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JPH07204686A - Method and apparatus for nitration-denitrification using biological membrane - Google Patents

Method and apparatus for nitration-denitrification using biological membrane

Info

Publication number
JPH07204686A
JPH07204686A JP570294A JP570294A JPH07204686A JP H07204686 A JPH07204686 A JP H07204686A JP 570294 A JP570294 A JP 570294A JP 570294 A JP570294 A JP 570294A JP H07204686 A JPH07204686 A JP H07204686A
Authority
JP
Japan
Prior art keywords
treated water
filter bed
biofilm
denitrification
anaerobic
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
JP570294A
Other languages
Japanese (ja)
Other versions
JP2721795B2 (en
Inventor
Yoshio Tomita
美穂 富田
Yoshihiko Nakayama
芳彦 中山
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP570294A priority Critical patent/JP2721795B2/en
Publication of JPH07204686A publication Critical patent/JPH07204686A/en
Application granted granted Critical
Publication of JP2721795B2 publication Critical patent/JP2721795B2/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

PURPOSE:To downsize equipment and to improve the recovery ratio of treated water. CONSTITUTION:Raw water is supplied from a raw water supply part 11 at the upper end of a nitrification-denitrification biological membrane filter bed 3 in which an aerobic biological membrane filter bed 1 is installed on the upper stage and an anaerobic biological membrane filter bed 2 is installed on the lower stage to nitrify MH4-N. The nitrified liquid, after being mixed with a hydrogen donor, is denitrified in the lower stage. The anaerobically treated water is returned to the upper end of the nitrification-denitrification biological membrane filter bed 1 by a circulating pump 6 and discharged as treated water from a treated water discharge part 12 placed between the upper and lower stages.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、下水の処理等に利用さ
れる生物膜を利用した硝化脱窒方法及び装置に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a nitrification denitrification method and apparatus utilizing a biofilm used for treating sewage and the like.

【0002】[0002]

【従来の技術】生物膜を利用した従来の硝化脱窒方法と
しては、図3に示すように上段に好気性生物膜ろ床1
を、下段に嫌気性生物膜ろ床2を設けた硝化脱窒生物膜
ろ床3の上端から原水を供給し、上段で硝化させた硝化
液にCH3OH を水素供与体として添加しつつ下段で脱窒す
る方法がある。
2. Description of the Related Art As a conventional nitrification denitrification method utilizing a biofilm, as shown in FIG.
The raw water is supplied from the upper end of the nitrifying / denitrifying biofilm filter bed 3 provided with the anaerobic biofilm filter bed 2 in the lower part, and CH 3 OH is added as a hydrogen donor to the nitrification solution nitrified in the upper part while the lower part is added. There is a method to denitrify.

【0003】ところがこのような従来の方法では、添加
したCH3OH が脱窒反応時にすべて使用されず、硝化脱窒
生物膜ろ床3の下端から取り出される処理水中に流出す
ることがある。また、CH3OH の添加によってSSが多く発
生して、処理水のSSが高くなる。このため、図3に示す
ように硝化脱窒生物膜ろ床3の後段に再曝気槽4を設
け、残余のCH3OH およびSSを除去する必要がある。従っ
て設備が大型化するという問題や、再曝気槽4も洗浄す
る必要があるために処理水の回収率が低下するといった
問題があった。
However, in such a conventional method, the added CH 3 OH may not be used at all during the denitrification reaction and may flow out into the treated water taken out from the lower end of the nitrifying / denitrifying biofilm filter bed 3. In addition, a large amount of SS is generated by the addition of CH 3 OH, and the SS of treated water becomes high. Therefore, as shown in FIG. 3, it is necessary to install a re-aeration tank 4 after the nitrification denitrification biofilm filter bed 3 to remove residual CH 3 OH and SS. Therefore, there are problems that the equipment becomes large and that the recovery rate of the treated water decreases because the re-aeration tank 4 also needs to be cleaned.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決して、設備を小型化することができ、ま
た処理水の回収率を向上させることができる生物膜を利
用した硝化脱窒方法とそのための装置を提供するために
完成されたものである。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, can downsize the equipment, and can improve the recovery rate of treated water. It has been completed to provide a denitrification method and a device therefor.

