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JP3688979B2 - Water level difference type membrane filtration device - Google Patents
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JP3688979B2 - Water level difference type membrane filtration device - Google Patents

Water level difference type membrane filtration device Download PDF

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Publication number
JP3688979B2
JP3688979B2 JP2000192850A JP2000192850A JP3688979B2 JP 3688979 B2 JP3688979 B2 JP 3688979B2 JP 2000192850 A JP2000192850 A JP 2000192850A JP 2000192850 A JP2000192850 A JP 2000192850A JP 3688979 B2 JP3688979 B2 JP 3688979B2
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Japan
Prior art keywords
water
membrane module
water level
filtration
level difference
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JP2002001330A (en
Inventor
吉次 神保
卓也 鬼塚
克己 樺沢
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Suido Kiko Kaisha Ltd
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Suido Kiko Kaisha Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、水位差利用型膜ろ過装置に関し、特に、越流堰或いは汲み上げポンプで定流量の原水を立ち上げ管に供給し、立ち上げ管の自由水面位置を透過膜モジュールのろ過抵抗水位と出口側配管抵抗水位との和以上として円滑な定流量ろ過を行うと共に、再ろ過開始時の膜破損等を防止するための新規な改良に関する。
【0002】
【従来の技術】
従来、用いられていたこの種の膜ろ過装置としては、図5の全量ろ過方式、図6のクロスフローろ過方式、平成12年2月に(社)日本工業用水協会発行の工業用水第497号の31頁及び32頁に開示されている図7の水位差利用型、図8の吸引型が採用されていた。
まず、図5の全量ろ過方式の場合、原水槽1からの原水は原水供給ポンプ2を介して透過膜モジュールよりなる膜ろ過装置3でろ過され、配管4を経て処理水槽5へ供給されるように構成されていた。
また、膜ろ過装置3を逆洗する場合には、処理水槽5と配管4との間に設けられた逆洗ポンプ6を駆動して膜ろ過装置3にろ過時と逆方向に原水を供給して逆洗し、排水していた。
【0003】
また、図6のクロスフローろ過方式の場合、基本的には図5の構成とほぼ同一であるが、膜ろ過装置3の一部の処理水を逆送配管7を介して原水槽1内に帰還させていた。
【0004】
また、図7の水位差利用型の場合、原水槽1の原水は膜モジュール型の膜ろ過水槽3aから吸引ポンプ2aを介して膜ろ過水槽3aAに送られ、膜ろ過水として取り出されていた。また、膜ろ過水槽3aには洗浄用の洗浄ブロア10が設けられていた。
【0005】
また、図8の吸引型の場合、原水が供給される槽が膜浸せき槽3bで形成され、吸引ポンプ2aを介して膜ろ過水槽3aAに送られて膜ろ過水が得られていた。
【0006】
【発明が解決しようとする課題】
従来の膜ろ過装置は、以上のように構成されていたため、次のような課題が存在していた。
すなわち、図5及び図6の場合、何れも原水槽と膜ろ過装置との間に水位差がなく、ポンプによって原水を膜ろ過装置に供給しなければならなかった。
また、図7及び図8の場合、原水槽が膜ろ過装置より高い位置で原水が膜ろ過装置に対して水位差を持っているため、前述のような原水供給用のポンプは不要であるが、膜ろ過水槽は浸漬型膜モジュール型であるため、その槽内に収納すべき充分な容積を必要とし、且つ、この槽はその水位差の圧力に耐える耐圧/密閉構造としなければならず、槽内の保有水量も大で、水を保有した場合の槽の重量は極めて大きく、その槽の据付工事においては基礎工事等に多大の費用を必要とした。
また、この槽が方形型であれば、なおさら耐圧設計を必要とした。
また、この方式において槽内を空気洗浄(エアスクラビング)する場合、膜ろ過水槽には水位差が作用しているため、空気洗浄に必要な空気供給圧は、この水位差以上としなければならず、圧縮空気を送るための大きい動力を発生するために大形のポンプやモータを必要とし、経済的にも不利となっていた。
【0007】
