JP2001029994A - Membrane separation activated sludge process facility with flow control function - Google Patents

Membrane separation activated sludge process facility with flow control function

Info

Publication number
JP2001029994A
JP2001029994A JP11203988A JP20398899A JP2001029994A JP 2001029994 A JP2001029994 A JP 2001029994A JP 11203988 A JP11203988 A JP 11203988A JP 20398899 A JP20398899 A JP 20398899A JP 2001029994 A JP2001029994 A JP 2001029994A
Authority
JP
Japan
Prior art keywords
tank
membrane separation
capacity
denitrification
immersion type
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
JP11203988A
Other languages
Japanese (ja)
Inventor
Kenichi Kashimura
健一 樫村
Buntaro Furuhata
文太郎 古畑
Akira Ichihara
昭 市原
Miki Sakuno
美樹 作野
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.)
JAPANESE ASSOCIATION OF RURAL SEWERAGE
Ebara Corp
Kubota Corp
Original Assignee
JAPANESE ASSOCIATION OF RURAL SEWERAGE
Ebara Corp
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 JAPANESE ASSOCIATION OF RURAL SEWERAGE, Ebara Corp, Kubota Corp filed Critical JAPANESE ASSOCIATION OF RURAL SEWERAGE
Priority to JP11203988A priority Critical patent/JP2001029994A/en
Publication of JP2001029994A publication Critical patent/JP2001029994A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To dispense with flow control tank for coping with the fluctuation of the amount of sewage influent, by making the tank capacity of a denitrification tank consist of a reference capacity to keep a retention time in the tank, required for a biological reaction by activated sludge in the tank, and a buffer capacity to absorb the inflow fluctuation. SOLUTION: Separated water from an aeration grit tank 2, which receives raw water 1 flowing into a system, is made to overflow to a raw water pump tank 3, the sedimented grit is discharged to a sand elimination tank 4, and the separated water is returned to the aeration grit tank 2. A denitrification tank 6, to which sewage flows from the raw water pump tank 3 through a screen tank 5, has a tank capacity consisting of a reference capacity to keep a retention time in the tank, required for a biological reaction by activated sludge in the tank, and a buffer capacity to absorb the inflow fluctuation. When the amount of the sewage flowing into a system increases, the increment is absorbed by the buffer capacity of the denitrification tank 6, and a plurality of suction pumps in a suction pump device are operated at the same time and the flow rate is increased, thereby increasing the suction amount.

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、膜分離活性汚泥方
式を採用する水処理施設の生物反応槽に係り、施設規模
の縮小化および維持管理性が向上する流量調整機能を有
する膜分離活性汚泥処理設備に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a biological reaction tank of a water treatment facility employing a membrane separation activated sludge system, and has a flow control function for reducing the facility scale and improving the maintenance and management. Regarding processing equipment.

【0002】[0002]

【従来の技術】従来、反応槽内の活性汚泥を浸漬膜によ
って分離する膜分離活性汚泥方式の水処理施設において
は、系内に流入する原水を曝気沈砂槽、原水ポンプ槽、
流量調整槽、脱窒槽、硝化槽の各槽へ順次に導いて処理
し、消毒槽、放流ポンプ槽を経て放流している。
2. Description of the Related Art Conventionally, in a water treatment facility of a membrane separation activated sludge system in which activated sludge in a reaction tank is separated by a submerged membrane, raw water flowing into the system is subjected to an aeration sand settling tank, a raw water pump tank,
The wastewater is guided to the flow control tank, the denitrification tank, and the nitrification tank sequentially for treatment, and discharged through the disinfection tank and the discharge pump tank.

