JP2010188349A - Medium and membrane filtration-combined filtration facility, and operation method therefor - Google Patents

Medium and membrane filtration-combined filtration facility, and operation method therefor Download PDF

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JP2010188349A
JP2010188349A JP2010130741A JP2010130741A JP2010188349A JP 2010188349 A JP2010188349 A JP 2010188349A JP 2010130741 A JP2010130741 A JP 2010130741A JP 2010130741 A JP2010130741 A JP 2010130741A JP 2010188349 A JP2010188349 A JP 2010188349A
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filtration
water
membrane
media
tank
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JP5072050B2 (en
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Takashi Sasaki
隆 佐々木
Ken Tanizawa
謙 谷澤
Jo Yamamoto
丈 山本
Shohei Fukada
尚平 深田
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HANSHIN WATER SUPPLY AUTHORITY
Shinko Pantec Co Ltd
Kubota Corp
JFE Engineering Corp
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HANSHIN WATER SUPPLY AUTHORITY
Kubota Corp
JFE Engineering Corp
Kobelco Eco Solutions Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a filtration facility and an operation method therefor with little risk and with extremely excellent water treatment efficiency, the facility achieved by combining filtration technologies of a conventional media filter basin and a membrane filtration apparatus to solve problems of both the technologies and made compact by reducing a installation space, and exactly and flexibly coping with the increase or fluctuation of water to be treated and variation of water quality. <P>SOLUTION: The medium and membrane filtration-combined filtration facility includes a media filter basin M and a membrane filtration apparatus S formed by disposing a plurality of membrane modules 16 in a filtration tank 11 of the media filter basin at a position lower than the water level L of the water to be treated at the filtration time. The water H to be treated fed to the filtration tank 11 is simultaneously filtered in both the media filter basin and membrane filtration apparatus, to simultaneously obtain treated water from both the media filter basin and membrane filtration apparatus. <P>COPYRIGHT: (C)2010,JPO&INPIT

Description

本発明は浄水場における浄水処理など各種の水処理に適したろ過設備に関し、特にメディアろ過池と膜ろ過装置とを有機的に組み合わせた複合ろ過設備及びその運転方法に関するものである。   The present invention relates to a filtration facility suitable for various types of water treatment such as water purification in a water purification plant, and more particularly to a combined filtration facility in which a media filtration pond and a membrane filtration device are organically combined and an operation method thereof.

従来、浄水場における水処理は、一般に砂、アンスラサイトあるいは粒状活性炭などの粒状ろ材をろ過層とした所謂メディアろ過池(メディアろ過器またはろ過装置)が採用されている。   Conventionally, water treatment in a water purification plant generally employs a so-called media filtration basin (media filter or filtration device) using a particulate filter medium such as sand, anthracite, or granular activated carbon as a filtration layer.

しかしながら、このメディアろ過池はろ過速度が一定(処理水量が一定)であるため処理水量の変動に対してはメディアろ過池の運転・停止などの運転操作を繰り返し行うなど施設としては効率的でなく、かつ緊急的な処理水量の増加に対応できないという問題がある。   However, this media filter basin has a constant filtration rate (the amount of treated water is constant), so it is not efficient as a facility to repeatedly operate and stop the media filter pond with respect to fluctuations in the treated water amount. In addition, there is a problem that it cannot cope with an urgent increase in the amount of treated water.

近年、かかるメディアろ過池に代わるろ過装置として膜ろ過装置が開発され、小規模浄水場を中心に普及が進んでいる。この膜ろ過装置はコンパクトであり、設置スペースが小さくて済み、また懸濁物質や微細な病原性原虫なども分離可能であるとともに膜の種類(MF膜、UF膜、NF膜など)を選択することによりさまざまな水質の被処理水を処理できる。さらに、その膜モジュールはユニット形式であるため被処理水の処理規模に応じて自在に対応でき、建設工期が短くて済む。   In recent years, membrane filtration devices have been developed as an alternative to such media filtration ponds, and are becoming popular mainly in small-scale water purification plants. This membrane filtration device is compact and requires only a small installation space. It can also separate suspended substances and minute pathogenic protozoa, and select the type of membrane (MF membrane, UF membrane, NF membrane, etc.) This makes it possible to treat water to be treated with various water qualities. Furthermore, since the membrane module is a unit type, it can be freely adapted according to the treatment scale of the water to be treated, and the construction period is short.

