JP2001062480A - Treatment of sewage - Google Patents
Treatment of sewageInfo
- Publication number
- JP2001062480A JP2001062480A JP23903199A JP23903199A JP2001062480A JP 2001062480 A JP2001062480 A JP 2001062480A JP 23903199 A JP23903199 A JP 23903199A JP 23903199 A JP23903199 A JP 23903199A JP 2001062480 A JP2001062480 A JP 2001062480A
- Authority
- JP
- Japan
- Prior art keywords
- air
- sewage
- diffuser
- membrane separation
- 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.)
- Granted
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
- Activated Sludge Processes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、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 sewage, and more particularly to a membrane separation activated sludge treatment technique for treating organic sewage having a high concentration of organic substances and nitrogen using a membrane separation apparatus.
【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5〜図6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. 5 and 6, the membrane separation device 21 includes a plurality of flat membrane cartridges 22 and an air diffuser 23 for ejecting 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によ
って膜カートリッジ22の膜面を洗浄し、分離機能の低
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 membrane surface of the membrane cartridge 22 is washed by the bubbles of the aerated air ejected from the air diffuser 23 and the upward flow generated by the bubbles, thereby suppressing the decrease in the separation function and causing the membrane separation device 21 to malfunction. Has been prevented.
【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3〜図4に示すものである。図3〜図4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2
1で固液を分離し、ろ液は減菌槽45を経て放流してい
る。The general structure of a water treatment facility using the above-mentioned membrane is shown in FIGS. 3 and 4, inflow sewage 41 is stored in a flow control tank 43 after removing contaminants in a pretreatment facility 42 and supplied from a flow control tank 43 to an aeration tank (biological treatment tank) 44 at a constant flow rate. I do. In the aeration tank 44, activated sludge decomposes and removes organic substances in the sewage, and the membrane separation device 2 immersed and disposed in the aeration tank 44
The solid-liquid is separated in 1 and the filtrate is discharged through a sterilization tank 45.
【0006】[0006]
【発明が解決しようとする課題】上述したような浸漬型
膜分離装置を使用する膜分離活性汚泥処理では、図4に
示すように、数台の膜分離装置21を曝気槽44に設置
して使用するが、処理規模が大きくなると数台から十数
台の膜分離装置21を一つの曝気槽44に設置する。こ
のような曝気槽44においては、流入汚水に希釈されて
汚水流入側の活性汚泥濃度は薄くなり、反対側の活性汚
泥濃度は極めて濃くなる濃度分布が発生する。In the membrane separation activated sludge treatment using the immersion type membrane separation device as described above, as shown in FIG. 4, several membrane separation devices 21 are installed in an aeration tank 44. Although used, when the processing scale becomes large, several to more than ten membrane separation devices 21 are installed in one aeration tank 44. In such an aeration tank 44, a concentration distribution in which the activated sludge concentration on the inflow side of the wastewater is reduced by dilution with the inflowing wastewater and the concentration of the activated sludge on the opposite side becomes extremely high occurs.
【0007】本発明は、浸漬型膜分離装置を使用する膜
分離活性汚泥法において、曝気槽内の全領域において活
性汚泥濃度を均一に維持することができる汚水の処理方
法を提供することを目的とする。[0007] It is an object of the present invention to provide a method for treating sewage which can maintain a uniform concentration of activated sludge in all regions in an aeration tank in a membrane separation activated sludge method using a submerged membrane separation apparatus. And
【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、請求項1に係る本発明の汚水の処理方法は、反応槽
内に複数の浸漬型膜分離装置を設置し、浸漬型膜分離装
置に配置した散気管から曝気用空気を散気し、反応槽内
に流入する汚水を活性汚泥で生物処理する膜分離活性汚
泥法において、流入汚水を前処理して夾雑物をスクリー
ンで除去し、その後に汚水を浸漬型膜分離装置の散気管
を通して曝気用空気とともに槽内に供給するものであ
る。According to a first aspect of the present invention, there is provided a method for treating sewage, comprising the steps of: installing a plurality of immersion type membrane separation devices in a reaction tank; In the membrane separation activated sludge method in which air for aeration is diffused from the air diffuser arranged in the apparatus and the wastewater flowing into the reaction tank is biologically treated with activated sludge, the inflowed wastewater is pretreated to remove impurities by a screen. Then, the sewage is supplied into the tank together with aeration air through the air diffuser of the immersion type membrane separation device.
