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JPH05111692A - Method for controlling septic tank - Google Patents

Method for controlling septic tank

Info

Publication number
JPH05111692A
JPH05111692A JP27441891A JP27441891A JPH05111692A JP H05111692 A JPH05111692 A JP H05111692A JP 27441891 A JP27441891 A JP 27441891A JP 27441891 A JP27441891 A JP 27441891A JP H05111692 A JPH05111692 A JP H05111692A
Authority
JP
Japan
Prior art keywords
tank
chamber
filter bed
anaerobic filter
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.)
Granted
Application number
JP27441891A
Other languages
Japanese (ja)
Other versions
JP2669737B2 (en
Inventor
Hachiro Sato
八郎 佐藤
Yoshito Kitai
良人 北井
Masaru Harada
大 原田
Kazuyuki Honda
和之 本田
Katsumi Hamada
勝己 浜田
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.)
Kubota Corp
Original Assignee
Kubota 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 Kubota Corp filed Critical Kubota Corp
Priority to JP27441891A priority Critical patent/JP2669737B2/en
Publication of JPH05111692A publication Critical patent/JPH05111692A/en
Application granted granted Critical
Publication of JP2669737B2 publication Critical patent/JP2669737B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Treatment Of Biological Wastes In General (AREA)

Abstract

PURPOSE:To minimize the release of settled sludge while well maintaining nitrification and denitrification treatments by intermittent aeration. CONSTITUTION:A 1st chamber N1 of an anaerobic filter bed tank, a 2nd chamber N2 of the anaerobic filter bed tank and a contact aeration tank E are provided in this order from a sewage inflow side. The aeration in the contact aeration tank E is intermittently executed. The treated water in the contact aeration tank E is returned to the 2nd chamber N2 of the anaerobic filter bed tank at the time of the aeration and is returned to the 1st chamber N1 of the anaerobic filter bed tank at the time of stopping the aeration.

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、汚水流入側から嫌気濾
床槽第1室、嫌気濾床槽第2室から成る嫌気濾床槽と接
触ばっ気槽をこの順に設けた浄化槽に対し、前記接触ば
っ気槽内のばっ気を間欠的に行うと共に、前記接触ばっ
気槽内の処理水を前記嫌気濾床槽に返送する浄化槽の制
御方法に関する。
BACKGROUND OF THE INVENTION The present invention relates to a septic tank in which an anaerobic filter bed tank comprising a anaerobic filter bed tank first chamber and an anaerobic filter bed tank second chamber and a contact aeration tank are provided in this order from the sewage inflow side. The present invention relates to a method for controlling a septic tank in which aeration in the contact aeration tank is intermittently performed and the treated water in the contact aeration tank is returned to the anaerobic filter bed tank.

【0002】[0002]

【従来の技術】間欠ばっ気を行うのは、ばっ気によって
前記接触ばっ気槽内の好気性微生物に酸素を供給して硝
化等の好気処理を行うと共に、ばっ気を止めることによ
って嫌気性微生物の働きを助けて脱窒等の嫌気処理を行
い、つまり、硝化、脱窒をバランスよく行い、併せて、
ばっ気のための動力を節約するためであるが、この様な
間欠ばっ気を行いながら、従来は、前記接触ばっ気槽内
の処理水を常時前記嫌気濾床槽第1室に返送していた。
2. Description of the Related Art Intermittent aeration is performed by supplying oxygen to aerobic microorganisms in the contact aeration tank by aeration to perform aerobic treatment such as nitrification, and at the same time, to stop anaerobic Anaerobic treatment such as denitrification is carried out by assisting the function of microorganisms, that is, nitrification and denitrification are performed in a well-balanced manner.
In order to save power for aeration, the treated water in the contact aeration tank is always returned to the anaerobic filter bed first chamber while performing such intermittent aeration. It was

【0003】[0003]

