JP2001062481A - Treatment of concentrated sewage - Google Patents

Treatment of concentrated sewage

Info

Publication number
JP2001062481A
JP2001062481A JP23903299A JP23903299A JP2001062481A JP 2001062481 A JP2001062481 A JP 2001062481A JP 23903299 A JP23903299 A JP 23903299A JP 23903299 A JP23903299 A JP 23903299A JP 2001062481 A JP2001062481 A JP 2001062481A
Authority
JP
Japan
Prior art keywords
sewage
air
oxygen
diffuser
tank
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
JP23903299A
Other languages
Japanese (ja)
Inventor
Seiji Izumi
清司 和泉
Yutaka Yamada
山田  豊
Taichi Kamisaka
太一 上坂
Tatsuya Uejima
達也 上島
Susumu Kawakami
進 川上
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 JP23903299A priority Critical patent/JP2001062481A/en
Publication of JP2001062481A publication Critical patent/JP2001062481A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

PROBLEM TO BE SOLVED: To provide a method for treating concd. sewage by which a necessary amt. of oxygen is sufficiently supplied to the activated sludge without increasing the amt. of aeration air. SOLUTION: An org. sewage 5 having high contents of org. matter and nitrogen is biologically treated in a reaction tank 1 in which an immersion-type membrane separator 21 is set in this membrane-separation activated sludge process. In this case, the concd. sewage 5 is pretreated by a pretreating equipment 6 to remove the foreign matter by a screen, and the concd. sewage 5 is injected into an air supply system 2 for supplying aeration air to a diffuser pipe 23 in the separator 21. Oxygen is dissolved in the concd. sewage 5 at high speed in the air supply system 2, and the concd. sewage 5 in which oxygen is sufficiently dissolved is supplied into the tank from the diffuser pipe 23 along with the aeration air.

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、高濃度汚水の処理
方法に関し、有機物、窒素濃度の高い有機性汚水を膜分
離装置を使用して活性汚泥処理する膜分離活性汚泥処理
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 method for treating high-concentration sewage, and more particularly to a membrane separation activated sludge treatment technology for treating organic sewage having a high concentration of organic substances and nitrogen using a membrane separation apparatus. is there.

【0002】[0002]

【従来の技術】従来、有機物、窒素濃度の高い有機性汚
水を処理する方法として活性汚泥処理があり、膜分離装
置を併用して槽内の活性汚泥濃度を高く維持する膜分離
活性汚泥処理がある。図3〜図4に示すように、膜分離
装置21は、複数枚の平板状膜カートリッジ22と、そ
の下方より膜面洗浄気体を噴出する散気管23とをケー
ス24の内部に配置したものである。ケース24は、搬
送やメンテナンスを容易にするために、膜ケース25と
散気ケース26とに分割形成し、散気管23より噴出す
る膜面洗浄気体の全量が膜ケース25内に入り込むよう
に形成している。
2. Description of the Related Art Conventionally, there is an activated sludge treatment as a method for treating organic matter and organic wastewater having a high nitrogen concentration. A membrane separation activated sludge treatment for maintaining a high concentration of activated sludge in a tank by using a membrane separation device together is known. is there. As shown in FIGS. 3 and 4, the membrane separation device 21 includes a plurality of flat membrane cartridges 22 and an air diffuser 23 that blows out a membrane cleaning gas from below the cartridges 22 in a case 24. is there. The case 24 is formed so as to be divided into a membrane case 25 and an air diffuser case 26 in order to facilitate transportation and maintenance, and formed so that the entire amount of the membrane surface cleaning gas ejected from the diffuser tube 23 enters the membrane case 25. are doing.