本発明は、以上のような課題を解決するためになされたもので、特に、越流堰或いは汲み上げポンプで定流量の原水を立ち上げ管に供給し、立ち上げ管の自由水面位置を透過膜モジュールのろ過抵抗水位と出口側配管抵抗水位との和以上として円滑な定流量ろ過を行うと共に、再ろ過開始時の膜破損等を防止するようにした水位差利用型膜ろ過装置を提供することを目的とする。
【0008】
【課題を解決するための手段】
本発明による水位差利用型膜ろ過装置は、原水槽より越流堰或いは汲み上げポンプ及び立ち上げ管を介して原水を透過膜モジュールへ供給し、水位差を用いて前記透過膜モジュールによりろ過操作を行うようにし、前記立ち上げ管内の自由水面高さ位置が、前記透過膜モジュールのろ過抵抗水位と前記透過膜モジュールの出口側のろ過水管のろ過水管抵抗水位との和以上である水位差利用型膜ろ過装置において、前記透過膜モジュールの下部に接続されかつ前記立ち上げ管に連通するサイホン型の逆洗排水用分岐管を有し、前記逆洗排水用分岐管の上端位置は前記透過膜モジュールの上部高さ位置にほぼ対応している構成であり、また、前記透過膜モジュールは、ケーシング収納型中空子膜モジュールである構成である。
【0009】
【発明の実施の形態】
以下、図面と共に本発明による水位差利用型膜ろ過装置の好適な実施の形態について説明する。なお、従来例と同一又は同等部分については同一符号を用いて説明する。
図1は本発明による全量ろ過方式の形態を示す構成図である。
図1において符号1で示されるものは原水槽(原水槽でない場合もある)であり、この原水槽1の原水はこの原水槽1に設けられた越流堰20A或いは図示しない汲み上げポンプ等を経て垂直に立上げられた立ち上げ管20に送られるように構成されている。
【0010】
前記立ち上げ管20の下部には、垂直に立ち上げて設けられ周知のケーシング収納型中空子膜モジュールからなる透過膜モジュール3が接続されている。
前記透過膜モジュール3には、その下部にドレン用のドレン弁VB1とその電磁部Bが接続され、その上部に排気用の排気弁VB2が接続されている。
【0011】
前記透過膜モジュール3の下部には、排気管としてのサイホン型をなす逆洗排水用分岐管21が接続され、この逆洗排水用分岐管21には排水弁23が接続されている。
前記透過膜モジュール3の上部には、ろ過した処理水をろ過水槽5に送るためのろ過水弁26を有するろ過水管4が接続されている。
前記ろ過水管4のろ過水弁26の手前位置には、前記ろ過水槽5の下部に連通する逆流洗浄管31が設けられ、この逆流洗浄管31には逆流洗浄ポンプ6及び逆洗開閉弁30が設けられている。なお、前記逆洗排水用分岐管21の上端位置21aは、前記透過膜モジュール3の上部高さ位置3aにほぼ対応している。
【0012】
次に、動作について説明する。まず、原水は定量流入装置である越流堰20Aにより一定流量立ち上げ管20に流入する。透過膜モジュール3の必要膜間差圧は、ろ過開始時は一般に数mの水位差で膜ろ過速度1m/d程度取れる。従って、立ち上げ間20の水位はろ過水管4に比べ数m高い水位WL1すなわちろ過水管4の上端位置WL0’との差である水位差H1でろ過を開始する。この時、ろ過水弁26は開、排水弁23は閉の状態である。
前述の膜ろ過を継続していくと、膜が目詰まりしてくるので、数十分おきに逆流洗浄を数十秒行うことが必要であり、逆洗はタイマー付の逆洗開閉弁30で制御し、ろ過水弁26を閉じ、排水弁23を開き、逆流洗浄ポンプ6を起動することにより行われる。このとき、立ち上げ管20内の原水も一緒に排水されるので、立ち上げ管20内の水位はWL0まで低下する。
次に、逆流洗浄ポンプ6を止め、排水弁23を閉め、ろ過水弁26を開けることによりろ過が再開されるが、立ち上げ管20内水位はWL0より始まる。
この時、透過膜モジュール3の膜にかかる差圧は極めて小さく、ろ過速度は低い。この状態を継続していると、原水流入量よりろ過水量が小さいので立ち上げ管20内の水位は徐々に上昇し、原水流入量とろ過水量が均衡した水位で停止する。
前述のサイクルを継続していくと、逆流洗浄では落としきれない汚れが膜に蓄積され、徐々に立ち上げ管20内水位は上昇していき、数ケ月経過後には膜間差圧の上限であるWL2に到達する。この場合、膜を薬品により洗浄し、初期の状態に戻す必要がある。
【0013】
前述の動作における時間的なろ過経過を図示すると図2の通りである。すなわち、前述したように、ろ過時間を経過して行くと、定期的な逆洗動作を行うにも拘わらず、透過膜モジュール3の膜の目詰まり状態が悪化(すなわち、ろ過抵抗が増加)し、前記水位WL1がWL1’で示すように上昇することになる。
従って、前述の水位差を用いて透過膜モジュール3により行う場合の前記立ち上げ管20内の自由水面高さ位置が、透過膜モジュール3のろ過抵抗水位と透過膜モジュール3の出口側のろ過水管4のろ過水管抵抗水位との和以上に設定することが必要である。
【0014】
前記ケーシング収納型膜モジュールの場合、逆洗は空気洗浄のみでもよいがより完全を期するためには水逆洗するのが好ましい。この場合、ろ過した処理水を逆流洗浄ポンプ6を用いて逆洗しているが、この逆流洗浄ポンプ6の動力を少しでも小さくするため、透過膜モジュール3の一次側(原水供給側)の水位を下げた状態で逆洗を行うことが好ましい。
この水位の下げる程度は透過膜モジュール3の上部近傍位置すなわちWL0でよい。このようにすることにより逆洗後、ろ過開始時に必要以上の圧力がかかり極端に速いろ過速度となって膜を破損したり膜の目詰まりを促進したりすることはなくなる。従って、透過膜モジュール3の逆洗排水用分岐管21をサイホン管としている。
