JP2000271581A - Membrane treatment type septic tank - Google Patents

Membrane treatment type septic tank

Info

Publication number
JP2000271581A
JP2000271581A JP11084107A JP8410799A JP2000271581A JP 2000271581 A JP2000271581 A JP 2000271581A JP 11084107 A JP11084107 A JP 11084107A JP 8410799 A JP8410799 A JP 8410799A JP 2000271581 A JP2000271581 A JP 2000271581A
Authority
JP
Japan
Prior art keywords
treatment tank
tank
membrane
water
sludge
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.)
Withdrawn
Application number
JP11084107A
Other languages
Japanese (ja)
Inventor
Takayoshi Nakaoka
敬善 中岡
Shinya Hirota
伸也 広田
Shin Matsugi
伸 真継
Hiroshi Kano
広志 加納
Shigeyuki Yamaguchi
重行 山口
Hitoshi Kitamura
仁史 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.)
Panasonic Electric Works Co Ltd
Original Assignee
Matsushita Electric Works 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 Matsushita Electric Works Ltd filed Critical Matsushita Electric Works Ltd
Priority to JP11084107A priority Critical patent/JP2000271581A/en
Publication of JP2000271581A publication Critical patent/JP2000271581A/en
Withdrawn legal-status Critical Current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

PROBLEM TO BE SOLVED: To keep the concn. of activated sludge in a secondary treatment tank proper by rationally grasping the generation of excessive sludge regardless of a treatment mode. SOLUTION: In a membrane treatment type septic tank equipped with a primary treatment tank 1 in which water to be treated is charged, a secondary treatment tank 2 performing the membrane treatment of the primarily treated water transferred from the primary treatment tank 1 by a membrane separator 6, a discharge pump 3 discharging the secondarily treated water in the secondary treatment tank 2 to the outside and a sludge withdrawing pump 4 returning excessive sludge in the secondary treatment tank 2 to the primary treatment tank 1, a control part 5 operating the sludge withdrawing pump 4 when integrated water quantity obtained by integrating the quantity of membrane-treated water in the membrane separator 6 reaches a specified quantity is provided.

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、膜処理浄化槽に関
し、詳しくは、処理モードに係わることなく余剰汚泥の
発生を適正に把握して二次処理槽における活性汚泥濃度
を適性に維持しようとする技術に係るものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a membrane treatment / purification tank, and more particularly, to appropriately grasp the generation of excess sludge and to maintain an appropriate concentration of activated sludge in a secondary treatment tank regardless of a treatment mode. It concerns technology.

【0002】[0002]

【従来の技術】従来、被処理水を投入する一次処理槽
と、一次処理槽からの一次処理水を移流して浸漬された
膜分離装置によって膜処理をおこなう二次処理槽と、二
次処理槽内の二次処理水を外部に放流する放流ポンプ
と、二次処理槽内の余剰汚泥を一次処理槽に返送する汚
泥引き抜きポンプとを備えた膜処理型浄化槽において、
二次処理槽における活性汚泥濃度を適性に保つために
は、適性量の余剰汚泥を引き抜く必要がある。
2. Description of the Related Art Conventionally, a primary treatment tank into which water to be treated is charged, a secondary treatment tank in which a primary treatment water is transferred from the primary treatment tank and subjected to membrane treatment by a membrane separator immersed therein, and a secondary treatment tank In a membrane treatment type purification tank equipped with a discharge pump that discharges secondary treatment water in the tank to the outside and a sludge extraction pump that returns excess sludge in the secondary treatment tank to the primary treatment tank,
In order to keep the activated sludge concentration in the secondary treatment tank at an appropriate level, it is necessary to extract an appropriate amount of excess sludge.

【0003】一般に、余剰汚泥の発生は流入負荷及びろ
過水量に比例するのであり、ろ過水量を検出することで
余剰汚泥の発生量を推定するのである。ところで、ろ過
水量の検出に際して、特別なセンサーを使用しないでお
こなうには、膜ろ過の処理回数、即ち、上限設定水位か
ら膜ろ過を開始し、放流ポンプを停止する下限設定水位
までを1サイクルとしてカウントし、カウント数が所定
回数になった時点で、汚泥引き抜きを実施する方法が考
えられる。
Generally, the generation of excess sludge is proportional to the inflow load and the amount of filtered water, and the amount of generated excess sludge is estimated by detecting the amount of filtered water. By the way, when detecting the amount of filtered water, without using a special sensor, the number of times of membrane filtration treatment, that is, the membrane filtration starts from the upper limit set water level, and the lower limit set water level to stop the discharge pump as one cycle. A method of counting and counting the number of counts to a predetermined number and performing sludge extraction is conceivable.

【0004】ところが、被処理水を投入する一次処理槽
と、一次処理槽にて処理された一次処理水を移流して間
欠ばっ気処理をおこなう二次処理槽を備えた膜分離型浄
化槽においては、一次及び二次処理槽における上下限の
水位情報に基づいて、ばっ気とばっ気停止とを所定時間
通りに繰り返す通常モード、一次処理槽としての夾雑物
分離貯留槽に被処理水(汚水)の流入がない時間帯にお
いて、膜分離装置における活性汚泥の活性を維持するた
めに最小限のばっ気運転のみをおこなう省エネモード、
及び、一次処理槽に被処理水が設計値以上に流入する
と、一次処理槽から二次処理槽へと連続的に一次処理水
を投入するとともに、膜分離装置における処理を連続的
におこなう高速モードに自動的に移行する自動運転シス
テムになっている。
However, a membrane separation type purification tank having a primary treatment tank into which water to be treated is charged, and a secondary treatment tank in which the primary treatment water treated in the primary treatment tank is transferred and intermittently aerated is performed. A normal mode in which aeration and aeration stop are repeated at predetermined time intervals based on upper and lower water level information in the primary and secondary treatment tanks, and water to be treated (sewage) is stored in the impurity separation and storage tank as the primary treatment tank. Energy-saving mode in which only a minimum aeration operation is performed in order to maintain the activity of activated sludge in the membrane separation device during the time when there is no inflow of
And, when the water to be treated flows into the primary treatment tank more than the design value, the primary treatment water is continuously supplied from the primary treatment tank to the secondary treatment tank, and the high-speed mode in which the treatment in the membrane separation device is continuously performed. It is an automatic driving system that automatically shifts to.