膜ろ過装置はこうした利点があるものの、精密な膜を使用しているため膜モジュールに目詰りを生じ、このため、年に数回の薬品洗浄を実施しなければならず、また膜に寿命があるため膜モジュールの交換を必要とし、装置コストに加えてランニングコストが高いという不利な面もある。   Although the membrane filtration device has these advantages, it uses a precise membrane, which causes clogging of the membrane module. Therefore, chemical cleaning must be performed several times a year. Therefore, the membrane module needs to be replaced, and there is a disadvantage that the running cost is high in addition to the apparatus cost.

また、このメディアろ過池と膜ろ過装置とを併用するろ過設備も提案されている(特許文献1など)。しかし、かかる設備はメディアろ過池の逆洗排水を原水に戻さず、膜ろ過装置を利用して処理し、メディアろ過池の負担を軽減するものであり、メディアろ過池とは別の場所に膜ろ過装置およびその付帯装置を設置する必要があり、その分全体の設備が大型となり、設置スペースもさらに大きく必要とする。しかも、被処理水の処理容量(浄水量)は基本的にはメディアろ過池のろ過速度に依存し、被処理水の供給量の大きな変動には対応できず、さらに場合によっては被処理水の水質の変化に対しても十分な対応ができないなど問題を有している。   Moreover, the filtration equipment which uses together this media filtration pond and a membrane filtration apparatus is also proposed (patent document 1 etc.). However, such equipment does not return the backwash wastewater from the media filtration basin to the raw water, but treats it using a membrane filtration device to reduce the burden on the media filtration basin. It is necessary to install a filtration device and its associated device, and the entire equipment becomes large and the installation space is further increased. Moreover, the treatment capacity (purified water volume) of the treated water basically depends on the filtration rate of the media filtration basin and cannot cope with large fluctuations in the supply amount of the treated water. There are problems such as inability to adequately respond to changes in water quality.

最近は、浄水場など水処理設備の敷地確保、これら設備やその運転、保守を含めた大型投資が一段と困難になっており、その一方で浄水などの処理水の増加や変動に対する的確な対応が要請されるとともに、処理水の水質基準もきめ細かく制限され、被処理水の水質変化に対しても処理水の十分な品質管理が要求され、これらに対するリスクを回避しなければならない状況となっている。
特開2003−236558号公報
Recently, it has become more difficult to secure large-scale investments including water treatment facilities such as water treatment plants, and to operate and maintain these facilities, and on the other hand, it is possible to respond accurately to the increase and fluctuation of treated water such as water purification. At the same time, the water quality standards for treated water are finely limited, and sufficient quality control of treated water is required even for changes in the quality of treated water, and the risks to these must be avoided. .
JP 2003-236558 A

本発明はこうした水処理における厳しい背景を踏まえ、従来のメディアろ過池および膜ろ過装置によるろ過技術を融合し、両者の問題点を解消し、その設置スペースが小さくて済むコンパクトな設備により、被処理水の増加、変動や水質変動に的確かつ柔軟に対応できるリスクの少ない極めて水処理効率に優れたろ過設備及びその運転方法を提供することをその目的としてなされたものである。   The present invention is based on such a severe background in water treatment, fusing the filtration technology using conventional media filtration ponds and membrane filtration devices, eliminating the problems of both, and compact equipment that requires less installation space, The purpose of the present invention is to provide a filtration facility having an extremely excellent water treatment efficiency and an operating method with a low risk that can accurately and flexibly cope with an increase, fluctuation and water quality fluctuation of water.