【発明が解決しようとする課題】ところが、前記接触ば
っ気槽E内の処理水を常時前記嫌気濾床槽第1室に返送
する従来の方法では、この返送水によって嫌気濾床槽第
1室内の沈殿貯留汚泥が常時攪拌されて下流に移流し易
く、放流されて満足な浄化処理ができなくなる虞があっ
た。そこで、本発明の目的は、間欠ばっ気によって硝
化、脱窒処理を良好に保ちながら、しかも沈降汚泥が移
流、放流されることを抑制することにある。
However, in the conventional method in which the treated water in the contact aeration tank E is constantly returned to the anaerobic filter bed first chamber, the returned water causes the anaerobic filter bed first chamber to be returned. The sludge in the settling pool was constantly stirred and was easily transferred to the downstream side, and there was a risk that the sludge would be discharged and a satisfactory purification process could not be performed. Therefore, an object of the present invention is to suppress advection and discharge of settled sludge while maintaining good nitrification and denitrification treatment by intermittent aeration.

【0004】[0004]

【課題を解決するための手段】この目的を達成するため
の本発明による浄化槽の制御方法の特徴手段は、接触ば
っ気槽内のばっ気を間欠的に行うと共に、前記接触ばっ
気槽内の処理水を、前記ばっ気時には、嫌気濾床槽第2
室に返送し、前記ばっ気停止時には、嫌気濾床槽第1室
に返送することにあり、その作用効果は次の通りであ
る。
To achieve this object, the characteristic means of the method for controlling a septic tank according to the present invention is to intermittently perform aeration in the contact aeration tank and to perform the aeration in the contact aeration tank. When the aeration is performed, the treated water is anaerobic filter bed second
It is returned to the chamber and returned to the anaerobic filter bed first chamber when the aeration is stopped. Its action and effect are as follows.

【0005】[0005]

【作用】ばっ気時には、接触ばっ気槽内の処理液が攪拌
されて剥離汚泥が全体に分散しているため、特に剥離汚
泥の濃度の高いところがない。従って、元々沈降汚泥の
少ない嫌気濾床槽第2室に処理液を返送した方が、沈殿
汚泥が多い嫌気濾床槽第1室に返送するよりも接触ばっ
気槽側への汚泥の移流が少ない。ばっ気停止時には、接
触ばっ気槽内の剥離汚泥が沈降し易いから、汚泥の濃度
の高い処理水を返送することができる。従って、この場
合は、汚泥濃度の高い処理水を嫌気濾床槽第1室に返送
した方が、ここである程度汚泥を沈降分離させることが
できるので、嫌気濾床槽第2室に返送する場合に比べて
接触ばっ気槽への沈殿汚泥の移流が少ない。従って、前
記接触ばっ気槽内の処理水を、ばっ気時には、嫌気濾床
槽第2室に返送し、ばっ気停止時には、嫌気濾床槽第1
室に返送することによって、常に嫌気濾床槽第1室に返
送していた従来の方法による場合に比べて、汚泥の流出
を少なく抑えることができる。
In the aeration, the treatment liquid in the contact aeration tank is agitated and the peeled sludge is dispersed in the whole, so that there is no particularly high concentration of the peeled sludge. Therefore, returning the treated liquid to the second chamber of the anaerobic filter bed tank, which originally has less sedimentation sludge, is more effective in advancing the sludge to the contact aeration tank side than returning it to the first chamber of the anaerobic filter bed tank, which has much sedimentation sludge. Few. When the aeration is stopped, the separated sludge in the contact aeration tank tends to settle, so that the treated water having a high sludge concentration can be returned. Therefore, in this case, if the treated water having a high sludge concentration is returned to the anaerobic filter bed first chamber, the sludge can be separated and settled to some extent here. There is less advection of settled sludge to the contact aeration tank compared to. Therefore, the treated water in the contact aeration tank is returned to the anaerobic filter bed second chamber during aeration, and when the aeration is stopped, the anaerobic filter tank first
By returning the sludge to the chamber, the outflow of sludge can be suppressed as compared with the case of the conventional method in which the sludge is always returned to the anaerobic filter bed first chamber.

