JP2000296302A - Sewage treatment - Google Patents

Sewage treatment

Info

Publication number
JP2000296302A
JP2000296302A JP11104707A JP10470799A JP2000296302A JP 2000296302 A JP2000296302 A JP 2000296302A JP 11104707 A JP11104707 A JP 11104707A JP 10470799 A JP10470799 A JP 10470799A JP 2000296302 A JP2000296302 A JP 2000296302A
Authority
JP
Japan
Prior art keywords
filtration
water
biological reaction
reaction tank
sewage
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
JP11104707A
Other languages
Japanese (ja)
Inventor
Hitoshi Daido
均 大同
Eiji Aso
栄治 麻生
Tetsuo Hasegawa
哲夫 長谷川
Mutsuro Nagai
睦郎 永井
Yoshinao Kishine
義尚 岸根
Shigeki Sawada
繁樹 澤田
Morio Sakata
守生 坂田
Kazuhisa Fukunaga
和久 福永
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.)
Kurita Water Industries Ltd
Nippon Steel Corp
Proterial Ltd
Original Assignee
Hitachi Metals Ltd
Kurita Water Industries Ltd
Nippon Steel 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 Hitachi Metals Ltd, Kurita Water Industries Ltd, Nippon Steel Corp filed Critical Hitachi Metals Ltd
Priority to JP11104707A priority Critical patent/JP2000296302A/en
Publication of JP2000296302A publication Critical patent/JP2000296302A/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 sewage treatment device capable of a continuous operation of filter units and also enabling to prevent deterioration of the water quality of treated water. SOLUTION: Sewage water is fed to the sewage treatment device provided with a biological reaction tank 1, plural filter units 3 in which at least one portion of a surrounding wall immersed and arranged along an inflow direction of the sewage in the inside comprises a water passing support body, partitioning walls 4 for partitioning respective filter units, an aeration means provided at the bottom of the biological reaction tank 1, a washing diffusion pipe arranged at the bottom of the filter units and a buffer tank having a lower water level than a water level of the biological reaction tank 1. Then the treated water is taken out from the filter units 3, and also the washing diffusion pipes are selectively operated, thus respective filtering units 3 are alternately washed along the arranging direction.

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、汚水を生物処理す
る汚水処理方法に係り、特に生物反応槽中に浸漬配置し
たろ過ユニットにより生物処理された汚泥を水から分離
する汚水処理方法に関する。
The present invention relates to a sewage treatment method for biologically treating sewage, and more particularly to a sewage treatment method for separating sludge biologically treated by a filtration unit immersed in a biological reaction tank from water.

【0002】[0002]

【従来の技術】生物反応により汚水中の有機物を分解処
理する活性汚泥法による汚水処理装置では、まず曝気槽
(生物反応槽)で汚水中の有機物を空気の存在下で微生
物に喰わせて、有機物を除去し、次いで沈殿池で有機物
を喰べて繁殖した微生物を汚泥として沈降させて水から
分離し、上澄み部分の水は集水されて次工程へ送られ、
一方沈殿池内に沈降した汚泥は掻き集められて次工程
(脱水工程等)に送られる。しかしながら、この汚水処
理装置では次のような問題がある。即ち、水量あるいは
汚泥濃度の負荷が変動すると処理水質が悪化する、沈殿
汚泥の濃度が低いので次工程に送る濃縮汚泥量が増大す
る、沈殿池で汚泥を沈殿させるためにはその中の流速を
極端に小さくしなければならず、そのため沈殿池の設置
面積を大きくする必要があるという問題を伴う。
2. Description of the Related Art In a sewage treatment apparatus by an activated sludge method for decomposing organic matter in wastewater by a biological reaction, first, an organic substance in the wastewater is eaten by microorganisms in the presence of air in an aeration tank (biological reaction tank). The organic matter is removed, then the organic matter is eaten in the sedimentation basin, and the microorganisms propagated are settled as sludge and separated from the water, and the supernatant water is collected and sent to the next step,
On the other hand, the sludge settled in the sedimentation basin is scraped and sent to the next step (dehydration step, etc.). However, this sewage treatment apparatus has the following problems. That is, if the load of the water amount or the sludge concentration fluctuates, the treated water quality deteriorates, the concentration of the settled sludge is low, so the amount of the concentrated sludge sent to the next step increases. There is a problem that the size of the sedimentation basin needs to be increased because it must be extremely small.