【0005】[0005]

【課題を解決するための手段】上記の課題を解決するた
めになされた本発明の生物膜を利用した硝化脱窒方法
は、上段に好気性生物膜ろ床を、下段に嫌気性生物膜ろ
床を設けた硝化脱窒生物膜ろ床の上端から原水を供給
し、上段で硝化させた硝化液に水素供与体を添加しつつ
下段で脱窒するとともに、得られた嫌気性処理水を硝化
脱窒生物膜ろ床の上端へ返送し、上段と下段の中間位置
から処理水として取り出すことを特徴とするものであ
る。また上記の課題を解決するためになされた本発明の
生物膜を利用した硝化脱窒装置は、上段に好気性生物膜
ろ床を、下段に嫌気性生物膜ろ床を設けた硝化脱窒生物
膜ろ床の上端に原水供給部を設けるとともに、嫌気性生
物膜ろ床の下端から取り出された嫌気性処理水を硝化脱
窒生物膜ろ床の上端へ返送する循環ポンプを設け、更に
上段と下段の中間位置に水素供与体添加部と処理水取出
部とを設けたことを特徴とするものである。
A method for nitrifying and denitrifying using a biofilm of the present invention, which has been made to solve the above problems, comprises an aerobic biofilm filter in the upper stage and an anaerobic biofilm filter in the lower stage. Raw water is supplied from the upper end of the nitrifying denitrification biofilm filter bed provided with a bed, while the hydrogen donor is added to the nitrification solution nitrified in the upper stage, while denitrifying in the lower stage, and the resulting anaerobic treated water is nitrified. It is characterized in that it is returned to the upper end of the denitrification biomembrane filter and taken out as treated water from an intermediate position between the upper and lower stages. Further, the nitrification denitrification apparatus utilizing the biofilm of the present invention made to solve the above-mentioned problems is a nitrification denitrification organism having an aerobic biofilm filter bed in the upper stage and an anaerobic biofilm filter bed in the lower stage. A raw water supply unit is installed at the upper end of the membrane filter bed, and a circulation pump that returns the anaerobic treated water taken out from the lower end of the anaerobic biomembrane filter bed to the upper end of the nitrifying / denitrifying biomembrane filter bed is provided. It is characterized in that a hydrogen donor addition section and a treated water extraction section are provided at an intermediate position in the lower stage.

【0006】[0006]

【作用】本発明によれば、嫌気性生物膜ろ床の下端から
取り出された嫌気性処理水を硝化脱窒生物膜ろ床の上端
へ返送し、上段と下段の中間位置から処理水として取り
出すので、嫌気性生物膜ろ床の下端から取り出された嫌
気性処理水(従来法では処理水)中に含まれるCH3OH お
よびSSは上段の好気性生物膜ろ床により除去される。こ
のために従来のようなCH3OH およびSSを除去するための
再曝気槽は不要となり、設備を小型化することができ、
また処理水の回収率を向上させることができる。このほ
か、本発明によれば嫌気性処理水の循環率を変更するこ
とにより、脱窒率の制御ができるという利点もある。
According to the present invention, the anaerobic treated water taken out from the lower end of the anaerobic biological membrane filter bed is returned to the upper end of the nitrifying denitrifying biological membrane filter bed and taken out as treated water from the intermediate position between the upper stage and the lower stage. Therefore, CH 3 OH and SS contained in the anaerobic treated water (treated water in the conventional method) taken out from the lower end of the anaerobic biofilm filter bed are removed by the upper aerobic biofilter bed. This eliminates the need for a re-aeration tank for removing CH 3 OH and SS, which is required in the past, and makes it possible to downsize equipment.
In addition, the recovery rate of treated water can be improved. In addition, according to the present invention, there is an advantage that the denitrification rate can be controlled by changing the circulation rate of the anaerobic treated water.