また、透過膜モジュール3の一次側の原水導入の立ち上げ管20の管径は小さい程その滞留水量が小さく揚水時の捨水量が少なくて済み無駄が少なく、また、透過膜モジュール3のろ過抵抗の変化にも立ち上げ管20の水位変動の応答も早くてよいかが、実用的には管内流速0.3〜0.5m/秒とするのが良好である。
【0015】
次に、図3で示される構成は、図1の他の形態であるクロスフローろ過方式を示す構成図である。なお、図1と同一部分には同一符号を付してその説明は重複を避けるために省略する。
前記透過膜モジュール3に接続された逆洗排水用分岐管21には、モータ22駆動の可変開閉弁を行う排水弁23が接続され、前記透過膜モジュール3の上部に接続されたクロスフロー排水管7にはクロスフロー排水弁24が設けられている。
前記ろ過水管4の下流位置には、ろ過水流量計26aに連動してモータ25駆動による可変開閉弁を行うろ過水弁26が設けられている。
【0016】
従って、図2のろ過動作は図1と基本的には同じであるが、クロスフローろ過方式であるため、ろ過水弁26の開度をモータ25によって図4のように可変とし、クロスフロー排水弁24の開閉を行うことが異なるのみである。
【0017】
【発明の効果】
本発明による水位差利用型膜ろ過装置は、以上のように構成されているため、次のような効果を得ることができる。
すなわち、越流堰との水位差を用いて透過膜モジュールに原水を供給しているため、従来用いられていた原水供給ポンプが不要となって装置構成が簡略化される。
また、ろ過装置として透過膜モジュールすなわちケーシング収納型中空子膜モジュールを用いているため、ろ過装置自体が小型であるため、従来の水位差利用型のような大型で高コストのろ過槽を用いる必要がなく、ローコストで高信頼性のろ過装置を得ることができる。
【図面の簡単な説明】
【図1】本発明による水位差利用型膜ろ過装置を示す構成図である。
【図2】図1の動作を示す説明図である。
【図3】図1の他の形態を示す構成図である。
【図4】図3の動作を示す説明図である。
【図5】従来の全量ろ過方式を示す構成図である。
【図6】従来のクロスフローろ過方式を示す構成図である。
【図7】従来の水位差利用型の構成を示す構成図である。
【図8】従来の吸引型の構成を示す構成図である。
【符号の説明】
1 原水槽
3 透過膜モジュール
3a 上部高さ位置
4 ろ過水管
20 立ち上げ管
20A 越流堰
21 逆洗排水用分岐管
21a 上端位置
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a water level difference type membrane filtration device, and in particular, feeds raw water at a constant flow rate to a riser pipe with an overflow weir or a pump, and sets the free water surface position of the riser pipe to the filtration resistance water level of the permeable membrane module. The present invention relates to a novel improvement for performing a smooth constant flow filtration that is equal to or higher than the sum of the outlet side pipe resistance water level and preventing membrane breakage at the start of refiltration.
[0002]
[Prior art]
Conventionally, as this type of membrane filtration device, the total amount filtration method shown in FIG. 5, the cross flow filtration method shown in FIG. 6, and industrial water No. 497 issued by Japan Industrial Water Association in February 2000 were used. The water level difference utilization type of FIG. 7 and the suction type of FIG. 8 disclosed on pages 31 and 32 of FIG.
First, in the case of the total amount filtration method of FIG. 5, the raw water from the raw water tank 1 is filtered through the raw water supply pump 2 by the membrane filtration device 3 composed of a permeable membrane module, and supplied to the treated water tank 5 through the pipe 4. Was configured.