【0003】膜カートリッジ22は、ABS樹脂製の濾
板22Aの両表面に濾過膜22Bを配置し、濾板22A
と濾過膜22Bとの間、および濾板22Aの内部に透過
液流路を形成し、透過液流路に連通する透過液取出口2
2Cを濾板22Aの上端縁に形成したものである。各膜
カートリッジ22は、透過液取出口22Cに接続したチ
ューブ27を介して集水管28に連通しており、集水管
28は膜透過液を導出する透過液導出管29に連通して
いる。膜ケース25の上部には膜カートリッジ22の浮
上を防止する押さえ板30を設けている。
[0003] The membrane cartridge 22 has a filter membrane 22B disposed on both surfaces of a filter plate 22A made of ABS resin.
And a filtration membrane 22B, and inside the filter plate 22A, forming a permeate flow path, and a permeate outlet 2 communicating with the permeate flow path.
2C is formed on the upper edge of the filter plate 22A. Each membrane cartridge 22 communicates with a water collecting pipe 28 via a tube 27 connected to a permeated liquid outlet 22C, and the water collecting pipe 28 communicates with a permeated liquid outlet pipe 29 for extracting the membrane permeated liquid. At the upper part of the membrane case 25, a holding plate 30 for preventing the membrane cartridge 22 from floating is provided.

【0004】この膜分離装置21を活性汚泥処理施設に
おいて使用する場合には、曝気槽内部の活性汚泥混合液
中に膜分離装置21を浸漬し、散気管23より曝気空気
を噴出させる状態において、原水中の有機物や窒素を活
性汚泥により処理しており、活性汚泥混合液は、槽内で
の水頭を駆動圧として膜カートリッジ22により重力濾
過し(透過液導出管29に吸引ポンプを介装することで
吸引濾過も可能である)、膜カートリッジ22の膜面を
透過した透過液を処理水として透過液導出管29を通じ
て槽外へ導出する。このとき、散気管23より噴出する
曝気空気の気泡およびそれにより生起される上昇流が掃
流となって膜カートリッジ22の膜面を洗浄し、ろ過能
力の低下を抑制して膜分離装置21が機能不全に至るこ
とを防止している。
When the membrane separation device 21 is used in an activated sludge treatment facility, the membrane separation device 21 is immersed in an activated sludge mixture in an aeration tank, and aerated air is blown out from a diffuser tube 23. Organic matter and nitrogen in the raw water are treated by activated sludge, and the activated sludge mixture is gravity-filtered by the membrane cartridge 22 using the head in the tank as a driving pressure (a suction pump is inserted in the permeated liquid outlet pipe 29). Thus, the permeated liquid that has passed through the membrane surface of the membrane cartridge 22 is led out of the tank through the permeated liquid outlet pipe 29 as treated water. At this time, the bubbles of the aerated air ejected from the air diffuser 23 and the upward flow generated thereby serve as a scavenging stream to wash the membrane surface of the membrane cartridge 22 and suppress a decrease in the filtration capacity, so that the membrane separation device 21 Prevents dysfunction.

【0005】上述した膜を利用する水処理設備の一般的
な構成は、図2に示すものである。図2において、流入
汚水41は、前処理設備42において夾雑物を除去した
後に流量調整槽43に貯留し、流量調整槽43から一定
の流量で曝気槽(生物処理槽)44に供給する。曝気槽
44では活性汚泥により汚水中の有機物質を分解除去
し、曝気槽44に浸漬配置した膜分離装置21で固液を
分離し、ろ液は減菌槽45を経て放流している。
A general structure of a water treatment facility using the above-mentioned membrane is shown in FIG. In FIG. 2, inflow sewage 41 is stored in a flow control tank 43 after removing impurities in a pretreatment facility 42, and is supplied from the flow control tank 43 to an aeration tank (biological treatment tank) 44 at a constant flow rate. In the aeration tank 44, organic substances in the wastewater are decomposed and removed by activated sludge, and solids and liquids are separated by the membrane separation device 21 immersed and arranged in the aeration tank 44. The filtrate is discharged through a sterilization tank 45.

【0006】[0006]