【0005】このように、窒素除去型膜分離合併処理浄
化槽は、各槽の水位情報をもとに通常モード、省エネモ
ード、高速モードのいずれかに自動的に移行するシステ
ムとなっているため、高速モ−ドに移行すると、通常モ
ードにおける水位検出に基づいて汚泥の引き抜きをおこ
なう上述の方法は実施できないという問題があった。
As described above, the nitrogen removal type membrane separation / combination treatment septic tank is a system that automatically shifts to any of the normal mode, the energy saving mode, and the high-speed mode based on the water level information of each tank. When the mode is shifted to the high-speed mode, there is a problem that the above-described method of extracting sludge based on the detection of the water level in the normal mode cannot be performed.

【0006】[0006]

【発明が解決しよとする課題】本発明はこのような問題
に鑑みてなされたものであり、処理モードに係わること
なく余剰汚泥の発生を適正に把握して二次処理槽におけ
る余剰汚泥を適性に引く抜いて活性汚泥濃度を適性に維
持することができる膜処理型浄化槽を提供することを課
題とするものである。
SUMMARY OF THE INVENTION The present invention has been made in view of such a problem, and properly grasps the generation of surplus sludge without depending on the treatment mode and removes the excess sludge in the secondary treatment tank. It is an object of the present invention to provide a membrane treatment type septic tank that can be appropriately pulled out to maintain the activated sludge concentration at an appropriate level.

【0007】[0007]

【課題を解決するための手段】請求項1においては、被
処理水を投入する一次処理槽1と、一次処理槽1からの
一次処理水を移流して浸漬された膜分離装置6によって
膜処理をおこなう二次処理槽2と、二次処理槽2内の二
次処理水を外部に放流する放流ポンプ3と、二次処理槽
2内の余剰汚泥を一次処理槽1に返送する汚泥引き抜き
ポンプ4とを備えた膜処理型浄化槽であって、膜処理装
置6における膜処理水量を積算した積算水量が一定量に
達したことによって汚泥引き抜きポンプ4を運転する制
御部5を備えていることを特徴とするものである。この
ような構成によれば、どのような処理モードにおいても
膜処理装置6における膜処理水量を積算することができ
るのであり、膜処理水量が増すのに伴って増加する余剰
汚泥の引き抜きを適性におこなうことができるものであ
る。
According to the first aspect of the present invention, the membrane treatment is performed by a primary treatment tank 1 into which water to be treated is charged, and a membrane separation device 6 in which the primary treatment water from the primary treatment tank 1 is transferred and immersed. Treatment tank 2 which performs the following, a discharge pump 3 for discharging secondary treatment water in the secondary treatment tank 2 to the outside, and a sludge extraction pump for returning excess sludge in the secondary treatment tank 2 to the primary treatment tank 1 And a control unit 5 for operating the sludge extraction pump 4 when the integrated water amount obtained by integrating the membrane treatment water amount in the membrane treatment device 6 reaches a certain amount. It is a feature. According to such a configuration, the amount of membrane treatment water in the membrane treatment device 6 can be integrated in any treatment mode, and the excess sludge withdrawal that increases as the amount of membrane treatment water increases can be appropriately removed. It is something that can be done.

【0008】請求項2においては、膜処理した積算水量
を、放流ポンプ3の運転時間を積算した積算時間によっ
て換算することを特徴とするものである。このような構
成によれば、膜処理水量の積算に比べて構成を簡素化で
きるものである。
According to a second aspect of the present invention, the integrated amount of water subjected to the membrane treatment is converted by the integrated time obtained by integrating the operation time of the discharge pump 3. According to such a configuration, the configuration can be simplified as compared with the integration of the amount of membrane treatment water.

【0009】請求項3においては、被処理水を投入する
一次処理槽1と、一次処理槽1からの一次処理水を移流
して浸漬された膜分離装置6によって膜処理をおこなう
二次処理槽2と、二次処理槽2内の二次処理水を外部に
放流する放流ポンプ3と、二次処理槽2内の余剰汚泥を
一次処理槽1に返送する汚泥引き抜きポンプ4とを備え
た膜処理型浄化槽であって、二次処理槽2における水位
が単位時間当たりにおいて1回以上上限設定水位H2に
達したことを1回とカウントし、そのカウント数が所定
数に達したで汚泥引き抜きポンプ4を運転する制御部5
を備えていることを特徴とするものである。このような
構成によれば、例えば過大流入により、単位時間当たり
に何度も上限設定水位H2を越えてもこれを1回として
カウントするのであり、高速モードにおいても過剰な汚
泥の引き抜きを回避することができ、適性な活性汚泥濃
度を維持することができるものである。
According to a third aspect of the present invention, there is provided a secondary treatment tank for performing a membrane treatment by a primary treatment tank 1 into which water to be treated is charged and a membrane separation device 6 in which the primary treatment water from the primary treatment tank 1 is transferred and immersed. 2, a discharge pump 3 for discharging secondary treatment water in the secondary treatment tank 2 to the outside, and a sludge extraction pump 4 for returning excess sludge in the secondary treatment tank 2 to the primary treatment tank 1. A treatment-type septic tank, in which the water level in the secondary treatment tank 2 reaches the upper limit set water level H2 at least once per unit time is counted as one time, and when the count reaches a predetermined number, the sludge removal pump is used. Control unit 5 for driving 4
It is characterized by having. According to such a configuration, even if the water level exceeds the upper limit set water level H2 many times per unit time due to, for example, an excessive inflow, the water level is counted as one time, and even in the high-speed mode, excessive sludge extraction is avoided. And can maintain an appropriate activated sludge concentration.