When the membrane filtration device 3 is backwashed, the backwash pump 6 provided between the treated water tank 5 and the pipe 4 is driven to supply raw water to the membrane filtration device 3 in the direction opposite to that during filtration. Backwashed and drained.
[0003]
In the case of the cross flow filtration method of FIG. 6, the configuration is basically the same as that of FIG. 5, but a part of the treated water of the membrane filtration device 3 is fed into the raw water tank 1 through the reverse feed pipe 7. I was returning.
[0004]
In the case of the water level difference utilization type of FIG. 7, the raw water in the raw water tank 1 is sent from the membrane module type membrane filtration water tank 3a to the membrane filtration water tank 3aA via the suction pump 2a and taken out as membrane filtration water. The membrane filtration water tank 3a is provided with a cleaning blower 10 for cleaning.
[0005]
In the case of the suction type shown in FIG. 8, the tank to which raw water is supplied is formed by the membrane soaking tank 3b and sent to the membrane filtration water tank 3aA via the suction pump 2a to obtain the membrane filtrate.
[0006]
[Problems to be solved by the invention]
Since the conventional membrane filtration apparatus was comprised as mentioned above, the following subjects existed.
That is, in both cases of FIGS. 5 and 6, there is no difference in water level between the raw water tank and the membrane filtration device, and the raw water must be supplied to the membrane filtration device by a pump.
Moreover, in the case of FIG.7 and FIG.8, since the raw | natural water has a water level difference with respect to a membrane filtration apparatus in a position where a raw | natural water tank is higher than a membrane filtration apparatus, the above pumps for raw water supply are unnecessary. Since the membrane filtration water tank is a submerged membrane module type, it needs a sufficient volume to be stored in the tank, and this tank must have a pressure resistant / sealed structure that can withstand the pressure of the water level, The amount of water held in the tank was large, and the weight of the tank when water was held was extremely large, and the installation work for the tank required a large amount of expenses for foundation work.
