JPH0985243A - Wastewater treatment device and operating method therefor - Google Patents

Wastewater treatment device and operating method therefor

Info

Publication number
JPH0985243A
JPH0985243A JP24754395A JP24754395A JPH0985243A JP H0985243 A JPH0985243 A JP H0985243A JP 24754395 A JP24754395 A JP 24754395A JP 24754395 A JP24754395 A JP 24754395A JP H0985243 A JPH0985243 A JP H0985243A
Authority
JP
Japan
Prior art keywords
liquid
wastewater treatment
treated
membrane
regions
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
JP24754395A
Other languages
Japanese (ja)
Inventor
Katsuji Uryu
勝嗣 瓜生
Yasutoshi Shimizu
康利 清水
Atsuo Watanabe
敦夫 渡辺
Yuichi Okuno
祐一 奥野
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.)
Toto Ltd
Original Assignee
Toto Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toto Ltd filed Critical Toto Ltd
Priority to JP24754395A priority Critical patent/JPH0985243A/en
Publication of JPH0985243A publication Critical patent/JPH0985243A/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 improve the scraping effect by liquid to be treated on the surface of a separating membrane and provide the permeable flux stable at all times by dividing the inside of a treatment tank into a plurality of areas, providing a circulating flow generating device for circulating the liquid to be treated in the treatment tank and providing membrane separating devices in central sections of respective areas. SOLUTION: The inside of a treatment tank 20 for storing liquid to be treated is divided into a plurality of areas S1-S3 by interstructures 21, 21 in the up and down direction, and the upper and lower sections of the areas S1-S3 are communicated with adjoining areas. Air is fed into the treatment tank 20 by an aeration device 23 disposed on a bottom section of the central area S1, and an upward flow of the liquid to be treated is formed in the area S1, while a downward flow is formed in the areas S2 and S3, and a circulating flow is formed as a whole. Membrane separating devices 25 in which hollow yarn membranes are hung in the lateral direction are disposed between collection pipes 26 connected with a suction pump 29 almost on the central sections of respective areas S1-S3. Cake layers accumulated on the membrane surfaces can be released efficiently by the above arrangement, and a permeable flux can be retained stably.

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】本発明は家庭からの廃水や工
場廃水を膜分離装置を用いて処理する廃水処理装置とそ
の運転方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wastewater treatment apparatus for treating domestic wastewater and industrial wastewater using a membrane separator and a method for operating the same.

【0002】[0002]

【従来の技術】生活廃水中には窒素成分等が多量に含ま
れており、これがそのまま川や海に流されると、環境汚
染の原因となる。そこで、微生物による硝化・脱窒プロ
セスを経て窒素成分をガス化して除去する廃水処理装置
が知られている。そして、この廃水処理装置として、被
処理液から微生物(菌体)を含む活性汚泥を分離し、処
理が終了した液のみを速やかに処理装置外に取り出すた
めに、膜分離装置を備えたものがある。
2. Description of the Related Art Domestic wastewater contains a large amount of nitrogen components and the like, and if it is directly discharged into a river or the sea, it will cause environmental pollution. Therefore, there is known a wastewater treatment device that gasifies and removes nitrogen components through a nitrification / denitrification process by microorganisms. Then, as this wastewater treatment device, one having a membrane separation device for separating activated sludge containing microorganisms (bacteria) from the liquid to be treated and quickly taking out only the liquid after the treatment is taken out of the treatment device. is there.

