JPH10323680A - Aerobic immersion filter bed device - Google Patents

Aerobic immersion filter bed device

Info

Publication number
JPH10323680A
JPH10323680A JP15575797A JP15575797A JPH10323680A JP H10323680 A JPH10323680 A JP H10323680A JP 15575797 A JP15575797 A JP 15575797A JP 15575797 A JP15575797 A JP 15575797A JP H10323680 A JPH10323680 A JP H10323680A
Authority
JP
Japan
Prior art keywords
filter bed
treatment tank
sludge
treatment
aeration
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.)
Pending
Application number
JP15575797A
Other languages
Japanese (ja)
Inventor
Fusakatsu Kitamura
総謁 北村
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.)
Inax Corp
Original Assignee
Inax 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 Inax Corp filed Critical Inax Corp
Priority to JP15575797A priority Critical patent/JPH10323680A/en
Publication of JPH10323680A publication Critical patent/JPH10323680A/en
Pending 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)

Abstract

PROBLEM TO BE SOLVED: To reduce troublesome cleaning and washing work by discharging sludge adhering on a filter bed to a downstream side by removing the sludge from the bed in a treatment wherein waste water containing organic substances are subjected to an aerobic treatment with biological sludge deposited on the filter bed immersed within a treatment tank. SOLUTION: When a waste water containing organic substance such as feces, air is jetted into an aeration treatment tank 1 through an aeration tube 3 in order to carry out aeration of an interior of the treatment tank 1 and a blower 4 is operated for causing convection within the treatment tank 1 and the waste water containing organic substance is circulated to a filter bed 2 for the purpose of carrying out purification treatment by use of biological sludge deposited on the filter bed 2. A backwash blower 6 is automatically operated at a predetermined interval in order to remove sludge adhering on the filter bed 2 by air jetted from a backwash nozzle toward the filter bed 2 at a periodic interval. The removed sludge is recirculated and dispersed into the treatment tank 1 sequentially and discharged to, for example, a sewerage system. Thus, the filter bed 2 is automatically prevented from being clogged so that purification function of the filter bed 2 can be kept in a good state for a long time.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、好気性浸漬濾床装置
に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an aerobic immersion filter bed apparatus.

【0002】[0002]

【従来の技術及びその課題】従来、図6の概略図で示す
ように、処理槽1内に、生ゴミとか便等の有機物を含む
排水を流入させて、処理槽1内に浸漬した濾床2に付着
させた生物汚泥により浄化処理する排水処理装置が存在
し、処理槽1の底側には散気管3が設けられ、この散気
管3にはバルブ51を介しブロア4が接続されて、散気
管3から曝気が常時行われて、前記濾床2に付着する好
気性菌に酸素が供給され、かつ、曝気により処理槽1内
に対流が形成されるように構成されており、また、前記
ブロア4には手動弁52を介し前記濾床2の底側に配設
した逆洗用ノズル5が連通されており、前記濾床2に付
着する汚泥量が過大になると濾床2を構成する濾材が閉
塞し、処理が著しく劣化してしまうため、従来において
は、前記手動弁52を定期的に開け、この時バルブ51
を閉めて、前記逆洗用ノズル5からエアを前記濾床2に
噴出させて、濾床2に付着する汚泥を剥離させ、濾床2
の洗浄を行っており、従来においては手動で濾床2の洗
浄を行う必要があり、また、濾床2から剥離した汚泥は
別途引き抜く等して清掃処理する必要があった。
2. Description of the Related Art Conventionally, as shown in a schematic diagram of FIG. 6, a wastewater containing organic matter such as garbage or stool flows into a treatment tank 1 and is immersed in the treatment tank 1. There is a wastewater treatment device for purifying the wastewater with the biological sludge attached to the treatment tank 2. A diffuser 3 is provided at the bottom of the treatment tank 1, and a blower 4 is connected to the diffuser 3 via a valve 51. Aeration is always performed from the air diffuser 3, oxygen is supplied to the aerobic bacteria attached to the filter bed 2, and convection is formed in the treatment tank 1 by the aeration. A backwash nozzle 5 disposed on the bottom side of the filter bed 2 is connected to the blower 4 via a manual valve 52. When the amount of sludge adhering to the filter bed 2 becomes excessive, the filter bed 2 is formed. In the prior art, the manual valve 5 Regularly open, this time valve 51
Is closed, and air is blown out from the backwash nozzle 5 to the filter bed 2 to remove sludge adhering to the filter bed 2.
In the past, it was necessary to manually wash the filter bed 2, and the sludge separated from the filter bed 2 had to be separately removed and cleaned.