【0007】[0007]

【実施例】以下に本発明を図示の実施例によって更に詳
細に説明する。図1は本発明の第1の実施例を示すもの
であり、3は従来例と同様に、上段の好気性生物膜ろ床
1と下段の嫌気性生物膜ろ床2とからなる硝化脱窒生物
膜ろ床である。好気性生物膜ろ床1は担体の表面に硝化
菌(亜硝酸菌や硝酸菌)を担持させたものであり、その
下部の散気装置5から供給される空気によって好気状態
に保たれている。この好気性生物膜ろ床1は、原水中の
NH4-N を硝化菌の作用によりNO2-N およびNO3-N に硝化
する作用を持つ。下段の嫌気性生物膜ろ床2は、担体の
表面に脱窒菌を担持させたものであり、上段と下段の中
間位置に設けられた水素供与体添加部10から供給される
CH3OH 等を水素供与体として、硝化液中のNO2-N および
NO3-Nを脱窒する。
The present invention will be described below in more detail with reference to the illustrated embodiments. FIG. 1 shows a first embodiment of the present invention, and 3 is a nitrifying denitrification consisting of an upper aerobic biofilm filter bed 1 and a lower anaerobic biofilm filter bed 2 as in the conventional example. It is a biomembrane filter. The aerobic biofilm filter bed 1 has nitrifying bacteria (nitrite bacteria and nitric acid bacteria) supported on the surface of a carrier, and is kept aerobic by the air supplied from the air diffuser 5 below the carrier. There is. This aerobic biomembrane filter bed 1
It has the effect of nitrifying NH 4 -N into NO 2 -N and NO 3 -N by the action of nitrifying bacteria. The lower anaerobic biofilm filter bed 2 has a denitrifying bacterium supported on the surface of a carrier, and is supplied from a hydrogen donor adding section 10 provided at an intermediate position between the upper and lower stages.
Using CH 3 OH, etc. as a hydrogen donor, NO 2 -N and
Denitrize NO 3 -N.

【0008】本発明では、このような好気性生物膜ろ床
1の上端の原水供給部11から原水を供給し、上段の好気
性生物膜ろ床1で硝化させた硝化液に水素供与体を添加
しつつ下段の嫌気性生物膜ろ床2で脱窒する。そして嫌
気性生物膜ろ床2の下端から取り出された嫌気性処理水
の全量を、循環ポンプ6によって硝化脱窒生物膜ろ床1
の上端へ返送する。そして上段と下段の中間位置に設け
られた処理水取出部12から処理水として取り出す。
In the present invention, raw water is supplied from the raw water supply unit 11 at the upper end of the aerobic biofilm filter bed 1 and a hydrogen donor is added to the nitrification solution nitrified by the aerobic biofilm filter bed 1 in the upper stage. While adding, denitrification is performed in the lower anaerobic biofilm filter bed 2. Then, the entire amount of the anaerobic treated water taken out from the lower end of the anaerobic biofilm filter bed 2 is converted by the circulation pump 6 into a nitrifying / denitrifying biofilm filter bed 1.
Return to the top of. Then, the treated water is taken out from the treated water take-out section 12 provided at an intermediate position between the upper stage and the lower stage.

【0009】このように本発明では嫌気性処理水の全量
を好気性生物膜ろ床1の上端の原水供給部11へ返送する
ため、嫌気性生物膜ろ床2で使用されなかった水素供与
体であるCH3OH は好気性生物膜ろ床1で曝気され分解さ
れる。また、水素供与体の添加により発生したSSも、好
気性生物膜ろ床1でろ過されて完全に除去される。この
ため、従来のような再曝気槽4を硝化脱窒生物膜ろ床3
の後段に設ける必要がなくなり、設備の小型化と処理水
の回収率の向上を図ることができる利点がある。また嫌
気性処理水の循環率を変更することにより、脱窒率の制
御を行うこともできる。
As described above, in the present invention, the entire amount of the anaerobic treated water is returned to the raw water supply section 11 at the upper end of the aerobic biofilm filter bed 1, so that the hydrogen donor not used in the anaerobic biofilm filter bed 2 is supplied. CH 3 OH is aerated in the aerobic biofilm filter bed 1 and decomposed. In addition, SS generated by the addition of the hydrogen donor is also completely removed by filtering with the aerobic biofilm filter bed 1. Therefore, the conventional re-aeration tank 4 is replaced with the nitrifying / denitrifying biofilm filter 3
It is not necessary to provide it in the latter stage, and there is an advantage that the equipment can be downsized and the recovery rate of treated water can be improved. Further, the denitrification rate can be controlled by changing the circulation rate of the anaerobic treated water.

