the first aspect of the present invention, ozone is supplied to the processing liquid obtained by the filtration unit, so that the chromaticity of the processing liquid can be removed, and the film is backwashed with the processing liquid. Therefore, a high cleaning effect of the film can be obtained. Further, since ozone is supplied to the liquid to be treated in the circulation line, it is possible to efficiently add ozone and suppress the gel-like substance from adhering to the film.

【0008】請求項2記載の発明によれば、反応槽の被
処理液を性状分析し、この分析結果に基づいて循環ライ
ン内の被処理液に供給するオゾン量を調節するので、常
に適切な量のオゾンを反応槽に供給することができる。
したがって、ろ過ユニットのろ過膜が閉塞することを必
要最小量のオゾンで効果的に抑制できる。
According to the second aspect of the present invention, the property of the liquid to be treated in the reaction tank is analyzed, and the amount of ozone supplied to the liquid to be treated in the circulation line is adjusted based on the result of the analysis. An amount of ozone can be supplied to the reactor.
Therefore, the clogging of the filtration membrane of the filtration unit can be effectively suppressed with a necessary minimum amount of ozone.

【0009】[0009]

【発明の実施の形態】以下添付図面に従って、本発明に
係る膜分離装置の好ましい実施の形態について詳説す
る。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of a membrane separation device according to the present invention will be described below in detail with reference to the accompanying drawings.

【0010】図1は、本発明に係る膜分離装置を適用し
た硝化・脱窒装置10の全体構成を示す概略図である。
FIG. 1 is a schematic diagram showing the entire configuration of a nitrification / denitrification apparatus 10 to which a membrane separation device according to the present invention is applied.

【0011】同図に示すように、硝化・脱窒装置10
は、仕切壁12によって脱窒槽14と硝化槽16とに仕
切られた反応槽を備えている。このうち脱窒槽14に
は、供給ライン18が接続され、この供給ライン18か
ら被処理液(原液)20が供給されて脱窒槽14に貯留
される。脱窒槽14は連通路22を介して硝化槽16に
連通されており、前記脱窒槽14に供給された被処理液
20は、この連通路22を介して硝化槽16に流入す
る。また、硝化槽16は、循環ライン24を介して脱窒
槽14に接続されている。循環ライン24には、ポンプ
26が配設されており、このポンプ26を駆動すること
によって、硝化槽16内の被処理液20の一部が循環ラ
イン24を介して脱窒槽14に戻される。これにより、
被処理液20は硝化槽16と脱窒槽14との間を循環す
る。
As shown in FIG. 1, a nitrification / denitrification device 10
Has a reaction tank partitioned by a partition wall 12 into a denitrification tank 14 and a nitrification tank 16. A supply line 18 is connected to the denitrification tank 14, and a liquid to be treated (raw liquid) 20 is supplied from the supply line 18 and stored in the denitrification tank 14. The denitrification tank 14 communicates with the nitrification tank 16 via a communication passage 22, and the liquid 20 to be treated supplied to the denitrification tank 14 flows into the nitrification tank 16 via the communication passage 22. The nitrification tank 16 is connected to the denitrification tank 14 via a circulation line 24. A pump 26 is provided in the circulation line 24. By driving the pump 26, a part of the liquid 20 to be treated in the nitrification tank 16 is returned to the denitrification tank 14 via the circulation line 24. This allows
The liquid to be treated 20 circulates between the nitrification tank 16 and the denitrification tank 14.

【0012】硝化槽16の内部には、ろ過ユニット28
が設けられ、このろ過ユニット28の下方に散気管30
が配設されている。散気管30は、エア供給ライン32
を介してブロア34に接続されており、ブロア34から
エアが供給されると、このエアを被処理液20中に細か
な気泡として散気する。これにより、被処理液20が攪
拌されるとともに、ろ過ユニット28のろ過膜(不図
示)に付着した付着物を剥離させることができ、さらに
は、被処理液20中の活性汚泥に酸素を供給することが
できる。
A filtration unit 28 is provided inside the nitrification tank 16.
A diffuser 30 is provided below the filtration unit 28.
Are arranged. The air diffuser 30 is provided with an air supply line 32.
When the air is supplied from the blower 34, the air is diffused into the liquid 20 to be treated as fine bubbles. As a result, the liquid 20 to be treated is agitated, and the deposits attached to the filtration membrane (not shown) of the filtration unit 28 can be peeled off. Further, oxygen is supplied to the activated sludge in the liquid 20 to be treated. can do.