Moreover, if this tank was a square type, a pressure resistance design was required.
In addition, when the inside of the tank is air-cleaned (air scrubbing) in this method, since the water level difference acts on the membrane filtration water tank, the air supply pressure required for air cleaning must be greater than this water level difference. In order to generate large power for sending compressed air, a large pump or motor is required, which is economically disadvantageous.
[0007]
The present invention has been made to solve the above-described problems. In particular, the raw water at a constant flow rate is supplied to the rising pipe by the overflow weir or the pump, and the free water surface position of the rising pipe is set to the permeable membrane. Provide a water level difference type membrane filtration device that performs smooth constant flow filtration that is equal to or higher than the sum of the filtration resistance water level of the module and the outlet side pipe resistance water level, and prevents membrane breakage at the start of refiltration. With the goal.
[0008]
[Means for Solving the Problems]
The water level difference type membrane filtration device according to the present invention supplies raw water from the raw water tank to the permeable membrane module via the overflow weir or pumping pump and the rising pipe, and performs filtration operation by the permeable membrane module using the water level difference. to perform, free water surface height position of the launch tube is, the water level difference utilizing the at permeation membrane module filtration resistance level and above the sum of the filtered water tube resistance level of the outlet-side filtration water pipe of the permeation membrane module In the mold membrane filtration apparatus, the backwash drainage branch pipe is connected to the lower part of the permeable membrane module and communicates with the rising pipe, and the upper end position of the backwash drainage branch pipe is the permeable membrane. Ri configuration der substantially corresponds to the upper height position of the module, also the permeation membrane module is a construction which is a casing accommodating hollow element membrane module.
[0009]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, preferred embodiments of a water level difference utilization type membrane filtration device according to the present invention will be described with reference to the drawings. The same or equivalent parts as those in the conventional example will be described using the same reference numerals.
FIG. 1 is a configuration diagram showing a form of a total amount filtration system according to the present invention.
In FIG. 1, reference numeral 1 denotes a raw water tank (which may not be a raw water tank). The raw water in this raw water tank 1 passes through an overflow weir 20A provided in this raw water tank 1 or a pumping pump (not shown). It is configured to be sent to a rising pipe 20 that is vertically raised.
[0010]
Connected to the lower portion of the rising pipe 20 is a permeable membrane module 3 which is provided vertically and is formed of a well-known casing housing type hollow membrane membrane module.
The permeable membrane module 3 is connected to a drain drain valve V B1 and an electromagnetic part B at a lower portion thereof, and to an exhaust exhaust valve V B2 at an upper portion thereof.
[0011]
A siphon type branch pipe for backwash drainage 21 as an exhaust pipe is connected to the lower part of the permeable membrane module 3, and a drain valve 23 is connected to the backwash drainage branch pipe 21.
A filtered water pipe 4 having a filtered water valve 26 for sending filtered treated water to the filtered water tank 5 is connected to the upper part of the permeable membrane module 3.
A backflow cleaning pipe 31 communicating with the lower part of the filtered water tank 5 is provided at a position before the filtered water valve 26 of the filtered water pipe 4, and the backflow cleaning pump 6 and the backwash opening / closing valve 30 are provided in the backflow cleaning pipe 31. Is provided. The upper end position 21 a of the backwash drainage branch pipe 21 substantially corresponds to the upper height position 3 a of the permeable membrane module 3.
[0012]
Next, the operation will be described. First, the raw water flows into the constant flow rising pipe 20 by the overflow weir 20A which is a constant inflow device. The required transmembrane pressure difference of the permeable membrane module 3 is generally about 1 m / d with a water level difference of several meters at the start of filtration. Therefore, the water level during the start-up 20 starts filtration at a water level difference H1 which is a difference from the water level WL1 which is several meters higher than the filtered water pipe 4, that is, the upper end position WL0 ′ of the filtered water pipe 4. At this time, the filtered water valve 26 is open and the drain valve 23 is closed.
