JPS59166292A - Backwashing method of fixed bed type sewage cleaning up tank - Google Patents

Backwashing method of fixed bed type sewage cleaning up tank

Info

Publication number
JPS59166292A
JPS59166292A JP58040135A JP4013583A JPS59166292A JP S59166292 A JPS59166292 A JP S59166292A JP 58040135 A JP58040135 A JP 58040135A JP 4013583 A JP4013583 A JP 4013583A JP S59166292 A JPS59166292 A JP S59166292A
Authority
JP
Japan
Prior art keywords
tank
biofilm
backwashing
light
biological film
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
JP58040135A
Other languages
Japanese (ja)
Inventor
Hiroshi Hoshikawa
星川 寛
Satoshi Nishikata
西方 聡
Yasunari Sasaki
康成 佐々木
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.)
Fuji Electric Co Ltd
Original Assignee
Fuji Electric Co Ltd
Fuji Electric Corporate Research and Development Ltd
Fuji Electric Manufacturing Co 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 Fuji Electric Co Ltd, Fuji Electric Corporate Research and Development Ltd, Fuji Electric Manufacturing Co Ltd filed Critical Fuji Electric Co Ltd
Priority to JP58040135A priority Critical patent/JPS59166292A/en
Publication of JPS59166292A publication Critical patent/JPS59166292A/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

Abstract

PURPOSE:To perform backwashing in an optimum timing by operating a biological membrane sensor consisting of a light emitting part, photodetecting part and biological film removing mechanism dipped in a tank and backwashing automatically a packing material when a preset number of operations are attained. CONSTITUTION:When a sewage treatment is continued, a biological film grows thickly on the surface of a packing material 3, and the degree thereof is detected with a biological film sensor 11. When the detected intensity of light attains a certain set value or below, a small sized motor 28 is rotated a washing brush 26 is rotated via a disc 29, a crank 30 and a washing brush supporting bar 27, on the inside of a sensor housing part 25 to that the brush 26 removes the biological film on the surface of the window 22 in the light emitting part and the window 24 in the photodetecting part. The biological film on the surface of the material 3 is stripped until an adequate thickness is attained and in succession, sludge is settled in the bottom of a cleaning up tank 2 and is discharged to the outside of the tank through a sludge discharging pipe 7 and a sludge discharging valve 8.

Description

【発明の詳細な説明】 この発明は、汚水を充填材表面に付1生育した微生物の
働きにより浄化処理する固定床型汚水浄化装置における
、充填材の逆洗浄洗に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to backwashing of a filler in a fixed bed type sewage purification apparatus in which wastewater is purified by the action of microorganisms grown on the surface of the filler.

汚水を微生物の働きにより浄化処理する方法として、従
来より活性汚泥法、散水ろ床法および固定床法がよく知
られている。固定床法は槽内にプラスチック製波板、網
等の充填材を充填し、汚水を機械攪拌装置又は散気によ
るエアーリフトを用いて攪拌し、前記充填材表面に付着
生育した微生物上循環接触させることにより浄化処理す
る方法で1.一般に槽内に空気を散気する好気性固定床
法と、空気を散気しない嫌気性固定床法に大別されてお
り、好気性固定床法では充填材表面に付着した微生物が
汚水中の有機物を酸化分解することにより、嫌気性固定
末法では微生物が汚水中の有機物を嫌気性消化すること
により浄化が行われる。
Activated sludge method, trickling filter method, and fixed bed method are well known as methods for purifying wastewater through the action of microorganisms. In the fixed bed method, a tank is filled with fillers such as plastic corrugated plates or nets, and the wastewater is stirred using a mechanical agitator or an air lift with aeration, and the microorganisms that have grown on the surface of the filler are circulated and brought into contact. 1. Generally, there are two types of methods: aerobic fixed bed method in which air is diffused into the tank, and anaerobic fixed bed method in which air is not diffused.In aerobic fixed bed method, microorganisms attached to the surface of the filler are In the anaerobic fixed powder method, microorganisms anaerobically digest the organic matter in wastewater, thereby purifying it by oxidizing and decomposing the organic matter.