【0010】請求項4においては、被処理水を投入する
一次処理槽1と、一次処理槽1からの一次処理水を移流
して浸漬された膜分離装置6によって膜処理をおこなう
二次処理槽2と、二次処理槽2内の二次処理水を外部に
放流する放流ポンプ3と、二次処理槽2内の余剰汚泥を
一次処理槽1に返送する汚泥引き抜きポンプ4とを備え
た膜処理型浄化槽であって、放流ポンプ3の積算運転時
間が所定時間に達することが単位時間あたりに1回あれ
ば1回の汚泥引き抜きポンプ4を運転し、その後におけ
る単位時間内の放流ポンプ3の運転時間を積算するのを
停止し、又、放流ポンプ3の積算運転時間が所定時間に
達することが単位時間あたりに無ければ、次の単位時間
においても運転時間を積算して所定時間に達した時点で
汚泥引き抜きポンプ4を運転する制御部5を備えている
ことを特徴とするものである。
According to a fourth aspect of the present invention, there is provided a primary treatment tank for charging the water to be treated, and a secondary treatment tank for carrying out the membrane treatment by the membrane separation device in which the primary treatment water from the primary treatment tank is transferred and immersed. 2, a discharge pump 3 for discharging secondary treatment water in the secondary treatment tank 2 to the outside, and a sludge extraction pump 4 for returning excess sludge in the secondary treatment tank 2 to the primary treatment tank 1. If the accumulated operation time of the discharge pump 3 reaches the predetermined time once per unit time, the sludge removal pump 4 is operated once, and the discharge pump 3 is operated within the unit time thereafter. If the integration of the operation time was stopped, and if the integrated operation time of the discharge pump 3 did not reach the predetermined time per unit time, the operation time was integrated even in the next unit time and reached the predetermined time. Sludge withdrawal pong at time And it is characterized in that it comprises a control unit 5 for operating a 4.

【0011】このような構成によれば、例えば多人数の
来客があった場合等に高速モードになって放流ポンプ3
の運転の積算時間が単位時間(例えば24時間)当たり
に所定時間に達すると、汚泥引き抜きポンプ4を作動さ
せて汚泥の引き抜きをおこなうのであるが、単位時間の
残りの時間においては、放流ポンプ3が運転されていて
も運転時間の積算をおこなうことがなく、単位時間に何
度も汚泥の引き抜きをおこなうことを回避することがで
き、過剰な汚泥の引き抜きを回避することができ、適性
な活性汚泥濃度を維持することができるものである。
According to such a configuration, for example, when there are a large number of visitors, the high-speed mode is set and the discharge pump 3
When the accumulated time of the operation reaches a predetermined time per unit time (for example, 24 hours), the sludge extraction pump 4 is operated to extract sludge. However, in the remaining time of the unit time, the discharge pump 3 It does not accumulate the operating time even when the system is operating, avoids sludge withdrawal many times per unit time, avoids excessive sludge withdrawal, and has an appropriate activity Sludge concentration can be maintained.

【0012】[0012]

【発明の実施の形態】以下、本発明の実施の形態を図面
に基づいて説明する。図1は浄化槽の説明図であり、図
2は通常モードを示すフローチャートである。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is an explanatory diagram of a septic tank, and FIG. 2 is a flowchart showing a normal mode.

【0013】図1に示すように、浄化槽は、例えば、ば
つ気とばつ気停止を単一槽で行う間欠ばつ気式の窒素除
去型膜分離合併浄化槽であって、不規則に流入する汚水
を一旦、一次処理槽1としての夾雑物分離貯留槽(流量
調整槽兼用)1aに貯留し、汚水の有機物濃度を均一に
した後、汚水移送槽内の移送ポンプ10で一定量ずつ二
次処理槽2としての膜分離装置6を備えた膜分離間欠ば
つ気槽2aに移送される。 膜分離間欠ばつ気槽2aに
おいては有機性汚水を膜分離装置6における活性汚泥に
より生物処理し、浸漬型の膜分離装置6にて固液分離を
おこなう。又、ばつ気用送風機7の停止および運転の繰
り返しで嫌気状態と好気状態がつくられて槽内の汚水の
溶存酸素量(DO)を制御することで窒素除去をおこな
う。又、槽内には汚泥引き抜きポンプ(工アリフトポン
プ)4が設けられ、制御部5の設定に応じ、一定量の余
剰汚泥を夾雑物分離貯留槽1aに引き抜き、MLSS
(活性汚泥濃度)が一定範囲内におさまるよう運転され
ている。符号15は散気管、17は汚泥引き抜き用送風
機である。
As shown in FIG. 1, the septic tank is, for example, an intermittent aeration type nitrogen removal type membrane separation / combination septic tank in which aeration and an aeration stop are performed in a single tank. Once stored in the impurity separation and storage tank (also serving as a flow rate adjustment tank) 1a as the primary treatment tank 1 to make the organic matter concentration of the sewage uniform, the secondary treatment tank is fixedly transferred by a transfer pump 10 in the sewage transfer tank. It is transferred to a membrane separation intermittent gas tank 2 a provided with a membrane separation device 6 as 2. In the intermittent membrane separation gas tank 2a, organic wastewater is biologically treated with activated sludge in the membrane separation device 6, and solid-liquid separation is performed in the immersion type membrane separation device 6. Further, the anaerobic state and the aerobic state are created by repeatedly stopping and operating the blower 7 and nitrogen is removed by controlling the dissolved oxygen amount (DO) of the sewage in the tank. Further, a sludge pulling pump (a lift pump) 4 is provided in the tank, and a certain amount of excess sludge is drawn into the impurity separating / storing tank 1a according to the setting of the control unit 5, and the MLSS
(Activated sludge concentration) is operated within a certain range. Reference numeral 15 denotes an air diffuser, and 17 denotes a blower for extracting sludge.

【0014】膜透過液の導出管8は浄化槽内の大気圧下
に開放された処理水槽9に接続されており、膜分離装置
6は水頭差吸引力hのサイホン作用でサイホン濾過を行
うように構成されている。膜透過液は放流ポンプ3で取
り出され、流量調整弁11の設定に応じ、一定流量で消
毒槽12を経て放流される。
The outlet pipe 8 for the membrane permeated liquid is connected to a treatment water tank 9 opened at atmospheric pressure in the purification tank, and the membrane separation device 6 performs siphon filtration by the siphon action of the head difference suction force h. It is configured. The membrane permeate is taken out by the discharge pump 3 and discharged through the disinfection tank 12 at a constant flow rate according to the setting of the flow control valve 11.