【0003】曝気沈砂槽、原水ポンプ槽は、前処理とし
て原水中のし渣および砂等を除去し、原水ポンプ槽から
流量調整槽に汚水を供給している。流量調整槽は流入す
る汚水を貯留して後工程の脱窒槽への供給水量を調整す
るもので、その槽容量は槽内滞留時間で例えば6〜7時
間である。脱窒槽、硝化槽は汚水を活性汚泥による生物
反応によって硝化・脱窒処理するものであり、脱窒槽の
槽内液を硝化槽へ導き、硝化槽の槽内液を脱窒槽へ返送
して槽内液を処理水量の数倍(5倍)の水量で循環し、
硝化槽内に浸漬した浸漬型膜分離装置により活性汚泥を
分離して処理水を消毒槽へ供給している。脱窒槽、硝化
槽の槽容量は槽内滞留時間で例えば6時間である。
The aeration sedimentation tank and the raw water pump tank remove sewage and sand from the raw water as pretreatment, and supply sewage from the raw water pump tank to the flow rate adjusting tank. The flow rate adjusting tank stores inflowing sewage and adjusts the amount of water supplied to the denitrification tank in a later process. The tank capacity is a residence time in the tank, for example, 6 to 7 hours. The denitrification tank and nitrification tank are for nitrifying and denitrifying wastewater by biological reaction with activated sludge. Circulates the internal solution at a volume of several times (5 times) the amount of treated water,
Activated sludge is separated by an immersion type membrane separation device immersed in a nitrification tank, and treated water is supplied to a disinfection tank. The tank capacity of the denitrification tank and the nitrification tank is a residence time in the tank, for example, 6 hours.

【0004】[0004]

【発明が解決しようとする課題】しかし、小規模汚水処
理施設の場合、流入汚水量の日間変動が大きく、処理負
荷の平準化のためには流量調整槽が不可欠である。しか
し、この流量調整槽を設置するスペースだけ施設が大き
くなり、小規模汚水処理施設においてその存在は大きな
ものである。
However, in the case of a small-scale sewage treatment plant, the amount of inflow sewage varies greatly from day to day, and a flow control tank is indispensable for leveling the treatment load. However, the facility becomes large only in the space where the flow control tank is installed, and its existence is large in a small-scale sewage treatment facility.

【0005】浸漬型膜分離装置における膜の交換や槽底
部に配置した散気装置の点検時には、硝化槽の運転を停
止する必要がある。本発明は上記した課題を解決するも
のであり、流入汚水量の変動に対処するに際して流量調
整槽が不要で、運転を停止することなく、硝化槽の浸漬
型膜分離装置や散気装置のメンテナンスを行なうことが
できる流量調整機能を有する膜分離活性汚泥処理設備を
提供することを目的とする。
It is necessary to stop the operation of the nitrification tank when replacing the membrane in the immersion type membrane separation apparatus or when checking the air diffuser arranged at the bottom of the tank. The present invention solves the above-described problems, and does not require a flow rate adjustment tank when dealing with fluctuations in the amount of inflowing sewage, without stopping the operation, and maintaining the immersion type membrane separation device and the aeration device of the nitrification tank. It is an object of the present invention to provide a membrane separation activated sludge treatment facility having a flow rate adjusting function capable of performing the following.

【0006】[0006]

【課題解決するための手段】上記課題を解決するため
に、請求項1に係る本発明の流量調整機能を有する膜分
離活性汚泥処理設備は、前処理した汚水が流入する脱窒
槽と、脱窒槽の槽内液が流入する硝化槽と、硝化槽に浸
漬した浸漬型膜分離装置と、浸漬型膜分離装置の下方に
配置する散気装置と、硝化槽からオーバーフローする槽
内液を脱窒槽へ返送する返送流路とを備え、脱窒槽は、
槽容量が槽内の活性汚泥による生物反応に必要な槽内滞
留時間を維持できる基準容量と汚水の流入変動を吸収す
る緩衝容量とからなり、硝化槽へ汚水を送る循環液ポン
プ装置を有し、硝化槽の浸漬型膜分離装置は、槽内液を
ろ過するろ過膜手段と、ろ過膜手段を通して吸引する処
理水の吸引量を調整可能な吸引ポンプ装置とを有する構
成としたものである。
According to a first aspect of the present invention, there is provided a membrane separation activated sludge treatment facility having a flow rate adjusting function, comprising: a denitrification tank into which pretreated wastewater flows; A nitrification tank into which the liquid in the tank flows, an immersion type membrane separator immersed in the nitrification tank, an air diffuser disposed below the immersion type membrane separator, and a denitrification tank for the liquid in the tank overflowing from the nitrification tank. And a return flow path for returning the denitrification tank,
The tank capacity consists of a reference capacity that can maintain the residence time in the tank required for biological reaction by activated sludge in the tank and a buffer capacity that absorbs fluctuations in the inflow of sewage, and has a circulating liquid pump device that sends sewage to the nitrification tank. The immersion type membrane separation device of the nitrification tank has a configuration including a filtration membrane means for filtering the liquid in the tank, and a suction pump apparatus capable of adjusting a suction amount of treated water sucked through the filtration membrane means.