【0003】膜分離装置を備えた廃水処理装置として
は、例えば、特開平4−190890号公報、特開平4
−247265号公報、特開平4−290529号公報
及び特開平7−227525号公報がある。特開平4−
190890号公報には、生物処理槽内を仕切壁で、処
理1室、処理2室に分け、処理1室に攪拌機を、処理2
室に分離膜を設け、処理1室内からの循環流を処理2室
の分離膜に供給しつつ処理を行う装置が開示されてい
る。特開平4−247265号公報には、生物処理槽内
にバッフル板(仕切板)で囲まれる領域を形成し、この
領域の底部に散気装置(曝気装置)を、上部に膜分離装
置を配置し、散気装置にてバッフル板で囲まれる領域内
に上昇流を形成する装置が開示されている。特開平4−
290529号公報には、生物処理槽内を仕切壁で複数
の領域(チャンバー)に分け、各領域内に板状分離膜を
上下方向に配置し、各領域内の底部に散気装置を配置
し、各領域内で循環流が生じるようにした装置が開示さ
れている。更に、特開平7−227525号公報には、
生物処理槽内に複数の板状分離膜を上下方向に配置する
とともに、板状分離膜の下方に散気装置を配置した装置
が開示されている。
As a wastewater treatment apparatus equipped with a membrane separation device, for example, JP-A-4-190890 and JP-A-4190890
There are JP-A-247265, JP-A-4-290529 and JP-A-7-227525. Japanese Patent Laid-Open No. 4-
In JP-A-190890, the inside of the biological treatment tank is divided into a treatment chamber and a treatment chamber by a partition wall, and an agitator is provided in the treatment chamber.
An apparatus is disclosed in which a separation membrane is provided in a chamber and a process is performed while supplying a circulating flow from the treatment 1 chamber to the separation membrane in the treatment 2 chamber. In Japanese Patent Laid-Open No. 4-247265, a region surrounded by a baffle plate (partition plate) is formed in a biological treatment tank, an air diffuser (aeration device) is arranged at the bottom of this region, and a membrane separation device is arranged at the top. However, a device for forming an ascending flow in a region surrounded by a baffle plate by an air diffuser is disclosed. Japanese Patent Laid-Open No. 4-
In Japanese Patent No. 290529, a biological treatment tank is divided into a plurality of regions (chambers) by a partition wall, a plate-like separation membrane is vertically arranged in each region, and an air diffuser is arranged at the bottom of each region. , A device that allows a circulating flow to occur in each region is disclosed. Further, in Japanese Patent Laid-Open No. 7-227525,
An apparatus is disclosed in which a plurality of plate-shaped separation membranes are arranged vertically in a biological treatment tank, and an air diffuser is arranged below the plate-shaped separation membranes.

【0004】[0004]

【発明が解決しようとする課題】先ず、特開平7−22
7525号公報に開示される装置では、被処理液が循環
流を形成しないので、分離膜表面に対する被処理液によ
る掻き取り効果が小さく、透過流束の回復が期待できな
い。
First, Japanese Patent Laid-Open No. 7-22
In the device disclosed in Japanese Patent No. 7525, since the liquid to be treated does not form a circulating flow, the effect of scraping the liquid to be treated on the surface of the separation membrane is small, and recovery of the permeation flux cannot be expected.

【0005】また、特開平4−190890号公報及び
特開平4−247265号公報に開示される装置にあっ
ては、循環流を形成して分離膜表面の被処理液の流速を
速くし掻き取り効果を高めることが可能であるが、特開
平4−190890号公報に開示の装置にあっては処理
1室が、特開平4−247265号公報に開示の装置に
あってはバッフル板の外側の空間がそれぞれ膜分離に関
与しない空間になり、膜の投影面積が小さくなり、装置
全体としての効率が悪い。
Further, in the devices disclosed in JP-A-4-190890 and JP-A-4-247265, a circulation flow is formed to increase the flow velocity of the liquid to be treated on the surface of the separation membrane and scrape it. Although it is possible to enhance the effect, in the apparatus disclosed in Japanese Patent Laid-Open No. 4-190890, the processing 1 chamber is provided, and in the apparatus disclosed in Japanese Patent Laid-Open No. 4-247265, the outside of the baffle plate is provided. Each space becomes a space that does not participate in the membrane separation, the projected area of the membrane becomes small, and the efficiency of the entire apparatus is poor.