【発明が解決しようとする課題】上記したような浸漬型
膜分離装置を使用する浸漬型膜分離活性汚泥法では、散
気管から噴出する空気が、活性汚泥への酸素供給のため
の曝気空気と、膜面洗浄を行なう掃流の駆動源とを兼ね
ている。ところで、有機物、窒素濃度の高い高濃度汚水
を処理する場合には、活性汚泥が必要とする酸素量が多
くなり、この酸素供給のために散気管から噴出する曝気
空気量を増加させる必要がある。一方、膜カートリッジ
22の濾過膜22Bを掃流によって洗浄するには、その
曝気強度(噴出速度、噴出圧力、噴出量によって定ま
る)に適値があり、曝気空気量が過剰に増加すると、濾
過膜22Bが損傷する恐れがある。
In the immersion type membrane separation activated sludge method using the immersion type membrane separation apparatus as described above, the air ejected from the diffuser pipe is mixed with aerated air for supplying oxygen to the activated sludge. , And also serves as a drive source for sweeping to perform film surface cleaning. By the way, when treating high-concentration sewage with a high concentration of organic matter and nitrogen, the amount of oxygen required by activated sludge increases, and it is necessary to increase the amount of aerated air spouted from a diffuser for this oxygen supply. . On the other hand, in order to clean the filtration membrane 22B of the membrane cartridge 22 by scavenging, the aeration intensity (determined by the ejection speed, the ejection pressure, and the ejection amount) has an appropriate value. 22B may be damaged.

【0007】このために、曝気槽の上流側に前曝気槽を
設け、膜分離装置のない前曝気槽において十分に曝気し
て酸素の不足を解消している。しかし、前曝気槽を設置
するためには設置スペースを必要とし、既設の面積の限
られた施設において前曝気槽を設置することは困難であ
った。本発明は上記した課題を解決するものであり、浸
漬型膜分離装置を使用する浸漬型膜分離活性汚泥法にお
いて、曝気空気量を増加させることなく、必要量の酸素
を活性汚泥に十分に供給することができる高濃度汚水の
処理方法を提供することを目的とする。
[0007] For this purpose, a preaeration tank is provided upstream of the aeration tank, and sufficient oxygen is eliminated in the preaeration tank without a membrane separation device to eliminate the lack of oxygen. However, installation space is required to install the pre-aeration tank, and it has been difficult to install the pre-aeration tank in an existing facility having a limited area. The present invention is to solve the above-mentioned problem, and in the immersion type membrane separation activated sludge method using the immersion type membrane separation apparatus, a sufficient amount of oxygen is sufficiently supplied to the activated sludge without increasing the amount of aerated air. It is an object of the present invention to provide a method for treating high-concentration sewage that can be performed.

【0008】[0008]

【課題を解決するための手段】上記課題を解決するため
に、本発明の高濃度汚水の処理方法は、有機物、窒素濃
度の高い有機性汚水を、浸漬型膜分離装置を設置した反
応槽内で生物処理する膜分離活性汚泥法において、汚水
を前処理して夾雑物をスクリーンで除去し、この汚水を
浸漬型膜分離装置の散気管に曝気空気を供給する空気供
給系に注入し、空気供給系内で汚水中に高速度で酸素を
溶解し、十分に酸素が溶解した汚水を散気管から曝気空
気とともに槽内に供給するものである。
In order to solve the above problems, a method for treating high-concentration sewage according to the present invention is directed to a method for treating organic sewage having a high concentration of organic substances and nitrogen in a reaction tank provided with a submerged membrane separation apparatus. In the membrane separation activated sludge method in which biological treatment is performed, wastewater is pretreated, impurities are removed by a screen, and this wastewater is injected into an air supply system that supplies aeration air to a diffuser pipe of a submerged membrane separation device, and is supplied with air. Oxygen is dissolved in sewage at a high speed in a supply system, and sewage in which oxygen is sufficiently dissolved is supplied from an air diffuser to the tank together with aerated air.

【0009】上記した構成により、汚水を空気供給系へ
注水することにより、系内で汚水中に高速度で酸素が溶
解し、散気管の空気孔から槽内液中に放出する際には、
汚水中の酸素濃度がほぼ飽和の状態となる。この酸素の
溶解効率の高まりによって、散気管を通して槽内に供給
する必要空気量を20〜30%低減でき、ブロアの出力
を抑制して消費エネルギーを削減できる。汚水には、通
常多量のSSや夾雑物が含まれているが、汚水を1mm
程度のスクリーンに通すことにより、散気管の空気孔
(10mm程度)に目詰まることはない。
By injecting sewage into the air supply system according to the above configuration, oxygen is dissolved in the sewage at high speed in the system, and when oxygen is released into the liquid in the tank from the air holes of the air diffuser,
The oxygen concentration in the sewage becomes almost saturated. Due to the increase in the oxygen dissolving efficiency, the required amount of air to be supplied into the tank through the diffuser can be reduced by 20 to 30%, and the output of the blower can be suppressed to reduce energy consumption. Sewage usually contains a large amount of SS and contaminants.
By passing the air through a screen of a certain degree, the air holes (about 10 mm) of the air diffuser are not clogged.