【0007】上記した構成により、系内に流入する汚水
は、脱窒槽から循環液ポンプ装置を通って硝化槽へ流入
し、硝化槽から返送流路を通って脱窒槽へ戻り、系内を
循環する。汚水は各槽で所定の槽内滞留時間を経る間に
槽内の活性汚泥の生物反応によって硝化・脱窒される。
一方で浸漬型膜分離装置が吸引ポンプ装置の吸引圧を受
けて硝化槽内の槽内液をろ過し、吸引ポンプ装置が処理
水を系外へ排出する。
[0007] With the above structure, the wastewater flowing into the system flows from the denitrification tank to the nitrification tank through the circulating fluid pump device, returns from the nitrification tank to the denitrification tank through the return flow path, and circulates in the system. I do. The sewage is nitrified and denitrified by the biological reaction of the activated sludge in the tank during a predetermined residence time in each tank.
On the other hand, the immersion type membrane separation device receives the suction pressure of the suction pump device to filter the liquid in the nitrification tank, and the suction pump device discharges the treated water out of the system.

【0008】系内に流入する汚水の流量が増加する場合
には、脱窒槽の緩衝容量によって増加分を吸収するとと
もに、吸引ポンプ装置の吸引量を増加させる。このこと
により、従来の流量調整槽を必要とせずに、汚水の流量
変動を系全体の作用によって吸収することができ、脱窒
槽に設ける緩衝容量は従来の流量調整槽容量より少なく
なり、設備全体の設置スペースの縮小化を図ることがで
きる。
When the flow rate of sewage flowing into the system increases, the increased amount is absorbed by the buffer capacity of the denitrification tank, and the suction amount of the suction pump device is increased. This makes it possible to absorb flow fluctuations of sewage by the action of the entire system without the need for a conventional flow control tank, and the buffer capacity provided in the denitrification tank is smaller than that of the conventional flow control tank. Can be reduced in installation space.

【0009】請求項2に係る本発明の流量調整機能を有
する膜分離活性汚泥処理設備は、硝化槽を複数の独立し
た槽体に形成し、各槽体に浸漬型膜分離装置を浸漬し、
各槽体の浸漬型膜分離装置の処理水を選択的に吸引可能
で、かつ吸引量を調整可能な吸引ポンプ装置を設けた構
成としたものである。上記した構成より、メンテナンス
のために浸漬型膜分離装置の運転を停止する場合には、
当該浸漬型膜分離装置を配置した槽体への送液を停止
し、他の槽体への送液量を増加し、吸引ポンプ装置にお
いて当該浸漬型膜分離装置の処理水の吸引を停止すると
ともに、他の槽体の浸漬型膜分離装置に対する吸引量を
増加させる。このことにより、硝化槽の運転を停止する
ことなく、メンテナンスを行なうことができる。
According to a second aspect of the present invention, there is provided a membrane separation activated sludge treatment facility having a flow rate adjusting function, wherein a nitrification tank is formed in a plurality of independent tanks, and an immersion type membrane separation device is immersed in each tank.
A suction pump device capable of selectively sucking the treated water of the immersion type membrane separation device of each tank body and adjusting the suction amount is provided. From the above configuration, when stopping the operation of the immersion type membrane separation device for maintenance,
The liquid supply to the tank in which the immersion type membrane separation device is arranged is stopped, the amount of liquid supply to the other tanks is increased, and the suction of the immersion type membrane separation device by the suction pump device is stopped. At the same time, the suction amount of the other tank body to the immersion type membrane separation device is increased. Thus, maintenance can be performed without stopping the operation of the nitrification tank.