【0003】[0003]

【課題を解決するための手段】本発明は上記従来の問題
点に鑑み案出したものであって、煩雑な洗浄とか清掃作
業を低減させることのできる好気性浸漬濾床装置を提供
せんことを目的とし、その第1の要旨は、有機物を含む
排水を、処理槽内に浸漬した濾床に付着させた生物汚泥
により好気処理する好気性浸漬濾床装置において、前記
濾床に付着した汚泥を剥離して下流側へ放流するように
構成したことである。また、第2の要旨は、前記汚泥を
定期的に自動的に剥離させるように構成したことであ
る。また、第3の要旨は、好気性浸漬濾床装置の下流側
に、放流水質が水質基準内であれば曝気し、水質基準外
であれば曝気を停止してSS分の固液分離を行う固液分
離槽を設けたことである。
SUMMARY OF THE INVENTION The present invention has been made in view of the above-mentioned conventional problems, and an object of the present invention is to provide an aerobic immersion filter bed apparatus which can reduce complicated washing and cleaning operations. The first object of the present invention is to provide an aerobic immersion filter apparatus for aerobically treating wastewater containing organic matter with biological sludge attached to a filter bed immersed in a treatment tank, wherein the sludge attached to the filter bed is provided. Is separated and discharged to the downstream side. A second gist is that the sludge is automatically and periodically peeled off. The third point is that aeration is performed on the downstream side of the aerobic immersion filter bed device if the discharged water quality is within the water quality standard, and if the discharged water quality is out of the water quality standard, the aeration is stopped to perform solid-liquid separation for SS. That is, a solid-liquid separation tank was provided.

【0004】[0004]

【実施例】以下、本発明の実施例を図面に基づいて説明
する。図1は、第1実施例の好気性浸漬濾床装置の概略
構成図であり、処理槽1内には濾床2が浸漬され、この
濾床2は、ハニカム状とか波板状または網目状等の濾材
で構成されており、この濾床2に生物汚泥が付着して好
気性条件下で排水の浄化処理を行うものとなっており、
処理槽1の底側には、ブロア4に接続された散気管3が
配設されており、また、前記濾床2の底側には複数の逆
洗用ノズル5,5,5が配設されて、この各逆洗用ノズ
ル5,5,5は逆洗ブロア6に接続されたものとなって
いる。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a schematic configuration diagram of an aerobic immersion filter bed apparatus of a first embodiment. A filter bed 2 is immersed in a treatment tank 1, and the filter bed 2 has a honeycomb shape, a corrugated shape, or a mesh shape. Etc., and biological sludge adheres to the filter bed 2 to purify wastewater under aerobic conditions.
A diffuser 3 connected to a blower 4 is provided at the bottom of the treatment tank 1, and a plurality of backwash nozzles 5, 5, 5 are provided at the bottom of the filter bed 2. Each of the backwash nozzles 5, 5, 5 is connected to a backwash blower 6.

【0005】このような構成において、常には前記ブロ
ア4を作動させ、散気管3からエアを噴出させて処理槽
1内で曝気が行われ、散気管3から噴出するエアにより
処理槽1内に図に示すような対流が形成されて、処理槽
1内に流入される有機物を含む排水が良好に濾床2に循
環されて、濾床2に付着する生物汚泥により浄化処理さ
れるものであり、処理水は下流側へ順次放流される。
In such a configuration, the blower 4 is always operated, and air is blown out from the diffuser tube 3 to perform aeration in the processing tank 1, and the air blown out from the diffuser tube 3 enters the processing tank 1. Convection as shown in the figure is formed, and wastewater containing organic matter flowing into the treatment tank 1 is circulated to the filter bed 2 satisfactorily, and is purified by biological sludge adhering to the filter bed 2. Then, the treated water is sequentially discharged to the downstream side.

【0006】本例では、前記逆洗ブロア6が定期的に自
動的に作動されて、前記逆洗用ノズル5から前記濾床2
に向かってエアが定期的に自動で噴出され、この噴出す
るエアにより濾床2に付着する汚泥が剥離されるように
構成されており、剥離した汚泥は順次処理槽1内で循環
分散されて、下流側、例えば下水道へ放流されるように
構成されている。
In the present embodiment, the backwash blower 6 is automatically operated periodically to allow the backwash nozzle 5 to pass through the filter bed 2.
Air is automatically and periodically ejected toward the filter bed, and the ejected air is configured to separate sludge adhering to the filter bed 2. The separated sludge is circulated and dispersed in the treatment tank 1 sequentially. , On the downstream side, for example, into the sewer.