ただし、このような処理を数カ月連続して行うと、汚水
の浄化に伴って増殖する微生物のため充填材表面の生物
膜の厚さが厚くなり、ついには生物膜自体を充填材表面
上に支えきれなくなって剥離し、処理水に混入して水質
悪化を招く。また生物膜は充填材の空隙に増殖する−た
め、次第に空隙の体積が減少する現象、つまり目詰まり
をおこし、浄化槽内の汚水の循環を悪化させ、浄化効率
を悪くする。このため、通常の処理においては、生物膜
の厚さがある程度以上になり目詰まりが進行してくると
逆洗を行い、強制的に生物膜を剥離し、剥離、汚泥を浄
化槽外に排出している。
However, if such treatment is continued for several months, the thickness of the biofilm on the surface of the filler increases due to microorganisms that proliferate as wastewater is purified, and eventually the biofilm itself becomes supported on the surface of the filler. It becomes difficult to clean, peels off, and mixes with treated water, causing deterioration of water quality. In addition, biofilm grows in the voids of the filler, which causes a phenomenon in which the volume of the voids gradually decreases, that is, clogging, which worsens the circulation of wastewater in the septic tank and impairs purification efficiency. For this reason, in normal treatment, when the thickness of the biofilm reaches a certain level and clogging progresses, backwashing is performed to forcibly peel off the biofilm, and the sludge and sludge are discharged to the outside of the septic tank. ing.

逆洗方法としては、好気性固定床では散気装置から吐出
させる空気の流量を急増させ、浄化槽内の汚水の循環流
速を増すか、充填材の下部に設置した逆洗用散気装置か
ら空気を吹き込み、気泡を充填材のを隙を通過させるこ
とによって肥厚した生物膜を剥離する方法が一般的であ
る。嫌気性固定床も逆洗方法はほぼ同様であるが、空気
のかわりにメタンガスを主成分とする消化ガスを利用す
ることもある。このように固定末法では、逆洗をくり返
しつつ汚水の浄化を行う訳であるが、逆洗時期の決定法
としては従来より、経験的にある一定期間が経過したら
手動にて行う、あるいはタイマーにて時間設定をしてお
き周期的に行う等の方法が依られていた。
For backwashing methods, in the case of an aerobic fixed bed, the flow rate of air discharged from the aeration device is rapidly increased to increase the circulation flow rate of wastewater in the septic tank, or the backwashing method is to increase the flow rate of air discharged from the aeration device, or to increase the circulation flow rate of wastewater in the septic tank. A common method is to remove the thickened biofilm by blowing air bubbles through the gaps in the filler. The backwashing method for anaerobic fixed beds is almost the same, but a digestion gas containing methane gas as the main component may be used instead of air. In this way, in the fixed powder method, sewage is purified by repeating backwashing, but conventional methods for deciding when to backwash have been based on experience, such as manually carrying out the process after a certain period of time, or using a timer. Methods such as setting a time and performing it periodically have been used.

しかしながらこれ等の方法は、必ずしも充填材の目詰ま
りの状況を正確に反映したものではないため、逆洗時期
が早すぎて、必要以上に生物膜を剥離し処理能力を低下
せしめて処理水質を悪化させたり、逆に逆洗が遅いため
水質が悪くなった状態で放置されたままになっていた等
のケースが多く見受けられた。
However, these methods do not necessarily accurately reflect the state of clogging of the filler material, and the backwashing period is too early, causing the biofilm to be peeled off more than necessary, reducing the treatment capacity, and reducing the quality of the treated water. There were many cases where the water quality deteriorated and was left unattended due to slow backwashing.

本発明はこれら従来法の問題点を解消し、充勇材の目詰
まりの状況を常に適確に把握し、最適の時期に逆洗を行
う固定床型汚水浄化装置の逆洗方法を提供することを目
的とする。
The present invention solves the problems of these conventional methods, and provides a method for backwashing a fixed-bed type sewage purification device that always accurately grasps the clogging situation of the filling material and performs backwashing at the optimal time. With the goal.