【0009】請求項2に係る本発明の汚水の処理方法
は、散気管へ汚水を供給する時に曝気用空気の供給を停
止するものである。請求項3に係る本発明の汚水の処理
方法は、汚水を供給する散気管を所定時間毎に変更しな
がら、各浸漬型膜分離装置の各散気管へ順次に注水する
ものである。According to a second aspect of the present invention, there is provided a method for treating sewage, wherein the supply of air for aeration is stopped when sewage is supplied to an air diffuser. According to a third aspect of the present invention, the method for treating wastewater is to sequentially inject water into each diffuser tube of each immersion type membrane separation device while changing the diffuser tube for supplying the wastewater every predetermined time.
【0010】上記した構成により、各浸漬型膜分離装置
の各散気管を通して汚水を槽内に分散して供給すること
で、生物処理の負荷である有機物が槽内に分散し、反応
槽内の全領域において活性汚泥濃度を均一に維持するこ
とができる。流入汚水には、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。汚水を散気管へ注水することにより、散
気管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2
0〜30%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。[0010] With the above structure, the wastewater is dispersed and supplied into the tank through each diffuser pipe of each immersion type membrane separation device, so that the organic matter which is a load of biological treatment is dispersed in the tank, and the organic matter in the reaction tank is dispersed. The activated sludge concentration can be maintained uniform in all regions. The inflowing sewage usually contains a large amount of SS and contaminants, but by passing the sewage through a screen of about 1 mm, the air holes (about 10 mm) of the air diffuser do not become clogged. By pouring the sewage into the diffuser, oxygen is dissolved in the sewage at a high speed in the diffuser and the oxygen concentration in the sewage is almost saturated when the oxygen is released into the tank from the air hole of the diffuser. State. Due to the increase in the oxygen dissolving efficiency, the required amount of air to be supplied into the tank through the diffuser is reduced by 2
0 to 30% can be reduced, and the output of the blower can be suppressed to reduce energy consumption.
【0011】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。散気管
への汚水の注水は、散気管へ曝気用空気を供給するブロ
アを停止して行なっても良く、また散気しながら注水し
ても良い。また、汚水は全ての浸漬型膜分離装置の散気
管へ同時に注水しても、順次に一定の時間毎、例えば1
分毎に注水する散気管を代えても良い。If the diffuser tube 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 tube 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. Injection of sewage into the air diffuser may be performed by stopping the blower that supplies air for aeration to the air diffuser, or may be performed while diffusing air. Further, even if the sewage is simultaneously injected into the air diffusers of all the immersion type membrane separation devices, the sewage may be sequentially removed at regular intervals, for example, 1 hour.
The air diffuser for injecting water every minute may be changed.
【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〜図2において、反応槽1
は、平面形状が長方形をなして、短辺と長辺との比が
1:3以上の長い形状を有しており、汚水中の有機物質
を槽内の活性汚泥により分解除去する生物処理を行な
う。Embodiments of the present invention will be described below with reference to the drawings. In FIG. 1 and FIG.
Has a long shape in which the plane shape is rectangular and the ratio of the short side to the long side is 1: 3 or more, and biological treatment for decomposing and removing organic substances in sewage by activated sludge in a tank is performed. Do.
【0013】反応槽1の内部には、複数(数台から十数
台)の浸漬型膜分離装置21が所定間隔で一列状に配置
してある。この浸漬型膜分離装置21は、図5〜図6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。各浸漬型膜分離装置21の各
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、曝気用空気を供給するブロア3と、ブロア3に
連通する空気供給本管4と、空気供給本管4と各散気管
23を連通する散気空気管5と、各散気空気管5に介装
した空気用バルブ6とからなる。Inside the reaction tank 1, a plurality (several to ten and several) of immersion type membrane separation devices 21 are arranged in a line at predetermined intervals. Since the immersion type membrane separation device 21 is the same as that described in FIGS. 5 and 6, the same reference numerals are given and the detailed description is omitted. Each diffuser tube 23 of each immersion type membrane separation device 21 has a plurality of air holes having a diameter of about 10 mm,
An air supply system 2 communicates with each of them. The air supply system 2 includes a blower 3 that supplies aeration air, an air supply main pipe 4 that communicates with the blower 3, an air diffuser pipe 5 that communicates the air supply main pipe 4 with each diffuser pipe 23, An air valve 6 interposed in the air diffuser pipe 5.