【0010】散気管は長期間にわたって使用している
と、活性汚泥濃度が高い場合(1〜2%程度)には、散
気管の空気孔に侵入した汚泥が空気乾燥されて粒状また
は粘土状の固形物となり、空気孔を閉塞することがあ
る。しかし、本発明のように汚水を散気管に注水するこ
とにより、散気管の空気孔の閉塞を防止できる。
[0010] When the diffuser is used for a long period of time, when the activated sludge concentration is high (about 1 to 2%), the sludge that has entered the air holes of the diffuser is air-dried and becomes granular or clay-like. It becomes a solid and may block air holes. However, by injecting sewage into the diffuser tube as in the present invention, it is possible to prevent the air holes of the diffuser tube from being blocked.

【0011】[0011]

【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において、反応槽1の内部に
配置する浸漬型膜分離装置21は、図3〜図4において
説明したものと同様であるので、同一番号を付して詳し
い説明を省略する。浸漬型膜分離装置21の散気管23
は口径10mm程度の複数の空気孔を有し、それぞれに
空気供給系2が連通している。この空気供給系2は、曝
気空気を供給するブロア3と、散気管23に連通する散
気空気管4とからなる。
Embodiments of the present invention will be described below with reference to the drawings. In FIG. 1, the immersion type membrane separation device 21 disposed inside the reaction tank 1 is the same as that described in FIGS. 3 and 4, and thus the same reference numerals are given and the detailed description is omitted. Aeration tube 23 of immersion type membrane separation device 21
Has a plurality of air holes having a diameter of about 10 mm, and the air supply system 2 communicates with each of the air holes. The air supply system 2 includes a blower 3 for supplying aerated air, and a diffuser air tube 4 communicating with a diffuser tube 23.

【0012】反応槽1の上流側には、流水する高濃度汚
水5の夾雑物を目幅が1mm程度のスクリーンで除去す
る前処理設備6を配置しており、前処理設備6の下流に
夾雑物を除去した高濃度汚水5を貯留する流量調整槽7
を設けている。流量調整槽7は汚水供給系8を介して空
気供給系2に連通している。汚水供給系8は、汚水を供
給する汚水ポンプ9と、散気空気管4に連通する汚水管
10とからなる。反応槽1の下流側には減菌槽11を設
けている。
On the upstream side of the reaction tank 1, there is disposed a pretreatment facility 6 for removing impurities of the high-concentration wastewater 5 flowing through a screen having a mesh width of about 1 mm. Flow control tank 7 for storing high-concentration sewage 5 from which waste has been removed
Is provided. The flow control tank 7 communicates with the air supply system 2 via a sewage supply system 8. The sewage supply system 8 includes a sewage pump 9 that supplies sewage and a sewage pipe 10 that communicates with the diffused air pipe 4. A sterilization tank 11 is provided downstream of the reaction tank 1.

【0013】以下、上記した構成における作用を説明す
る。流入する高濃度汚水5は、通常多量のSSや夾雑物
が含まれているので、前処理設備6において夾雑物を除
去することで、下流の散気管23の空気孔(10mm程
度)が目詰まることを防止する。この夾雑物を除去した
高濃度汚水5を流量調整槽7に貯留し、汚水供給系8を
通して浸漬型膜分離装置21の各散気管23に定量供給
する。一方、空気供給系2はブロア3で供給する曝気空
気を、散気空気管4を通して散気管23に供給する。
The operation of the above configuration will be described below. The inflowing high-concentration sewage 5 usually contains a large amount of SS and contaminants. Therefore, by removing the contaminants in the pretreatment facility 6, the air holes (about 10 mm) of the downstream air diffuser 23 are clogged. To prevent that. The high-concentration sewage 5 from which the contaminants have been removed is stored in the flow rate adjusting tank 7, and supplied to the respective diffuser tubes 23 of the immersion type membrane separator 21 through the sewage supply system 8. On the other hand, the air supply system 2 supplies the aerated air supplied by the blower 3 to the air diffuser 23 through the air diffuser 4.