【0006】[0006]

【発明の効果】つまり、間欠ばっ気によって硝化、脱窒
処理を良好に保ちながら、しかも沈降汚泥が放流される
ことを最小限に抑えることができる。
In other words, it is possible to keep the nitrification and denitrification treatment in good condition by intermittent aeration, and at the same time, to minimize the discharge of settled sludge.

【0007】[0007]

【実施例】以下、本願の実施例を図面に基づいて説明す
る。図1に、本願の浄化槽の縦断側面図を示す。この浄
化槽は、上流側から、嫌気濾床槽第1室N1と嫌気濾床
槽第2室N2から成る嫌気濾床槽N、接触ばっ気槽E、
そして沈殿槽Pを、この順に備えて構成されている。以
下、各槽N、E、Pについて更に説明を加える。前記嫌
気濾床槽Nの上方には、マンホールM’を設けてある。
嫌気濾床槽第1室N1は、流入口2から流入する処理水
中の粗大浮遊懸濁物を浮上又は沈殿させて除去するとと
もに、嫌気濾床槽第2室N2と同様に有機物の嫌気分解
処理や後述する硝化液の脱窒を行う。そのため、この嫌
気濾床槽第1室N1と嫌気濾床槽第2室N2には、前記
有機物を嫌気分解する嫌気性微生物を生息させ、その生
物膜として定着させるために、プラスチック製の第1、
第2濾床F1、F2が設けられている。ここで、嫌気濾
床槽第1室N1の第1濾床F1は、目詰まりしにくい粗
い格子間隔のハニカムチューブ状濾材メッシュで形成さ
れ、嫌気濾床槽第2室N2の第2濾床F2は嫌気濾床槽
第1室N1の第1濾床F1よりも密なハニカムチューブ
状濾材メッシュで形成されている。次に前記接触ばっ気
槽Eについて説明する。接触ばっ気槽Eは、主として処
理水中の有機物を酸化分解したり、アンモニア性窒素を
硝化するものであり、この目的で好気性微生物を定着さ
せるプラスチック製の接触材Cを設けてある。更に、接
触ばっ気槽E内に処理水の循環流を生ぜしめて、有機物
を含む処理水を前記接触材Cに定着させた好気性微生物
とよく接触させるとともに、この好気性微生物に必要な
酸素を与えるためブロワーLからのエアーを槽内に供給
する散気管Dが接触ばっ気槽E内に配設されている。
尚、接触ばっ気槽E内においては、主として前記好気性
微生物を生息させてこれを利用しているものの、通性嫌
気性菌等の嫌気性微生物も生息しており、ばっ気を止め
て嫌気状態に近い状態にすると、これら一部の嫌気性微
生物が働きやすくなり、硝化液を更に窒素ガス等に分解
する謂ゆる脱窒処理もある程度行うことができる。更
に、接触ばっ気槽E内の硝化液及び剥離汚泥を嫌気濾床
槽Nに返送して、上流側で汚泥を沈降させ、脱窒処理を
促進するために、エアリフトポンプAと返送路Bが備え
られている。接触ばっ気槽Eの上方にはマンホールMを
設けてある。次に、前記沈殿槽Pについて説明すると、
この槽Pには消毒槽Qが備えられ、接触ばっ気槽Eから
の排水に対して、その浮遊懸濁物を沈殿除去した後、消
毒して放流口3から放流するようにしてある。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 shows a vertical side view of the septic tank of the present application. This septic tank comprises, from the upstream side, an anaerobic filter bed tank N composed of an anaerobic filter bed tank first chamber N1 and an anaerobic filter bed tank N2, a contact aeration tank E,
The settling tank P is provided in this order. Hereinafter, each tank N, E, and P is further explained. A manhole M ′ is provided above the anaerobic filter bed tank N.
The anaerobic filter bed tank first chamber N1 removes the floating suspension suspended in the treated water flowing from the inflow port 2 by floating or settling, and the anaerobic decomposition treatment of organic substances similarly to the anaerobic filter bed tank second chamber N2. And denitrification of the nitrification solution described later. Therefore, in the anaerobic filter bed first chamber N1 and the anaerobic filter bed second chamber N2, in order to make the anaerobic microorganisms that anaerobically decompose the organic matter inhabit and to be fixed as a biofilm thereof, the plastic first ,