【0007】前記逆洗ブロア6を自動的に作動させる時
間等は処理水質基準範囲内で制御されている。即ち、例
えば処理槽1からの放流水の水質基準が300mg/リッ
トルBOD,300mg/リットルSSに規定されている
場合、処理槽1内に1000mg/リットルBODの有機
物を含む排水が流入すると、処理槽1内で、濾床2での
生物処理により流入した1000mg/リットルBODの
排水はCO2 とH2 Oに分解されて700mg/リットル
が処理されるが、このうち1割の70mg/リットルはS
Sとなり、この70mg/リットルのSSが前記濾床2に
付着して徐々に濾床2を閉塞してしまうため、定期的に
自動で前記逆洗ブロア6を作動させて、この70mg/リ
ットルの生成されたSSを剥離して下流側へ放流するよ
うに制御すれば、濾床2が閉塞することがなく、良好な
処理機能を持続させることができるものとなる。
The time for automatically operating the backwash blower 6 is controlled within a reference range of treated water quality. That is, for example, when the water quality standard of the effluent from the treatment tank 1 is set to 300 mg / liter BOD and 300 mg / liter SS, when wastewater containing 1000 mg / liter BOD of organic matter flows into the treatment tank 1, In 1, the 1000 mg / liter BOD wastewater flowing in through the biological treatment in the filter bed 2 is decomposed into CO 2 and H 2 O and 700 mg / liter is treated, of which 70% / 70% is S
Since the 70 mg / liter SS adheres to the filter bed 2 and gradually closes the filter bed 2, the backwash blower 6 is automatically and periodically operated, and the 70 mg / liter SS If the generated SS is controlled to be separated and discharged to the downstream side, the filter bed 2 will not be blocked and a good processing function can be maintained.

【0008】従って、剥離させるSSの量を、前記逆洗
ブロア6の作動時間等の制御によりコントロールするこ
とができ、このようにコントロールすることにより、従
来のような手動による逆洗を行う必要がなくなり、ま
た、剥離した汚泥を引き抜く清掃作業を行う必要もなく
なり、処理能力を良好に持続させることができるものと
なる。
Accordingly, the amount of SS to be stripped can be controlled by controlling the operation time of the backwashing blower 6 and the like, so that it is necessary to perform the conventional manual backwashing. In addition, there is no need to perform a cleaning operation for pulling out the separated sludge, and the treatment capacity can be maintained satisfactorily.

【0009】次に、図2は第2実施例を示すものであ
り、図2では、処理槽1内に濾床2が浸漬されており、
処理槽1の底側には散気管3が配設されているが、この
散気管3には散気管路7が接続され、散気管路7内には
自動で開閉する自動開閉バルブ8が設けられ、ブロア4
に接続されたものとなっており、また、前記濾床2の底
側に複数配設される逆洗用ノズル5には逆洗管路9が接
続されて、この逆洗管路9内には自動で開閉する自動開
閉バルブ10が設けられたものとなっており、逆洗管路
9は前記ブロア4に接続されている。
Next, FIG. 2 shows a second embodiment. In FIG. 2, a filter bed 2 is immersed in a treatment tank 1.
An air diffuser 3 is disposed on the bottom side of the treatment tank 1, and a diffuser 7 is connected to the diffuser 3, and an automatic opening / closing valve 8 that opens and closes automatically is provided in the diffuser 7. And blower 4
The backwashing pipe 9 is connected to a plurality of backwashing nozzles 5 arranged on the bottom side of the filter bed 2. Is provided with an automatic opening / closing valve 10 that opens and closes automatically, and a backwash pipe 9 is connected to the blower 4.