そして、このような目的達成のために完成された本発明の要旨とする特徴は以下の通りである。
(1)メディアろ過池と、該メディアろ過池のろ過槽に、ろ過時における被処理水の水位よりも下方となる位置に複数の膜モジュールを配設した膜ろ過装置とからなり、前記ろ過槽に供給された被処理水を、前記メディアろ過池と前記膜ろ過装置の双方によって同時にろ過処理して前記メディアろ過池と前記膜ろ過装置の双方からろ過後の浄水を同時に得るように構成したことを特徴とするメディア及び膜ろ過複合ろ過設備(請求項1)。
(2)膜ろ過装置の膜モジュールの配設位置がメディアろ過池のろ過槽の内部上方である前記(1)に記載のメディア及び膜ろ過複合ろ過設備(請求項2)。
(3)メディアろ過池には被処理水が流入するガリットを有し、膜モジュールがガリットの溝の中に収容された状態で配置される前記(1)または(2)に記載のメディア及び膜ろ過複合ろ過設備(請求項3)。
(4)前記ガリットにはその直角方向に分岐したトラフが配設されている前記(3)に記載のメディア及び膜ろ過複合ろ過設備(請求項4)。
(5)前記(1)に記載のメディア及び膜ろ過複合ろ過設備を用いた運転方法において、被処理水の供給量の変動、要求浄水量の変動または被処理水の水質変化に対して、メディアろ過と膜ろ過の処理量の比率を変化させて浄水を製造するメディア及び膜ろ過複合ろ過設備の運転方法(請求項5)。
And the feature made into the summary of this invention completed for achieving such an objective is as follows.
(1) A media filtration pond and a membrane filtration device in which a plurality of membrane modules are disposed in a filtration tank of the media filtration pond at a position below the water level of the water to be treated at the time of filtration. The treated water supplied to the filter is simultaneously filtered by both the media filtration basin and the membrane filtration device, and the filtered water is obtained simultaneously from both the media filtration pond and the membrane filtration device. A medium and membrane filtration combined filtration facility characterized in that (Claim 1).
(2) The media and membrane filtration combined filtration facility according to (1), wherein the position of the membrane module of the membrane filtration device is located above the inside of the filtration tank of the media filtration basin (Claim 2).
(3) The media and the membrane according to (1) or (2), wherein the media filtration pond has a galit into which treated water flows, and the membrane module is disposed in a state where the membrane module is accommodated in a groove of the galit. Filtration combined filtration equipment (Claim 3).
(4) The media and membrane filtration combined filtration facility according to (3), wherein a trough branched in a direction perpendicular to the galit is disposed.
(5) In the operation method using the medium and the membrane filtration combined filtration facility described in (1) above, the medium can be used for fluctuations in the supply amount of the treated water, fluctuations in the required purified water amount, or changes in the quality of the treated water. A medium for producing purified water by changing the ratio of filtration and membrane filtration, and a method for operating a membrane filtration combined filtration facility (Claim 5).

本発明によればメディアろ過池と膜ろ過装置を有機的に組み合わせて一体化したろ過設備を提供することにより、設置スペースが小さくコンパクトな設備形態になり、被処理水の増加、変動や水質変化に的確且つ柔軟に対応でき、しかもリスクの少ない水処理効率に極めて優れた低コストの複合ろ過技術の実現とその確立を可能とするものである。   According to the present invention, by providing a filtration facility in which a media filtration pond and a membrane filtration device are combined organically and integrated, the installation space is small and a compact facility form is obtained, and the increase, fluctuation and water quality change of treated water. It is possible to realize and establish a low-cost composite filtration technology that can be accurately and flexibly dealt with, and that is extremely excellent in water treatment efficiency with low risk.

本発明の複合ろ過設備の一実施形態を説明する浄水処理設備全体の概要図である。It is a schematic diagram of the whole water purification processing equipment explaining one embodiment of the compound filtration equipment of the present invention. 本発明の複合ろ過設備の一実施形態を説明する図1のろ過槽の側断面概要図である。FIG. 2 is a schematic side sectional view of the filtration tank of FIG. 1 for explaining an embodiment of the composite filtration equipment of the present invention. 本発明の複合ろ過設備の基本的な特長概念を示す模式図(正面図)である。It is a schematic diagram (front view) which shows the basic feature concept of the composite filtration equipment of this invention. 本発明の複合ろ過設備の他の実施形態を示す正面切欠き斜視図である。It is a front notch perspective view which shows other embodiment of the composite filtration equipment of this invention. 上記図4における本発明の複合ろ過設備の他の実施形態による複合ろ過時のフローを示した正面切欠き斜視図である。It is the front notch perspective view which showed the flow at the time of the composite filtration by other embodiment of the composite filtration equipment of this invention in the said FIG. 同図4における本発明の複合ろ過設備の他の実施形態による膜ろ過装置の膜モジュールの逆洗時のフローを示した正面切欠き斜視図である。It is the front notch perspective view which showed the flow at the time of the backwashing of the membrane module of the membrane filtration apparatus by other embodiment of the composite filtration equipment of this invention in FIG. 同図4における本発明の複合ろ過設備の他の実施形態によるメディアろ過池のろ材層1の逆洗時のフローを示した正面切欠き斜視図である。FIG. 5 is a front cutaway perspective view showing a flow during backwashing of a filter medium layer 1 of a media filtration pond according to another embodiment of the composite filtration facility of the present invention in FIG. 4.