【0015】夾雑物分離貯留槽1aには水位センサ13
が設けられ、L1(最低水位)、H1(最高水位)を検
出可能である。通常、L1とH1の間を流量調整範囲と
して運転されるよう槽容量が設計されている。一方、膜
分離間欠ばつ気槽2aにはL2(最低水位)、H2(最
高水位)が検出可能な水位センサ14が設けられ、1サ
イクルの濾過量はL2、H2で規定される容量に対応す
る。これらの水位情報に基づき、制御部5は下記内容の
自動運転をおこなう。
A water level sensor 13 is provided in the impurity separation storage tank 1a.
Is provided, and L1 (lowest water level) and H1 (highest water level) can be detected. Usually, the tank capacity is designed so that the operation is performed with the flow rate adjustment range between L1 and H1. On the other hand, the membrane separation intermittent gas tank 2a is provided with a water level sensor 14 capable of detecting L2 (lowest water level) and H2 (highest water level), and the amount of filtration in one cycle corresponds to the capacity defined by L2 and H2. . Based on the water level information, the control unit 5 performs the following automatic operation.

【0016】即ち、移送ポンプ10はばつ気停止時間に
夾雑物分離貯留槽水位L1(最低水位)以上で動作し、
膜分離間欠ばつ気槽2aの水位がH2(最高水位)にな
るまで動作する。ばつ気時間終了時、夾雑物分離貯留槽
1aの水位がL1より低い場合、汚泥の活性を維持する
最小限のばつ気運転のみをおこなうモード(省エネモー
ド)に切り替わり、電気代の低減を図る。一方、夾雑物
分離貯留槽1aの水位H1(最高水位)以上になると、
高速モードに切り替わり、膜分離間欠ばつ気槽2aに汚
水を投入するとともに、膜処理を連続的に実施する。放
流ポンプ3は、ばっ気時間中にのみ稼働し、膜分離間欠
ばつ気槽2aの水位がH2(最高水位)からL2(最低
水位)まで動作し膜処理をおこなう。
That is, the transfer pump 10 operates at the level of the contaminant separation and storage tank L1 (minimum water level) during the abrupt stop time,
The operation is performed until the water level of the intermittent membrane separation air tank 2a becomes H2 (the highest water level). At the end of the aeration time, if the water level of the impurity separation and storage tank 1a is lower than L1, the mode is switched to a mode in which only the minimum aeration operation for maintaining the activity of the sludge (an energy saving mode) is performed, thereby reducing the electricity bill. On the other hand, when the water level becomes higher than the water level H1 (highest water level) of the impurity separation storage tank 1a,
The mode is switched to the high-speed mode, and the sewage is charged into the intermittently-absorbed membrane tank 2a, and the membrane treatment is continuously performed. The discharge pump 3 is operated only during the aeration time, and performs the membrane treatment by operating the water level of the intermittent membrane separation aeration tank 2a from H2 (highest water level) to L2 (lowest water level).

【0017】更に、通常モードは、図2に示すように、
例えば、膜分離間欠ばっ気槽2aの最高水位H2の検出
結果に基づいてばっ気用送風機7を30分運転するばっ
気運転時においては、移送ポンプ10が停止され、放流
ポンプ3が作動して膜分離装置6からの処理水を消毒槽
12へと移送するのであり、膜分離間欠ばっ気槽2aの
水位が最低位置L2に達すると、この検出結果に基づい
て、放流ポンプ3が停止され、膜分離間欠ばっ気槽2a
の水位が最低水位L2に維持され、ばっ気用送風機7が
暫く運転されて停止され、ばっ気停止運転に移行する。
ばっ気停止運転の初期に移送ポンプ10が運転されて、
夾雑物分離貯留槽1aから膜分離間欠ばっ気槽2aに最
高水位に至るまで移流される。このようなばっ気停止運
転が例えば、30分おこなわれ、以降は上述のばっ気運
転となり、これの繰り返しとなる。
Further, in the normal mode, as shown in FIG.
For example, in the aeration operation in which the aeration blower 7 is operated for 30 minutes based on the detection result of the maximum water level H2 in the intermittent aeration tank 2a, the transfer pump 10 is stopped and the discharge pump 3 is operated. The treated water from the membrane separation device 6 is transferred to the disinfection tank 12, and when the water level in the intermittent membrane separation aeration tank 2a reaches the lowest position L2, the discharge pump 3 is stopped based on the detection result, Membrane separation intermittent aeration tank 2a
Is maintained at the minimum water level L2, the aeration blower 7 is operated for a while and stopped, and the operation shifts to the aeration stop operation.
The transfer pump 10 is operated at the beginning of the aeration stop operation,
The water is transferred from the impurity separation storage tank 1a to the membrane separation intermittent aeration tank 2a up to the highest water level. Such an aeration stop operation is performed, for example, for 30 minutes, and thereafter, the above-described aeration operation is performed, and this is repeated.

【0018】以上のような構成の膜処理型浄化槽におい
て請求項1の発明は、膜処理装置6における膜処理水量
を積算した積算水量が一定量に達したことによって汚泥
引き抜きポンプ4を運転するようにしたものである。具
体的には、例えば放流水路16に水量計を設置し、水量
を積算して検出結果を制御部5に入力すればよい。しか
して、通常モードはもちろん高速モードにおいても膜処
理装置6における膜処理水量を積算することができるの
であり、膜処理水量が増すのに伴って増加する余剰汚泥
の引き抜きを適性におこなうことができるものである。
In the membrane treatment type septic tank constructed as described above, the invention of claim 1 operates the sludge extraction pump 4 when the integrated water amount obtained by integrating the membrane treatment water amount in the membrane treatment device 6 reaches a certain amount. It was made. Specifically, for example, a water meter may be installed in the discharge water channel 16, the amount of water may be integrated, and the detection result may be input to the control unit 5. Thus, the amount of membrane treatment water in the membrane treatment device 6 can be integrated not only in the normal mode but also in the high-speed mode, and the excess sludge that increases as the amount of membrane treatment water increases can be appropriately extracted. Things.

【0019】図3は請求項2の実施の形態を示すフロー
チャートであり、本実施の形態においては、膜分離装置
6により膜処理した積算水量を得るのに、放流ポンプ3
の運転時間を積算した積算時間によって換算するように
したものである。以下、詳述する。
FIG. 3 is a flow chart showing a second embodiment of the present invention. In the present embodiment, the discharge pump 3 is used to obtain the integrated water amount subjected to membrane treatment by the membrane separation device 6.
Is converted by the accumulated time obtained by accumulating the operation time. The details will be described below.