【0003】このような問題点を解消し、沈殿槽を設置
することなく生物処理された汚泥を水から分離するた
め、間隔保持用の通水性多孔質材を間に介在させて重ね
合わせた通水性シートの周囲を密封して形成した袋状の
ろ過体を曝気槽内の曝気部の上方に浸漬配置し、このろ
過体内より低い水頭差によりろ過水を低い吸引力でかつ
緩やかな速度で吸引することにより、吸引管から曝気槽
外に引出すようにした装置が提案されている(例えば特
開平5−185078号参照)。この処理装置によれ
ば、上記ろ過体により汚水中の浮遊物質がろ別され、そ
れが継続されるとろ過体の表面に濃縮された汚泥のケー
キ層が形成され、そして汚水中の微粒子はこのケーキ層
のフィルター作用によって補促される。この処理装置で
は、上述した低い吸引力と低いろ過速度を保つことによ
り、ケーキ層は胞弱になりろ過体への付着と剥離が繰返
えされてその厚さが一定に保たれ、もって一定のろ過速
度を維持することができる。
[0003] In order to solve such problems and to separate sludge that has been biologically treated from water without installing a sedimentation tank, a water-permeable porous material for maintaining a distance is interposed between the sludge and the sludge. A bag-shaped filter body formed by sealing the periphery of the aqueous sheet is immersed and arranged above the aeration unit in the aeration tank, and the filtered water is suctioned at a low suction force and at a slow speed due to a lower head difference than the filter body. By doing so, an apparatus has been proposed in which the suction pipe is drawn out of the aeration tank (for example, see Japanese Patent Application Laid-Open No. 5-185078). According to this treatment apparatus, suspended solids in the sewage are filtered out by the filter, and when the filtration is continued, a cake layer of concentrated sludge is formed on the surface of the filter, and fine particles in the sewage are separated from the fine particles by this filter. Assisted by the filtering action of the cake layer. In this processing apparatus, by maintaining the above-mentioned low suction force and low filtration rate, the cake layer becomes weak and the adhesion and peeling to the filter are repeated, so that the thickness is kept constant, and thus the thickness is kept constant. Filtration speed can be maintained.

【0004】[0004]

【発明が解決しようとする課題】上述した特定のろ過体
を有する処理装置によれば、生物処理後の沈殿池を省略
することができ、またろ過性能の点では優れているが、
工業的見地から生物反応槽内に汚水の流入方向に沿って
複数のろ過体を浸漬設置し、ろ過ユニットの洗浄を行う
場合に問題がある。すなわち、上記処理装置でも、長期
間ろ過を継続すると、通水性支持体の表面に形成される
ろ過層の圧密化によりろ過速度が低下してくるという問
題がある。この対策としてろ過ユニットの下方に散気手
段を設け、この散気手段から空気を供給してろ過層を除
去することにより、ろ過速度を回復することが行われて
いる。ろ過ユニットの洗浄方法としては、例えば生物反
応槽内に汚水の流入方向に沿って配置された複数のろ過
ユニットを順次のろ過動作を中断し、その間にろ過ユニ
ットに洗浄用散気手段により空気を供給することが考え
られる。しかるにこの方法では、洗浄されるろ過ユニッ
トの下方にある散気手段を作動させると、散気手段から
放出された気泡がそのろ過ユニットに隣接するろ過ユニ
ットにも供給されて当該ユニットのろ過層が除去される
ので、当該ろ過ユニットの周囲のフィルター作用を持つ
ケーキ層も剥離され、もってろ過ユニットから取出され
る処理水の水質が悪化するという問題がある。したがっ
て本発明の目的は、複数のろ過ユニットの連続運転が可
能でありかつ処理水の水質低下を防止することのできる
汚水処理方法を提供することである。
According to the treatment apparatus having the above-mentioned specific filter, the sedimentation basin after the biological treatment can be omitted and the filtration performance is excellent.
From an industrial point of view, there is a problem when a plurality of filter bodies are immersed and installed in the biological reaction tank along the inflow direction of the wastewater to wash the filtration unit. That is, even in the above treatment apparatus, if filtration is continued for a long period of time, there is a problem that the filtration rate is reduced due to the consolidation of the filtration layer formed on the surface of the water-permeable support. As a countermeasure, a diffuser is provided below the filtration unit, and air is supplied from the diffuser to remove the filtration layer, thereby recovering the filtration speed. As a method of cleaning the filtration unit, for example, a plurality of filtration units arranged along the inflow direction of the wastewater in the biological reaction tank interrupts the sequential filtration operation, during which time air is supplied to the filtration unit by the cleaning air diffuser. It is conceivable to supply. However, in this method, when the air diffuser below the filtration unit to be cleaned is operated, the air bubbles released from the air diffuser are also supplied to the filtration unit adjacent to the filtration unit, and the filtration layer of the unit is formed. Since it is removed, the cake layer having a filter action around the filtration unit is also peeled off, and there is a problem that the quality of treated water taken out from the filtration unit is deteriorated. Therefore, an object of the present invention is to provide a sewage treatment method capable of continuously operating a plurality of filtration units and preventing a decrease in the quality of treated water.