【0006】一方、特開平4−290529号公報に開
示される装置にあっては、仕切壁で区切られた全ての領
域内に分離膜を設け、更に循環流を形成するようにして
いるが、分離膜自体が板状の分離膜であるので、分離膜
自体が壁になってしまう。その結果分離膜表面での流速
が小さくなり、安定した透過流束が得られない。
On the other hand, in the apparatus disclosed in Japanese Patent Laid-Open No. 4-290529, a separation membrane is provided in all the areas partitioned by the partition wall to further form a circulating flow. Since the separation membrane itself is a plate-shaped separation membrane, the separation membrane itself becomes a wall. As a result, the flow velocity on the surface of the separation membrane becomes small, and a stable permeation flux cannot be obtained.

【0007】更に、上述した各先行技術にあっては処理
槽内の被処理液の流れが常に一定方向なので、繊維が膜
に絡まると取れにくい。
Furthermore, in each of the above-mentioned prior arts, the flow of the liquid to be treated in the treatment tank is always in a constant direction, so that it is difficult to remove the fibers when they are entangled in the membrane.

【0008】[0008]

【課題を解決するための手段】上記課題を解決すべく本
発明に係る廃水処理装置は、被処理液を貯留する処理槽
内を上下方向の隔壁にて複数の領域に仕切り、これら複
数の領域のうち互いに隣接する領域は上部及び下部にて
連通せしめ、また処理槽内には互いに隣接する領域の一
方を上昇流とし、他方を下降流とすることで被処理液を
循環せしめる循環流発生装置を設け、更に各領域内の流
速が速くなる中央部に集水管間に中空糸膜を横方向に架
設した膜分離装置を配設した。
In order to solve the above-mentioned problems, a wastewater treatment apparatus according to the present invention divides the inside of a treatment tank for storing a liquid to be treated into a plurality of regions by vertical partition walls, Areas adjacent to each other are communicated with each other at the upper and lower parts, and a circulation flow generator for circulating the liquid to be treated by making one of the areas adjacent to each other into an upward flow and the other into a downward flow in the processing tank. Further, a membrane separation device having a hollow fiber membrane laterally installed between water collecting pipes was arranged at the central portion where the flow velocity in each region was high.

【0009】ここで、前記循環流発生装置としては曝気
装置、若しくはプロペラ装置が考えられ、曝気装置を用
いた場合には、循環流のうちの上昇流が気液二相流とな
り、プロペラ装置を用いた場合には上昇流、下降流とも
液体のみになる。
Here, an aeration device or a propeller device can be considered as the circulation flow generation device. When an aeration device is used, the ascending flow of the circulation flow becomes a gas-liquid two-phase flow and the propeller device is used. When used, both the upflow and downflow are liquid only.

【0010】また、本発明に係る廃水処理装置の運転方
法は、被処理液を貯留する処理槽内を上下方向の隔壁に
て複数の領域に仕切り、これら複数の領域のうち互いに
隣接する領域は上部及び下部にて連通するとともに各領
域内に膜分離装置を配設した廃水処理装置の運転方法に
おいて、所定時間互いに隣接する領域の一方を上昇流と
し他方を下降流として循環流を形成した後、上昇流と下
降流の向きを反転して逆向きの循環流を形成するように
した。
Further, in the method for operating the wastewater treatment apparatus according to the present invention, the inside of the treatment tank for storing the liquid to be treated is partitioned into a plurality of regions by partition walls in the vertical direction. In a method of operating a wastewater treatment device in which upper and lower parts communicate with each other and a membrane separator is arranged in each region, after forming a circulating flow by making one of the regions adjacent to each other an upflow and the other downflow for a predetermined time. , The direction of the ascending flow and the direction of the descending flow were reversed to form the circulation flow in the opposite direction.

【0011】尚、安定した透過流束を得るためには、循
環流の速度を0.1m以上1.0m以下とし、被処理液
の濃度を8000mg/リットル以上50000mg/リットル
以下とすることが好ましい。
In order to obtain a stable permeation flux, it is preferable that the speed of the circulation flow is 0.1 m or more and 1.0 m or less and the concentration of the liquid to be treated is 8000 mg / l or more and 50,000 mg / l or less. .