【0020】1日(24時間)にわたって通常モードの
運転をおこなうと、放流ポンプ3は約12時間運転され
るのである。本実施の形態においては、放流ポンプ3の
運転時間を積算するタイマーが12時間に達したこと
で、ろ過水量が1日分の処理量に達したとみなして汚泥
引き抜きポンプ4を作動させるのである[図3(a)の
イ参照]。この場合、ばっ気時間の途中で放流ポンプ3
の運転積算時間が所定時間(12時間)に達すると[図
3(b)のロ参照]、これをトリガーとしてタイマーを
リセットの上、次回のばっ気運転開始時に汚泥引き抜き
ポンプ4の運転を開始する[図3(b)のハ参照]。
When the normal mode operation is performed for one day (24 hours), the discharge pump 3 is operated for about 12 hours. In the present embodiment, when the timer for accumulating the operation time of the discharge pump 3 reaches 12 hours, the sludge extraction pump 4 is operated on the assumption that the amount of filtered water has reached the processing amount for one day. [Refer to FIG. 3 (a)]. In this case, the discharge pump 3
When the accumulated operation time reaches a predetermined time (12 hours) [see (b) in FIG. 3B], this is used as a trigger to reset the timer and start the operation of the sludge extraction pump 4 at the start of the next aeration operation. [See FIG. 3 (b)].

【0021】高速モードに移行した場合においても放流
ポンプ3の運転時間を積算するタイマーのカウントを続
行するのであり、高速モード中にタイムアップしたら
[図3(a)のニ参照]、次回の通常モード移行後の最
初のばっ気時間開始時に汚泥引き抜きポンプ4の運転を
開始する。つまり、高速モードでは、一次処理槽1から
被処理水を移送中のため、一次処理槽1への引き抜き汚
泥の返送は実施しない。このような方法によって、高速
モード移行時においても、処理水量に応じた汚泥引き抜
きが可能である。
Even when the mode shifts to the high-speed mode, the counting of the timer for integrating the operation time of the discharge pump 3 is continued. If the time is up during the high-speed mode [see FIG. At the start of the first aeration time after the mode shift, the operation of the sludge extraction pump 4 is started. That is, in the high-speed mode, since the water to be treated is being transferred from the primary treatment tank 1, the return of the drawn sludge to the primary treatment tank 1 is not performed. By such a method, even at the time of transition to the high-speed mode, sludge extraction according to the amount of treated water can be performed.

【0022】同様に1日の間に数時間、省エネモードに
入り、通常モード中に所定時間に達した場合[図3
(a)のホ参照]、省エネモード中は放流ポンプ3は動
かないので、運転時間積算タイマーは停止し、通常モー
ド時の放流ポンプ3の運転時間の積算により汚泥引き抜
きをおこなうことができる。
Similarly, when the energy saving mode is entered for several hours during one day and reaches a predetermined time during the normal mode [FIG.
(See (a) e)], since the discharge pump 3 does not operate during the energy saving mode, the operation time integration timer is stopped, and sludge can be extracted by integrating the operation time of the discharge pump 3 in the normal mode.

【0023】ところで、請求項3の発明においては、高
速モ−ドにおいて、二次処理槽2における水位が単位時
間当たりに1回以上上限設定水位H2に達したことを1
回とカウントし、そのカウント数が所定数に達したで汚
泥引き抜きポンプ4を運転するようにしたものである。
しかして、例えば過大流入により、単位時間当たりに何
度も上限設定水位H2を越えてもこれを1回としてカウ
ントするのであり、高速モードにおいても過剰な汚泥の
引き抜きを回避することができ、適性な活性汚泥濃度を
維持することができるものである。
According to the third aspect of the present invention, in the high-speed mode, it is determined that the water level in the secondary treatment tank 2 has reached the upper limit set water level H2 at least once per unit time.
The number of times is counted, and the sludge extraction pump 4 is operated when the counted number reaches a predetermined number.
Therefore, even if the water level exceeds the upper limit set water level H2 many times per unit time due to, for example, excessive inflow, the water level is counted as one time. Therefore, even in the high-speed mode, it is possible to avoid excessive sludge withdrawal. Activated sludge concentration can be maintained.

【0024】図4は請求項4の実施の形態を示すフロー
チャートである。恒常的に被処理水の流入水量が多い場
合、頻繁に高速モードに入るのであり、このため図3に
おいて述べた実施の形態においては汚泥引き抜きを過剰
におこなうことになり、その結果、二次処理槽2の活性
汚泥濃度が低くなり、活性汚泥による処理能力が悪化す
る可能性がある。そこで、請求項4の発明においては、
放流ポンプ3の積算運転時間が所定時間に達することが
単位時間(24時間)あたりに1回あれば1回の汚泥引
き抜きポンプ4を運転し、その後における単位時間(2
4時間)内の放流ポンプ3の運転時間を積算するのを停
止し、又、放流ポンプ3の積算運転時間が所定時間に達
することが単位時間(24時間)あたりに無ければ、次
の単位時間(24時間)においても運転時間を積算して
所定時間に達した時点で汚泥引き抜きポンプ4を運転す
るようにしたものである。以下、詳述する。
FIG. 4 is a flow chart showing the fourth embodiment. When the amount of inflowing water to be treated is large constantly, the high-speed mode is frequently entered. For this reason, in the embodiment described with reference to FIG. 3, sludge extraction is performed excessively. There is a possibility that the activated sludge concentration in the tank 2 becomes low and the treatment capacity by the activated sludge is deteriorated. Therefore, in the invention of claim 4,
If the integrated operation time of the discharge pump 3 reaches the predetermined time once per unit time (24 hours), the sludge extraction pump 4 is operated once, and the unit time (2
(4 hours), the integration of the operating time of the discharge pump 3 is stopped, and if the integrated operation time of the discharge pump 3 does not reach the predetermined time within a unit time (24 hours), the next unit time Also in (24 hours), the sludge extraction pump 4 is operated when the operation time is accumulated and reaches a predetermined time. The details will be described below.