本発明は、光源を有する発光部と、発光部からの光を受
光しその強度を測定する受光部と、発光部および受光部
の窓の表面に付着した生物膜を除去する生物膜除去機構
を備えた生物膜センサを浄化槽内に浸漬し、充填材表面
上の生物膜の成長状況を正確に検知することにより、生
物膜の成長状況に応じて逆洗時期を決定することを特徴
とする固定床型汚水浄化槽の逆洗方法である。
The present invention includes a light-emitting section having a light source, a light-receiving section that receives light from the light-emitting section and measures its intensity, and a biofilm removal mechanism that removes biofilm attached to the surfaces of the windows of the light-emitting section and the light-receiving section. A fixing method characterized by immersing a biofilm sensor equipped in a septic tank into a septic tank and accurately detecting the growth status of biofilm on the surface of the filler material, thereby determining the time for backwashing according to the growth status of the biofilm. This is a method for backwashing a floor-type sewage septic tank.

以下に図面に基づいて実施例を説明する。第1図に示す
実施例は、汚水が流入する流入管1、汚水を処理する浄
化槽2、空気を遮断する覆蓋12、生物膜が形成される
充填材3、攪拌用の消化ガスを吐出する散気装置4、逆
洗用散気装置5、処理水が流出する流出管6、逆洗時に
剥離した生物膜よりなる汚泥を除去するための排泥管7
、排泥弁8、消化ガスを送る第1コンプレツサ9、逆洗
用の空気を供給する第2コンプレツサ10よりなる嫌気
性固定床型汚水浄化装置である。逆洗時期を検知する生
物膜センサ11は、浄化槽2の壁面に固定されており、
その一部は槽内の汚水中に浸漬されている。
Examples will be described below based on the drawings. The embodiment shown in FIG. 1 includes an inlet pipe 1 through which sewage flows, a septic tank 2 for treating the sewage, a cover 12 for blocking air, a filler 3 in which biofilm is formed, and a diffuser for discharging digestion gas for stirring. Aeration device 4, backwashing aeration device 5, outflow pipe 6 through which treated water flows out, and sludge drainage pipe 7 for removing sludge made of biofilm peeled off during backwashing.
This is an anaerobic fixed-bed type sewage purification device consisting of a sludge valve 8, a first compressor 9 that sends digestion gas, and a second compressor 10 that supplies air for backwashing. A biofilm sensor 11 that detects the backwashing period is fixed to the wall of the septic tank 2.
Part of it is immersed in sewage inside the tank.

流入管1を通って流入した汚水は、浄化槽2内で攪拌さ
れ、充填材30表面に付着生育し生物膜を形成した微生
物と接触することにより浄化される。攪拌には浄化槽2
内七生成するメタンガスを主成分とした嫌気性消化ガス
を用いたエアーリフトが使用され、浄化された処理水は
流出管6を通して排出される。また、余剰の鎌気性消化
ガスも同様に流出管6を通して排出される。
The sewage that has flowed in through the inflow pipe 1 is agitated in the septic tank 2 and is purified by coming into contact with microorganisms that have grown on the surface of the filler 30 and formed a biofilm. Septic tank 2 for stirring
An air lift using anaerobic digestion gas mainly composed of methane gas is used, and the purified treated water is discharged through an outflow pipe 6. Further, excess sickle gas digestion gas is similarly discharged through the outflow pipe 6.

このような処理を続けていると、充填材3の表面上に生
物膜が肥厚してくるが、その程度は生物膜センサ11で
検出する。ここで生物膜センサ11の構造と機能を図面
により詳細に説明する。
If such processing continues, the biofilm will thicken on the surface of the filler 3, and the extent of this will be detected by the biofilm sensor 11. Here, the structure and function of the biofilm sensor 11 will be explained in detail with reference to the drawings.

第2図は生物膜センサ11の構造を示す分解斜視図であ
る。生物膜センサ11は、光を発する発光部21、その
光が透過する発光部窓n、光の強度を検知する受光部n
、検知する光が透過する受光部窓列、それらを保持収納
するセンナ収納部部1発光部窓nおよび受光部窓列の汚
れを洗浄するための洗浄ブラシ26.さらに洗浄ブラシ
支持棒27.洗浄ブラシ部を駆動するための小型モータ
浸2円盤四。
FIG. 2 is an exploded perspective view showing the structure of the biofilm sensor 11. The biofilm sensor 11 includes a light emitting section 21 that emits light, a light emitting section window n through which the light passes, and a light receiving section n that detects the intensity of the light.
, a cleaning brush 26 for cleaning dirt from the light receiving window row through which the light to be detected passes, the senna storage section 1 for holding and storing them, the light emitting window n, and the light receiving window row. Furthermore, the cleaning brush support rod 27. 2 discs with 4 small motors to drive the cleaning brush section.