【0014】汚水供給系7は、汚水を供給する汚水ポン
プ8と、汚水ポンプ8に連通する汚水供給本管9と、汚
水供給本管9と各散気空気管5を連通する汚水管10
と、各汚水管10に介装した汚水バルブ11とからな
る。図2に示すように、反応槽1の上流側には、流水す
る汚水41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42を配置しており、前処理設備4
2の下流には夾雑物を除去した汚水を貯留する流量調整
槽43を設けている。反応槽1の下流側には減菌槽45
を設けている。The sewage supply system 7 includes a sewage pump 8 for supplying sewage, a sewage supply main pipe 9 communicating with the sewage pump 8, and a sewage pipe 10 connecting the sewage supply main pipe 9 and each diffused air pipe 5.
And a sewage valve 11 interposed in each sewage pipe 10. As shown in FIG. 2, on the upstream side of the reaction tank 1, a pretreatment facility 42 for removing impurities of the flowing wastewater 41 with a screen having a mesh width of about 1 mm is arranged.
Downstream of 2, a flow control tank 43 for storing sewage from which impurities have been removed is provided. A sterilization tank 45 is provided downstream of the reaction tank 1.
Is provided.
【0015】以下、上記した構成における作用を説明す
る。流入する汚水41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42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
汚水41を流量調整槽43に貯留し、汚水供給系7を通
して各浸漬型膜分離装置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で供給する曝気用
空気を、空気供給本管4、空気用バルブ6、散気空気管
5を通して各散気管23に供給する。The operation of the above configuration will be described below. Since the inflowing sewage 41 usually contains a large amount of SS and impurities, removing the impurities in the pretreatment facility 42 can prevent the air holes (about 10 mm) of the downstream air diffuser 23 from being clogged. To prevent. The sewage 41 from which the contaminants have been removed is stored in a flow control tank 43, and is supplied through the sewage supply system 7 to each diffuser 23 of each immersion type membrane separation device 21 in a constant amount. On the other hand, the air supply system 2 supplies the air for aeration supplied by the blower 3 to each of the diffuser pipes 23 through the main air supply pipe 4, the air valve 6, and the diffuser air pipe 5.
【0016】汚水供給系7は、汚水ポンプ8によって供
給する汚水41を、汚水供給本管9、汚水バルブ11、
汚水管10を通して各散気空気管5に注入する。この散
気空気管5へ注水した汚水41には、散気空気管5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8のサクション配管にはストレーナ等を設け
ることもある。The sewage supply system 7 supplies sewage 41 supplied by a sewage pump 8 to a sewage supply main pipe 9, a sewage valve 11,
The air is injected into each diffused air pipe 5 through the sewage pipe 10. Oxygen dissolves in the sewage 41 injected into the diffuser air pipe 5 at a high speed while flowing through the diffuser air pipe 5 and the diffuser pipe 23.
The suction pipe of the sewage pump 8 may be provided with a strainer or the like.
【0017】このため、曝気用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汚水41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。この
ように、各浸漬型膜分離装置21の各散気管23を通し
て汚水41を槽内に分散して供給することで、生物処理
の負荷である有機物が槽内に分散し、反応槽1の全領域
において活性汚泥濃度を均一に維持することができる。Therefore, the air diffuser 23 and the air for aeration are used.
The oxygen concentration of the sewage 41 discharged into the liquid in the tank from the air hole 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. In this way, by dispersing and supplying the sewage 41 into the tank through each diffuser 23 of each immersion type membrane separation device 21, the organic matter which is a load of biological treatment is dispersed in the tank, and the entirety of the reaction tank 1 is dispersed. Activated sludge concentration can be maintained uniform in the region.