If the above-mentioned membrane filtration is continued, the membrane becomes clogged, so it is necessary to carry out backwashing every several tens of seconds for several tens of seconds. Backwashing is performed by the backwash on / off valve 30 with a timer. This is done by closing the filtered water valve 26, opening the drain valve 23, and starting the backwash pump 6. At this time, since the raw water in the rising pipe 20 is also drained together, the water level in the rising pipe 20 is lowered to WL0.
Next, the backwash pump 6 is stopped, the drain valve 23 is closed, and the filtered water valve 26 is opened, so that the filtration is resumed, but the water level in the rising pipe 20 starts from WL0.
At this time, the differential pressure applied to the membrane of the permeable membrane module 3 is extremely small, and the filtration rate is low. If this state is continued, the filtered water amount is smaller than the raw water inflow amount, so that the water level in the rising pipe 20 gradually rises and stops at a water level where the raw water inflow amount and the filtered water amount are balanced.
As the above-described cycle is continued, dirt that cannot be removed by backwashing accumulates in the membrane, the water level in the riser 20 gradually rises, and after several months, the upper limit of the transmembrane pressure difference is reached. Reach WL2. In this case, it is necessary to clean the membrane with chemicals and return it to the initial state.
[0013]
FIG. 2 shows a temporal filtration process in the above operation. That is, as described above, when the filtration time elapses, the clogged state of the membrane of the permeable membrane module 3 deteriorates (that is, the filtration resistance increases) despite the regular backwashing operation. The water level WL1 rises as indicated by WL1 ′.
Therefore, the free water surface height position in the riser pipe 20 when the permeation membrane module 3 is used by using the above water level difference is the filtration resistance water level of the permeation membrane module 3 and the filtration water tube on the outlet side of the permeation membrane module 3. It is necessary to set it to be equal to or higher than the sum of the filtered water pipe resistance level of 4.
[0014]
In the case of the casing housing type membrane module, the backwashing may be performed only by air washing, but it is preferable to backwash with water in order to ensure completeness. In this case, the filtered treated water is backwashed using the backwash pump 6, but in order to reduce the power of the backwash pump 6 as much as possible, the water level on the primary side (raw water supply side) of the permeable membrane module 3. It is preferable to perform backwashing in a state where the pressure is lowered.
The lowering level of the water level may be a position near the upper part of the permeable membrane module 3, that is, WL0. By doing so, after backwashing, pressure more than necessary is applied at the start of filtration, and an extremely fast filtration rate is prevented so that the membrane is not damaged or clogging of the membrane is not promoted. Therefore, the backwash drainage branch pipe 21 of the permeable membrane module 3 is a siphon pipe.
Moreover, the smaller the pipe diameter of the starting water introduction pipe 20 on the primary side of the permeable membrane module 3, the smaller the amount of accumulated water and the less waste water during pumping, and less waste, and the filtration resistance of the permeable membrane module 3. Whether the response to the change in the water level of the rising pipe 20 may be fast or not, it is practically preferable to set the flow velocity in the pipe to 0.3 to 0.5 m / second.
[0015]
Next, the configuration shown in FIG. 3 is a configuration diagram showing a cross flow filtration system which is another form of FIG. The same parts as those in FIG. 1 are denoted by the same reference numerals, and description thereof is omitted to avoid duplication.
A branch valve 21 for backwash drainage connected to the permeable membrane module 3 is connected to a drain valve 23 that performs a variable on-off valve driven by a motor 22, and a cross-flow drain pipe connected to the upper part of the permeable membrane module 3. 7 is provided with a cross flow drain valve 24.
At the downstream position of the filtered water pipe 4, a filtered water valve 26 that performs a variable on-off valve driven by a motor 25 in conjunction with a filtered water flow meter 26a is provided.