【0005】[0005]

【課題を解決するための手段】上記目的を達成するため
に、本発明においては、生物反応槽と、その内部に汚水
の流れ方向に沿って浸漬配置された周囲壁の少くとも一
部が通水性支持体からなる複数のろ過体を有する複数個
のろ過ユニットと、各ろ過ユニット間を仕切る隔壁と、
生物反応槽の下部に設けられた曝気手段と、前記ろ過ユ
ニットの下方に配置された洗浄用散気手段と、生物反応
槽の水位より低い水位を有する緩衝槽とを備えた汚水処
理装置に汚水を供給し、前記ろ過ユニットから処理水を
取出すと共に、前記洗浄用散気手段を選択的に作用させ
て、前記ろ過ユニットをその配列方向に沿って交互に洗
浄する、という技術的手段を採用した。
In order to achieve the above object, according to the present invention, at least a part of a biological reaction tank and a peripheral wall immersed therein along the flow direction of sewage flow through. A plurality of filtration units having a plurality of filtration bodies composed of an aqueous support, and a partition partitioning each filtration unit,
A sewage treatment apparatus provided with an aeration unit provided at a lower portion of a biological reaction tank, an aeration unit for washing disposed below the filtration unit, and a buffer tank having a water level lower than the water level of the biological reaction tank. And removing the treated water from the filtration unit, and selectively operating the cleaning aeration means to alternately wash the filtration units along the arrangement direction thereof, employing a technical means. .

【0006】[0006]

【発明の実施の形態】以下図面を参照して本発明の実施
例を説明する。図1は本発明の一実施例に係る汚水処理
装置の概略平面図、図2は図1のA−A線断面図であ
る。同図において、1は生物反応槽であり、生物反応槽
1は、その中央部に設けられた隔壁2により2つの区画
に分割され、且つ隔壁2の上部と下部には2つの区画中
の水が連通できるように上部連通部2Aと下部連通部2
Bが形成されている。生物反応槽1の右側区画には、ろ
過ユニット3が配置され、ろ過ユニット3に連通した集
水管7の排出端は緩衝槽(図示せず)中に落としこみ、
左側区画には散気管5が配置されている。各ろ過ユニッ
ト3の間は、ユニット間隔壁4で仕切られている。また
各ろ過ユニット3の下方には、洗浄用散気管6が配置さ
れている。この場合緩衝槽の水位を生物反応槽1の水位
より低く設定してあるため、集水管7のサイフォン効果
により、ろ過ユニット3内は常に水頭差による負圧が作
用する。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a schematic plan view of a sewage treatment apparatus according to one embodiment of the present invention, and FIG. 2 is a sectional view taken along line AA of FIG. In FIG. 1, reference numeral 1 denotes a biological reaction tank, and the biological reaction tank 1 is divided into two sections by a partition wall 2 provided at a central portion thereof, and water in the two sections is provided above and below the partition wall 2. Upper communication part 2A and lower communication part 2 so that
B is formed. In the right section of the biological reaction tank 1, a filtration unit 3 is disposed, and the discharge end of the water collecting pipe 7 communicating with the filtration unit 3 is dropped into a buffer tank (not shown).
An air diffuser 5 is arranged in the left section. Each filtration unit 3 is separated by a unit spacing wall 4. In addition, a cleaning air diffuser 6 is disposed below each filtration unit 3. In this case, since the water level of the buffer tank is set lower than the water level of the biological reaction tank 1, a negative pressure due to the head difference always acts in the filtration unit 3 due to the siphon effect of the water collecting pipe 7.