【0010】このような構成において、常には前記自動
開閉バルブ8が開けられて散気管3からエアが噴出され
て曝気されるものであるが、定期的に自動で前記自動開
閉バルブ10が開かれ、逆洗管路9を通り逆洗用ノズル
5からエアが前記濾床2に噴出されて、濾床2に付着す
る汚泥を剥離するように構成されており、この自動開閉
バルブ10が開かれた時には前記自動開閉バルブ8を閉
じるように構成して、より強力なエアを逆洗用ノズル5
から濾床2に噴出させるように構成することもでき、前
記自動開閉バルブ10の開閉制御は、処理槽1内に流入
される排水の量と、処理槽1内で処理により生成される
SSの量と、処理槽1からの放流水の水質基準値に基づ
いてコントロールすることができ、濾床2に付着する処
理により生成された分量のSSを順次自動開閉バルブ1
0を自動開閉させて剥離除去し、濾床2への汚泥付着量
を適正なものに制御して、濾床2の閉塞を防ぎ、濾床2
の処理機能を良好に持続させることができるものとな
る。従って、従来のような定期的な手動による洗浄とか
清掃等を省略することができるものとなる。
In such a configuration, the automatic opening / closing valve 8 is always opened and air is blown out from the air diffuser 3 to be aerated, but the automatic opening / closing valve 10 is automatically opened periodically. Air is blown from the backwash nozzle 5 through the backwash pipe 9 to the filter bed 2 to separate sludge adhering to the filter bed 2, and the automatic opening / closing valve 10 is opened. The automatic opening and closing valve 8 is configured to be closed when the
The automatic opening / closing valve 10 can be controlled to open and close the filter bed 2 by controlling the amount of wastewater flowing into the processing tank 1 and the amount of SS generated by processing in the processing tank 1. And the amount of SS generated by the treatment adhering to the filter bed 2 can be sequentially controlled by the automatic opening / closing valve 1.
0 is automatically opened and closed to peel off and remove, and the amount of sludge adhering to the filter bed 2 is controlled to an appropriate level to prevent the filter bed 2 from being clogged.
Can be favorably maintained. Therefore, it is possible to omit the conventional manual cleaning or cleaning as in the related art.

【0011】次に、図3は第3実施例を示すものであ
り、処理槽1内に浸漬された濾床2の下部には逆洗用ノ
ズル5が配設され、この逆洗用ノズル5にはブロア6が
接続されており、また、自動逃がし弁11が設けられた
ものとなっている。この図3の構成では、前記ブロア6
を常時は少風量で運転して前記逆洗用ノズル5,5,5
から曝気させ、濾床2に空気を供給するとともに、処理
槽1内に対流が生じる程度の空気量とするが、濾床2に
付着するSSを剥離する時には、前記ブロア6の風量を
大とし、逆洗用ノズル5から濾床2に向かって気泡を噴
出させてSSの剥離を行うようにし、定期的に自動で前
記ブロア6が逆洗用の大風量に切替制御されるように構
成したものである。このような構成では、別途、曝気用
のブロア4とか散気管3を省略することができ、処理槽
内の装置を簡略化してコンパクトに形成することができ
るものとなる。
Next, FIG. 3 shows a third embodiment, in which a backwash nozzle 5 is provided below the filter bed 2 immersed in the treatment tank 1. Is connected to a blower 6, and an automatic relief valve 11 is provided. In the configuration of FIG.
Is normally operated with a small air volume to operate the backwash nozzles 5, 5, 5
And air is supplied to the filter bed 2 and the amount of air is such that convection occurs in the treatment tank 1. However, when the SS adhering to the filter bed 2 is separated, the air volume of the blower 6 is increased. Air bubbles are ejected from the backwash nozzle 5 toward the filter bed 2 to separate the SS, and the blower 6 is automatically and periodically switched to the large airflow for backwash. Things. In such a configuration, the aeration blower 4 and the diffuser 3 can be omitted separately, and the apparatus in the processing tank can be simplified and formed compact.