[0016]
Accordingly, the filtration operation of FIG. 2 is basically the same as that of FIG. 1, but since it is a cross flow filtration system, the opening degree of the filtrate water valve 26 is made variable by the motor 25 as shown in FIG. Only the opening and closing of the valve 24 is different.
[0017]
【The invention's effect】
Since the water level difference utilizing membrane filtration device according to the present invention is configured as described above, the following effects can be obtained.
That is, since raw water is supplied to the permeable membrane module using a difference in water level with the overflow weir, a conventionally used raw water supply pump is not required, and the apparatus configuration is simplified.
In addition, since a permeable membrane module, that is, a casing housing type hollow core membrane module is used as a filtration device, the filtration device itself is small, so it is necessary to use a large and high-cost filtration tank like a conventional water level difference type. Therefore, a low-cost and highly reliable filtration device can be obtained.
[Brief description of the drawings]
FIG. 1 is a configuration diagram illustrating a water level difference type membrane filtration device according to the present invention.
FIG. 2 is an explanatory diagram showing the operation of FIG. 1;
FIG. 3 is a configuration diagram showing another embodiment of FIG. 1;
4 is an explanatory diagram showing the operation of FIG. 3. FIG.
FIG. 5 is a block diagram showing a conventional total filtration method.
FIG. 6 is a configuration diagram showing a conventional cross-flow filtration method.
FIG. 7 is a configuration diagram showing a conventional water level difference type configuration.
FIG. 8 is a configuration diagram showing a configuration of a conventional suction type.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Raw water tank 3 Permeation membrane module 3a Upper part height position 4 Filtration water pipe 20 Startup pipe 20A Overflow weir 21 Branch pipe 21a for backwash drainage Upper end position

Claims (2)

原水槽(1)より越流堰(20A)或いは汲み上げポンプ及び立ち上げ管(20)を介して原水を透過膜モジュール(3)へ供給し、水位差を用いて前記透過膜モジュール(3)によりろ過操作を行うようにし、前記立ち上げ管(20)内の自由水面高さ位置が、前記透過膜モジュール(3)のろ過抵抗水位と前記透過膜モジュール(3)の出口側のろ過水管(4)のろ過水管抵抗水位との和以上であるようにした水位差利用型膜ろ過装置において、前記透過膜モジュール(3)の下部に接続されかつ前記立ち上げ管(20)に連通するサイホン型の逆洗排水用分岐管(21)を有し、前記逆洗排水用分岐管(21)の上端位置(21a)は前記透過膜モジュール(3)の上部高さ位置(3a)にほぼ対応していることを特徴とする水位差利用型膜ろ過装置。Raw water is supplied from the raw water tank (1) to the permeable membrane module (3) through the overflow weir (20A) or the pumping pump and the rising pipe (20), and the permeable membrane module (3) uses the water level difference. to perform the filtration operation, the free water surface height position of the launch tube (20) is, the permeation membrane module (3) outlet filtered water tubes of the filtration resistance level and the permeable membrane module (3) of ( in the water level difference-using membrane filtration apparatus which der so that more than the sum of the filtered water tube resistance level of 4), communicating with the permeable membrane module (3) is connected to the lower of and the rising pipe (20) siphon Type backwash drainage branch pipe (21), the upper end position (21a) of the backwash drainage branch pipe (21) substantially corresponds to the upper height position (3a) of the permeable membrane module (3) A water level difference type membrane filtration device characterized by 前記透過膜モジュール(3)は、ケーシング収納型中空子膜モジュールであることを特徴とする請求項1記載の水位差利用型膜ろ過装置。  The water level difference type membrane filtration device according to claim 1, wherein the permeable membrane module (3) is a casing housing type hollow core membrane module.
JP2000192850A 2000-06-27 2000-06-27 Water level difference type membrane filtration device Expired - Fee Related JP3688979B2 (en)

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