【0013】ろ過ユニット28は、排出ライン36を介
して処理水槽38に連通されている。排出ライン36に
は、弁46と、ポンプ40が配設されており、このポン
プ40を駆動することによってろ過ユニット28の内部
に被処理液20を吸引する。その際、被処理液20は、
ろ過ユニット28のろ過膜(不図示)を透過して固液分
離処理され、処理された処理液42が排出ライン36を
介して排出され、処理水槽38に貯留される。
The filtration unit 28 is connected to a treated water tank 38 via a discharge line 36. The discharge line 36 is provided with a valve 46 and a pump 40. By driving the pump 40, the liquid to be treated 20 is sucked into the filtration unit 28. At that time, the liquid 20 to be treated
The solid-liquid separation treatment is performed through a filtration membrane (not shown) of the filtration unit 28, and the treated treatment liquid 42 is discharged through a discharge line 36 and stored in a treatment water tank 38.

【0014】処理水槽38は、注入ライン44を介し
て、弁46よりも上流側の排出ライン36に接続され
る。この注入ライン44には、弁48、ポンプ50が配
設されており、ポンプ50を駆動することによって、処
理水槽38の処理液42がろ過ユニット28内に逆流す
る。これにより、ろ過ユニット28のろ過膜を逆洗する
ことができる。
The treated water tank 38 is connected via an injection line 44 to a discharge line 36 upstream of a valve 46. The injection line 44 is provided with a valve 48 and a pump 50. By driving the pump 50, the processing liquid 42 in the processing water tank 38 flows back into the filtration unit 28. Thereby, the filtration membrane of the filtration unit 28 can be backwashed.

【0015】処理水槽38の底部には、オゾン散気管5
2が配設されている。このオゾン散気管52は、オゾン
供給ライン54を介してオゾン発生器56に連通されて
いる。したがって、オゾン発生器56からオゾン供給ラ
イン54にオゾンガスを供給すると、オゾン散気管52
から処理液42中にオゾンガスが散気される。これによ
り、処理液42がオゾンを含有する。
An ozone diffuser 5 is provided at the bottom of the treated water tank 38.
2 are provided. The ozone diffuser 52 is connected to an ozone generator 56 via an ozone supply line 54. Therefore, when ozone gas is supplied from the ozone generator 56 to the ozone supply line 54, the ozone diffuser 52
Then, the ozone gas is diffused into the processing liquid 42. Thus, the processing liquid 42 contains ozone.

【0016】前記オゾン発生器56は、オゾン供給ライ
ン58を介して循環ライン24に接続されている。した
がって、硝化槽16から脱窒槽14に循環する被処理液
20に、オゾンガスを供給することができる。これによ
り、オゾンを含んだ被処理液20が硝化槽16と脱窒槽
14とを循環する。
The ozone generator 56 is connected to the circulation line 24 via an ozone supply line 58. Therefore, ozone gas can be supplied to the liquid to be treated 20 circulating from the nitrification tank 16 to the denitrification tank 14. As a result, the liquid to be treated 20 containing ozone circulates through the nitrification tank 16 and the denitrification tank 14.

【0017】次に上記の如く構成された硝化・脱窒装置
10の作用について説明する。
Next, the operation of the nitrification / denitrification device 10 configured as described above will be described.

【0018】通常運転時には、弁48を閉じて弁46を
開くとともに、ポンプ40を駆動する。これによって、
被処理液20が生物学的に処理されてろ過ユニット28
に吸引され、吸引された処理液42が排出ライン36を
介して処理水槽38に流入する。処理水槽38に流入し
た処理液42には、オゾン発生器56からオゾンガスが
供給され、このオゾンガスによって処理液42の色度成
分が除去される。したがって、処理液42は、再利用に
適した状態で排水管60から排水される。
During normal operation, the valve 48 is closed and the valve 46 is opened, and the pump 40 is driven. by this,
The liquid to be treated 20 is biologically treated and the filtration unit 28
The suctioned processing liquid 42 flows into the processing water tank 38 via the discharge line 36. Ozone gas is supplied from an ozone generator 56 to the processing liquid 42 flowing into the processing water tank 38, and the chromaticity component of the processing liquid 42 is removed by the ozone gas. Therefore, the processing liquid 42 is drained from the drain pipe 60 in a state suitable for reuse.