【0014】汚水供給系8は、汚水ポンプ9によって供
給する高濃度汚水5を、汚水管10を通して散気空気管
4に注入する。この散気空気管4へ注水した汚水5に
は、散気空気管4および散気管23を流れる間に、高速
度で酸素が溶解する。汚水ポンプ9のサクション配管部
分に夾雑物除去のためのストレーナ等を設けることもあ
る。
The sewage supply system 8 injects high-concentration sewage 5 supplied by a sewage pump 9 into a diffused air pipe 4 through a sewage pipe 10. Oxygen is dissolved at high speed in the sewage 5 injected into the diffuser air pipe 4 while flowing through the diffuser air pipe 4 and the diffuser pipe 23. A strainer or the like for removing contaminants may be provided in the suction pipe portion of the sewage pump 9.

【0015】このため、曝気空気とともに散気管23の
空気孔から槽内液中に放出する高濃度汚水5は、その酸
素濃度がほぼ飽和の状態となる。この酸素の溶解効率の
高まりによって、空気供給系2を通して槽内に供給する
必要空気量を従来に比べて20〜30%低減でき、ブロ
ア3の出力を抑制して消費エネルギーを削減できる。ま
た、高濃度汚水5を散気管23に注水することにより、
散気管23の空気孔に侵入した汚泥が空気乾燥して空気
孔を閉塞することがなくなり、活性汚泥濃度が高い状態
にあっても散気管23を長期間にわたって使用できる。
Therefore, the oxygen concentration of the high-concentration sewage 5 discharged into the tank liquid through the air holes of the air diffuser 23 together with the aerated air is substantially saturated. Due to the increase in the oxygen dissolving efficiency, the required amount of air to be supplied into the tank through the air supply system 2 can be reduced by 20 to 30% as compared with the conventional case, and the output of the blower 3 can be suppressed to reduce energy consumption. Also, by injecting the high concentration sewage 5 into the air diffuser 23,
Sludge that has entered the air holes of the air diffuser tube 23 does not dry out and closes the air holes, so that the air diffuser tube 23 can be used for a long time even when the activated sludge concentration is high.

【0016】散気管23から噴出する高濃度汚水5は、
曝気空気の気泡およびそれにより生起される上昇流に乗
って膜カートリッジ22の膜面に対してクロスフローで
流れながらろ過される。このクロスフローは膜面にケー
キ層が形成されることを抑制し、その流速は高濃度汚水
5の噴出圧力、噴出流量を調整することにより、或いは
曝気空気の噴出圧力、噴出流量を調整することにより、
あるいはそれらを組み合わせることにより制御すること
ができる。
The high-concentration sewage 5 spouting from the diffuser 23
The air is filtered while cross-flowing on the membrane surface of the membrane cartridge 22 on the bubbles of the aerated air and the upward flow generated thereby. This cross-flow suppresses the formation of a cake layer on the membrane surface, and the flow velocity is adjusted by adjusting the ejection pressure and the ejection flow rate of the high-concentration sewage 5 or adjusting the ejection pressure and the ejection flow rate of the aerated air. By
Alternatively, it can be controlled by combining them.

【0017】反応槽1に複数の浸漬型膜分離装置21を
配置する場合には、高濃度汚水5を供給する散気管23
を所定時間毎(例えば1分間)に変更しながら、各浸漬
型膜分離装置21の各散気管23へ順次に注水しても良
い。さらに、反応槽1へ流入する高濃度汚水5の量が少
ない場合には、高濃度汚水5の注水終了後に処理水もし
くは清水を散気管23に注水することもできる。また、
高濃度汚水5には油分が含まれることもあり、そのため
通常1日に1回程度は、処理水か清水で散気管23を洗
浄する。
When a plurality of immersion type membrane separation devices 21 are arranged in the reaction tank 1, a diffuser pipe 23 for supplying high-concentration sewage 5 is used.
May be sequentially injected into each diffuser tube 23 of each immersion type membrane separation device 21 while changing the value at predetermined time intervals (for example, for one minute). Furthermore, when the amount of the high-concentration sewage 5 flowing into the reaction tank 1 is small, treated water or fresh water can be injected into the air diffuser 23 after the completion of the injection of the high-concentration sewage 5. Also,
Since the high-concentration sewage 5 may contain oil, the air diffuser 23 is usually washed with treated water or fresh water about once a day.