【0010】図2は本発明の第2の実施例を示すもので
あり、原水供給部11に原水流量センサ7を、また処理水
取出部12に処理水流量センサ8をそれぞれ取り付け、そ
れらの出力に応じて制御装置9が循環ポンプ6を制御す
るようにしたものである。このように構成すれば嫌気性
処理水の循環率を自動制御し、脱窒率の制御が行える利
点がある。
FIG. 2 shows a second embodiment of the present invention. A raw water flow rate sensor 7 is attached to a raw water supply section 11 and a treated water flow rate sensor 8 is attached to a treated water extraction section 12, and their outputs are provided. The control device 9 controls the circulation pump 6 in accordance with the above. With this configuration, there is an advantage that the circulation rate of the anaerobic treated water can be automatically controlled and the denitrification rate can be controlled.

【0011】[0011]

【発明の効果】以上に説明したように、本発明によれば
従来のような再曝気槽が不要となるので設備を小型化す
ることができ、また再曝気槽の洗浄も不要となるので処
理水の回収率を向上させることができる。更に本発明に
よれば脱窒率の制御を行なうことができる利点もある。
しかも原水中のNH4-N は100 %除去することができると
ともに、T-N(トータル窒素) を50%以上除去することが
できることが確認された。
As described above, according to the present invention, the conventional re-aeration tank is unnecessary, so that the equipment can be downsized, and the cleaning of the re-aeration tank is also unnecessary. The recovery rate of water can be improved. Further, according to the present invention, there is an advantage that the denitrification rate can be controlled.
Moreover, it was confirmed that 100% of NH 4 -N in raw water can be removed and TN (total nitrogen) of 50% or more can be removed.

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

【図1】本発明の第1の実施例を示すフローシートであ
る。
FIG. 1 is a flow sheet showing a first embodiment of the present invention.

【図2】本発明の第2の実施例を示すフローシートであ
る。
FIG. 2 is a flow sheet showing a second embodiment of the present invention.

【図3】従来例を示すフローシートである。FIG. 3 is a flow sheet showing a conventional example.

【符号の説明】[Explanation of symbols]

1 好気性生物膜ろ床、2 嫌気性生物膜ろ床、3 硝
化脱窒生物膜ろ床、4再曝気槽、5 散気装置、6 循
環ポンプ、7 原水流量センサ、8 処理水流量セン
サ、9 制御装置、10 水素供与体添加部、11 原水供
給部、12 処理水取出部
1 aerobic biofilm filter bed, 2 anaerobic biofilm filter bed, 3 nitrification denitrification biofilm filter bed, 4 re-aeration tank, 5 aeration device, 6 circulation pump, 7 raw water flow sensor, 8 treated water flow sensor, 9 control device, 10 hydrogen donor addition part, 11 raw water supply part, 12 treated water extraction part