【0019】また、通常運転中、循環ライン24のポン
プ26を駆動することによって、被処理液20は、硝化
槽16と脱窒槽14とを循環している。このとき、オゾ
ン発生器56から循環ライン24にオゾンガスが供給さ
れるので、循環する被処理液20に含まれる難分解性物
質(生物代謝物)が低分子化される。したがって、生物
処理を促進させることができ、ろ過ユニット28のろ過
膜にゲル状物質が付着することを抑制することができ
る。なお、循環ライン24へのオゾンガスの供給は、間
欠的であっても、連続的であってもよい。
During the normal operation, the liquid to be treated 20 is circulated in the nitrification tank 16 and the denitrification tank 14 by driving the pump 26 of the circulation line 24. At this time, since the ozone gas is supplied from the ozone generator 56 to the circulation line 24, the hardly decomposable substances (biological metabolites) contained in the circulating liquid to be treated 20 are reduced in molecular weight. Therefore, biological treatment can be promoted, and the attachment of the gel-like substance to the filtration membrane of the filtration unit 28 can be suppressed. The supply of the ozone gas to the circulation line 24 may be intermittent or continuous.

【0020】ろ過ユニット28のろ過膜にゲル状物質が
付着した場合には、ポンプ40を停止して弁46を閉じ
るとともに、弁48を開いてポンプ50を駆動する。こ
れにより、処理水槽38の処理液42が注入ライン44
を介してろ過ユニット28に逆流する。ろ過ユニット2
8に逆流した処理液42は、通常運転時のろ過方向と反
対方向にろ過膜を透過し、ろ過膜に付着したゲル状物質
をろ過膜から剥離させる。このとき、処理液42にはオ
ゾンが残留しているので、ろ過膜は、オゾンの強い酸化
力によって殺菌される。したがって、ろ過膜の洗浄効果
が大きく、洗浄後に高い膜透過流速が得られる。
When the gel substance adheres to the filtration membrane of the filtration unit 28, the pump 40 is stopped to close the valve 46, and the valve 48 is opened to drive the pump 50. As a result, the processing liquid 42 in the processing water tank 38 is
Through the filter unit 28. Filtration unit 2
The treatment liquid 42 flowing back to 8 permeates the filtration membrane in the direction opposite to the filtration direction during normal operation, and peels off the gel-like substance attached to the filtration membrane from the filtration membrane. At this time, since ozone remains in the processing liquid 42, the filtration membrane is sterilized by the strong oxidizing power of ozone. Therefore, the washing effect of the filtration membrane is large, and a high membrane permeation flow rate can be obtained after washing.

【0021】このように本実施の形態の硝化・脱窒装置
10によれば、処理液42にオゾンを供給したので、色
度除去を行うことができるとともに、ろ過膜の逆洗効果
を増加させることができる。
As described above, according to the nitrification / denitrification apparatus 10 of the present embodiment, since ozone is supplied to the processing liquid 42, chromaticity can be removed and the effect of backwashing the filtration membrane can be increased. be able to.

【0022】また、硝化・脱窒装置10によれば、循環
ライン24にオゾンを供給し、オゾンを含んだ被処理液
20を硝化槽16と脱窒槽14とに循環させたので、ろ
過ユニット28の膜の閉塞を抑制することができる。し
たがって、ろ過膜を薬液洗浄する頻度を減少させること
ができ、ろ過膜の寿命を向上させることができる。
According to the nitrification / denitrification apparatus 10, ozone is supplied to the circulation line 24, and the liquid to be treated 20 containing ozone is circulated through the nitrification tank 16 and the denitrification tank 14, so that the filtration unit 28 Blockage of the film can be suppressed. Therefore, the frequency of cleaning the filtration membrane with a chemical solution can be reduced, and the life of the filtration membrane can be improved.

【0023】また、常に所定量の被処理液20が流れる
循環ライン24にオゾンを供給したので、脱窒槽14及
び硝化槽16に効率良くオゾンを供給できるとともに、
脱窒槽14及び硝化槽16の内部のオゾン濃度が偏るこ
とを防止できる。
Since ozone is supplied to the circulation line 24 through which a predetermined amount of the liquid to be treated 20 flows, ozone can be efficiently supplied to the denitrification tank 14 and the nitrification tank 16.
It is possible to prevent the ozone concentration in the denitrification tank 14 and the nitrification tank 16 from being biased.