【0025】24時間(単位時間)タイマーの作動を開
始した後、放流ポンプ3の運転時間を積算させるタイマ
ーの作動が開始されてこの運転時間積算タイマーが12
時間(所定時間)に達した時点で、運転時間積算タイマ
ーをリセットするとともに、汚泥引き抜きポンプ3を作
動させるトリガーとする。汚泥引き抜きポンプ4の運転
タイミングは、図3の実施の形態と同様、トリガーがか
かった後、最初のばっ気時間開始時(通常モード)とす
る。ところで、24時間タイマーは計時を継続するが、
運転時間積算タイマーは24時間タイマーがタイムアッ
プした時点でリセットし、その後、両タイマーを再スタ
ートする。
After the operation of the 24-hour (unit time) timer is started, the operation of the timer for integrating the operation time of the discharge pump 3 is started.
When the time (predetermined time) has been reached, the operation time integration timer is reset and a trigger for operating the sludge extraction pump 3 is set. The operation timing of the sludge extraction pump 4 is the same as in the embodiment of FIG. 3, at the start of the first aeration time after the trigger is activated (normal mode). By the way, the 24-hour timer keeps measuring time,
The running time integration timer is reset when the 24-hour timer expires, and then both timers are restarted.

【0026】一方、24時間以内に運転時間積算タイマ
ーが所定時間に達することがなくてタイムアップしなか
った場合は、24時間タイマーをリセットしたうえ、停
止させる。その後、運転時間積算タイマーがタイムアッ
プした時点を、汚泥引き抜きトリガーとし、同時に24
時間タイマーの作動を開始するものである。
On the other hand, if the running time integration timer has not reached the predetermined time within 24 hours and has not timed out, the 24-hour timer is reset and stopped. Thereafter, the time when the operation time integration timer has expired is used as a sludge extraction trigger, and at the same time,
It starts the operation of the time timer.

【0027】このような構成によれば、例えば多人数の
来客があった場合等に高速モードになって放流ポンプ3
の運転の積算時間が単位時間(24時間)当たりに所定
時間に達すると、汚泥引き抜きポンプ4を作動させて汚
泥の引き抜きをおこなうのであるが、単位時間の残りの
時間においては、放流ポンプ3が運転されていても運転
時間の積算をおこなうことがなく、単位時間に何度も汚
泥の引き抜きをおこなうことを回避することができ、過
剰な汚泥の引き抜きを回避することができ、適性な活性
汚泥濃度を維持することができる。
According to such a configuration, for example, when there are a large number of customers, the high-speed mode is set and the discharge pump 3
When the integrated time of the operation reaches a predetermined time per unit time (24 hours), the sludge withdrawal pump 4 is operated to perform sludge withdrawal. In the remaining time of the unit time, the discharge pump 3 Even during operation, the operation time is not integrated, and it is possible to avoid pulling out sludge many times in a unit time, and it is possible to avoid excessive sludge withdrawal. The concentration can be maintained.

【0028】[0028]

【発明の効果】請求項1においては、被処理水を投入す
る一次処理槽と、一次処理槽からの一次処理水を移流し
て浸漬された膜分離装置によって膜処理をおこなう二次
処理槽と、二次処理槽内の二次処理水を外部に放流する
放流ポンプと、二次処理槽内の余剰汚泥を一次処理槽に
返送する汚泥引き抜きポンプとを備えた膜処理型浄化槽
であって、膜処理装置における膜処理水量を積算した積
算水量が一定量に達したことによって汚泥引き抜きポン
プを運転する制御部を備えているから、処理モードに関
係なく膜処理装置における膜処理水量を積算することが
できるのであり、膜処理水量が増すのに伴って増加する
余剰汚泥の引き抜きを適性におこなうことができるとい
う利点がある。
According to the first aspect of the present invention, there is provided a primary treatment tank into which water to be treated is charged, and a secondary treatment tank in which the primary treatment water is transferred from the primary treatment tank and subjected to membrane treatment by a membrane separation device immersed therein. A membrane treatment type purification tank comprising a discharge pump for discharging secondary treatment water in the secondary treatment tank to the outside, and a sludge extraction pump for returning excess sludge in the secondary treatment tank to the primary treatment tank, Since the control unit that operates the sludge extraction pump is provided when the integrated water amount obtained by integrating the membrane treatment water amount in the membrane treatment device reaches a certain amount, it is necessary to integrate the membrane treatment water amount in the membrane treatment device regardless of the treatment mode. Therefore, there is an advantage that the excess sludge, which increases with an increase in the amount of membrane treatment water, can be appropriately extracted.

【0029】請求項2においては、膜処理した積算水量
を、放流ポンプの運転時間を積算した積算時間によって
換算するから、請求項1の効果に加えて、膜処理水量の
積算に比べて構成を簡素化できるという利点がある。
According to the second aspect, the integrated water amount subjected to the membrane treatment is converted by the integrated time obtained by integrating the operation time of the discharge pump. There is an advantage that it can be simplified.

【0030】請求項3においては、被処理水を投入する
一次処理槽と、一次処理槽からの一次処理水を移流して
浸漬された膜分離装置によって膜処理をおこなう二次処
理槽と、二次処理槽内の二次処理水を外部に放流する放
流ポンプと、二次処理槽内の余剰汚泥を一次処理槽に返
送する汚泥引き抜きポンプとを備えた膜処理型浄化槽で
あって、二次処理槽における水位が単位時間当たりにお
いて1回以上上限設定水位に達したことを1回とカウン
トし、そのカウント数が所定数に達したことで汚泥引き
抜きポンプを運転する制御部を備えているから、例えば
過大流入により、単位時間当たりに何度も上限設定水位
を越えてもこれを1回としてカウントするのであり、高
速モードにおいても過剰な汚泥の引き抜きを回避するこ
とができ、適性な活性汚泥濃度を維持することができる
という利点がある。
According to a third aspect of the present invention, there is provided a primary treatment tank into which water to be treated is charged, a secondary treatment tank in which the primary treatment water from the primary treatment tank is transferred and subjected to membrane treatment by a membrane separator immersed therein. A membrane treatment type purification tank comprising a discharge pump for discharging secondary treatment water in the secondary treatment tank to the outside, and a sludge extraction pump for returning excess sludge in the secondary treatment tank to the primary treatment tank. The control unit operates the sludge extraction pump when the water level in the treatment tank reaches the upper limit set water level at least once per unit time and is counted as one, and when the count reaches a predetermined number. For example, even if the upper limit water level is exceeded many times per unit time due to an excessive inflow, the water level is counted as one time. Therefore, even in the high-speed mode, it is possible to avoid excessive sludge withdrawal. There is an advantage that it is possible to maintain the sexual sludge concentration.