【0010】[0010]

【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。系内に流入する下水等の原水1を
受け入れる曝気沈砂槽2は、前処理として原水のし渣お
よび砂等を除去するものであり、分離水が原水ポンプ槽
3へ溢流し、沈砂を排砂槽4へ排出し、その分離水が曝
気沈砂槽2へ還流する。
Embodiments of the present invention will be described below with reference to the drawings. The aeration and sedimentation tank 2 for receiving the raw water 1 such as sewage flowing into the system is for removing the residue and sand of the raw water as pretreatment, and the separated water overflows to the raw water pump tank 3 to remove the sediment. The water is discharged to the tank 4 and the separated water is returned to the aeration sand settling tank 2.

【0011】原水ポンプ槽3から2mmスクリーン槽5
をとおして汚水が流入する脱窒槽6は、汚水を活性汚泥
による生物反応によって脱窒処理するものであり、脱窒
槽6の槽内液が循環液計量槽7および一対の1mmスク
リーン8を通して一対の硝化槽9へそれぞれ均量が流入
する。脱窒槽6の余剰汚泥は汚泥濃縮貯留槽10へ排出
し、汚泥濃縮貯留槽10の脱離水が原水ポンプ槽3へ還
流する。
From the raw water pump tank 3 to the 2 mm screen tank 5
The denitrification tank 6 into which the sewage flows through is subjected to a denitrification treatment of the sewage by a biological reaction by activated sludge, and the liquid in the denitrification tank 6 is passed through a circulating liquid measuring tank 7 and a pair of 1 mm screens 8 to form a pair. The equal amount flows into the nitrification tank 9 respectively. Excess sludge in the denitrification tank 6 is discharged to the sludge concentration storage tank 10, and desorbed water from the sludge concentration storage tank 10 is returned to the raw water pump tank 3.

【0012】硝化槽9は、汚水を活性汚泥による生物反
応によって硝化し、オーバーフローする槽内液を返送流
路11を通して脱窒槽6へ返送するもので、脱窒槽6と
硝化槽9の間には処理水量の数倍(5倍)の水量で汚泥
水が循環し、処理水が消毒槽12および放流ポンプ13
を通って系外へ流れ出る。図2に示すように、脱窒槽6
は、その槽容量が槽内の活性汚泥による生物反応に必要
な槽内滞留時間を維持できる基準容量(例えば6時間)と
汚水の流入変動を吸収する緩衝容量(例えば4時間)とか
らなり、槽内には硝化槽9へ汚水を送る循環液ポンプ装
置14と攪拌装置15と余剰汚泥を取り出す汚泥引抜ポ
ンプ16を有している。循環液ポンプ装置14は、2台
の循環ポンプ14aと各ポンプに対応して配置するバル
ブ14bからなり、各ポンプ14aの運転を停止、起動
することにより、循環液計量槽7および一対の1mmス
クリーン8を通して硝化槽9へ送る送液量を調整する。
The nitrification tank 9 is for nitrifying sewage by biological reaction with activated sludge and returning the overflowing tank liquid to the denitrification tank 6 through the return flow path 11. The sludge water circulates at an amount of several times (five times) the amount of the treated water, and the treated water is supplied to the disinfecting tank 12 and the discharge pump 13.
Flows out of the system. As shown in FIG.
The tank capacity is composed of a reference capacity (for example, 6 hours) that can maintain the residence time in the tank required for biological reaction due to activated sludge in the tank (for example, 6 hours) and a buffer capacity (for example, 4 hours) that absorbs fluctuations in wastewater inflow, In the tank, there are provided a circulating liquid pump device 14 for sending sewage to the nitrification tank 9, a stirring device 15, and a sludge extraction pump 16 for taking out excess sludge. The circulating fluid pump device 14 includes two circulating pumps 14a and valves 14b arranged corresponding to the respective pumps. By stopping and starting the operation of each pump 14a, the circulating fluid measuring tank 7 and a pair of 1 mm screens are provided. The amount of liquid sent to the nitrification tank 9 through 8 is adjusted.