【0018】[0018]

【発明の効果】以上のように、本発明によれば、浸漬型
膜分離装置の散気管を通して汚水を槽内に供給し、空気
供給系内で汚水中に高速度で酸素を溶解させることで、
曝気空気量を増加させることなく、必要量の酸素を活性
汚泥に十分に供給することができ、散気管を通して供給
する必要空気量を低減して消費エネルギーを抑制でき、
高濃度汚水にあっても、散気管の空気孔において汚泥を
空気乾燥させず、散気管の空気孔の閉塞を防止できる。
As described above, according to the present invention, sewage is supplied into the tank through the air diffuser of the immersion type membrane separation apparatus, and oxygen is dissolved in the sewage at a high speed in the air supply system. ,
The required amount of oxygen can be sufficiently supplied to the activated sludge without increasing the amount of aerated air, and the required amount of air supplied through the air diffuser can be reduced to reduce energy consumption.
Even in the case of high-concentration sewage, it is possible to prevent the sludge from being air-dried in the air holes of the air diffuser and prevent the air holes of the air diffuser from being blocked.

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

【図1】同実施の形態における汚水の処理方法を示すフ
ローシートである。
FIG. 1 is a flow sheet showing a wastewater treatment method according to the embodiment.

【図2】従来の汚水の処理方法を示すフローシートであ
る。
FIG. 2 is a flow sheet showing a conventional method for treating wastewater.

【図3】膜分離装置を示す横断面図である。FIG. 3 is a cross-sectional view showing a membrane separation device.

【図4】膜分離装置を示す縦断面図である。FIG. 4 is a longitudinal sectional view showing a membrane separation device.

【符号の説明】[Explanation of symbols]

1 反応槽 2 空気供給系 3 ブロア 4 散気空気管 5 高濃度汚水 6 前処理設備 7 流量調整槽 8 汚水供給系 9 汚水ポンプ 10 汚水管 11 減菌槽 21 浸漬型膜分離装置 23 散気管 REFERENCE SIGNS LIST 1 reaction tank 2 air supply system 3 blower 4 diffuser air pipe 5 high concentration sewage 6 pretreatment equipment 7 flow rate control tank 8 sewage supply system 9 sewage pump 10 sewage pipe 11 sterilization tank 21 immersion type membrane separation device 23 diffuser pipe

フロントページの続き (72)発明者 上坂 太一 大阪府大阪市浪速区敷津東一丁目2番47号 株式会社クボタ内 (72)発明者 上島 達也 大阪府大阪市浪速区敷津東一丁目2番47号 株式会社クボタ内 (72)発明者 川上 進 大阪府大阪市浪速区敷津東一丁目2番47号 株式会社クボタ内 Fターム(参考) 4D006 GA06 GA07 HA34 HA91 HA93 JA31Z JA34Z KA02 KA31 KA44 KB14 KB22 KC12 KC14 MA02 MB02 PA02 PA05 PB08 PB70 PC64 4D028 AA08 AB00 BA00 BD06 BD17Continuation of the front page (72) Inventor Taichi Uesaka 1-2-47, Shikitsu-Higashi 1-chome, Namiwa-ku, Osaka-shi, Osaka (72) Inventor Tatsuya Ueshima 1-2-2, Shikitsu-higashi, Namiwa-ku, Osaka-shi, Osaka No. 47 Kubota Co., Ltd. (72) Susumu Kawakami Inventor F-term (reference) 4D006 GA06 GA07 HA34 HA91 HA93 JA31Z JA34Z KA02 KA31 KA44 KB14 KB22 KC12 KC14 MA02 MB02 PA02 PA05 PB08 PB70 PC64 4D028 AA08 AB00 BA00 BD06 BD17