Second filter beds F1 and F2 are provided. Here, the first filter bed F1 of the anaerobic filter bed tank first chamber N1 is formed of a honeycomb tubular filter medium mesh with a coarse lattice spacing that is unlikely to be clogged, and the second filter bed F2 of the anaerobic filter bed tank second chamber N2 is used. Is formed of a honeycomb tubular filter medium mesh that is denser than the first filter bed F1 of the anaerobic filter bed first chamber N1. Next, the contact aeration tank E will be described. The contact aeration tank E mainly oxidizes and decomposes organic substances in treated water and nitrifies ammoniacal nitrogen, and is provided with a plastic contact material C for fixing aerobic microorganisms for this purpose. Further, a circulating flow of the treated water is generated in the contact aeration tank E so that the treated water containing an organic substance is brought into good contact with the aerobic microorganisms fixed on the contact material C, and oxygen necessary for the aerobic microorganisms is generated. An air diffuser D for supplying the air from the blower L into the tank for giving is provided in the contact aeration tank E.
In the contact aeration tank E, although the aerobic microorganisms are mainly inhabited and used, anaerobic microorganisms such as facultative anaerobic bacteria also inhabit, and the aeration is stopped and the anaerobic is stopped. When the state is close to the state, some of these anaerobic microorganisms are likely to work, and so-called denitrification treatment for further decomposing the nitrification solution into nitrogen gas or the like can be performed to some extent. Further, the air lift pump A and the return passage B are provided in order to return the nitrification liquid and the separated sludge in the contact aeration tank E to the anaerobic filter bed tank N to settle the sludge on the upstream side and accelerate the denitrification process. It is equipped. A manhole M is provided above the contact aeration tank E. Next, the precipitation tank P will be described.
The tank P is provided with a disinfecting tank Q, and the drainage from the contact aeration tank E is subjected to sedimentation and removal of the suspended suspension thereof, followed by disinfection and discharge from the discharge port 3.