【0013】各硝化槽9は、個々に独立した槽体に浸漬
型膜分離装置17を浸漬しており、浸漬型膜分離装置1
7の下方に散気装置18を配置している。浸漬型膜分離
装置17は、例えば複数のろ過膜カートリッジを所定間
隔で平行に配置したものであり、散気装置18から噴出
する曝気空気が気液混相流で膜面に沿ってクロスフロー
で流れて膜面を洗浄する。
In each of the nitrification tanks 9, the immersion type membrane separation device 17 is immersed in an independent tank body.
An air diffuser 18 is arranged below 7. The immersion type membrane separation device 17 is, for example, a device in which a plurality of filtration membrane cartridges are arranged in parallel at a predetermined interval, and the aerated air ejected from the diffusion device 18 flows in a cross-flow along the membrane surface in a gas-liquid multiphase flow. To clean the membrane surface.

【0014】双方の浸漬型膜分離装置17には、各膜カ
ートリッジに吸引負圧を与えて、ろ過膜を透過した処理
水を取り出すための吸引ポンプ装置19を接続してい
る。吸引ポンプ装置19は3台の吸引ポンプ19aと、
各ポンプの前後に配置するバルブ19bおよび逆止弁1
9cを有し、各ポンプ19aの運転の停止、起動もしく
はその吐出流量を制御することにより、任意のポンプで
選択的に双方の浸漬型膜分離装置17を吸引可能であ
り、その処理水の吸引量を調整可能である。
A suction pump device 19 for applying suction negative pressure to each of the membrane cartridges and extracting the treated water that has passed through the filtration membrane is connected to both immersion type membrane separation devices 17. The suction pump device 19 includes three suction pumps 19a,
Valve 19b and check valve 1 arranged before and after each pump
9c, by stopping and starting the operation of each pump 19a or controlling the discharge flow rate thereof, it is possible to selectively suction both immersion type membrane separation devices 17 with an arbitrary pump, and to suction the treated water. The amount is adjustable.

【0015】各吸引ポンプ19aは系内に流入する日平
均汚水量Qに相当する処理水を吸引可能で、1Q〜3Q
の範囲で処理水量を調整できる。また、各浸漬型膜分離
装置17は、最大で日平均汚水量Qの3倍の処理水を取
り出すことが可能なろ過膜面積および膜カートリッジ数
の処理能力を有している。以下、上記した構成における
作用を説明する。通常において系内に流入する原水1
は、曝気沈砂槽2、原水ポンプ槽3、2mmスクリーン
槽5を通って脱窒槽6に流入し、循環液ポンプ装置14
の1台の循環液ポンプ14aを運転し、定量の槽内液を
循環液計量槽7および一対の1mmスクリーン8を通し
て均量に分割して各硝化槽9へそれぞれ流入し、各硝化
槽9から返送流路11を通って脱窒槽6へ戻り、系内を
循環する。
Each of the suction pumps 19a is capable of sucking treated water corresponding to the daily average amount of wastewater Q flowing into the system.
The amount of treated water can be adjusted within the range. In addition, each immersion type membrane separation device 17 has a filtration membrane area and a treatment capacity of the number of membrane cartridges capable of extracting treated water up to three times the daily average sewage amount Q. Hereinafter, the operation of the above configuration will be described. Raw water 1 that normally flows into the system
Flows into the denitrification tank 6 through the aeration sedimentation tank 2, the raw water pump tank 3, and the 2 mm screen tank 5, and the circulating liquid pump device 14
The circulating liquid pump 14a is operated to divide the fixed amount of the liquid in the tank through the circulating liquid measuring tank 7 and the pair of 1 mm screens 8 into equal amounts and flow into the respective nitrification tanks 9, respectively. It returns to the denitrification tank 6 through the return flow path 11 and circulates through the system.