【0018】また、汚水41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
が高い場合(1〜2%程度)でも散気管23を長期間に
わたって使用できる。散気管23から噴出する汚水41
は、曝気用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、その流速は汚水
41の噴出圧力、噴出流量を調整することにより、或い
は曝気用空気の噴出圧力、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。Further, by injecting the sewage 41 into the air diffuser 23, the sludge that has entered the air holes of the air diffuser 23 does not dry out and block the air holes. (About 2%), the air diffuser 23 can be used for a long time. Sewage 41 spouting from the diffuser 23
Is filtered while flowing in a cross flow with respect to the membrane surface of the membrane cartridge 22 on the bubbles of the aeration 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 sewage 41, or by adjusting the ejection pressure and the ejection flow rate of the aeration air. , Or by combining them.
【0019】散気管23への汚水41の供給は、各空気
バルブ6を閉栓し、もしくはブロア3を停止して曝気用
空気の供給を停止する状態において行なっても良い。ま
た、各汚水バルブ11を適宜に開閉操作することによ
り、汚水41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へ流入する汚水41の量が少ない場合には、汚水41
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、汚水41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。The supply of the sewage 41 to the air diffuser 23 may be performed in a state where the air valves 6 are closed or the blower 3 is stopped to stop supplying the air for aeration. Further, by appropriately opening and closing the respective sewage valves 11, the air diffuser 23 for supplying the sewage 41 is changed at predetermined time intervals (for example, one minute), and the air diffuser 23 of each immersion type membrane separation device 21 is changed. Water may be injected sequentially. Further, when the amount of the sewage 41 flowing into the reaction tank 1 is small,
After the completion of the water injection, treated water or clean water can be injected into the air diffuser 23. In addition, the sewage 41 may contain oil, so that the air diffuser 23 is usually washed with treated water or fresh water about once a day.
【0020】[0020]
【発明の効果】以上のように、本発明によれば、各浸漬
型膜分離装置の各散気管を通して汚水を槽内に分散して
供給することで、有機物を槽内に分散し、反応槽内の全
領域において活性汚泥濃度を均一に維持することができ
る。散気管内で汚水中に高速度で酸素を溶解させること
で、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る。活性汚泥濃度が高い場合(1
〜2%程度)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, organic matter is dispersed in the tank by dispersing and supplying sewage into the tank through each diffuser pipe of each immersion type membrane separation apparatus. Activated sludge concentration can be maintained uniform in all regions in the inside. By dissolving oxygen at high speed in the sewage in the air diffuser, the amount of air required to be supplied through the air diffuser can be reduced and the energy consumption can be suppressed. When activated sludge concentration is high (1
(About 2%), the sludge is not air-dried in the air holes of the air diffuser, and the air holes of the air diffuser can be prevented from being blocked.
【図1】本発明の実施の形態における反応槽の構成を示
す模式図である。FIG. 1 is a schematic diagram illustrating a configuration of a reaction tank according to an embodiment of the present invention.
【図2】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. 2 is a flow sheet showing a method for treating wastewater in the embodiment.
【図3】従来の汚水の処理方法を示すフローシートであ
る。FIG. 3 is a flow sheet showing a conventional method for treating wastewater.
【図4】従来の反応槽の構成を示す模式図である。FIG. 4 is a schematic diagram showing a configuration of a conventional reaction vessel.
【図5】膜分離装置を示す横断面図である。FIG. 5 is a cross-sectional view showing a membrane separation device.
【図6】膜分離装置を示す縦断面図である。FIG. 6 is a longitudinal sectional view showing a membrane separation device.