【0012】[0012]

【発明の実施の形態】以下に本発明の実施の形態を添付
図面に基づいて説明する。図1は本発明に係る廃水処理
装置の効果を確認するために製作した実験装置の全体図
であり、実験装置は被処理液を貯留する処理槽1内を上
下方向の隔壁2にて第1領域3と第2領域4に分け、各
領域3,4内に管状膜5,5を設置し、第1領域3の底
部には外部のブロア6からエアが供給される曝気装置7
を設置している。
Embodiments of the present invention will be described below with reference to the accompanying drawings. FIG. 1 is an overall view of an experimental device manufactured for confirming the effect of the wastewater treatment device according to the present invention. The experimental device has a first partition 2 in a vertical direction in a treatment tank 1 for storing a liquid to be treated. The region 3 and the second region 4 are divided, and the tubular membranes 5 and 5 are installed in the respective regions 3 and 4, and the aeration device 7 in which air is supplied to the bottom of the first region 3 from an external blower 6
Is installed.

【0013】また、前記各管状膜5,5には集水管8,
8を接続し、これら集水管8,8を電子天秤9,9上に
セットした容器10,10につなげ、更に容器10,1
0内をアスピレータポンプ11にて減圧している。尚、
12は電子天秤9,9につながるデータ収集用パソコン
である。
Further, a water collecting pipe 8 is provided on each of the tubular membranes 5 and 5.
8 is connected, and these water collecting pipes 8 and 8 are connected to the containers 10 and 10 set on the electronic balance 9 and 9, and the containers 10 and 1 are further connected.
The inside of 0 is decompressed by the aspirator pump 11. still,
Reference numeral 12 is a personal computer for data collection connected to the electronic balances 9, 9.

【0014】以上において、アスピレータポンプ11を
駆動するとともに、曝気装置7からエアを処理槽1内に
供給すると、曝気装置7は第1領域3の直下に位置する
ため、第1領域3内に上昇流が形成され、この上昇流が
形成されることで第2領域4内の被処理液は下方から第
1領域3内に入り込み、処理槽1内に循環流が形成され
る。
In the above, when the aspirator pump 11 is driven and air is supplied from the aeration device 7 into the processing tank 1, the aeration device 7 is located immediately below the first region 3 and thus rises into the first region 3. A flow is formed, and by the formation of this upward flow, the liquid to be treated in the second region 4 enters the first region 3 from below, and a circulation flow is formed in the treatment tank 1.

【0015】ところで、上記の曝気量と循環流の関係を
表わしたのが図2であり、この図から、上昇流線速度は
下降流線速度に比べて僅かに高くなるが、気泡のボイド
率分を補正すると、両者は一致し、しかも線速度は曝気
量の0.3乗に比例することが分る。
By the way, FIG. 2 shows the relationship between the aeration amount and the circulation flow. From this figure, the upward streamline velocity is slightly higher than the downward streamline velocity, but the void fraction of the bubbles is high. When the minute is corrected, it is found that the two agree with each other, and the linear velocity is proportional to the aeration amount to the power of 0.3.

【0016】吸引濾過実験での透過流束は、濾過開始よ
り2時間〜8時間でほぼ一定値を示した。そこで、1時
間当りの透過流束の低下率が5%以下になった時点での
透過流束値を透過流束の定常値とした。この定常値と前
記循環流の線速度との関係を図3に示す。
The permeation flux in the suction filtration experiment showed a substantially constant value from 2 hours to 8 hours after the start of filtration. Therefore, the permeation flux value at the time point when the rate of decrease of permeation flux per hour became 5% or less was taken as the steady value of the permeation flux. The relationship between this steady value and the linear velocity of the circulating flow is shown in FIG.