以下に本発明をその典型的な実施形態に基づき詳細について説明する。なお、以下においては本発明にかかる水処理設備の処理対象として浄水処理を中心に述べるが、本発明はこれに限らず、工業用水、生活用水、下水など各種の分野で発生する不純物を含む様々な排水の処理に適用できるものである。   The present invention will be described in detail below based on typical embodiments thereof. In the following, although water purification treatment is mainly described as a treatment target of the water treatment facility according to the present invention, the present invention is not limited to this, and various types including impurities generated in various fields such as industrial water, domestic water, and sewage. It can be applied to the treatment of wastewater.

図1は本発明の複合ろ過設備の一実施形態を説明する浄水処理設備全体の概要図である。ここにおいて、1は河川などから原水Gを導く着水井でありこの着水井1に貯留された原水は前処理設備Aに供給されて前処理がなされ、さらに被処理水Hとして本発明にかかる複合ろ過設備Bに供給されて浄水となるものである。   FIG. 1 is a schematic diagram of the whole water purification treatment facility for explaining an embodiment of the combined filtration facility of the present invention. Here, reference numeral 1 denotes a landing well that guides the raw water G from a river or the like. The raw water stored in the landing well 1 is supplied to a pretreatment facility A for pretreatment, and is further treated as water H to be treated according to the present invention. It is supplied to the filtration facility B to become purified water.

まず、原水Gは前処理設備Aの急速攪拌槽2に供給され、ここで凝集剤が添加されるとともに急速攪拌がなされ、原水G中の汚濁物質は凝集剤と接触混合されフロックとなる。急速攪拌後の原水Gは次の緩速攪拌槽3に供給され、ここで緩やかな攪拌が施されてフロックはさらに凝集、成長する。次いで、原水Gは沈澱池4に導かれ、成長したフロックは重力により沈降分離される。なお、富栄養化などにより原水水質が悪化している水源ではフロックが分離された上澄みの原水はオゾン攪拌槽5及び活性炭吸着槽6により異臭味、有機物などが分解、吸着除去され、被処理水Hとして本発明の複合ろ過設備Bに供給される。   First, the raw water G is supplied to the rapid stirring tank 2 of the pretreatment facility A, where a flocculant is added and rapid stirring is performed, and the pollutant in the raw water G is contacted and mixed with the flocculant to form a floc. The raw water G after rapid stirring is supplied to the next slow stirring tank 3, where gentle stirring is performed, and the flocs further aggregate and grow. Next, the raw water G is guided to the settling basin 4, and the grown floc is separated by gravity. In the case of water sources whose raw water quality has deteriorated due to eutrophication or the like, the raw raw water from which flocs have been separated is decomposed and adsorbed by the ozone agitation tank 5 and activated carbon adsorption tank 6 to remove off-flavors, organic substances, etc. H is supplied to the combined filtration equipment B of the present invention.

この複合ろ過設備Bはメディアろ過池(以下、単にメディアということがある)Mと膜ろ過装置(以下、メンブレンろ過装置又は単にメンブレンということがある)Sの二つの異なったろ過手段(ろ過装置)が設備として一体となって構成されている。メディアろ過池Mは被処理水Hをろ過槽(以下、槽と略称することがある)11の下部にろ材層12を有しており、その上部にはトラフ13が設けられている。この槽11のろ材層12下部には集水装置14があり、メディアろ過された集水装置14から浄水J1が配管を介して浄水池15に送られるようになっている。そして、メディアろ過池Mの槽11の内部上方で被処理水の水位(L)よりも下方となる位置に複数の膜モジュール16をユニット化して配設した浸漬型の膜ろ過装置Sが設置されている。膜モジュール16は例えば中空糸あるいはセラミックで構成される。   This combined filtration facility B has two different filtration means (filtration devices): a media filtration pond (hereinafter sometimes referred to simply as media) M and a membrane filtration device (hereinafter also referred to as membrane filtration device or simply as membrane) S. Are integrated as a facility. The media filtration basin M has a filter medium layer 12 below a filtration tank (hereinafter sometimes abbreviated as a tank) 11 for water to be treated H, and a trough 13 is provided above the filter medium layer 12. A water collecting device 14 is provided at the lower part of the filter medium layer 12 of the tank 11, and purified water J1 is sent from the water collecting device 14 subjected to media filtration to the purified water reservoir 15 through a pipe. Then, an immersion type membrane filtration device S in which a plurality of membrane modules 16 are arranged as a unit at a position below the water level (L) of the water to be treated is installed inside the tank 11 of the media filtration pond M. ing. The membrane module 16 is made of, for example, a hollow fiber or ceramic.