【0024】さらに、硝化・脱窒装置10によれば、処
理水槽38にオゾンを供給するオゾン発生器56によっ
て、循環ライン24にオゾンを供給するようにしたの
で、装置が大型化することを防止できる。
Further, according to the nitrification / denitrification apparatus 10, ozone is supplied to the circulation line 24 by the ozone generator 56 which supplies ozone to the treated water tank 38, so that the apparatus is prevented from being enlarged. it can.

【0025】図2は、オゾンガス注入量調整手段を備え
た硝化・脱窒装置62の全体構成を示す概略図である。
FIG. 2 is a schematic diagram showing the overall configuration of a nitrification / denitrification device 62 provided with an ozone gas injection amount adjusting means.

【0026】同図に示す硝化・脱窒槽装置62は、オゾ
ン供給ライン58に電磁弁64が配設されている。電磁
弁64は、制御器66によって開閉制御される。
The nitrification / denitrification tank device 62 shown in FIG. 1 has an ozone supply line 58 provided with a solenoid valve 64. The opening and closing of the solenoid valve 64 is controlled by the controller 66.

【0027】制御器66は、電磁弁64の開放時間を制
御することによって循環ライン24に注入されるオゾン
ガス量を調節する。
The controller 66 controls the amount of ozone gas injected into the circulation line 24 by controlling the opening time of the solenoid valve 64.

【0028】また、硝化・脱窒装置62は、性状分析装
置68を備えている。性状分析装置68は、汚泥引込み
管70、汚泥戻し管72を介して硝化槽16に連通され
ており、汚泥引込み管70を介して硝化槽16から汚泥
サンプルを採取する。そして、この汚泥サンプルを分析
し、TOC濃度やろ過比抵抗等の汚泥性状に関するデー
タを獲得した後、汚泥サンプルを汚泥戻し管72を介し
て硝化槽16に返送する。
The nitrification / denitrification device 62 has a property analyzer 68. The property analyzer 68 is connected to the nitrification tank 16 via a sludge inlet pipe 70 and a sludge return pipe 72, and collects a sludge sample from the nitrification tank 16 via the sludge inlet pipe 70. Then, the sludge sample is analyzed, and data on sludge properties such as TOC concentration and filtration specific resistance are acquired. Then, the sludge sample is returned to the nitrification tank 16 via the sludge return pipe 72.

【0029】前記制御器66は、この性状分析装置68
が獲得したデータに基づいて電磁弁64の開放時間、即
ちオゾンガスの注入量を制御する。例えば、性状分析装
置68がTOC濃度のデータを得た場合、制御器66
は、図3に示す曲線に基づいて電磁弁64の開放時間を
制御する。即ち、被処理液20のTOC濃度が高いほ
ど、電磁弁64の開放時間を長く設定して、多量のオゾ
ンガスを循環ライン24に注入する。被処理液20のT
OC濃度が高い場合、被処理液20の濾過性が悪く、ろ
過ユニット28のろ過膜が閉塞しやすい。したがって、
オゾンガスの注入量を増加させることによってろ過膜の
閉塞を効果的に抑制できる。逆に、被処理液20のTO
C濃度が低い場合には、被処理液20はろ過性が良く、
ろ過膜が閉塞されにくいので、オゾンガスの注入量を減
少させる。これにより、オゾンガスの無駄な消費を抑え
ることができる。
The controller 66 includes a property analyzer 68
Controls the opening time of the solenoid valve 64, that is, the injection amount of ozone gas, based on the data acquired by the computer. For example, when the property analyzer 68 obtains the data of the TOC concentration, the controller 66
Controls the opening time of the solenoid valve 64 based on the curve shown in FIG. That is, as the TOC concentration of the liquid to be treated 20 is higher, the opening time of the solenoid valve 64 is set longer, and a larger amount of ozone gas is injected into the circulation line 24. T of liquid 20 to be treated
When the OC concentration is high, the filterability of the liquid to be treated 20 is poor, and the filtration membrane of the filtration unit 28 is easily clogged. Therefore,
Blockage of the filtration membrane can be effectively suppressed by increasing the amount of ozone gas injected. Conversely, the TO of the liquid 20 to be treated
When the C concentration is low, the liquid to be treated 20 has good filterability,
Since the filtration membrane is not easily blocked, the injection amount of ozone gas is reduced. Thereby, useless consumption of ozone gas can be suppressed.

