JPH09215988A - Biological membrane filter - Google Patents

Biological membrane filter

Info

Publication number
JPH09215988A
JPH09215988A JP8048237A JP4823796A JPH09215988A JP H09215988 A JPH09215988 A JP H09215988A JP 8048237 A JP8048237 A JP 8048237A JP 4823796 A JP4823796 A JP 4823796A JP H09215988 A JPH09215988 A JP H09215988A
Authority
JP
Japan
Prior art keywords
draft tube
water
filter medium
tank
biological 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
JP8048237A
Other languages
Japanese (ja)
Other versions
JP3432668B2 (en
Inventor
Yutaka Yoneyama
豊 米山
Hiroshi Sakuma
博司 佐久間
Riyuuu Kou
龍雨 黄
Yuuko Shichimori
祐子 七森
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.)
Ebara Corp
Original Assignee
Ebara Corp
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 Ebara Corp filed Critical Ebara Corp
Priority to JP04823796A priority Critical patent/JP3432668B2/en
Publication of JPH09215988A publication Critical patent/JPH09215988A/en
Application granted granted Critical
Publication of JP3432668B2 publication Critical patent/JP3432668B2/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

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

Abstract

PROBLEM TO BE SOLVED: To provide a biological membrane filter which does not require to ensure washing water and incidental equipment caused by washing operation by omitting a washing process. SOLUTION: In an ascending flow biological membrane filter apparatus having a packet bad of a floated filter material 10 is passing raw water through the packed bad as ascending flow, a draft tube 9 is arranged in the packed bed and a jet pipe 8 is provided in the draft tube 9 and water streams or air accompanied by water streams is downwardly introduced into the draft tube 9 to continuously move the floatable filter material 10 from the upper part of a tank to the lower part thereof.

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BOD、アンモニア性
窒素、有機体窒素を含有する下水、し尿、産業廃水を対
象とした上向流生物膜濾過装置に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an upflow biofilm filter for sewage, human waste and industrial wastewater containing BOD, ammonia nitrogen and organic nitrogen.

【0002】[0002]

【従来の技術】最近、直径3〜10mmの球形の水に浮く
浮上濾材を用いた上向流生物膜濾過法の開発が盛んに行
われている。図5は生物膜濾過装置の一例を示す概略図
である。生物膜濾過装置は濾材充填部6を備え、濾材充
填部6の上部には濾材流出防止を兼ねた集水板7が設け
られている。濾材充填部6に浮上濾材を充填し、原水1
を上向流に通水し、廃水中のBOD、アンモニア性窒素、
有機体窒素除去を行うことができる。この濾過方法は、
濾層内にBOD酸化菌、あるいは硝化菌、脱窒素菌を高濃
度で維持できるため、高速処理が可能な技術である。な
お、図5において、符号2は処理水、符号3は洗浄水排
出口、符号4は洗浄水供給配管、符号5は空気配管であ
る。
2. Description of the Related Art Recently, an upflow biofilm filtration method using a levitation filter medium having a diameter of 3 to 10 mm and floating in water has been actively developed. FIG. 5 is a schematic view showing an example of the biofilm filtration device. The biofilm filtration device is provided with a filter medium filling section 6, and a water collecting plate 7 which also functions as a filter medium outflow prevention is provided above the filter medium filling section 6. Float filter medium is filled in the filter medium filling section 6 and raw water 1
Through the upflow, BOD in the wastewater, ammonia nitrogen,
Organic nitrogen removal can be performed. This filtration method
BOD oxidizing bacteria, nitrifying bacteria, and denitrifying bacteria can be maintained at a high concentration in the filter bed, which is a technology that enables high-speed processing. In FIG. 5, reference numeral 2 is treated water, reference numeral 3 is wash water outlet, reference numeral 4 is wash water supply pipe, and reference numeral 5 is air pipe.