この膜モジュール16は、図1の槽11の側断面を示した図2のように、槽11の下部両側に分割して設けられたろ材層12及びその上にあるトラフ13の中央に配設されたメディアろ過池Mにおける被処理水Hの逆洗排水の排出用の樋状を有したガリット(溝)19の直上に浸漬配置されている。ガリット19は槽11の全長に亘って設けられ、トラフ13はその左右に分岐された形で連絡され、流入渠(後述)を通じて供給された被処理水Hはこのガリット19に入り、複数の左右対になったトラフ13(図では2つ)を介して左右に分流されてから、下部のろ材層12を通過してろ過される。膜モジュール16はこのガリット19のトラフ13との連絡部を避けた位置に間隔をあけて設けられている。   The membrane module 16 is disposed at the center of the filter medium layer 12 provided separately on both sides of the lower portion of the tank 11 and the trough 13 thereon, as shown in FIG. 2 showing a side cross section of the tank 11 of FIG. In the media filtration basin M, the garrit (groove) 19 having a bowl shape for discharging backwash drainage of the water to be treated H is immersed and disposed. The galit 19 is provided over the entire length of the tank 11, the trough 13 is connected to the left and right of the trough 13, and the treated water H supplied through the inflow trough (described later) enters the galit 19, After being diverted to the left and right through a pair of troughs 13 (two in the figure), they are filtered through the lower filter medium layer 12. The membrane module 16 is provided at a position away from the connecting portion of the garit 19 with the trough 13.

膜ろ過装置Sにおいては、槽11に供給、貯留された被処理水Hが各膜モジュール16からポンプ17により配管を介して吸引ろ過され、前記浄水池15に浄水J2となって送られる。なお、18は流量計であり、これにより浄水J2の流量を測定し、ポンプ17にフィードバックすることで、任意の膜ろ過流束、または任意の流量に調整することができる。なお、場合によっては、槽11と浄水池15の水位差を利用して流量計18と流量調節弁でろ過を行うことができる。   In the membrane filtration device S, the to-be-treated water H supplied and stored in the tank 11 is suction filtered from each membrane module 16 via a pipe by a pump 17 and sent to the water purification basin 15 as purified water J2. Reference numeral 18 denotes a flow meter, which can be adjusted to an arbitrary membrane filtration flux or an arbitrary flow rate by measuring the flow rate of the purified water J2 and feeding it back to the pump 17. In some cases, it is possible to perform filtration with the flow meter 18 and the flow control valve using the difference in water level between the tank 11 and the water purification tank 15.

メディアろ過池Mの上方には、メディアろ過池Mのろ材層12及び膜ろ過装置Sの膜モジュール16の目詰まりによるろ過効率の低下を防止すべく、これらの洗浄(逆洗)を行うために使用される洗浄水Kが貯留された洗浄水槽23が高架上に設置されている。なお、高架式洗浄水槽が設置できない場合、浄水池15にメディアろ過池Mと膜ろ過装置Sの逆洗のための専用ポンプを設置する。この洗浄水槽23はその配管により、ろ過処理されたそれぞれの浄水J1及びJ2を浄水池15に送る配管の※1及び※2の位置に接続されており、洗浄水Kをメディアろ過池Mのろ材層12及び膜ろ過装置Sの膜モジュール16のそれぞれに供給できるように構成されている。なお、図示しないがこれらの配管には通常のろ過時と逆洗時の切換えのためのバルブが設けられている。この例では、洗浄水槽23が高架上にあるため、メディアろ過池Mと膜ろ過装置Sの逆洗のための専用ポンプがともに不要となり、設備上有利である。24はこの洗浄水による逆洗効果を高めるためにメディアろ過池Mのろ材層12及び膜ろ過装置Sの膜モジュール16の底部に配設された空気バブリング装置(図示しない)に空気を供給するための洗浄用ブロアである。洗浄用ブロア24は両者の逆洗に共用でき一つで済むので、やはり設備面で有利である。   In order to prevent the filtration efficiency from decreasing due to clogging of the filter medium layer 12 of the media filtration pond M and the membrane module 16 of the membrane filtration device S above the media filtration pond M A washing water tank 23 in which the washing water K to be used is stored is installed on the elevated. If an elevated washing tank cannot be installed, a dedicated pump for backwashing the media filtration basin M and the membrane filtration device S is installed in the water purification basin 15. This washing water tank 23 is connected to the positions of * 1 and * 2 of the pipes that send the filtered purified water J1 and J2 to the purified water basin 15 through the pipes. It can be supplied to each of the layer 12 and the membrane module 16 of the membrane filtration device S. Although not shown, these pipes are provided with valves for switching between normal filtration and backwashing. In this example, since the washing water tank 23 is on the elevated, a dedicated pump for backwashing the media filtration basin M and the membrane filtration device S becomes unnecessary, which is advantageous in terms of equipment. 24 is for supplying air to an air bubbling device (not shown) disposed at the bottom of the filter medium layer 12 of the media filtration basin M and the membrane module 16 of the membrane filtration device S in order to enhance the backwashing effect by the washing water. This is a cleaning blower. Since only one cleaning blower 24 can be used for both backwashing, it is advantageous in terms of equipment.