【0030】このように硝化・脱窒装置62によれば、
硝化槽16の汚泥の性状に応じて適切な量のオゾンガス
を循環ライン24に注入するので、必要最小量のオゾン
ガスによってろ過膜の閉塞を効果的に抑制できる。
As described above, according to the nitrification / denitrification device 62,
Since an appropriate amount of ozone gas is injected into the circulation line 24 according to the properties of the sludge in the nitrification tank 16, clogging of the filtration membrane can be effectively suppressed by a necessary minimum amount of ozone gas.

【0031】[0031]

【発明の効果】以上説明したように本発明に係る膜分離
装置によれば、処理液にオゾンを供給したので、処理液
の色度除去を行うことができるとともに、この処理液に
よって膜を逆洗したので、膜の高い洗浄効果を得ること
ができ、さらには、循環する被処理液にオゾンを供給し
たので、膜にゲル状物質が付着することを抑制できる。
したがって、本発明の膜分離装置は、膜の薬品洗浄頻度
が少なく、且つ、膜の処理性能と生物処理性能が優れて
いるので、排水処理を効率良く、低コストで行うことが
できる。
As described above, according to the membrane separation apparatus of the present invention, since ozone is supplied to the processing liquid, the chromaticity of the processing liquid can be removed, and the film is reversed by the processing liquid. Since the cleaning is performed, a high cleaning effect of the film can be obtained. Further, since ozone is supplied to the circulating liquid to be processed, it is possible to suppress the gel-like substance from being attached to the film.
Therefore, the membrane separation device of the present invention can perform wastewater treatment efficiently and at low cost because the frequency of chemical cleaning of the membrane is low and the treatment performance and biological treatment performance of the membrane are excellent.

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

【図1】本発明に係る膜分離装置を適用した硝化・脱窒
装置の全体構成を示す概略図
FIG. 1 is a schematic diagram showing the overall configuration of a nitrification / denitrification apparatus to which a membrane separation device according to the present invention is applied.

【図2】オゾンガス注入量調整手段を備えた硝化・脱窒
装置の全体構成を示す概略図
FIG. 2 is a schematic diagram showing the overall configuration of a nitrification / denitrification device having an ozone gas injection amount adjusting means.

【図3】TOC濃度による制御例を示す図FIG. 3 is a diagram showing a control example based on TOC concentration;

【符号の説明】[Explanation of symbols]

10…硝化・脱窒装置、14…脱窒槽、16…硝化槽、
18…供給ライン、20…被処理液、24…循環ライ
ン、28…ろ過ユニット、30…散気管、36…排出ラ
イン、38…処理水槽、42…処理液、44…注入ライ
ン、52…オゾン散気管、54…オゾン供給ライン、5
6…オゾン発生器、58…オゾン供給ライン、64…電
磁弁、66…制御器、68…性状分析装置
10: nitrification / denitrification equipment, 14: denitrification tank, 16: nitrification tank,
18 ... supply line, 20 ... liquid to be treated, 24 ... circulation line, 28 ... filtration unit, 30 ... diffuser tube, 36 ... discharge line, 38 ... treatment water tank, 42 ... treatment liquid, 44 ... injection line, 52 ... ozone dispersion Trachea, 54 ozone supply line, 5
6 ozone generator, 58 ozone supply line, 64 solenoid valve, 66 controller, 68 property analyzer

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 3/12 ZAB C02F 3/12 ZABS Fターム(参考) 4D006 GA02 HA93 KA02 KA31 KA63 KB22 KB23 KC03 KC13 KC16 KD21 PA02 PB08 PC62 PC64 4D028 AC03 AC09 BC17 BD00 BD08 BD17 CA00 CB03 CC06 4D050 AA12 AB03 BB02 BD08 CA09 CA17 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI theme coat ゛ (Reference) C02F 3/12 ZAB C02F 3/12 ZABS F-term (Reference) 4D006 GA02 HA93 KA02 KA31 KA63 KB22 KB23 KC03 KC13 KC16 KD21 PA02 PB08 PC62 PC64 4D028 AC03 AC09 BC17 BD00 BD08 BD17 CA00 CB03 CC06 4D050 AA12 AB03 BB02 BD08 CA09 CA17