クランク加、そしてこれらを一体に保持するための固定
用パイプ31より構成きれている。発光部21の光源と
しては通常タングステンランプ又は発光ダイオード等を
用い、受光部乙の光電変換素子としてはシリコンフォト
ダイオード又は硫化カドミウムン万トセル等を用いる。
It consists of a crankshaft and a fixing pipe 31 for holding these together. A tungsten lamp or a light emitting diode is usually used as a light source for the light emitting section 21, and a silicon photodiode or a cadmium sulfide cell is used as a photoelectric conversion element for the light receiving section B.

発光部窓部および受光部窓列の材質はガラス又は透明プ
ラスチックで、センサ収納部乙に密着して取り付けられ
でいる。
The light emitting section window section and the light receiving section window row are made of glass or transparent plastic, and are attached in close contact with the sensor storage section B.

次に機能を説明する。前記のような構造の生物膜センサ
11のセンサ収納部6および洗浄ブラシがを槽内の汚水
中に浸漬すると、センサ収納部5は形状が円筒型となっ
ているため汚水は内側を自由に通過することができる6
そのため充填材3と同様に、時間が経過するにしたがっ
て生物膜が、発光部窓22および受光部窓240表面上
に成長して光の通過を妨げ、受光部るにおいて検出され
る光の強度を低下させる。一方、洗浄ブラシ部は光の検
出強度がある設定値以下になると駆動される。つまり、
元の強度があらかじめ定められたある値以下になると小
型モーターあが回転し、円盤四、クランク30.洗浄ブ
ラシ支持棒Mを介して洗浄ブラシUが、センサ収納部部
の内側で上下し、発光部窓22および受光部窓列表面上
の生物膜を除去する。
Next, the functions will be explained. When the sensor storage part 6 and the cleaning brush of the biofilm sensor 11 having the above-described structure are immersed in waste water in the tank, the sensor storage part 5 has a cylindrical shape, so the waste water can freely pass through the inside. can6
Therefore, like the filler 3, as time passes, biofilm grows on the surfaces of the light emitting window 22 and the light receiving window 240, blocking the passage of light and reducing the intensity of light detected at the light receiving part. lower. On the other hand, the cleaning brush section is driven when the detected intensity of light falls below a certain set value. In other words,
When the original strength falls below a certain predetermined value, a small motor rotates, disk 4, crank 30. The cleaning brush U moves up and down inside the sensor housing section via the cleaning brush support rod M, and removes biofilm on the surfaces of the light emitting section window 22 and the light receiving section window array.

尚、洗浄ブラシ26を上下に駆動する方法としてはラッ
クとピニオン等の機構を用いても良い。洗浄時間は1分
間程度に設定しておけば充分で、所定時間が経過し小型
モータ一部の電源が切れると、洗浄ブラシ加は自重で下
降しセンサ収納部6より。
Note that a mechanism such as a rack and pinion may be used as a method for driving the cleaning brush 26 up and down. It is sufficient to set the cleaning time to about 1 minute, and when the predetermined time elapses and a part of the small motor is turned off, the cleaning brush is lowered by its own weight and released from the sensor storage part 6.

低い位置に止まるため、ここで再び汚水はセンサ収納部
5の内側を通過することが可能となる。
Since the wastewater stops at a low position, it is possible for the dirty water to pass through the inside of the sensor housing section 5 again.

すなわち洗浄ブラシ26は、発光部窓nおよび受光部窓
列表面上の生物膜がある一定の厚さになる毎に駆動され
る訳である。ところで、生物膜センサ11の発光部窓n
および受光部窓列表面上の生物膜と、充填材3の表面上
の生物膜の関係を見ると、どちらも同一槽内に浸漬され
ているため、それぞれの生物膜を形成している微生物の
種類には大差がないと考えることができ、それぞれの生
物膜の成長速度は、はぼ同様であると見なすことができ
る。これは、ある時点、例えば充填材3の逆洗直後をス
タートポイントとすると、その後における生物膜センサ
11の洗浄ブラシあの作動回数(以後洗浄回数と呼ぶ)
は充填材3表面上の生物膜厚の増加分と比例関係にある
ことを示している。
That is, the cleaning brush 26 is driven every time the biofilm on the surfaces of the light emitting window n and the light receiving window array reaches a certain thickness. By the way, the light emitting part window n of the biofilm sensor 11
Looking at the relationship between the biofilm on the surface of the light-receiving window row and the biofilm on the surface of the filler 3, since both are immersed in the same tank, the microorganisms forming each biofilm are It can be considered that there is no major difference between the types, and the growth rate of each biofilm can be considered to be almost the same. This is the number of times the cleaning brush of the biofilm sensor 11 is operated after that time (hereinafter referred to as the number of cleaning times), starting from a certain point in time, for example, immediately after backwashing the filling material 3.
indicates that there is a proportional relationship with the increase in biofilm thickness on the surface of the filler 3.