【0016】汚水は脱窒槽6、硝化槽9で所定の槽内滞
留時間を経る間に槽内の活性汚泥の生物反応によって硝
化・脱窒される。一方で浸漬型膜分離装置17は吸引ポ
ンプ装置19の1台の吸引ポンプ19aを駆動すること
により、あるいは複数の吸引ポンプ19aを同時に運転
するとともに、その流量を調整することにより、吸引圧
を受けて硝化槽9の槽内液をろ過し、吸引ポンプ装置1
9が処理水を系外へ排出する。
The wastewater is denitrified and denitrified by a biological reaction of the activated sludge in the denitrification tank 6 and the nitrification tank 9 during a predetermined residence time in the tank. On the other hand, the immersion type membrane separation device 17 receives a suction pressure by driving one suction pump 19a of the suction pump device 19 or simultaneously operating a plurality of suction pumps 19a and adjusting the flow rate thereof. The liquid in the nitrification tank 9 is filtered by the suction pump device 1
9 discharges the treated water out of the system.

【0017】系内に流入する汚水の流量が増加するとき
は、脱窒槽6の緩衝容量によって増加分を吸収させ、吸
引ポンプ装置19の複数の吸引ポンプ19aを同時に運
転するとともに、その流量を増加させることにより、吸
引量を増加させる。このことにより、従来において槽内
滞留時間で6〜7時間の槽容量である流量調整槽が不要
となり、汚水の流量変動を系全体の作用によって吸収す
ることができる。また、脱窒槽6に設ける緩衝容量は槽
内滞留時間において従来の流量調整槽容量より少ない4
時間であり、設備全体の設置スペースの縮小化を図るこ
とができる。本実施の形態における脱窒槽6の槽容量は
槽内滞留時間で6時間+4時間であり、従来の流量調整
槽と脱窒槽の槽容量は6時間+6時間であり、その比は
10時間/12時間で約0.8倍となる。
When the flow rate of the sewage flowing into the system increases, the increased amount is absorbed by the buffer capacity of the denitrification tank 6, and the plurality of suction pumps 19a of the suction pump device 19 are simultaneously operated and the flow rate is increased. By doing so, the suction amount is increased. This eliminates the need for a flow rate adjusting tank having a tank capacity of 6 to 7 hours in the tank in the related art, and can absorb flow rate fluctuations of sewage by the action of the entire system. Also, the buffer capacity provided in the denitrification tank 6 is smaller than the conventional flow control tank capacity during the residence time in the tank.
It is time, and the installation space of the entire equipment can be reduced. The tank capacity of the denitrification tank 6 in the present embodiment is 6 hours + 4 hours as the residence time in the tank, and the tank capacity of the conventional flow control tank and the denitrification tank is 6 hours + 6 hours, and the ratio is 10 hours / 12. It becomes about 0.8 times in time.

【0018】メンテナンスのために一方の浸漬型膜分離
装置17の運転を停止する場合には、当該浸漬型膜分離
装置17を配置した硝化槽9の槽体への送液を停止し、
他の槽体への送液量を増加する。また、吸引ポンプ装置
19において当該浸漬型膜分離装置17の処理水の吸引
を停止するとともに、他の槽体の浸漬型膜分離装置17
に対する吸引量を増加させる。このとき、浸漬型膜分離
装置17は最大1.5日(36時間)にわたって日平均汚
水量Qの2倍の処理能を発揮し、あるいは最大24時間
にわたって日平均汚水量Qの3倍の処理能を発揮し、硝
化槽9の運転を停止することなく、ろ過膜カートリッジ
の取り替え等のメンテナンスを行なうことができる。
When the operation of one immersion type membrane separation device 17 is stopped for maintenance, the liquid supply to the nitrification tank 9 in which the immersion type membrane separation device 17 is arranged is stopped,
Increase the amount of liquid sent to other tanks. Further, the suction pump device 19 stops the suction of the treatment water of the immersion type membrane separation device 17 and the immersion type membrane separation device 17 of another tank body.
Increase the amount of suction for. At this time, the immersion type membrane separation device 17 exhibits a treatment capacity twice as large as the daily average sewage volume Q for a maximum of 1.5 days (36 hours), or a treatment capacity three times the daily average sewage volume Q for a maximum of 24 hours. Therefore, maintenance such as replacement of the filtration membrane cartridge can be performed without stopping the operation of the nitrification tank 9.