1 反応槽 2 空気供給系 3 ブロア 4 空気供給本管 5 散気空気管 6 空気用バルブ 7 汚水供給系 8 汚水ポンプ 9 汚水供給本管 10 汚水管 11 汚水バルブ 21 浸漬型膜分離装置 23 散気管 41 汚水 42 前処理設備 43 流量調整槽 45 減菌槽 Reference Signs List 1 reaction tank 2 air supply system 3 blower 4 air supply main pipe 5 diffused air pipe 6 air valve 7 sewage supply system 8 sewage pump 9 sewage supply main pipe 10 sewage pipe 11 sewage valve 21 immersion type membrane separation device 23 diffuser pipe 41 sewage 42 pretreatment equipment 43 flow control tank 45 sterilization tank
───────────────────────────────────────────────────── 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 GA02 HA41 HA93 KA12 KA44 KA47 KA64 KA66 KB22 MA03 PA01 PB08 PC62 4D028 BA00 BC17 BC22 BC24 BD17 CA09 CB08 ──────────────────────────────────────────────────続 き Continued on the front page (72) Taichi Uesaka 2-47, Shikitsu Higashi 1-chome, Namiwa-ku, Osaka-shi, Osaka Prefecture No. 2-47, Kubota Co., Ltd. (72) Susumu Kawakami, Inventor 1-47, Shishitsuhigashi, Naniwa-ku, Osaka-shi, Osaka F-term (reference) 4D006 GA02 HA41 HA93 KA12 KA44 KA47 KA64 KA66 KB22 MA03 PA01 PB08 PC62 4D028 BA00 BC17 BC22 BC24 BD17 CA09 CB08
Claims (3)
置し、浸漬型膜分離装置に配置した散気管から曝気用空
気を散気し、反応槽内に流入する汚水を活性汚泥で生物
処理する膜分離活性汚泥法において、流入汚水を前処理
して夾雑物をスクリーンで除去し、その後に汚水を浸漬
型膜分離装置の散気管を通して曝気用空気とともに槽内
に供給することを特徴とする汚水の処理方法。1. A plurality of immersion type membrane separation devices are installed in a reaction tank, air for aeration is diffused from a diffuser tube arranged in the immersion type membrane separation device, and waste water flowing into the reaction tank is activated sludge. In the membrane separation activated sludge method for biological treatment, inflow wastewater is pretreated to remove impurities by a screen, and then the wastewater is supplied into the tank together with aeration air through the diffuser pipe of the immersion type membrane separation device. Wastewater treatment method.
の供給を停止することを特徴とする請求項1に記載の汚
水の処理方法。2. The method for treating sewage according to claim 1, wherein the supply of aeration air is stopped when the sewage is supplied to the air diffuser.
更しながら、各浸漬型膜分離装置の各散気管へ順次に注
水することを特徴とする請求項1又は2に記載の汚水の
処理方法。3. The sewage water according to claim 1, wherein water is sequentially injected into each of the air diffusion tubes of each immersion type membrane separation device while changing the air diffusion tube for supplying the waste water at predetermined time intervals. Processing method.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP23903199A JP4046445B2 (en) | 1999-08-26 | 1999-08-26 | Wastewater treatment method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP23903199A JP4046445B2 (en) | 1999-08-26 | 1999-08-26 | Wastewater treatment method |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2001062480A true JP2001062480A (en) | 2001-03-13 |
JP4046445B2 JP4046445B2 (en) | 2008-02-13 |
Family
ID=17038865
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP23903199A Expired - Lifetime JP4046445B2 (en) | 1999-08-26 | 1999-08-26 | Wastewater treatment method |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP4046445B2 (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001062481A (en) * | 1999-08-26 | 2001-03-13 | Kubota Corp | Treatment of concentrated sewage |
JP2007152282A (en) * | 2005-12-07 | 2007-06-21 | Mitsubishi Rayon Eng Co Ltd | Membrane separation active sludge treatment method |
JP4874231B2 (en) * | 2005-02-28 | 2012-02-15 | 株式会社クボタ | Water treatment system |
CN103613191A (en) * | 2013-12-05 | 2014-03-05 | 乐山世峰环保科技有限责任公司 | Aeration sewage treatment pond |
JP2017012995A (en) * | 2015-06-30 | 2017-01-19 | 水ing株式会社 | Activated sludge processing device |
JP2022546913A (en) * | 2019-07-16 | 2022-11-10 | フィブラキャスト リミティド | Systems and methods for supplying submerged membrane units |
Citations (8)
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 |
JPH06106167A (en) * | 1992-09-28 | 1994-04-19 | Kubota Corp | Method and apparatus for solid-liquid separation of waste water |
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 |
JP2001062481A (en) * | 1999-08-26 | 2001-03-13 | Kubota Corp | Treatment of concentrated sewage |
-
1999
- 1999-08-26 JP JP23903199A patent/JP4046445B2/en not_active Expired - Lifetime
Patent Citations (8)
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 |