したがって、あらかじめ実験的にこd関係を求めておけ
ば、その後は生物膜センサ11の洗浄回数より、充填材
3表面上の生物膜の厚さすなわち充填材3の目詰まりの
程度を推定することができる。
Therefore, if the d relationship is determined experimentally in advance, then the thickness of the biofilm on the surface of the filling material 3, that is, the degree of clogging of the filling material 3, can be estimated from the number of times the biofilm sensor 11 is washed. I can do it.

疫 これは流入汚水の有機物の濃度沁、流入汚水量には無関
係に成立する。なぜならば、有機物の量が増加すれば、
白熱充填材3@面上の生物膜の成長速度は速(なるが、
生物膜センサ11の洗浄回数も同様に増加するからであ
る。
This is true regardless of the concentration of organic matter in the inflowing sewage or the amount of inflowing sewage. This is because if the amount of organic matter increases,
The growth rate of biofilm on the incandescent filler 3@ surface is fast (although
This is because the number of times the biofilm sensor 11 is washed also increases.

本実施例において上記の原理を利用した逆洗時期の検知
法および逆洗法をさらに説明すると、あらかじめ生物膜
が肥厚し剥離を始める寸前、の状態における生物膜セン
サ11の洗浄回数を逆洗時を起点として求めておくと、
その後は洗浄回数が所定の回数になった時逆洗を自動的
に行えばよい。つまり洗浄回数を自動的に計数し、設定
した値に達すると汚水の流入および第1コンプレツサ9
の運転を止め、第2コンプレツサ10を起動し逆洗用散
気装置5より空気を吹き込み゛、充填材3表面上の生物
膜を適度の厚さになるまで剥離し、つづいて浄化槽2底
部に汚泥を沈降させ、排泥管7および排泥弁8を介して
槽外に取り出すのである。逆洗が終了すれば、再び汚水
を流入させ、第1コンプレツサ9を起動し、生物膜セン
サの洗浄回数を0にリセットして定常運転に復帰する。
To further explain the backwashing timing detection method and backwashing method using the above-mentioned principle in this embodiment, the number of times the biofilm sensor 11 is washed in a state where the biofilm is about to thicken and begin to peel off is determined in advance during backwashing. If we find it as a starting point, we get
Thereafter, backwashing may be automatically performed when the number of washings reaches a predetermined number. In other words, the number of times of cleaning is automatically counted, and when the set value is reached, the waste water is inflowed into the first compressor 9.
The operation of the septic tank 2 is stopped, the second compressor 10 is started, and air is blown from the backwashing air diffuser 5 to peel off the biofilm on the surface of the filler 3 to an appropriate thickness, and then to the bottom of the septic tank 2. The sludge is allowed to settle and is taken out of the tank via the sludge pipe 7 and sludge valve 8. When the backwashing is completed, sewage is allowed to flow in again, the first compressor 9 is activated, the number of times the biofilm sensor is washed is reset to 0, and normal operation is resumed.