【0017】図3から、線速度が0.1m以上1.0m
以下の範囲では、気泡が存在する上昇流が形成される領
域3における透過流束の定常値と、気泡が存在しない下
降流が形成される領域4における透過流束の定常値とが
ほぼ等しくことが分った。尚、被処理液の濃度について
は8000mg/リットル以上50000mg/リットル以下が
好ましく、20000mg/リットルより大きくなると高粘
度となり動力費が高くなるため、望ましくは8000m
g/リットル以上20000mg/リットル以下とする。
From FIG. 3, the linear velocity is 0.1 m or more and 1.0 m.
In the following range, the steady-state value of the permeation flux in the region 3 in which the upward flow with bubbles is formed and the steady-state value of the permeation flux in the region 4 in which the downward flow without bubbles are formed are substantially equal to each other. I understood. The concentration of the liquid to be treated is preferably 8,000 mg / liter or more and 50,000 mg / liter or less, and when it is more than 20,000 mg / liter, the viscosity becomes high and the power cost becomes high.
It should be g / liter or more and 20000 mg / liter or less.

【0018】以上の実験から、透過流束を所定範囲とす
るのであれば、気液二相流中に分離膜を浸漬しなくと
も、膜面に対する掻き取り効果が発揮されるといえる。
From the above experiments, it can be said that if the permeation flux is within the predetermined range, the scraping effect on the membrane surface can be exhibited without immersing the separation membrane in the gas-liquid two-phase flow.

【0019】図4は上記の知見に基づいて作製した本発
明に係る廃水処理装置の断面図、図5は図4のAーA方
向断面図であり、廃水処理装置は被処理液を貯留する処
理槽20内を上下方向の隔壁21,21にて複数の領域
S1,S2,S3に仕切り、これら領域は隣接する領域
と上部及び下部にて連通している。
FIG. 4 is a sectional view of a wastewater treatment apparatus according to the present invention produced based on the above findings, and FIG. 5 is a sectional view taken along the line AA of FIG. 4, in which the wastewater treatment apparatus stores the liquid to be treated. The inside of the processing tank 20 is partitioned into a plurality of regions S1, S2, S3 by partition walls 21 and 21 in the vertical direction, and these regions communicate with the adjacent regions at the upper and lower portions.

【0020】また、中央の領域S1の底部にはブロア2
2からのエアを処理槽20内に供給する曝気装置23を
配置している。而して、曝気装置23から供給されるエ
アにて中央の領域S1には被処理液の上昇流が形成さ
れ、また左右の領域S2,S3には下降流が形成され、
全体として循環流が形成される。
A blower 2 is provided at the bottom of the central area S1.
An aeration device 23 that supplies the air from 2 into the processing tank 20 is arranged. Thus, due to the air supplied from the aeration device 23, an upflow of the liquid to be treated is formed in the central region S1, and a downflow is formed in the left and right regions S2 and S3.
A circulating flow is formed as a whole.

【0021】尚、循環流を形成する装置としては、図6
に示すようなプロペラ装置24を配置してもよい。この
場合は、領域S1内に気液二相の上昇流は形成されない
が、全体として循環流は形成される。
An apparatus for forming a circulating flow is shown in FIG.
You may arrange | position the propeller apparatus 24 as shown in FIG. In this case, a gas-liquid two-phase upward flow is not formed in the region S1, but a circulating flow is formed as a whole.

【0022】また、各領域S1,S2,S3の略中央部
には膜分離装置25を配置している。膜分離装置25は
左右に離間した上下方向の集水管26間に中空糸膜27
を横方向に架設してなり、集水管26をパイプ28を介
して吸引ポンプ29に接続している。
Further, a membrane separation device 25 is arranged at a substantially central portion of each of the areas S1, S2 and S3. The membrane separation device 25 includes a hollow fiber membrane 27 between water collecting pipes 26 in the vertical direction which are separated from each other in the left and right directions.
Is horizontally installed, and the water collection pipe 26 is connected to a suction pump 29 via a pipe 28.

【0023】ここで、各領域S1,S2,S3の中央部
は循環流の線速度が最も速くなる箇所であり、本発明に
あっては、膜分離装置として中空糸膜を用いているた
め、線速度が速くなる箇所に膜を設置できることにな
り、効率よく膜表面に堆積したケーキ層を剥離し、透過
流束を維持することができる。因みに、板状の分離膜を
設置した場合には膜自体が隔壁になり、膜表面の線速度
は極めて小さくなる。
Here, the central portion of each of the regions S1, S2, S3 is a portion where the linear velocity of the circulating flow is the highest, and in the present invention, since the hollow fiber membrane is used as the membrane separation device, The membrane can be installed at a location where the linear velocity is high, and the cake layer deposited on the membrane surface can be efficiently separated to maintain the permeation flux. Incidentally, when a plate-shaped separation membrane is installed, the membrane itself becomes a partition wall, and the linear velocity on the membrane surface becomes extremely small.