【0031】請求項4においては、被処理水を投入する
一次処理槽と、一次処理槽からの一次処理水を移流して
浸漬された膜分離装置によって膜処理をおこなう二次処
理槽と、二次処理槽内の二次処理水を外部に放流する放
流ポンプと、二次処理槽内の余剰汚泥を一次処理槽に返
送する汚泥引き抜きポンプとを備えた膜処理型浄化槽で
あって、放流ポンプの積算運転時間が所定時間に達する
ことが単位時間あたりに1回あれば1回の汚泥引き抜き
ポンプを運転し、その後における単位時間内の放流ポン
プの運転時間を積算するのを停止し、又、放流ポンプの
積算運転時間が所定時間に達することが単位時間あたり
に無ければ、次の単位時間においても運転時間を積算し
て所定時間に達した時点で汚泥引き抜きポンプを運転す
る制御部を備えているから、例えば多人数の来客があっ
た場合等に高速モードになって放流ポンプの運転の積算
時間が単位時間(例えば24時間)当たりに所定時間に
達すると、汚泥引き抜きポンプを作動させて汚泥の引き
抜きをおこなうのであるが、単位時間の残りの時間にお
いては、放流ポンプが運転されていても運転時間の積算
をおこなうことがなく、単位時間に何度も汚泥の引き抜
きをおこなうことを回避することができ、過剰な汚泥の
引き抜きを回避することができ、適性な活性汚泥濃度を
維持することができるという利点がある。
According to a fourth aspect of the present invention, there is provided a secondary treatment tank in which water to be treated is charged, a secondary treatment tank in which the primary treatment water from the primary treatment tank is transferred and subjected to membrane treatment by a membrane separator immersed therein. A membrane treatment type purification tank comprising a discharge pump for discharging secondary treatment water in the secondary treatment tank to the outside, and a sludge extraction pump for returning excess sludge in the secondary treatment tank to the primary treatment tank. If the integrated operation time of the predetermined time reaches the predetermined time once per unit time, the sludge extraction pump is operated once, and the accumulation of the operation time of the discharge pump within the unit time after that is stopped, and If the integrated operation time of the discharge pump does not reach the predetermined time per unit time, the control unit operates the sludge extraction pump at the time when the operation time is integrated and reaches the predetermined time even in the next unit time. Therefore, for example, when there is a large number of visitors, the high-speed mode is set, and when the integrated time of the operation of the discharge pump reaches a predetermined time per unit time (for example, 24 hours), the sludge extraction pump is operated to activate the sludge removal pump. In the remaining time of the unit time, even if the discharge pump is operated, the operation time is not integrated, and the sludge is not repeatedly extracted in the unit time. This has the advantage that excessive sludge extraction can be avoided and an appropriate activated sludge concentration can be maintained.

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

【図1】本発明の浄化槽の説明図である。FIG. 1 is an explanatory view of a septic tank according to the present invention.

【図2】同上の通常モードを示すフローチャートであ
る。
FIG. 2 is a flowchart showing a normal mode according to the first embodiment;

【図3】(a)(b)は同上の実施の形態1のフローチ
ャートである。
FIGS. 3A and 3B are flowcharts of the first embodiment.

【図4】同上の実施の形態2のフローチャートである。FIG. 4 is a flowchart of the second embodiment.

【符号の説明】[Explanation of symbols]

1 一次処理槽 2 二次処理槽 3 放流ポンプ 4 汚泥引き抜きポンプ 5 制御部 6 膜分離装置 DESCRIPTION OF SYMBOLS 1 Primary treatment tank 2 Secondary treatment tank 3 Discharge pump 4 Sludge extraction pump 5 Control part 6 Membrane separation device

フロントページの続き (72)発明者 真継 伸 大阪府門真市大字門真1048番地松下電工株 式会社内 (72)発明者 加納 広志 大阪府門真市大字門真1048番地松下電工株 式会社内 (72)発明者 山口 重行 大阪府門真市大字門真1048番地松下電工株 式会社内 (72)発明者 北村 仁史 大阪府門真市大字門真1048番地松下電工株 式会社内 Fターム(参考) 4D006 GA02 HA93 KA12 KB22 PA01 PB08 PC65 4D027 AA01 AA14 4D028 AA08 BC17 BD08 BD11 BD17 CA09 CA15 CB02 CB08 CD00 CD05 Continuing on the front page (72) Inventor Shin Shin, 1048, Kadoma, Kadoma, Osaka Prefecture Inside Matsushita Electric Works Co., Ltd. (72) Inventor Hiroshi Kano 1048, Oaza, Kadoma, Kadoma, Osaka Prefecture Matsushita Electric Works Co., Ltd. (72) Invention Person Shigeyuki Yamaguchi 1048 Kazuma Kadoma, Kadoma City, Osaka Prefecture Inside the Matsushita Electric Works, Ltd. PC65 4D027 AA01 AA14 4D028 AA08 BC17 BD08 BD11 BD17 CA09 CA15 CB02 CB08 CD00 CD05