JPH06106167A (en) * | 1992-09-28 | 1994-04-19 | Kubota Corp | Method and apparatus for solid-liquid separation of waste water |
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 |
JP2001062481A (en) * | 1999-08-26 | 2001-03-13 | Kubota Corp | Treatment of concentrated sewage |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001062481A (en) * | 1999-08-26 | 2001-03-13 | Kubota Corp | Treatment of concentrated sewage |
JP4874231B2 (en) * | 2005-02-28 | 2012-02-15 | 株式会社クボタ | Water treatment system |
JP2007152282A (en) * | 2005-12-07 | 2007-06-21 | Mitsubishi Rayon Eng Co Ltd | Membrane separation active sludge treatment method |
CN103613191A (en) * | 2013-12-05 | 2014-03-05 | 乐山世峰环保科技有限责任公司 | Aeration sewage treatment pond |
JP2017012995A (en) * | 2015-06-30 | 2017-01-19 | 水ing株式会社 | Activated sludge processing device |
JP2022546913A (en) * | 2019-07-16 | 2022-11-10 | フィブラキャスト リミティド | Systems and methods for supplying submerged membrane units |
Also Published As
Publication number | Publication date |
---|---|
JP4046445B2 (en) | 2008-02-13 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US7276171B2 (en) | Method for cleaning separation membrane | |
JPH07155758A (en) | Waste water treating device | |
JP2007130579A (en) | Filtration membrane cleaning apparatus and method for membrane filtration unit in activated sludge treatment | |
JPH1015574A (en) | Sewage treatment apparatus | |
JP4793635B2 (en) | Recycling method of organic wastewater | |
JP5648387B2 (en) | Aeration device and method of operating membrane separation device | |
JP2001062480A (en) | Treatment of sewage | |
JPH04290590A (en) | Membrane separator in septic tank | |
WO2010101152A1 (en) | Device for membrane separation type activated-sludge treatment and method therefor | |
JP5423184B2 (en) | Filtration membrane module cleaning method and cleaning apparatus | |
JP2007190488A (en) | Membrane separation activated sludge treatment apparatus | |
JP2001170677A (en) | Air diffuser for high-concentration sewage | |
JP2005193075A (en) | Filtration apparatus and filtering method using the same | |
JP3278560B2 (en) | Water treatment equipment | |
JP2005279495A (en) | Immersed membrane separator, washing method for diffuser, and membrane separation method | |
JP2001062483A (en) | Treatment of concentrated sewage | |
JP2001062481A (en) | Treatment of concentrated sewage | |
JP4023959B2 (en) | High-concentration wastewater treatment method | |
JP4111579B2 (en) | Operation method and apparatus of organic sewage treatment apparatus | |
JP2004249235A (en) | Membrane separation device of activated sludge treatment system, membrane separation method, and activated sludge treatment system equipped with membrane separation device | |
JP2003033764A (en) | Method and apparatus for washing filtration body by using ozone | |
JP2001062471A (en) | Device for treating sewage containing nitrogen | |
JP2001170674A (en) | Treating device for high-concentration sewage | |
JP2000051889A (en) | Sewage treatment equipment | |
JP2000084554A (en) | Method for operating water treating apparatus having membrane separator |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20050908 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20070530 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20070612 |
|
A521 | Written amendment |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20070810 |
|
TRDD | Decision of grant or rejection written | ||
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20071023 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20071120 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20101130 Year of fee payment: 3 |
|
R150 | Certificate of patent or registration of utility model |
Ref document number: 4046445 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20101130 Year of fee payment: 3 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20111130 Year of fee payment: 4 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20111130 Year of fee payment: 4 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20121130 Year of fee payment: 5 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20131130 Year of fee payment: 6 |
|
EXPY | Cancellation because of completion of term |