【0003】[0003]

【発明が解決しようとする課題】上述の方法では、通水
を連続的に行うと、捕捉したSS(浮遊物質)の蓄積とBO
Dの分解あるいは窒素処理に伴い増殖した菌体による生
物膜の肥大により、濾過抵抗が増加するため、定期的な
洗浄が必要であった。このため、逆洗用の洗浄水の確
保、空気洗浄用の空気、さらには逆洗に必要な付帯設備
が必要であった。
In the above method, when water is continuously supplied, the accumulated SS (suspended matter) and BO
Periodic washing was necessary because the filtration resistance increased due to the enlargement of the biofilm due to the decomposition of D or the growth of bacterial cells accompanying nitrogen treatment. For this reason, it was necessary to secure cleaning water for backwashing, air for air washing, and additional equipment necessary for backwashing.

【0004】本発明は上述の事情に鑑みなされたもの
で、洗浄工程を省略することにより洗浄水を確保する必
要がなく、かつ洗浄操作に起因した付帯設備を省略する
ことができる生物膜濾過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 circumstances, and it is not necessary to secure the washing water by omitting the washing step, and it is possible to omit the auxiliary equipment resulting from the washing operation. The purpose is to provide.

【0005】[0005]

【課題を解決するための手段】上述の目的を達成するた
め本発明は、充填層に浮上性の濾材を充填し、原水を上
向流にて通水する上向流生物膜濾過装置において、充填
層内にドラフトチュ−ブを設置し、ドラフトチュ−ブ内
に噴出管を設け、下方向に水流あるいは水流に同伴した
空気をドラフトチュ−ブ内に導入することにより、浮上
濾材を槽上部から下部に連続移動させることを特徴とす
るものである。
In order to achieve the above-mentioned object, the present invention provides an upflow biofilm filtration device in which a packed bed is filled with a buoyant filter medium and raw water is passed in an upward flow. A draft tube is installed in the packed bed, an ejection pipe is provided in the draft tube, and a floating water filter or the air entrained in the water flow is introduced downward into the draft tube, whereby the flotation filter medium is placed above the tank. It is characterized by continuously moving from the bottom to the bottom.

【0006】[0006]

【実施例】以下、本発明に係る生物膜濾過装置の実施例
を図1乃至図4を参照して説明する。図1は本発明の生
物膜濾過装置の概念図である。生物膜濾過装置は濾材充
填部6を備えており、濾材充填部6の上部に濾材流出防
止用の集水板7が設けられている。充填層中央部にはド
ラフトチュ−ブ9が設置してあり、ドラフトチュ−ブ9
内に水流あるいは水流に同伴した空気を下方に噴出する
噴出管8が設けられている。浮上濾材10はドラフトチ
ューブ9内に形成される下向きの水流に同伴し、槽上部
にある浮上濾材はドラフトチュ−ブ9を通り槽下部に移
動する。槽下部のドラフトチュ−ブ外側に移動した浮上
濾材は再び槽上部に移動する。このように浮上濾材10
が連続的に移動するため、濾材間に補捉されたSS及び
肥大した生物膜は剥離され、処理水と共に系外に排出さ
れる。処理水と共に系外に排出されたSSは放流水質に応
じ、重力沈殿、凝集沈殿、浮上濾過等種々の物理化学的
処理法により除去される。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the biofilm filtration device according to the present invention will be described below with reference to FIGS. FIG. 1 is a conceptual diagram of the biofilm filtration device of the present invention. The biofilm filtration device includes a filter medium filling section 6, and a water collecting plate 7 for preventing the filter medium outflow is provided above the filter medium filling section 6. A draft tube 9 is installed at the center of the packed bed.
An ejection pipe 8 for ejecting a water flow or air entrained in the water flow downward is provided therein. The floating filter medium 10 is entrained in the downward water flow formed in the draft tube 9, and the floating filter medium at the upper part of the tank moves through the draft tube 9 to the lower part of the tank. The floating filter medium that has moved to the outside of the draft tube at the bottom of the tank moves to the top of the tank again. In this way, the floating filter medium 10
, The SS trapped between the filter media and the enlarged biofilm are peeled off, and are discharged out of the system together with the treated water. The SS discharged out of the system together with the treated water is removed by various physicochemical treatment methods such as gravity precipitation, coagulation sedimentation, and floating filtration depending on the quality of the discharged water.