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 上段に好気性生物膜ろ床を、下段に嫌気
性生物膜ろ床を設けた硝化脱窒生物膜ろ床の上端から原
水を供給し、上段で硝化させた硝化液に水素供与体を添
加しつつ下段で脱窒するとともに、得られた嫌気性処理
水を硝化脱窒生物膜ろ床の上端へ返送し、上段と下段の
中間位置から処理水として取り出すことを特徴とする生
物膜を利用した硝化脱窒方法。
1. Raw water is supplied from the upper end of a nitrifying denitrification biofilm filter bed having an aerobic biofilm filter bed in the upper stage and an anaerobic biofilm filter bed in the lower stage, and hydrogen is added to the nitrification solution nitrified in the upper stage. It is characterized by denitrifying while adding a donor, returning the obtained anaerobic treated water to the upper end of the nitrifying denitrifying biofilm filter, and taking out as treated water from an intermediate position between the upper and lower stages. A nitrification denitrification method using a biofilm.
【請求項2】 上段に好気性生物膜ろ床を、下段に嫌気
性生物膜ろ床を設けた硝化脱窒生物膜ろ床の上端に原水
供給部を設けるとともに、嫌気性生物膜ろ床の下端から
取り出された嫌気性処理水を硝化脱窒生物膜ろ床の上端
へ返送する循環ポンプを設け、更に上段と下段の中間位
置に水素供与体添加部と処理水取出部とを設けたことを
特徴とする生物膜を利用した硝化脱窒装置。
2. A raw water supply unit is provided at the upper end of the nitrifying / denitrifying biofilm filter having an aerobic biofilter on the upper side and an anaerobic biofilter on the lower side. A circulation pump was provided to return the anaerobic treated water taken out from the lower end to the upper end of the nitrifying denitrification biomembrane filter bed, and a hydrogen donor addition part and a treated water take-out part were provided at an intermediate position between the upper and lower stages. A nitrification denitrification device using a biofilm.
【請求項3】 原水供給部と処理水取出部にそれぞれ流
量センサを取付け、それらの出力により循環ポンプを制
御する制御装置を設けた請求項2に記載の生物膜を利用
した硝化脱窒装置。
3. The nitrification denitrification apparatus using a biofilm according to claim 2, wherein a flow rate sensor is attached to each of the raw water supply section and the treated water extraction section, and a control device for controlling the circulation pump is provided by the outputs of the flow rate sensors.
JP570294A 1994-01-24 1994-01-24 Nitrification and denitrification equipment using biofilm Expired - Fee Related JP2721795B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP570294A JP2721795B2 (en) 1994-01-24 1994-01-24 Nitrification and denitrification equipment using biofilm

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP570294A JP2721795B2 (en) 1994-01-24 1994-01-24 Nitrification and denitrification equipment using biofilm

Publications (2)

Publication Number Publication Date
JPH07204686A true JPH07204686A (en) 1995-08-08
JP2721795B2 JP2721795B2 (en) 1998-03-04

Family

ID=11618451

Family Applications (1)

Application Number Title Priority Date Filing Date
JP570294A Expired - Fee Related JP2721795B2 (en) 1994-01-24 1994-01-24 Nitrification and denitrification equipment using biofilm

Country Status (1)

Country Link
JP (1) JP2721795B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020068712A (en) * 2001-02-22 2002-08-28 조웅현 A waste water treatment plant
WO2015076562A2 (en) * 2013-11-22 2015-05-28 주식회사 이피에스이앤이 Biofilm water treatment device having non-powered backwashing function
CN110723820A (en) * 2019-12-10 2020-01-24 倪佳佳 Combined ecological filter bed capable of multistage operation in series connection

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5681197A (en) * 1979-12-06 1981-07-02 Ebara Infilco Co Ltd Apparatus for nitrificating and denitrificating waste water biologically
JPS6447495A (en) * 1987-08-14 1989-02-21 Takenaka Komuten Co Waste water treating device
JPH05245496A (en) * 1992-02-28 1993-09-24 Hitachi Kiden Kogyo Ltd Sewage treatment apparatus

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5681197A (en) * 1979-12-06 1981-07-02 Ebara Infilco Co Ltd Apparatus for nitrificating and denitrificating waste water biologically
JPS6447495A (en) * 1987-08-14 1989-02-21 Takenaka Komuten Co Waste water treating device
JPH05245496A (en) * 1992-02-28 1993-09-24 Hitachi Kiden Kogyo Ltd Sewage treatment apparatus

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020068712A (en) * 2001-02-22 2002-08-28 조웅현 A waste water treatment plant
WO2015076562A2 (en) * 2013-11-22 2015-05-28 주식회사 이피에스이앤이 Biofilm water treatment device having non-powered backwashing function
WO2015076562A3 (en) * 2013-11-22 2015-08-13 주식회사 이피에스이앤이 Biofilm water treatment device having non-powered backwashing function
CN110723820A (en) * 2019-12-10 2020-01-24 倪佳佳 Combined ecological filter bed capable of multistage operation in series connection
CN110723820B (en) * 2019-12-10 2024-05-28 倪佳佳 Combined ecological filter bed capable of operating in multiple stages in series

Also Published As

Publication number Publication date
JP2721795B2 (en) 1998-03-04

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