【0007】図3は、ろ過ユニット3を構成するろ過モ
ジュールの一部を切欠いた平面図、図4は図3のB−B
断面図である。両図において10はろ過モジュールであ
り、ろ過板11(間隔保持部材)とその表面に額縁状の
押え板18で固定されたろ過膜支持部材(スペーサ)1
2と、その表面に保持された通水性支持膜(以下ろ過膜
という)13とを有する。ろ過板11には図3に示す如
く、集水溝14がろ過板11の両面に縦横に形成されて
いる。ろ過板11の最上部に位置する両面の集水溝14
と連通する横孔15が穿設され、ろ過板11の端面から
横孔15に至るネジ孔16が設けられ、このネジ孔16
にろ過水を引き抜くための吸引管17が螺着されてい
る。吸引管17は集水管(図2参照)に連結され、ろ過
モジュール10から取出された処理水は集水管7を経由
して緩衝槽(図示せず)へ搬送される。
FIG. 3 is a plan view showing a part of a filtration module constituting the filtration unit 3 in a cut-away manner. FIG.
It is sectional drawing. In both figures, reference numeral 10 denotes a filtration module, which is a filtration plate 11 (spacing member) and a filtration membrane support member (spacer) 1 fixed to a surface thereof by a frame-shaped holding plate 18.
2 and a water-permeable supporting membrane (hereinafter referred to as a filtration membrane) 13 held on the surface thereof. As shown in FIG. 3, water collecting grooves 14 are formed on both sides of the filter plate 11 vertically and horizontally. Water collecting groove 14 on both sides located at the top of filter plate 11
And a screw hole 16 extending from the end surface of the filter plate 11 to the horizontal hole 15 is provided.
A suction pipe 17 for pulling out filtered water is screwed on. The suction pipe 17 is connected to a water collecting pipe (see FIG. 2), and the treated water extracted from the filtration module 10 is transported to a buffer tank (not shown) via the water collecting pipe 7.

【0008】ろ過膜13としては、例えば、ポリエステ
ル、ポリプロピレン等の高分子繊維からなる不織布や金
属製不織布を用い得る。この金属製不織布は厚さが0.
1から4mmで、その断面方向にも表面方向と同等の繊
維構造を有し、且つ表面方向の開口の大きさは10μm
より大きくなっている。ろ過膜の厚さは、厚すぎると汚
泥がろ過膜内に蓄積して目詰りを生じ易くなり、一方薄
すぎると機械的強度が低下してしまうので、0.1〜4
mm程度であることが望ましい。またろ過膜の目開き
は、分離粒径が10μm以上(好ましくは10〜200
μm)であることが望ましい。
As the filtration membrane 13, for example, a nonwoven fabric made of a polymer fiber such as polyester or polypropylene or a metal nonwoven fabric can be used. This metal nonwoven fabric has a thickness of 0.
1 to 4 mm, the cross-sectional direction has the same fiber structure as the surface direction, and the size of the opening in the surface direction is 10 μm
It is getting bigger. If the thickness of the filtration membrane is too large, sludge accumulates in the filtration membrane and clogging is likely to occur. On the other hand, if it is too small, the mechanical strength is reduced.
mm. The opening of the filtration membrane has a separation particle size of 10 μm or more (preferably 10 to 200 μm).
μm).