【0008】以下に、上記の浄化槽の制御方法について
説明する。前記接触ばっ気槽E内のばっ気及びエアーリ
フトポンプへの給気は、1台の前記ブロワーLを共用し
て行っている。前記ばっ気は、ブロワーLから散気管D
へのエアーの供給を電磁弁Vdを開閉することにより間
欠的に行う。一方エアーリフトポンプは常時運転してい
る。Vaはエアーリフトポンプ用の流量調整弁である
が、これは最初に適当な流量に調整すれば、以後はその
ままにしておけばよい。返送路Bは、返送水を嫌気濾床
槽第1室N1と第2室N2のいずれにでも返送できるよ
うに途中で分岐させると共に、第2室N2への分岐管の
途中に前記電磁弁Vdと連動する電磁弁Vbを設け、前
記ばっ気時には、電磁弁Vbが開いて処理水が嫌気濾床
槽第2室N2に返送され、前記ばっ気停止時には、電磁
弁Vbが閉じて前記嫌気濾床槽第1室N1に返送される
ようにしてある。図中Sは、電磁弁Vdが開くと電磁弁
Vbが開き、電磁弁Vdが閉じると電磁弁Vbが閉じる
ように、両電磁弁Vd、Vbを連動させるシーケンス制
御装置である。以上に述べた構成の浄化槽で、ばっ気時
には、接触ばっ気槽E内の処理水を嫌気濾床槽第2室N
2に返送し、ばっ気停止時には、嫌気濾床槽第1室に返
送することによって、接触ばっ気槽内の処理水を常に嫌
気濾床槽第1室に返送していた従来の方法による場合に
比べて、汚泥の流出を少なく抑えることができる。尚、
嫌気濾床槽第1室N1には膜濾過装置Rを設けてもよ
い。濾過膜装置Rを作動させるポンプは用いず、嫌気濾
床槽第1室N1から第2室N2への溢流口の高さを、第
2室N2の水位よりも充分高くすることによって、第1
室N1と第2室N2の水位に高低差を生ぜしめ、その水
頭差によって濾過圧が得られるようにしてある。嫌気濾
床槽第1室N1の処理水は、溢流することなく、この膜
濾過装置を通って第2室N2に移流するので、流量の変
動が緩和されると共に、下流側への浮遊懸濁物の移流が
さらに低減して脱窒処理がより容易になり、併せて汚泥
等浮遊懸濁物が放流されることが、より確実に防止され
る。
The method for controlling the above septic tank will be described below. Aeration in the contact aeration tank E and air supply to the air lift pump are performed by using one blower L in common. The aeration is from the blower L to the air diffuser D
Air is supplied to the chamber intermittently by opening and closing the solenoid valve Vd. On the other hand, the air lift pump is always operating. Va is a flow rate adjusting valve for the air lift pump, but this may be adjusted to an appropriate flow rate first and then left as it is thereafter. The return passage B is branched so that the return water can be returned to either the first chamber N1 or the second chamber N2 of the anaerobic filter bed tank, and the solenoid valve Vd is provided in the middle of the branch pipe to the second chamber N2. An electromagnetic valve Vb is provided to interlock with the anaerobic filter, and when the aeration is performed, the electromagnetic valve Vb is opened and the treated water is returned to the anaerobic filter bed second chamber N2. When the aeration is stopped, the electromagnetic valve Vb is closed and the anaerobic filter is closed. It is designed to be returned to the floor tank first chamber N1. In the figure, S is a sequence control device that interlocks both solenoid valves Vd and Vb so that the solenoid valve Vb opens when the solenoid valve Vd opens and the solenoid valve Vb closes when the solenoid valve Vd closes. In the septic tank having the above-described configuration, the treated water in the contact aeration tank E is supplied to the anaerobic filter bed second chamber N during aeration.
In the case of the conventional method in which the treated water in the contact aeration tank is always returned to the anaerobic filter bed first chamber by returning it to No. 2 and returning to the anaerobic filter bed first chamber when aeration is stopped. Compared with, the outflow of sludge can be reduced. still,
A membrane filtration device R may be provided in the anaerobic filter bed first chamber N1. The pump for operating the filtration membrane device R is not used, and the height of the overflow port from the first chamber N1 of the anaerobic filter bed tank is made sufficiently higher than the water level of the second chamber N2. 1
A height difference is produced between the water levels of the chamber N1 and the second chamber N2, and the filtration pressure is obtained by the difference in the water heads. The treated water in the anaerobic filter bed first chamber N1 is admitted to the second chamber N2 through this membrane filtration device without overflowing, so that fluctuations in the flow rate are alleviated and the suspended suspension to the downstream side is reduced. The advection of suspended solids is further reduced, the denitrification process becomes easier, and at the same time, the release of suspended suspended matters such as sludge is more reliably prevented.