【0007】ドラフトチュ−ブ9内の噴出管8から水流
のみを排出する場合はBODの酸化、窒素の硝化に必要な
空気を供給するため、槽底部よりドラフトチュ−ブ外側
部を曝気する。一方、水流と同伴空気の場合は槽底部よ
りドラフトチュ−ブ外側部の曝気は行わない。だだし、
BOD負荷、アンモニア負荷の高いとき、空気量が多く必
要な場合は前者の方式を用いることが好ましい。水流に
空気を同伴する方法は図1で示したポンプ16の吐出側
に空気配管5を接続させるほかに、エジェクタ−等を利
用しても良い。ドラフトチュ−ブ9内の噴出管8の位置
はドラフトチュ−ブ長さ、管径により異なる。また濾材
の移動速度に応じて噴出管の位置を適宜決定する。さら
に、噴出管の直径をd、ドラフトチューブの直径をDと
すると、両者のd/D比は、0.4〜0.6が通常用いられる
が、気体の吹込み量が少ない場合はd/D比を大きくす
ることができる。濾材の移動速度は濾材の見かけ比重に
より変わり、見かけ比重の大きいもの程ドラフトチュー
ブ内の移動速度は大きくなる。したがって、濾材の見か
け比重に応じて液量、空気量を調節することが必要とな
る。なお、図1において、符号17はブロワーである。
When only the water flow is discharged from the jet pipe 8 in the draft tube 9, the air necessary for the oxidation of BOD and the nitrification of nitrogen is supplied, so that the outside of the draft tube is aerated from the bottom of the tank. On the other hand, in the case of water flow and entrained air, the outside of the draft tube is not aerated from the bottom of the tank. However,
When the BOD load and the ammonia load are high and a large amount of air is required, it is preferable to use the former method. As a method of entraining air in the water flow, an ejector or the like may be used instead of connecting the air pipe 5 to the discharge side of the pump 16 shown in FIG. The position of the ejection pipe 8 in the draft tube 9 varies depending on the draft tube length and the pipe diameter. Further, the position of the ejection pipe is appropriately determined according to the moving speed of the filter medium. Further, assuming that the diameter of the ejection pipe is d and the diameter of the draft tube is D, a d / D ratio of both is usually 0.4 to 0.6. However, when the gas injection amount is small, the d / D ratio is increased. can do. The moving speed of the filter medium changes depending on the apparent specific gravity of the filter medium, and the moving speed in the draft tube increases as the apparent specific gravity increases. Therefore, it is necessary to adjust the liquid amount and the air amount according to the apparent specific gravity of the filter medium. In FIG. 1, reference numeral 17 is a blower.

【0008】次に窒素処理に本法を適用した例を図2を
参照して説明する。 図2に示す生物膜濾過装置は、第
一番目に原水を上向流で通水する脱窒槽11を配置し、
続いて硝化槽12を配置し、硝化液の一部を前記脱窒槽
1に戻しBOD、窒素を処理するようにしている。脱窒槽
1、硝化槽2には、それぞれ浮上性の粒状濾材が充填さ
れ、槽上部には濾材流出防止を兼ねた集水板が設けられ
ている。そして、原水を上向流に通水し、硝化槽12で
は原水中のアンモニア性窒素を硝化菌の作用で硝酸性窒
素に酸化処理し、脱窒槽11では硝化液中の硝酸性窒素
を脱窒菌の作用で原水中のBOD成分を利用しながら窒素
ガスに還元処理する。
Next, an example in which the present method is applied to nitrogen treatment will be described with reference to FIG. In the biofilm filtration device shown in FIG. 2, the denitrification tank 11 for passing raw water in an upward flow is arranged firstly,
Subsequently, the nitrification tank 12 is arranged, and a part of the nitrification solution is returned to the denitrification tank 1 to treat BOD and nitrogen. The denitrification tank 1 and the nitrification tank 2 are each filled with a buoyant granular filter medium, and a water collecting plate that also functions as a filter medium outflow prevention is provided at the upper part of the tank. Then, the raw water is passed upward, the nitrification tank 12 oxidizes the ammoniacal nitrogen in the raw water into nitrate nitrogen by the action of nitrifying bacteria, and the denitrification tank 11 denitrifies the nitrate nitrogen in the nitrification solution. By the action of, the reduction treatment to nitrogen gas is performed while utilizing the BOD component in the raw water.