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】反応槽に設けられ、該反応槽に供給された
被処理液を膜でろ過して処理液を得るろ過ユニットと、
該ろ過ユニットで得られた処理液を前記ろ過ユニットに
逆流させて前記膜を逆洗する逆洗手段と、を備えた膜分
離装置において、 前記反応槽に接続された循環ラインを介して、前記被処
理液を循環させる循環手段と、 該循環手段によって循環する前記循環ライン内の被処理
液と、前記ろ過ユニットで得られた処理液とに、オゾン
を供給するオゾン供給手段を備えたことを特徴とする膜
分離装置。
1. A filtration unit provided in a reaction tank, wherein a filtration target liquid supplied to the reaction tank is filtered through a membrane to obtain a processing liquid.
A backwash means for backflowing the treatment liquid obtained in the filtration unit to the filtration unit and backwashing the membrane; anda membrane separation device comprising: a circulating line connected to the reaction tank; Circulating means for circulating the liquid to be treated, ozone supplying means for supplying ozone to the liquid to be treated in the circulation line circulated by the circulating means, and the processing liquid obtained by the filtration unit. Characteristic membrane separation device.
【請求項2】前記オゾン供給手段が前記循環ライン内の
被処理液に供給するオゾン量を調節する調節手段と、 前記反応槽の被処理液を性状分析する分析手段と、 該分析手段の分析結果に基づいて前記調節手段を制御す
る制御手段と、 を備えたことを特徴とする請求項1記載の膜分離装置。
2. An adjusting means for adjusting an amount of ozone to be supplied to the liquid to be treated in the circulation line by the ozone supply means; an analyzing means for analyzing the properties of the liquid to be treated in the reaction tank; The membrane separation device according to claim 1, further comprising: a control unit that controls the adjustment unit based on a result.
JP2000368269A 2000-12-04 2000-12-04 Membrane separator Expired - Fee Related JP3832232B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000368269A JP3832232B2 (en) 2000-12-04 2000-12-04 Membrane separator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000368269A JP3832232B2 (en) 2000-12-04 2000-12-04 Membrane separator

Publications (2)

Publication Number Publication Date
JP2002166139A true JP2002166139A (en) 2002-06-11
JP3832232B2 JP3832232B2 (en) 2006-10-11

Family

ID=18838553

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
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JP2005103406A (en) * 2003-09-30 2005-04-21 Kubota Corp Chemical cleaning device
WO2005077839A1 (en) * 2004-02-13 2005-08-25 Asahi Organic Chemicals Industry Co., Ltd. Method for treating organic wastewater
JP2007222830A (en) * 2006-02-27 2007-09-06 Kubota Corp Treatment method of nitrogen-containing organic wastewater, and treatment apparatus for it
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JP2010207657A (en) * 2009-03-06 2010-09-24 Hitachi Plant Technologies Ltd Wastewater treatment apparatus and wastewater treatment method
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Publication number Priority date Publication date Assignee Title
JP2005103406A (en) * 2003-09-30 2005-04-21 Kubota Corp Chemical cleaning device
WO2005077839A1 (en) * 2004-02-13 2005-08-25 Asahi Organic Chemicals Industry Co., Ltd. Method for treating organic wastewater
JP2007222830A (en) * 2006-02-27 2007-09-06 Kubota Corp Treatment method of nitrogen-containing organic wastewater, and treatment apparatus for it
JP2010069359A (en) * 2008-09-16 2010-04-02 Kobelco Eco-Solutions Co Ltd Water treatment device and water treatment method
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JP2010207657A (en) * 2009-03-06 2010-09-24 Hitachi Plant Technologies Ltd Wastewater treatment apparatus and wastewater treatment method
CN106186592A (en) * 2016-09-12 2016-12-07 南京大学 A kind of device removing nitrate nitrogen in resin desorption liquid and technique for applying thereof
CN106186592B (en) * 2016-09-12 2020-08-04 南京大学 Device for removing nitrate nitrogen in resin desorption liquid and application process thereof
JP2018192419A (en) * 2017-05-17 2018-12-06 株式会社クボタ Organic waste water treatment method and organic waste water treatment system
JP7015117B2 (en) 2017-05-17 2022-02-02 株式会社クボタ Organic wastewater treatment method and organic wastewater treatment system
JP6430091B1 (en) * 2018-05-30 2018-11-28 三菱電機株式会社 Membrane cleaning apparatus and membrane cleaning method
WO2019229866A1 (en) * 2018-05-30 2019-12-05 三菱電機株式会社 Membrane cleaning device and membrane cleaning method

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