【0009】上記構成による汚水処理装置によれば、汚
水は次のようにして処理される。例えば最初沈殿池(図
示せず)から生物反応槽1へ流入した汚水(活性汚泥微
粒子と水との混合水)は散気管5からの空気バブリング
によって左側区画内で上昇流となり、隔壁2の上部連通
部2Aを通って右側区画に流れ、そこで下向流となっ
て、下部連通部2Bを経由し、再び左側区画に戻るよう
に循環する。この循環中に右側区画中に浸漬配置された
ろ過ユニット3によって、混合水中の活性汚泥微粒子が
ろ過ユニット3に捕捉される。すなわちろ過の初期には
活性汚泥微粒子はろ過膜の開口を通過するが、徐々にろ
過膜の表面に付着して開口を塞いでゆき、汚泥微粒子に
よるケーキ層が形成され、成長して、この活性汚泥微粒
子からなるケーキ層によるフィルター作用で水中の活性
汚泥微粒子が捕捉されて、ろ過作用が進行する。一方処
理水はろ過ユニット3中に設けられた集水管7を経由し
て緩衝槽(図示せず)に流入する。ろ過モジュール10
内では、水頭差よる差圧が作用して吸引ろ過が行われる
が、水頭と流束が比例するので、この差圧を水柱で50
0mm程度以内に設定することにより、透過流速が1〜
3m/day程度のものが得られる。
According to the sewage treatment apparatus having the above configuration, sewage is treated as follows. For example, the sewage (mixed water of activated sludge fine particles and water) flowing into the biological reaction tank 1 from the first sedimentation basin (not shown) becomes an ascending flow in the left compartment by air bubbling from the air diffuser 5, and the upper part of the partition 2 It flows to the right section through the communication section 2A, where it flows downward, passes through the lower communication section 2B, and circulates back to the left section again. During this circulation, the activated sludge fine particles in the mixed water are captured by the filtration unit 3 by the filtration unit 3 immersed in the right compartment. That is, the activated sludge fine particles pass through the opening of the filtration membrane in the early stage of filtration, but gradually adhere to the surface of the filtration membrane to close the opening, and a cake layer of the sludge fine particles is formed and grows. The activated sludge fine particles in the water are captured by the filter action of the cake layer composed of the sludge fine particles, and the filtration action proceeds. On the other hand, the treated water flows into a buffer tank (not shown) via a water collecting pipe 7 provided in the filtration unit 3. Filtration module 10
Inside, suction filtration is performed by the differential pressure due to the head difference, but since the head is proportional to the flux, this differential pressure is
By setting it within about 0 mm, the permeation flow rate becomes 1 to
About 3 m / day can be obtained.

【0010】透過流束が低下し、ろ過ユニット3に目詰
りが生じたと判断された場合は、次のようにしてろ過ユ
ニット3の洗浄を行う。まず汚水の流入方向に沿って上
流側のろ過ユニット3の下方に設置された洗浄用散気
管6により曝気を行うことにより、ろ過ユニット3
ろ過膜の表面に形成されたろ過層(ケーキ層)を洗浄す
る。次にろ過ユニット3の下方に設置された洗浄用散
気管6により曝気を行うことにより、ろ過ユニット3
の表面に形成されたろ過層(ケーキ層)を洗浄・除去す
る。このようにして汚水の流入方向に沿って上流側にあ
るろ過ユニットから順次洗浄するので、ろ過ユニットの
連続運転を行うことができる。この場合、各ろ過ユニッ
トはユニット間隔壁4で仕切られているので、任意のろ
過ユニットの下方にある散気管の曝気作用はそれに隣接
するろ過ユニットに波及せず、もってろ過ユニットから
取出された処理水の水質悪化を防止することができる。
If it is determined that the permeation flux has decreased and the filtration unit 3 has been clogged, the filtration unit 3 is washed as follows. By performing aeration by cleaning aeration tube 6 disposed on the lower filtration unit 3 1 on the upstream side is first along the inflow direction of the sewage, filtration layer formed on the surface of the filtration unit 3 1 of the filter membrane (cake Layer). By performing aeration by tracheal 6 next diffuser cleaning was installed in the lower filter unit 3 2, filtration unit 3 2
Wash and remove the filtration layer (cake layer) formed on the surface of. In this way, since the washing is sequentially performed from the upstream of the filtration unit along the inflow direction of the sewage, the continuous operation of the filtration unit can be performed. In this case, since each filtration unit is separated by the unit spacing wall 4, the aeration effect of the air diffuser below any of the filtration units does not spread to the filtration unit adjacent thereto, and the processing removed from the filtration unit Water quality deterioration can be prevented.

【0011】[0011]