【0009】図3は一槽で窒素を除去する生物膜濾過装
置の例を示す図である。図3に示す生物膜濾過装置は嫌
気部11′と好気部12′とを備え、好気部12′でア
ンモニア性窒素を硝化し、硝化により生じた硝酸性窒素
を含む処理水の一部を嫌気部11′で原水中のBODを利
用して循環水中の硝酸性窒素を除去する。これらの両系
列の硝化槽12(図2)あるいは好気部12′(図3)
にドラフトチュ−ブ9を設け、図1に示すように浮上濾
材の連続移動を行うことにより、濾材間に補捉されたS
S及び肥大した生物膜は剥離され、処理水と共に系外に
排出される。図2及び図3において、符号13は硝化槽
循環液を示し、符号5は空気配管を示す。
FIG. 3 is a diagram showing an example of a biofilm filtration device for removing nitrogen in one tank. The biofilm filtration device shown in FIG. 3 includes an anaerobic part 11 'and an aerobic part 12', and nitrifies ammoniacal nitrogen in the aerobic part 12 ', and a part of treated water containing nitrate nitrogen produced by nitrification. In the anaerobic section 11 ', the nitrate nitrogen in the circulating water is removed by using the BOD in the raw water. Both of these series of nitrification tanks 12 (Fig. 2) or aerobic section 12 '(Fig. 3)
The draft tube 9 is provided on the above, and the floating filter medium is continuously moved as shown in FIG.
S and the enlarged biofilm are peeled off and discharged out of the system together with the treated water. 2 and 3, reference numeral 13 indicates a nitrification tank circulating liquid, and reference numeral 5 indicates an air pipe.

【0010】図4は装置が大規模になった場合の本法の
適用例を示す図である。槽間に隔壁14を設け、各槽毎
にドラフトチュ−ブ9を設け、ドラフトチューブ9内に
水流あるいは水流に同伴した空気を下方に噴出する噴出
管8を設ける。これによって、図1に示すと同様に浮上
濾材の連続移動を行うことにより、濾材間に補捉された
SS及び肥大した生物膜は剥離され、処理水と共に系外
に排出される。
FIG. 4 is a diagram showing an application example of the present method when the apparatus becomes large-scale. A partition 14 is provided between the tanks, a draft tube 9 is provided for each tank, and a jet tube 8 for jetting a water flow or air entrained in the water flow downward is provided in the draft tube 9. As a result, by continuously moving the floating filter medium as shown in FIG. 1, the SS trapped between the filter medium and the enlarged biofilm are peeled off and discharged together with the treated water to the outside of the system.

【0011】[0011]

【発明の効果】以上説明したように、本発明によれば、
充填層に浮上性の濾材を充填し、原水を上向流にて通水
する上向流生物膜濾過装置において、充填層内にドラフ
トチュ−ブを設置し、ドラフトチュ−ブ内に噴出管を設
けることにより、下方向に水流あるいは水流に同伴した
空気を噴出させ、浮上濾材を槽上部から下部に連続移動
させることにより、濾材間に捕捉されたSS及び肥大し
た生物膜は剥離して処理水と共に系外に排出される。そ
のため、従来の浮上濾材を用いた上向流生物膜濾過処理
で行っていた洗浄工程が省略でき、また、洗浄水の確
保、空気洗浄用設備等洗浄操作に起因した付帯設備がな
くなる他に、連続的な排水処理が可能となる。
As described above, according to the present invention,
In an upflow biofilm filtration device in which a packed bed is filled with a buoyant filter medium and raw water is passed through in an upward flow, a draft tube is installed in the packed bed, and an ejection pipe is installed in the draft tube. By providing a water flow or air entrained in the water flow downward and continuously moving the levitation filter medium from the upper part to the lower part of the tank, the SS trapped between the filter media and the enlarged biofilm are separated and treated. It is discharged out of the system together with water. Therefore, it is possible to omit the washing step that was carried out in the upflow biofilm filtration treatment using the conventional flotation filter material, and also to secure the wash water, and to eliminate the incidental equipment due to the washing operation such as the equipment for air washing, Enables continuous wastewater treatment.