【0009】尚、特許請求の範囲の項に図面との対照を
便利にするために符号を記すが、該記入により本発明は
添付図面の構成に限定されるものではない。
It should be noted that reference numerals are given in the claims for convenience of comparison with the drawings, but the present invention is not limited to the configurations of the accompanying drawings by the entry.

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

【図1】本願の実施例における浄化槽の縦断側面図FIG. 1 is a vertical sectional side view of a septic tank according to an embodiment of the present application.

【符号の説明】[Explanation of symbols]

N 嫌気濾床槽 N1 嫌気濾床槽第1室 N2 嫌気濾床槽第2室 E 接触ばっ気槽 N Anaerobic filter bed tank N1 Anaerobic filter bed tank 1st chamber N2 Anaerobic filter bed tank 2nd chamber E Contact aeration tank

フロントページの続き (72)発明者 本田 和之 滋賀県甲賀郡甲西町高松2番地の1 株式 会社クボタ滋賀工場内 (72)発明者 浜田 勝己 滋賀県甲賀郡甲西町高松2番地の1 株式 会社クボタ滋賀工場内Front Page Continuation (72) Inventor Kazuyuki Honda, 1 Takamatsu, Kosai-cho, Koga-gun, Shiga Prefecture 1 Stock company, Kubota Plant (72) Inventor Katsumi Hamada, 1-share, Takamatsu, Koga-gun, Shiga Prefecture Kubota Company, Ltd. Inside the Shiga factory

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 汚水流入側から嫌気濾床槽第1室(N
1)、嫌気濾床槽第2室(N2)から成る嫌気濾床槽
(N)と接触ばっ気槽(E)をこの順に設けた浄化槽に
対し、前記接触ばっ気槽(E)内のばっ気を間欠的に行
うと共に、前記接触ばっ気槽(E)内の処理水を前記嫌
気濾床槽(N)に返送する浄化槽の制御方法であって、 前記処理水を、前記ばっ気時には、前記嫌気濾床槽第2
室(N2)に返送し、前記ばっ気停止時には、前記嫌気
濾床槽第1室(N1)に返送する浄化槽の制御方法。
1. An anaerobic filter bed first chamber (N
1), the anaerobic filter bed tank (N) consisting of the second chamber (N2) of the anaerobic filter bed tank and the contact aeration tank (E) are provided in this order, in contrast to the septic tank, in the contact aeration tank (E) A method of controlling a septic tank, in which the treated water in the contact aeration tank (E) is returned to the anaerobic filter bed tank (N) while performing air intermittently, wherein the treated water is at the time of the aeration. The anaerobic filter bed second
A method for controlling a septic tank which is returned to the chamber (N2) and is returned to the anaerobic filter bed first chamber (N1) when the aeration is stopped.
JP27441891A 1991-10-23 1991-10-23 Control method of septic tank Expired - Lifetime JP2669737B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27441891A JP2669737B2 (en) 1991-10-23 1991-10-23 Control method of septic tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP27441891A JP2669737B2 (en) 1991-10-23 1991-10-23 Control method of septic tank

Publications (2)

Publication Number Publication Date
JPH05111692A true JPH05111692A (en) 1993-05-07
JP2669737B2 JP2669737B2 (en) 1997-10-29

Family

ID=17541397

Family Applications (1)

Application Number Title Priority Date Filing Date
JP27441891A Expired - Lifetime JP2669737B2 (en) 1991-10-23 1991-10-23 Control method of septic tank

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002001369A (en) * 2000-06-23 2002-01-08 Hitachi Chem Co Ltd Sewage septic tank with bioreactor charged with precipitating carrier
JP2020157255A (en) * 2019-03-27 2020-10-01 株式会社ハウステック Septic tank and septic tank operation method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002001369A (en) * 2000-06-23 2002-01-08 Hitachi Chem Co Ltd Sewage septic tank with bioreactor charged with precipitating carrier
JP4689007B2 (en) * 2000-06-23 2011-05-25 株式会社ハウステック Wastewater purification method
JP2020157255A (en) * 2019-03-27 2020-10-01 株式会社ハウステック Septic tank and septic tank operation method

Also Published As

Publication number Publication date
JP2669737B2 (en) 1997-10-29

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