【0012】次に、図4は第4実施例を示すものであ
り、処理槽1及びその内部の装置は前記図1のものと同
様であるが、処理槽1の下流側に固液分離槽12を設
け、この固液分離槽12内に前記処理槽1からの処理水
を入れるように構成したものであり、固液分離槽12内
の下部には散気管13が設けられ、この散気管13には
ブロア14が接続されている。常にはブロア14が運転
されて散気管13から曝気が行われて、固液分離槽12
の上面側から下水等に放流が成されるもので、放流水の
水質が水質基準内であれば図4のように散気管13から
曝気を行うものであるが、前記処理槽1から固液分離槽
12内に入り込む処理水の水質が水質基準外であれば図
5に示すように前記ブロア14の運転を停止し、散気管
13からの曝気を停止して、この状態で固液分離槽12
内にて固液分離を行い、固液分離槽12の底側にSS分
を沈降させて、固液分離槽12から放流される放流水が
水質基準をクリアするように処理するものである。即
ち、計画値以上の排水及び負荷流入などが原因で処理槽
1からの放流水が水質基準外となる場合が考えられ、こ
のような場合に図5のように、固液分離槽12内で固液
を分離してSS分を沈降させるものであり、この固液分
離槽12内に貯留されたSS分は清掃あるいは引抜き等
により送出されるものである。
Next, FIG. 4 shows a fourth embodiment, in which the processing tank 1 and its internal device are the same as those in FIG. 1, but a solid-liquid separation tank is provided downstream of the processing tank 1. The solid-liquid separation tank 12 is configured to receive the processing water from the processing tank 1, and a diffuser 13 is provided at a lower portion in the solid-liquid separation tank 12. A blower 14 is connected to 13. The blower 14 is always operated to aerate from the air diffuser 13, and the solid-liquid separation tank 12
The water is discharged from the upper surface side to sewage or the like. If the quality of the discharged water is within the water quality standard, aeration is performed from the diffuser 13 as shown in FIG. If the quality of the treated water entering the separation tank 12 is out of the water quality standard, the operation of the blower 14 is stopped and the aeration from the diffuser 13 is stopped as shown in FIG. 12
The solid-liquid separation is performed in the inside, the SS component is settled at the bottom side of the solid-liquid separation tank 12, and the discharged water discharged from the solid-liquid separation tank 12 is processed so as to meet the water quality standard. That is, it is conceivable that the water discharged from the treatment tank 1 is out of the water quality standard due to drainage and load inflow exceeding the planned values. In such a case, as shown in FIG. The solid component is separated to settle the SS component, and the SS component stored in the solid-liquid separation tank 12 is sent out by cleaning or drawing.

【0013】[0013]

【発明の効果】本発明は、有機物を含む排水を、処理槽
内に浸漬した濾床に付着させた生物汚泥により好気処理
する好気性浸漬濾床装置において、前記濾床に付着した
汚泥を剥離して下流側へ放流するように構成したことに
より、処理槽内の処理により生成される分の汚泥を剥離
して、処理水質基準範囲内の水質を維持した状態で剥離
した汚泥を下流側へ順次放流させ、濾床への付着汚泥量
を一定化させて、濾床の閉塞を防ぐことができる効果を
有する。
According to the present invention, there is provided an aerobic immersion filter apparatus for aerobically treating wastewater containing organic matter with biological sludge attached to a filter bed immersed in a treatment tank. By being configured to be separated and discharged to the downstream side, the sludge generated by the treatment in the treatment tank is separated and the separated sludge is maintained on the downstream side while maintaining the water quality within the treated water quality standard range. And the amount of sludge adhering to the filter bed is made constant, thereby preventing the filter bed from being clogged.

【0014】また、前記汚泥を定期的に自動的に剥離さ
せるように構成したことにより、定期的に自動で逆洗等
により濾床に付着する余分な汚泥を剥離させて、処理槽
内で処理により生成されるSS分を順次定期的に自動で
放流除去することができ、濾床の閉塞を自動的に防ぎ、
濾床の浄化機能を良好に維持できる効果を有する。
Further, the sludge is automatically and periodically peeled off, so that excess sludge adhering to the filter bed is periodically and automatically peeled off by backwashing and the like, and the sludge is treated in the treatment tank. Can be automatically discharged sequentially and periodically to prevent clogging of the filter bed,
This has the effect that the purification function of the filter bed can be maintained well.

【0015】また、前記好気性浸漬濾床装置の下流側
に、放流水質が水質基準内であれば曝気し、水質基準外
であれば曝気を停止してSS分の固液分離を行う固液分
離槽を設けたことにより、水質基準範囲外の放流水が好
気性浸漬濾床装置から放流されたような非常時には、固
液分離槽内でSS分を良好に除去して水質基準をクリア
する放流水とすることができ、固液分離槽を介し好気性
浸漬濾床装置の浄化機能を良好に補助することができる
効果を有する。
Further, downstream of the aerobic immersion filter bed apparatus, aeration is performed if the discharged water quality is within the water quality standard, and if the discharged water quality is out of the water quality standard, aeration is stopped to perform solid-liquid separation for SS. By providing a separation tank, in an emergency such as when effluent water out of the water quality standard range is discharged from the aerobic immersion filter bed device, the SS content is satisfactorily removed in the solid-liquid separation tank to clear the water quality standard It can be discharged water and has the effect of favorably assisting the purification function of the aerobic immersion filter bed device through the solid-liquid separation tank.