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

【図1】本発明に係る生物膜濾過装置の一実施例を示す
概略図である。
FIG. 1 is a schematic view showing an embodiment of a biofilm filtration device according to the present invention.

【図2】本発明に係る生物膜濾過装置の他の実施例を示
す概略図である。
FIG. 2 is a schematic view showing another embodiment of the biofilm filtration device according to the present invention.

【図3】本発明に係る生物膜濾過装置の更に他の実施例
を示す概略図である。
FIG. 3 is a schematic view showing still another embodiment of the biofilm filtration device according to the present invention.

【図4】本発明に係る生物膜濾過装置の更に他の実施例
を示す概略図である。
FIG. 4 is a schematic view showing still another embodiment of the biofilm filtration device according to the present invention.

【図5】従来の生物膜濾過装置を示す概略図である。FIG. 5 is a schematic view showing a conventional biofilm filtration device.

【符号の説明】[Explanation of symbols]

1 原水 2 処理水 3 洗浄水排出口 4 洗浄水供給配管 5 空気配管 6 濾材充填部 7 集水板 8 噴出管 9 ドラフトチューブ 10 浮上濾材 11 脱窒槽 11′ 嫌気部 12 硝化槽 12′ 好気部 13 硝化槽循環液 14 隔壁 1 Raw water 2 Treated water 3 Wash water outlet 4 Wash water supply pipe 5 Air pipe 6 Filter medium filling part 7 Water collecting plate 8 Jet pipe 9 Draft tube 10 Floating filter medium 11 Denitrification tank 11 'Anaerobic part 12 Nitrification tank 12' Aerobic part 13 Nitrification tank circulating liquid 14 Partition wall

───────────────────────────────────────────────────── フロントページの続き (72)発明者 七森 祐子 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 (72) Inventor Yuko Nanamori 11-11 Haneda Asahi-cho, Ota-ku, Tokyo Inside EBARA CORPORATION

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 充填層に浮上性の濾材を充填し、原水を
上向流にて通水する上向流生物膜濾過装置において、充
填層内にドラフトチュ−ブを設置し、ドラフトチュ−ブ
内に噴出管を設け、下方向に水流あるいは水流に同伴し
た空気をドラフトチューブ内に導入することにより、浮
上濾材を槽上部から下部に連続移動させることを特徴と
する上向流生物膜濾過装置。
1. An upflow biofilm filtration device in which a packed bed is filled with a buoyant filter medium and raw water is passed through in an upward flow, and a draft tube is installed in the packed bed to provide a draft tube. Upflow biofilm filtration characterized by continuously moving the levitation filter medium from the upper part of the tank to the lower part by installing a jetting pipe in the tank and introducing water flow or air entrained in the water flow downward into the draft tube. apparatus.
JP04823796A 1996-02-09 1996-02-09 Biofilm filtration device Expired - Fee Related JP3432668B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP04823796A JP3432668B2 (en) 1996-02-09 1996-02-09 Biofilm filtration device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP04823796A JP3432668B2 (en) 1996-02-09 1996-02-09 Biofilm filtration device

Publications (2)

Publication Number Publication Date
JPH09215988A true JPH09215988A (en) 1997-08-19
JP3432668B2 JP3432668B2 (en) 2003-08-04

Family

ID=12797847

Family Applications (1)

Application Number Title Priority Date Filing Date
JP04823796A Expired - Fee Related JP3432668B2 (en) 1996-02-09 1996-02-09 Biofilm filtration device

Country Status (1)

Country Link
JP (1) JP3432668B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006263605A (en) * 2005-03-24 2006-10-05 Ngk Insulators Ltd Suspended carrier-used biological treatment apparatus
CN111995051A (en) * 2020-08-03 2020-11-27 河海大学 Integrated bio-membrane reactor

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006263605A (en) * 2005-03-24 2006-10-05 Ngk Insulators Ltd Suspended carrier-used biological treatment apparatus
CN111995051A (en) * 2020-08-03 2020-11-27 河海大学 Integrated bio-membrane reactor

Also Published As

Publication number Publication date
JP3432668B2 (en) 2003-08-04

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