【実施例】以下の実施例により本発明をより具体的に説
明する。図1〜4に示す装置により次の条件で汚水処理
を行った。汚水は、BOD180mg/L、SS130
mg/Lの下水を使用し、実効容量1m3の生物反応槽
により、曝気槽の滞留時間を6時間とする標準曝気活性
汚泥の条件で連続処理を行った。この場合、生物反応槽
内には、側面面積40cm×40cmのろ過モジュール
を有するろ過ユニット5個を浸漬配置し、自然流下で処
理水を取出した。ろ過モジュールとしては、ABS樹脂
製ろ過板の表面(両面)にネットスペーサを固着し、そ
の表面にポリエステル製不織布(厚さ0.12mm、目
付15g/m、表面方向の開口の平均大きさ120μ
m)を固着したものを使用した。ろ過ユニットの運転開
始から30min間隔にて、洗浄用散気管から10m
/m/hrの流量で3minの曝気洗浄をろ過ユニッ
ト3から3まで順次行った。また比較のために、ユ
ニット間隔壁を除去した以外は、上記と同様の条件で汚
水処理実験を行った。
The present invention will be described more specifically with reference to the following examples. Sewage treatment was performed under the following conditions using the apparatus shown in FIGS. Sewage is BOD180mg / L, SS130
Using sewage of mg / L, continuous treatment was performed in a biological reaction tank having an effective volume of 1 m 3 under the conditions of standard aeration activated sludge in which the residence time in the aeration tank was 6 hours. In this case, five filtration units each having a filtration module with a side surface area of 40 cm × 40 cm were immersed in the biological reaction tank, and treated water was taken out under natural flow. As the filtration module, a net spacer is fixed to the surface (both sides) of an ABS resin filter plate, and a polyester nonwoven fabric (thickness: 0.12 mm, basis weight: 15 g / m 2 , average opening size in the surface direction: 120 μm)
m) was used. At an interval of 30 min from the start of operation of the filtration unit, 10 m 3 from the cleaning air diffuser
/ M sequentially conducted 2 / hr of the aeration washing 3min at a flow rate from the filtration unit 3 1 to 3 5. For comparison, a sewage treatment experiment was performed under the same conditions as above except that the unit spacing wall was removed.

【0012】上記実験の結果、ろ過ユニット間にユニッ
ト間隔壁を設けない場合は、BOD25mg/L、SS
20mg/L程度の処理水質にとどまった。これに対
し、本発明の場合は、BOD10mg/L、SS5mg
/Lと処理水質が改善された。
As a result of the above experiment, when no unit spacing wall is provided between the filtration units, BOD 25 mg / L, SS
The treated water quality was about 20 mg / L. In contrast, in the case of the present invention, BOD 10 mg / L, SS 5 mg
/ L and treated water quality were improved.

【0013】[0013]

【発明の効果】本発明は、上記構成としたから、複数の
ろ過ユニットの連続運転が可能で、しかも処理水の水質
の低下を防止することができる。
According to the present invention having the above-mentioned structure, a plurality of filtration units can be operated continuously, and a decrease in the quality of treated water can be prevented.

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

【図1】本発明の一実施例に係わる汚水処理装置の概略
縦平面図である。
FIG. 1 is a schematic vertical plan view of a sewage treatment apparatus according to one embodiment of the present invention.

【図2】図1のA−A断面図である。FIG. 2 is a sectional view taken along line AA of FIG.

【図3】本発明の一実施例に係わるろ過モジュールの一
部破断した平面図である。
FIG. 3 is a partially broken plan view of a filtration module according to one embodiment of the present invention.

【図4】図3のB−B断面図である。FIG. 4 is a sectional view taken along line BB of FIG. 3;

【符号の説明】[Explanation of symbols]

1 生物反応槽、2 隔壁、3 ろ過ユニット、4 ユ
ニット間隔壁、5 散気管、6 洗浄用散気管、7 集
水管、10 ろ過モジュール、11 ろ過板、12 ろ
過膜支持部材、13 ろ過膜
DESCRIPTION OF SYMBOLS 1 Biological reaction tank, 2 partition walls, 3 filtration units, 4 unit interval walls, 5 diffuser tubes, 6 diffuser tubes for washing, 7 water collecting tubes, 10 filtration modules, 11 filtration plates, 12 filtration membrane support members, 13 filtration membranes