以上の通り本発明では、生物膜センサ11を浄化槽内に
浸漬し、充填材表面上の生物膜の成長状況を正確に検知
することにより、目詰まりの状況に応じて逆洗時期を決
定できるため、逆洗時期が早すぎて生物膜を過剰に剥離
し処理能力を低下せしめて処理水質を悪化させたり、逆
に逆洗が遅れて水質が悪いまま放置したりすることを防
ぐことができる。また浄化槽に流入する有機物の量や流
入汚水の流量が変動しても、その変動に応じた適確な逆
洗時期を自動的に検知することができる。さらに、従来
のように水質を見なから経駿的に逆洗時期を判断する方
法に比べて、自動的に逆洗時期を決定するため無人で適
宜逆洗を行うことができ、メンテナンスのための人件費
を大巾に節約することができる。
As described above, in the present invention, by immersing the biofilm sensor 11 in the septic tank and accurately detecting the growth status of biofilm on the surface of the filler material, the backwashing timing can be determined according to the clogging status. It is possible to prevent backwashing from occurring too early, resulting in excessive exfoliation of biofilms and reducing treatment capacity, resulting in deterioration of treated water quality, or conversely, from backwashing being delayed and leaving water with poor quality. Furthermore, even if the amount of organic matter flowing into the septic tank or the flow rate of inflowing sewage fluctuates, the appropriate backwashing timing can be automatically detected in accordance with the fluctuations. Furthermore, compared to the conventional method of determining the time for backwashing without looking at the water quality, it automatically determines the time for backwashing, so backwashing can be carried out unattended, making it easier for maintenance. You can save a lot of labor costs.

本発明は、いままで説明した嫌気性固定床型浄化槽のほ
かに空気曝気を行う好気性固定床凋浄化槽にも適用でき
る。
The present invention can be applied not only to the anaerobic fixed-bed type septic tank described above but also to an aerobic fixed-bed septic tank that performs air aeration.

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

第1図は本発明の実施例の概略断面図であり、第2図は
本発明に用いる生物膜センサの分解斜視図である。 2・・・浄化槽、3・・・充填材、4・・・散気装置、
5・・・逆洗用散気装置、9・・・第1コンプレツサ、
10°゛・第2コンプレツサ、11・・・生物膜上ンサ
、21・・・発光部、お・・・受光部、あ・・・洗浄ブ
ラシ。 ヤ1の テ20
FIG. 1 is a schematic sectional view of an embodiment of the present invention, and FIG. 2 is an exploded perspective view of a biofilm sensor used in the present invention. 2...Septic tank, 3...Filling material, 4...Diffuser,
5... Backwash diffuser, 9... First compressor,
10°゛・Second compressor, 11...biofilm sensor, 21...light emitting section, oh...light receiving section, ah...cleaning brush. te 20 of ya 1

Claims (1)

【特許請求の範囲】[Claims] 1)汚水を、充填材を沈設した槽に流入させ、該充填材
表面に付着生育した微生物により循環処理する固定床型
汚水浄化槽を逆洗する方法であって、発光部、受光部、
生物膜除去機構よりなる生物膜センサを槽内に浸漬し、
発光部および受光部の汚れ具合に応じて生物膜除去機構
を作動させ、“その作動回数があらかじめ設定したある
回数に達した時、自動的に充填材の逆洗を行うことを特
徴とする固定床型汚水浄化槽の逆洗方法。
1) A method for backwashing a fixed bed type sewage septic tank in which sewage flows into a tank in which a filler is deposited and is circulated through microorganisms grown on the surface of the filler, comprising: a light-emitting part, a light-receiving part,
A biofilm sensor consisting of a biofilm removal mechanism is immersed in a tank,
A fixed device that operates a biofilm removal mechanism depending on the degree of dirt on the light emitting part and the light receiving part, and automatically backwashes the filling material when the number of activations reaches a preset number of times. How to backwash a floor-type sewage septic tank.
JP58040135A 1983-03-11 1983-03-11 Backwashing method of fixed bed type sewage cleaning up tank Pending JPS59166292A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58040135A JPS59166292A (en) 1983-03-11 1983-03-11 Backwashing method of fixed bed type sewage cleaning up tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58040135A JPS59166292A (en) 1983-03-11 1983-03-11 Backwashing method of fixed bed type sewage cleaning up tank

Publications (1)

Publication Number Publication Date
JPS59166292A true JPS59166292A (en) 1984-09-19

Family

ID=12572346

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58040135A Pending JPS59166292A (en) 1983-03-11 1983-03-11 Backwashing method of fixed bed type sewage cleaning up tank

Country Status (1)

Country Link
JP (1) JPS59166292A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1331773C (en) * 2002-12-26 2007-08-15 中国科学院生态环境研究中心 Membrane rector with rotary brush

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1331773C (en) * 2002-12-26 2007-08-15 中国科学院生态环境研究中心 Membrane rector with rotary brush

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