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 有機物、窒素濃度の高い有機性汚水を、
浸漬型膜分離装置を設置した反応槽内で生物処理する膜
分離活性汚泥法において、汚水を前処理して夾雑物をス
クリーンで除去し、この汚水を浸漬型膜分離装置の散気
管に曝気空気を供給する空気供給系に注入し、空気供給
系内で汚水中に高速度で酸素を溶解し、十分に酸素が溶
解した汚水を散気管から曝気空気とともに槽内に供給す
ることを特徴とする高濃度汚水の処理方法。
An organic matter, an organic wastewater having a high nitrogen concentration,
In a membrane separation activated sludge method in which biological treatment is performed in a reaction tank equipped with an immersion type membrane separation device, sewage is pretreated to remove impurities by a screen, and the sewage is aerated with an air diffuser pipe of the immersion type membrane separation device. Is injected into the air supply system that supplies oxygen, dissolves oxygen at high speed in the sewage in the air supply system, and supplies the sewage with sufficient oxygen dissolved into the tank together with aeration air from the air diffuser. High concentration wastewater treatment method.
JP23903299A 1999-08-26 1999-08-26 Treatment of concentrated sewage Pending JP2001062481A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP23903299A JP2001062481A (en) 1999-08-26 1999-08-26 Treatment of concentrated sewage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP23903299A JP2001062481A (en) 1999-08-26 1999-08-26 Treatment of concentrated sewage

Publications (1)

Publication Number Publication Date
JP2001062481A true JP2001062481A (en) 2001-03-13

Family

ID=17038878

Family Applications (1)

Application Number Title Priority Date Filing Date
JP23903299A Pending JP2001062481A (en) 1999-08-26 1999-08-26 Treatment of concentrated sewage

Country Status (1)

Country Link
JP (1) JP2001062481A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001062480A (en) * 1999-08-26 2001-03-13 Kubota Corp Treatment of sewage
JP2004305886A (en) * 2003-04-07 2004-11-04 Kubota Corp Aeration device
US11434157B2 (en) 2018-09-27 2022-09-06 Kubota Corporation Operating method for organic wastewater treatment apparatus and organic wastewater treatment apparatus

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52130147A (en) * 1976-04-23 1977-11-01 Nippon Mining Co Method of preventing clogging of diffusing pipe for aeration
JPH04290590A (en) * 1991-03-19 1992-10-15 Kubota Corp Membrane separator in septic tank
JPH1043789A (en) * 1996-08-08 1998-02-17 Kubota Corp Cleaner of air diffusion pipe
JPH1099663A (en) * 1996-09-27 1998-04-21 Mitsubishi Rayon Co Ltd Membrane treatment apparatus
JPH10151480A (en) * 1996-11-25 1998-06-09 Maezawa Ind Inc Wastewater treatment apparatus and operation method
JPH10151485A (en) * 1996-11-25 1998-06-09 Maezawa Ind Inc Wastewater treatment apparatus and operation method
JP2001062480A (en) * 1999-08-26 2001-03-13 Kubota Corp Treatment of sewage

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52130147A (en) * 1976-04-23 1977-11-01 Nippon Mining Co Method of preventing clogging of diffusing pipe for aeration
JPH04290590A (en) * 1991-03-19 1992-10-15 Kubota Corp Membrane separator in septic tank
JPH1043789A (en) * 1996-08-08 1998-02-17 Kubota Corp Cleaner of air diffusion pipe
JPH1099663A (en) * 1996-09-27 1998-04-21 Mitsubishi Rayon Co Ltd Membrane treatment apparatus
JPH10151480A (en) * 1996-11-25 1998-06-09 Maezawa Ind Inc Wastewater treatment apparatus and operation method
JPH10151485A (en) * 1996-11-25 1998-06-09 Maezawa Ind Inc Wastewater treatment apparatus and operation method
JP2001062480A (en) * 1999-08-26 2001-03-13 Kubota Corp Treatment of sewage

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001062480A (en) * 1999-08-26 2001-03-13 Kubota Corp Treatment of sewage
JP2004305886A (en) * 2003-04-07 2004-11-04 Kubota Corp Aeration device
JP4530621B2 (en) * 2003-04-07 2010-08-25 株式会社クボタ Cleaning method for air diffuser
US11434157B2 (en) 2018-09-27 2022-09-06 Kubota Corporation Operating method for organic wastewater treatment apparatus and organic wastewater treatment apparatus

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