【0024】以上において、吸引ポンプ29を駆動する
とともに曝気装置23からエアを供給し、処理槽20内
に循環流を形成しつつ、被処理液の固液分離を行う。こ
こで、図示例にあっては処理槽20を単独で示したが、
処理槽20を別の嫌気性処理室或いは好気性処理室に一
体的に接続してもよい。
In the above, the suction pump 29 is driven and air is supplied from the aeration device 23 to form a circulating flow in the processing tank 20 while performing solid-liquid separation of the liquid to be processed. Here, in the illustrated example, the processing tank 20 is shown alone,
The treatment tank 20 may be integrally connected to another anaerobic treatment chamber or an aerobic treatment chamber.

【0025】図7は別実施例を示す図4と同様の断面
図、図8は図7に示した装置の運転方法を示す図であ
り、この実施例にあっては領域S1の底部に曝気装置2
3aを配置し、領域S2,S3の底部に曝気装置23b
を配置している。そして、曝気装置23aと曝気装置2
3bの運転を弁30を切換えることで交互に行うこと
で、処理槽20内に形成される循環流の方向が一定時間
毎に反転するようにしている。
FIG. 7 is a sectional view similar to FIG. 4 showing another embodiment, and FIG. 8 is a diagram showing an operating method of the apparatus shown in FIG. 7. In this embodiment, the bottom of the region S1 is aerated. Device 2
3a is arranged, and the aeration device 23b is provided at the bottom of the regions S2 and S3.
Has been arranged. Then, the aeration device 23a and the aeration device 2
The operation of 3b is alternately performed by switching the valve 30 so that the direction of the circulation flow formed in the processing tank 20 is reversed at regular intervals.

【0026】このように、循環流の向きを一定時間毎に
反転することで、中空糸膜27に絡まってしまった繊維
などを有効に剥がすことができる。
In this way, by inverting the direction of the circulating flow at regular intervals, the fibers and the like entangled in the hollow fiber membrane 27 can be effectively removed.

【0027】[0027]

【発明の効果】以上に説明した如く本発明に係る廃水処
理装置は、被処理液を貯留する処理槽内を上下方向の隔
壁にて複数の領域に仕切り、これら複数の領域のうち互
いに隣接する領域は上部及び下部にて連通せしめ、また
処理槽内には互いに隣接する領域の一方を上昇流とし、
他方を下降流とすることで被処理液を循環せしめる曝気
装置やプロペラ装置等の循環流発生装置を設け、更に各
領域内の流速が速くなる中央部に集水管間に中空糸膜を
横方向に架設した膜分離装置を配設したので、分離膜表
面に対する被処理液による掻き取り効果を高め、安定し
た透過流束が得られる。しかも、全ての領域内に膜分離
装置を配設しているので、膜設置投影面積の比率を大き
くでき、結果として装置を小型化することができる。
As described above, in the wastewater treatment apparatus according to the present invention, the inside of the treatment tank for storing the liquid to be treated is partitioned into a plurality of regions by vertical partition walls, and these regions are adjacent to each other. The regions are made to communicate with each other at the upper part and the lower part, and one of the regions adjacent to each other is set as an upflow in the processing tank,
A circulation flow generator such as an aeration device or a propeller device that circulates the liquid to be treated by setting the other as a downward flow is installed, and a hollow fiber membrane is laterally placed between the water collection pipes in the central part where the flow velocity in each region becomes faster. Since the membrane separation device installed over the separation membrane is provided, the effect of scraping the surface of the separation membrane with the liquid to be treated is enhanced, and a stable permeation flux can be obtained. Moreover, since the membrane separation device is arranged in all the regions, the ratio of the projected area of the membrane installation can be increased, and as a result, the device can be downsized.