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

【図1】第1実施例の好気性浸漬濾床装置の概略構成図
である。
FIG. 1 is a schematic configuration diagram of an aerobic immersion filter bed device of a first embodiment.

【図2】第2実施例の好気性浸漬濾床装置の概略構成図
である。
FIG. 2 is a schematic configuration diagram of an aerobic immersion filter bed device of a second embodiment.

【図3】第3実施例の好気性浸漬濾床装置の概略構成図
である。
FIG. 3 is a schematic configuration diagram of an aerobic immersion filter bed device of a third embodiment.

【図4】さらに下流側に固液分離槽を設置した状態の概
略構成図である。
FIG. 4 is a schematic configuration diagram in a state where a solid-liquid separation tank is further installed on the downstream side.

【図5】固液分離槽内でSS分を固液分離させる概略構
成図である。
FIG. 5 is a schematic configuration diagram for performing solid-liquid separation of SS in a solid-liquid separation tank.

【図6】従来の好気性浸漬濾床装置の概略構成図であ
る。
FIG. 6 is a schematic configuration diagram of a conventional aerobic immersion filter bed device.

【符号の説明】[Explanation of symbols]

1 処理槽 2 濾床 3 散気管 4 ブロア 5 逆洗用ノズル 6 逆洗ブロア 8,10 自動開閉バルブ 12 固液分離槽 13 散気管 14 ブロア REFERENCE SIGNS LIST 1 treatment tank 2 filter bed 3 diffuser 4 blower 5 backwash nozzle 6 backwash blower 8,10 automatic open / close valve 12 solid-liquid separation tank 13 diffuser 14 blower

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 有機物を含む排水を、処理槽内に浸漬し
た濾床に付着させた生物汚泥により好気処理する好気性
浸漬濾床装置において、前記濾床に付着した汚泥を剥離
して下流側へ放流するように構成したことを特徴とする
好気性浸漬濾床装置。
1. An aerobic immersion filter apparatus for aerobically treating wastewater containing organic matter with biological sludge attached to a filter bed immersed in a treatment tank. An aerobic immersion filter bed device configured to be discharged to the side.
【請求項2】 前記汚泥を定期的に自動的に剥離させる
ように構成した請求項1に記載の好気性浸漬濾床装置。
2. The aerobic immersion filter bed apparatus according to claim 1, wherein the sludge is automatically and periodically peeled off.
【請求項3】 前記好気性浸漬濾床装置の下流側に、放
流水質が水質基準内であれば曝気し、水質基準外であれ
ば曝気を停止してSS分の固液分離を行う固液分離槽を
設けたことを特徴とする請求項1または請求項2に記載
の好気性浸漬濾床装置。
3. A solid-liquid separator for downstream of the aerobic immersion filter bed apparatus, wherein aeration is performed if the discharged water quality is within the water quality standard, and aeration is stopped if the discharged water quality is out of the water quality standard to perform solid-liquid separation for SS. The aerobic immersion filter bed device according to claim 1 or 2, further comprising a separation tank.
JP15575797A 1997-05-28 1997-05-28 Aerobic immersion filter bed device Pending JPH10323680A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15575797A JPH10323680A (en) 1997-05-28 1997-05-28 Aerobic immersion filter bed device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15575797A JPH10323680A (en) 1997-05-28 1997-05-28 Aerobic immersion filter bed device

Publications (1)

Publication Number Publication Date
JPH10323680A true JPH10323680A (en) 1998-12-08

Family

ID=15612755

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15575797A Pending JPH10323680A (en) 1997-05-28 1997-05-28 Aerobic immersion filter bed device

Country Status (1)

Country Link
JP (1) JPH10323680A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100488471B1 (en) * 2002-12-12 2005-05-16 (주)담덕 Backwashing apparatus of tertiary sewage treatment system
JP2008104999A (en) * 2006-10-27 2008-05-08 Samutekku:Kk Apparatus for treating water to be treated

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100488471B1 (en) * 2002-12-12 2005-05-16 (주)담덕 Backwashing apparatus of tertiary sewage treatment system
JP2008104999A (en) * 2006-10-27 2008-05-08 Samutekku:Kk Apparatus for treating water to be treated

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