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 被処理水を投入する一次処理槽と、一次
処理槽からの一次処理水を移流して浸漬された膜分離装
置によって膜処理をおこなう二次処理槽と、二次処理槽
内の二次処理水を外部に放流する放流ポンプと、二次処
理槽内の余剰汚泥を一次処理槽に返送する汚泥引き抜き
ポンプとを備えた膜処理型浄化槽であって、膜処理装置
における膜処理水量を積算した積算水量が一定量に達し
たことによって汚泥引き抜きポンプを運転する制御部を
備えて成ることを特徴とする膜処理型浄化槽。
1. A primary treatment tank into which water to be treated is charged, a secondary treatment tank in which a primary treatment water from the primary treatment tank is transferred and subjected to membrane treatment by a membrane separator immersed therein, and a secondary treatment tank And a sludge removal pump for returning excess sludge in the secondary treatment tank to the primary treatment tank. A membrane treatment type purification tank comprising a control unit for operating a sludge extraction pump when the integrated water amount obtained by integrating the water amount reaches a certain amount.
【請求項2】 膜処理した積算水量を、放流ポンプの運
転時間を積算した積算時間によって換算することを特徴
とする請求項1記載の膜処理型浄化槽。
2. The membrane-treated septic tank according to claim 1, wherein the integrated amount of water subjected to the membrane treatment is converted by the integrated time obtained by integrating the operation time of the discharge pump.
【請求項3】 被処理水を投入する一次処理槽と、一次
処理槽からの一次処理水を移流して浸漬された膜分離装
置によって膜処理をおこなう二次処理槽と、二次処理槽
内の二次処理水を外部に放流する放流ポンプと、二次処
理槽内の余剰汚泥を一次処理槽に返送する汚泥引き抜き
ポンプとを備えた膜処理型浄化槽であって、二次処理槽
における水位が単位時間当たりにおいて1回以上上限設
定水位に達したことを1回とカウントし、そのカウント
数が所定数に達したことで汚泥引き抜きポンプを運転す
る制御部を備えて成ることを特徴とする膜処理型浄化
槽。
3. A primary treatment tank into which water to be treated is charged, a secondary treatment tank in which a primary treatment water from the primary treatment tank is transferred and subjected to membrane treatment by a membrane separation device immersed therein, and a secondary treatment tank. And a sludge extraction pump for returning excess sludge in the secondary treatment tank to the primary treatment tank, wherein the water level in the secondary treatment tank is provided. Is characterized by comprising a control unit that counts at least once per unit time to reach the upper limit set water level as one time, and operates the sludge extraction pump when the counted number reaches a predetermined number. Membrane treatment type septic tank.
【請求項4】 被処理水を投入する一次処理槽と、一次
処理槽からの一次処理水を移流して浸漬された膜分離装
置によって膜処理をおこなう二次処理槽と、二次処理槽
内の二次処理水を外部に放流する放流ポンプと、二次処
理槽内の余剰汚泥を一次処理槽に返送する汚泥引き抜き
ポンプとを備えた膜処理型浄化槽であって、放流ポンプ
の積算運転時間が所定時間に達することが単位時間あた
りに1回あれば1回の汚泥引き抜きポンプを運転し、そ
の後における単位時間内の放流ポンプの運転時間を積算
するのを停止し、又、放流ポンプの積算運転時間が所定
時間に達することが単位時間あたりに無ければ、次の単
位時間においても運転時間を積算して所定時間に達した
時点で汚泥引き抜きポンプを運転する制御部を備えて成
ることを特徴とする膜処理型浄化槽。
4. A primary treatment tank into which water to be treated is charged, a secondary treatment tank for performing a membrane treatment by a membrane separation device in which primary treatment water is advected and immersed from the primary treatment tank, and a secondary treatment tank. A membrane treatment type purification tank provided with a discharge pump for discharging the secondary treatment water to the outside and a sludge extraction pump for returning excess sludge in the secondary treatment tank to the primary treatment tank, and the cumulative operation time of the discharge pump If the predetermined time is reached once per unit time, the sludge pulling pump is operated once, and the accumulation of the operating time of the discharge pump within the unit time thereafter is stopped. If the operation time does not reach the predetermined time per unit time, a control unit is provided that operates the sludge extraction pump when the operation time is integrated and reaches the predetermined time even in the next unit time. To be Membrane treatment type septic tank.
JP11084107A 1999-03-26 1999-03-26 Membrane treatment type septic tank Withdrawn JP2000271581A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11084107A JP2000271581A (en) 1999-03-26 1999-03-26 Membrane treatment type septic tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11084107A JP2000271581A (en) 1999-03-26 1999-03-26 Membrane treatment type septic tank

Publications (1)

Publication Number Publication Date
JP2000271581A true JP2000271581A (en) 2000-10-03

Family

ID=13821311

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11084107A Withdrawn JP2000271581A (en) 1999-03-26 1999-03-26 Membrane treatment type septic tank

Country Status (1)

Country Link
JP (1) JP2000271581A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6863817B2 (en) 2002-12-05 2005-03-08 Zenon Environmental Inc. Membrane bioreactor, process and aerator
WO2017098941A1 (en) * 2015-12-11 2017-06-15 三菱重工環境・化学エンジニアリング株式会社 Biological treatment device

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6863817B2 (en) 2002-12-05 2005-03-08 Zenon Environmental Inc. Membrane bioreactor, process and aerator
WO2017098941A1 (en) * 2015-12-11 2017-06-15 三菱重工環境・化学エンジニアリング株式会社 Biological treatment device
JP2017104833A (en) * 2015-12-11 2017-06-15 三菱重工環境・化学エンジニアリング株式会社 Biological treatment apparatus
CN107848850A (en) * 2015-12-11 2018-03-27 三菱重工环境·化学工程株式会社 Biological treatment device
TWI643662B (en) * 2015-12-11 2018-12-11 日商三菱重工環境 化學工程股份有限公司 Biological treatment apparatus

Similar Documents

Publication Publication Date Title
EP0794927B1 (en) Method and apparatus for sewage water treatment
KR20200042273A (en) Membrane combined Advanced wastewater treatment system which applies Trisectional aeration and Changed inflow course and it's operation methods
JP2000271581A (en) Membrane treatment type septic tank
JP4666902B2 (en) MLSS control method
KR20060120370A (en) Method for flushing filter of water purifier
JP5025672B2 (en) Membrane separator
JPH07148482A (en) Method and apparatus for controlling hydrogen sulfide in waste water chemical injection
JP3773360B2 (en) Septic tank with membrane separation
JP2000271580A (en) Septic tank
JPH10290994A (en) Septic tank
JP2008253901A (en) Solid-liquid separator and water treatment apparatus equipped with it
KR0149559B1 (en) Apparatus for the treatment of water of purifier
JPH1157765A (en) Septic tank
JP3370864B2 (en) Septic tank
JP2008238042A (en) Method for reducing amount of organic sludge
JPH07256294A (en) Living waste water treatment apparatus
JP2000000589A (en) Sewage treatment apparatus
CN217972855U (en) Groundwater treatment system
JP2000279978A (en) Septic tank
JP3739203B2 (en) Waste water treatment apparatus and operation method thereof
FI121506B (en) Biological purification procedure
JP2003285093A (en) Biological denitrification method and apparatus therefor
JPH0839088A (en) Purifying tank and operation thereof
JP2003200025A (en) Liquid membrane-separating apparatus
JP2001212588A (en) Aeration method of aerobic treatment tank

Legal Events

Date Code Title Description
A300 Withdrawal of application because of no request for examination

Free format text: JAPANESE INTERMEDIATE CODE: A300

Effective date: 20060606