【0019】[0019]

【発明の効果】以上のように、本発明によれば、流入汚
水量が増加する場合に、脱窒槽の緩衝容量によって増加
分を吸収し、吸引ポンプ装置の吸引量を増加させること
により、流量調整槽を要せずに、汚水の流量変動を系全
体の作用によって吸収し、設備全体の設置スペースの縮
小化を図ることができる。メンテナンス時には、一方の
浸漬型膜分離装置への送液を停止し、他の槽体への送液
量を増加し、吸引ポンプ装置において当該浸漬型膜分離
装置の処理水の吸引を停止するとともに、他の槽体の浸
漬型膜分離装置に対する吸引量を増加させることによ
り、硝化槽の運転を停止することなく、メンテナンスを
行なうことができる。
As described above, according to the present invention, when the amount of inflowing sewage increases, the increased amount is absorbed by the buffer capacity of the denitrification tank, and the suction amount of the suction pump device is increased, whereby the flow rate is increased. Without the need for an adjusting tank, fluctuations in the flow rate of sewage can be absorbed by the action of the entire system, and the installation space of the entire facility can be reduced. At the time of maintenance, the supply of liquid to one immersion type membrane separation device is stopped, the amount of liquid supply to the other tank is increased, and the suction of the immersion type membrane separation device by the suction pump device is stopped. The maintenance can be performed without stopping the operation of the nitrification tank by increasing the suction amount of the other tank body to the immersion type membrane separation device.

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

【図1】本発明の実施の形態を示す流量調整機能を有す
る膜分離活性汚泥処理設備のフローシートである。
FIG. 1 is a flow sheet of a membrane separation activated sludge treatment facility having a flow rate adjusting function according to an embodiment of the present invention.

【図2】同膜分離活性汚泥処理設備の脱窒槽と硝化槽を
示す模式図である。
FIG. 2 is a schematic view showing a denitrification tank and a nitrification tank of the membrane separation activated sludge treatment facility.

【符号の説明】[Explanation of symbols]

1 原水 2 曝気沈砂槽 6 脱窒槽 9 硝化槽 11 返送流路 14 循環液ポンプ装置 14a 循環液ポンプ 17 浸漬型膜分離装置 18 散気装置 19 吸引ポンプ装置 19a 吸引ポンプ DESCRIPTION OF SYMBOLS 1 Raw water 2 Aeration sand tank 6 Denitrification tank 9 Nitrification tank 11 Return flow path 14 Circulating fluid pump device 14a Circulating fluid pump 17 Immersion type membrane separation device 18 Air diffuser 19 Suction pump device 19a Suction pump

フロントページの続き (72)発明者 樫村 健一 東京都中央区日本橋室町3丁目1番3号 株式会社クボタ東京本社内 (72)発明者 古畑 文太郎 東京都中央区日本橋室町3丁目1番3号 株式会社クボタ東京本社内 (72)発明者 市原 昭 東京都港区港南1丁目6番27号 株式会社 荏原製作所品川事務所内 (72)発明者 作野 美樹 東京都港区港南1丁目6番27号 株式会社 荏原製作所品川事務所内 Fターム(参考) 4D006 GA02 KB22 KB23 KE01Q KE03Q PA02 PB08 PC62 4D040 BB52 BB91 Continued on the front page (72) Inventor Kenichi Kashimura 3-3-1 Nihombashi Muromachi, Chuo-ku, Tokyo Kubota Tokyo Head Office (72) Inventor Buntaro Furuhata 3-1-1 Nihonbashi Muromachi, Chuo-ku, Tokyo Co., Ltd. Kubota Tokyo Head Office (72) Inventor Akira Ichihara 1-6-27 Konan, Minato-ku, Tokyo Inside Ebara Corporation Shinagawa Office (72) Inventor Miki Sakuno 1-6-27 Konan, Minato-ku, Tokyo Ebara Corporation F term in the Shinagawa office of the factory (reference) 4D006 GA02 KB22 KB23 KE01Q KE03Q PA02 PB08 PC62 4D040 BB52 BB91