【0028】また、膜分離装置の運転方法として、一定
時間毎に循環流の流れを逆転するようにしたので、膜に
絡まった繊維等を運転中に取り除くことができる。特
に、循環流の速度を0.1m以上1.0m以下とし、ま
た被処理液の濃度を8000mg/リットル以上50000
mg/リットル以下とすることで安定した透過流束を得るこ
とができる。
Further, as a method of operating the membrane separation device, the flow of the circulating flow is reversed at regular intervals, so that the fibers entangled in the membrane can be removed during operation. In particular, the circulation flow velocity is set to 0.1 m or more and 1.0 m or less, and the concentration of the liquid to be treated is 8000 mg / liter or more and 50,000 or more.
A stable permeation flux can be obtained by setting it to be mg / liter or less.

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

【図1】本発明に係る廃水処理装置の効果を確認するた
めに製作した実験装置の全体図
FIG. 1 is an overall view of an experimental device manufactured to confirm the effects of a wastewater treatment device according to the present invention.

【図2】曝気量と循環流の線速度との関係を示すグラフFIG. 2 is a graph showing the relationship between the amount of aeration and the linear velocity of the circulating flow.

【図3】循環流の線速度と透過流束(定常値)との関係
を示すグラフ
FIG. 3 is a graph showing the relationship between the linear velocity of the circulating flow and the permeation flux (steady value).

【図4】本発明に係る廃水処理装置の断面図FIG. 4 is a sectional view of a wastewater treatment device according to the present invention.

【図5】図4のAーA方向断面図5 is a sectional view taken along line AA of FIG.

【図6】別実施例を示す図4と同様の断面図FIG. 6 is a sectional view similar to FIG. 4 showing another embodiment.

【図7】別実施例を示す図4と同様の断面図FIG. 7 is a sectional view similar to FIG. 4, showing another embodiment.

【図8】図7に示した装置の運転方法を示す図FIG. 8 is a diagram showing a method of operating the apparatus shown in FIG.

【符号の説明】[Explanation of symbols]