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01D 29/04 510D 520A 530A (71)出願人 000001063 栗田工業株式会社 東京都新宿区西新宿3丁目4番7号 (71)出願人 000006655 新日本製鐵株式会社 東京都千代田区大手町2丁目6番3号 (72)発明者 大同 均 東京都新宿区西新宿二丁目8番1号東京都 下水道局内 (72)発明者 麻生 栄治 東京都新宿区西新宿二丁目8番1号東京都 下水道局内 (72)発明者 長谷川 哲夫 埼玉県熊谷市三ヶ尻5200番地日立金属株式 会社環境エンジニアリング事業部内 (72)発明者 永井 睦郎 埼玉県熊谷市三ケ尻5200番地日立金属株式 会社環境エンジニアリング事業部内 (72)発明者 岸根 義尚 東京都新宿区西新宿三丁目4番7号栗田工 業株式会社内 (72)発明者 澤田 繁樹 東京都新宿区西新宿三丁目4番7号栗田工 業株式会社内 (72)発明者 坂田 守生 東京都千代田区大手町2−6−3新日本製 鐵株式会社内 (72)発明者 福永 和久 千葉県富津市新富20−1新日本製鐵株式会 社内 Fターム(参考) 4D028 BC12 BC17 BD17 4D029 AA01 AB06 BB10 DD01 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification FI FI Theme Court ゛ (Reference) B01D 29/04 510D 520A 530A (71) Applicant 000001063 Kurita Kogyo Co., Ltd. 3-4-1 Nishishinjuku, Shinjuku-ku, Tokyo No. 7 (71) Applicant 000006655 Nippon Steel Corporation 2-6-3, Otemachi, Chiyoda-ku, Tokyo (72) Inventor Hitoshi Daido 2-2-1, Nishishinjuku, Shinjuku-ku, Tokyo Inside the Tokyo Sewerage Bureau ( 72) Inventor Eiji Aso 2-2-1, Nishi-Shinjuku, Shinjuku-ku, Tokyo Tokyo Metropolitan Government Sewerage Bureau Mutsuro 5200 Sankajiri, Kumagaya City, Saitama Prefecture Hitachi Metals Co., Ltd.Environmental Engineering Division (72) Inventor Yoshinao Kishine Kurita Kogyo Co., Ltd., 3-4-7 Nishi-Shinjuku, Shinjuku-ku, Tokyo (72) Inventor Shigeki Sawada Kurita Kogyo Co., Ltd., 3-4-2-7 Nishi-Shinjuku, Shinjuku-ku, Tokyo Morio Sakata 2-6-3 Otemachi, Chiyoda-ku, Tokyo Nippon Steel Corporation (72) Inventor Kazuhisa Fukunaga 20-1 Shintomi, Futtsu-shi, Chiba Nippon Steel Corporation F-term (reference) 4D028 BC12 BC17 BD17 4D029 AA01 AB06 BB10 DD01

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 生物反応槽と、その内部に汚水の流れ方
向に沿って浸漬配置された周囲壁の少なくとも一部が通
水性支持体からなる複数のろ過ユニットと、各ろ過ユニ
ットを仕切る隔壁と、生物反応槽の下部に設けられた曝
気手段と、前記ろ過ユニットの下方に配置されたろ過ユ
ニット洗浄用散気手段と、生物反応槽の水位より低い水
位を有する緩衝槽とを有する汚水処理装置に汚水を供給
し、前記ろ過ユニットから処理水を取出すと共に、前記
洗浄用散気手段を選択的に作動させて、前記ろ過ユニッ
トをその配列方向に沿って交互に洗浄することを特徴と
する汚水処理方法。
1. A biological reaction tank, a plurality of filtration units having at least a portion of a peripheral wall immersed and disposed in the interior thereof along the flow direction of sewage, and a plurality of filtration units each formed of a water-permeable support; A sewage treatment apparatus comprising: an aeration unit provided at a lower part of a biological reaction tank; a filtration unit cleaning aeration unit provided below the filtration unit; and a buffer tank having a water level lower than that of the biological reaction tank. Sewage, supplying treated water from the filtration unit, removing treated water from the filtration unit, and selectively operating the cleaning air diffuser to alternately wash the filtration unit along the arrangement direction thereof. Processing method.
JP11104707A 1999-04-13 1999-04-13 Sewage treatment Pending JP2000296302A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11104707A JP2000296302A (en) 1999-04-13 1999-04-13 Sewage treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11104707A JP2000296302A (en) 1999-04-13 1999-04-13 Sewage treatment

Publications (1)

Publication Number Publication Date
JP2000296302A true JP2000296302A (en) 2000-10-24

Family

ID=14387967

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11104707A Pending JP2000296302A (en) 1999-04-13 1999-04-13 Sewage treatment

Country Status (1)

Country Link
JP (1) JP2000296302A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009527349A (en) * 2006-02-23 2009-07-30 ナムローゼ・フエンノートシャップ・ベカート・ソシエテ・アノニム Filter plate used in filter stack
CN110404307A (en) * 2019-08-29 2019-11-05 威孔过滤科技(苏州)有限公司 Board-like filter plate and its application is concentrated in precision

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009527349A (en) * 2006-02-23 2009-07-30 ナムローゼ・フエンノートシャップ・ベカート・ソシエテ・アノニム Filter plate used in filter stack
CN110404307A (en) * 2019-08-29 2019-11-05 威孔过滤科技(苏州)有限公司 Board-like filter plate and its application is concentrated in precision

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