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 前処理した汚水が流入する脱窒槽と、脱
窒槽の槽内液が流入する硝化槽と、硝化槽に浸漬した浸
漬型膜分離装置と、浸漬型膜分離装置の下方に配置する
散気装置と、硝化槽からオーバーフローする槽内液を脱
窒槽へ返送する返送流路とを備え、脱窒槽は、槽容量が
槽内の活性汚泥による生物反応に必要な槽内滞留時間を
維持できる基準容量と汚水の流入変動を吸収する緩衝容
量とからなり、硝化槽へ汚水を送る循環液ポンプ装置を
有し、硝化槽の浸漬型膜分離装置は、槽内液をろ過する
ろ過膜手段と、ろ過膜手段を通して吸引する処理水の吸
引量を調整可能な吸引ポンプ装置とを有することを特徴
とする流量調整機能を有する膜分離活性汚泥処理設備。
1. A denitrification tank into which pretreated wastewater flows, a nitrification tank into which a liquid in the denitrification tank flows, an immersion type membrane separation apparatus immersed in the nitrification tank, and a lower part of the immersion type membrane separation apparatus A degassing device, and a return flow path for returning the liquid in the tank overflowing from the nitrification tank to the denitrification tank.The denitrification tank has a tank capacity that reduces the residence time in the tank required for a biological reaction due to activated sludge in the tank. It has a circulating fluid pump device that sends sewage to the nitrification tank, consisting of a reference capacity that can be maintained and a buffer capacity that absorbs fluctuations in sewage inflow.The immersion type membrane separation device in the nitrification tank is a filtration membrane that filters the liquid in the tank. And a suction pump device capable of adjusting a suction amount of the treated water sucked through the filtration membrane means.
【請求項2】 硝化槽を複数の独立した槽体に形成し、
各槽体に浸漬型膜分離装置を浸漬し、各槽体の浸漬型膜
分離装置の処理水を選択的に吸引可能で、かつ吸引量を
調整可能な吸引ポンプ装置を設けたことを特徴とする請
求項1に記載の流量調整機能を有する膜分離活性汚泥処
理設備。
2. The nitrification tank is formed in a plurality of independent tank bodies,
The immersion type membrane separation device is immersed in each tank body, and a suction pump device capable of selectively suctioning the treatment water of the immersion type membrane separation device of each tank body and adjusting the suction amount is provided. A membrane separation activated sludge treatment facility having a flow rate adjusting function according to claim 1.
JP11203988A 1999-07-19 1999-07-19 Membrane separation activated sludge process facility with flow control function Pending JP2001029994A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11203988A JP2001029994A (en) 1999-07-19 1999-07-19 Membrane separation activated sludge process facility with flow control function

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11203988A JP2001029994A (en) 1999-07-19 1999-07-19 Membrane separation activated sludge process facility with flow control function

Publications (1)

Publication Number Publication Date
JP2001029994A true JP2001029994A (en) 2001-02-06

Family

ID=16482932

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11203988A Pending JP2001029994A (en) 1999-07-19 1999-07-19 Membrane separation activated sludge process facility with flow control function

Country Status (1)

Country Link
JP (1) JP2001029994A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005500156A (en) * 2001-08-24 2005-01-06 エンビロゲン,インコーポレイティド System and method for collecting permeate through a filter and cleaning the filter in that position
JPWO2005053410A1 (en) * 2003-12-04 2007-06-28 不二製油株式会社 Bread improvers and breads containing the same
JP2012000585A (en) * 2010-06-18 2012-01-05 Kubota Corp Wastewater treatment facility, wastewater treatment method and method of reconstructing wastewater treatment facility

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005500156A (en) * 2001-08-24 2005-01-06 エンビロゲン,インコーポレイティド System and method for collecting permeate through a filter and cleaning the filter in that position
JPWO2005053410A1 (en) * 2003-12-04 2007-06-28 不二製油株式会社 Bread improvers and breads containing the same
JP4736807B2 (en) * 2003-12-04 2011-07-27 不二製油株式会社 Bread improvers and breads containing the same
JP2012000585A (en) * 2010-06-18 2012-01-05 Kubota Corp Wastewater treatment facility, wastewater treatment method and method of reconstructing wastewater treatment facility

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