1…処理槽、2…隔壁、3…第1領域、4…第2領域、
5…管状膜、6…ブロア、7…曝気装置、8…集水管、
9…電子天秤、20…処理槽、21…隔壁、23,23
a,23b…曝気装置、24…プロペラ装置、25…膜
分離装置、26…集水管、27…中空糸膜、29…吸引
ポンプ、30…切換え弁、S1,S2,S3…領域。
1 ... Processing tank, 2 ... Partition wall, 3 ... 1st area | region, 4 ... 2nd area | region,
5 ... Tubular membrane, 6 ... Blower, 7 ... Aeration device, 8 ... Water collection pipe,
9 ... Electronic balance, 20 ... Processing tank, 21 ... Partition wall, 23, 23
a, 23b ... Aeration device, 24 ... Propeller device, 25 ... Membrane separation device, 26 ... Water collecting pipe, 27 ... Hollow fiber membrane, 29 ... Suction pump, 30 ... Switching valve, S1, S2, S3 ... Region.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 渡辺 敦夫 福岡県北九州市小倉北区中島2丁目1番1 号 東陶機器株式会社内 (72)発明者 奥野 祐一 福岡県北九州市小倉北区中島2丁目1番1 号 東陶機器株式会社内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Atsuo Watanabe 2-1, 1-1 Nakajima, Kokurakita-ku, Kitakyushu, Fukuoka Prefecture Totoki Equipment Co., Ltd. (72) Yuichi Okuno 2 Nakajima, Kokurakita-ku, Kitakyushu, Fukuoka 1st-1st Totoki Equipment Co., Ltd.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 被処理液を貯留する処理槽内を上下方向
の隔壁にて複数の領域に仕切り、これら複数の領域のう
ち互いに隣接する領域は上部及び下部にて連通し、また
処理槽内には互いに隣接する領域の一方を上昇流とし、
他方を下降流とすることで被処理液を循環せしめる循環
流発生装置を設け、更に各領域内の流速が速くなる中央
部に集水管間に中空糸膜を横方向に架設した膜分離装置
を配設したことを特徴とする廃水処理装置。
1. A processing tank for storing a liquid to be processed is partitioned into a plurality of regions by vertical partition walls, and adjacent regions of the plurality of regions communicate with each other at an upper portion and a lower portion. Has one of the areas adjacent to each other as an upflow,
A circulation flow generator that circulates the liquid to be treated is provided by setting the other as a downward flow, and a membrane separation device in which a hollow fiber membrane is laterally installed between the water collection pipes is provided in the center where the flow velocity in each region becomes faster. A wastewater treatment device characterized by being provided.
【請求項2】 請求項1に記載の廃水処理装置におい
て、前記循環流発生装置は処理槽内の底部に設けられる
曝気装置、若しくはプロペラ装置であることを特徴とす
る廃水処理装置。
2. The wastewater treatment apparatus according to claim 1, wherein the circulating flow generator is an aeration device or a propeller device provided at the bottom of the treatment tank.
【請求項3】 被処理液を貯留する処理槽内を上下方向
の隔壁にて複数の領域に仕切り、これら複数の領域のう
ち互いに隣接する領域は上部及び下部にて連通するとと
もに各領域内に膜分離装置を配設した廃水処理装置の運
転方法において、所定時間互いに隣接する領域の一方を
上昇流とし他方を下降流として循環流を形成した後、上
昇流と下降流の向きを反転して逆向きの循環流を形成す
るようにしたことを特徴とする廃水処理装置の運転方
法。
3. A processing tank for storing a liquid to be processed is partitioned into a plurality of regions by vertical partition walls, and adjacent regions of the plurality of regions are connected to each other at an upper portion and a lower portion, and each region is connected to each other. In a method for operating a wastewater treatment device provided with a membrane separation device, one of the regions adjacent to each other for a predetermined time is formed as an upflow and the other is formed as a downflow to form a circulation flow, and then the directions of the upflow and the downflow are reversed. A method for operating a wastewater treatment device, characterized in that a reverse circulation flow is formed.
【請求項4】 請求項3に記載の廃水処理装置の運転方
法において、前記循環流の速度を0.1m以上1.0m
以下とすることを特徴とする廃水処理装置の運転方法。
4. The method for operating the wastewater treatment apparatus according to claim 3, wherein the speed of the circulating flow is 0.1 m or more and 1.0 m or more.
A method for operating a wastewater treatment device characterized by the following.
【請求項5】 請求項3に記載の廃水処理装置の運転方
法において、前記被処理液の濃度を8000mg/リットル
以上50000mg/リットル以下とすることを特徴とする
廃水処理装置の運転方法。
5. The method for operating a wastewater treatment device according to claim 3, wherein the concentration of the liquid to be treated is 8000 mg / liter or more and 50000 mg / liter or less.
JP24754395A 1995-09-26 1995-09-26 Wastewater treatment device and operating method therefor Pending JPH0985243A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24754395A JPH0985243A (en) 1995-09-26 1995-09-26 Wastewater treatment device and operating method therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24754395A JPH0985243A (en) 1995-09-26 1995-09-26 Wastewater treatment device and operating method therefor

Publications (1)

Publication Number Publication Date
JPH0985243A true JPH0985243A (en) 1997-03-31

Family

ID=17165065

Family Applications (1)

Application Number Title Priority Date Filing Date
JP24754395A Pending JPH0985243A (en) 1995-09-26 1995-09-26 Wastewater treatment device and operating method therefor

Country Status (1)

Country Link
JP (1) JPH0985243A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8999162B2 (en) 2010-02-04 2015-04-07 Econopure Water Systems, Llc Water treatment systems and methods
US10513446B2 (en) 2014-10-10 2019-12-24 EcoDesal, LLC Depth exposed membrane for water extraction

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8999162B2 (en) 2010-02-04 2015-04-07 Econopure Water Systems, Llc Water treatment systems and methods
US10513446B2 (en) 2014-10-10 2019-12-24 EcoDesal, LLC Depth exposed membrane for water extraction

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