本発明にかかるこの複合ろ過設備Bの基本的なろ過の特長概念を図3の模式図(正面図)によって説明すると、被処理水Hは槽11の図の上部左側から流入し、その一部は槽11内の上部に設置されたメンブレンろ過装置(膜ろ過装置)Sの膜モジュール16に入って、図の右側に吸引されて流れ、膜モジュール16を通過する過程で膜ろ過がなされ、浄水J2として槽11外に排出される。そして、この膜ろ過と同時に被処理水Hの残りの一部は槽11内を下降して流れ、メディアろ過池Mのろ材層12を図の上から下に通過し、この過程でメディアろ過がなされ、集水装置14を経て、浄水J1として槽11外に排出される。そして、これら膜ろ過によって得られた浄水J1とメディアろ過によって得られた浄水J2とが浄水池15において一緒に集水(J)され、水道水等の浄水用途に使用される。   The basic concept of filtration of the composite filtration equipment B according to the present invention will be described with reference to the schematic diagram (front view) of FIG. 3. Enters the membrane module 16 of the membrane filtration device (membrane filtration device) S installed in the upper part of the tank 11 and is sucked and flows to the right side of the figure. It is discharged out of the tank 11 as J2. At the same time as the membrane filtration, the remaining part of the treated water H flows down in the tank 11 and passes through the filter medium layer 12 of the media filtration pond M from the top to the bottom. Then, after passing through the water collecting device 14, it is discharged out of the tank 11 as purified water J1. The purified water J1 obtained by the membrane filtration and the purified water J2 obtained by the media filtration are collected together (J) in the purified water pond 15 and used for water purification purposes such as tap water.

このように、本発明では、メディアろ過池Mとこれに一体的に組み込まれた膜ろ過装置
(メンブレンろ過装置)Sとからなる複合ろ過設備によって、メディアろ過と膜ろ過の双方を同時並行して行うことが可能な複合ろ過プロセスを実現できるものである。従って、本発明の採用により、運転形態の異なるメディアろ過と膜ろ過を積極的に併用、協同させることによってそれぞれのプロセスの利点を最大限に生かしたリスクの少ない極めて効率的なプロセスによってさまざまな水処理を行うことができる。
As described above, in the present invention, both the media filtration and the membrane filtration are performed simultaneously by the composite filtration facility including the media filtration basin M and the membrane filtration device (membrane filtration device) S integrated therein. It is possible to realize a composite filtration process that can be performed. Therefore, by adopting the present invention, media filtration and membrane filtration with different operation modes are actively used together and cooperated, and various water treatments are performed by an extremely efficient process with less risk that maximizes the advantages of each process. Processing can be performed.

すなわち、本発明によるとメディアろ過と膜ろ過を同時に実施できることから、メディアろ過池単独によるろ過に比べて、高速でろ過することができ、且つ両者のろ過速度(流速)を調整して処理量をコントロールすることにより、被処理水の供給量の増加や変動(あるいは浄水量の変動要求)への対応力が大幅に向上する。この供給量の増加に対しては、例えば100m2/池の急速ろ過をモデルとした場合、従来のメディアろ過池では12,000〜24,000m3/日/池であるのに対して、本発明では12,000〜48,000m3/日/池の対応が可能となる。 That is, according to the present invention, media filtration and membrane filtration can be performed at the same time, so that filtration can be performed at a higher speed compared to filtration by a media filtration pond alone, and the throughput can be adjusted by adjusting the filtration rate (flow rate) of both. By controlling, the ability to cope with an increase or fluctuation in the amount of treated water (or demand for fluctuations in the amount of purified water) is greatly improved. For example, when the rapid filtration of 100 m 2 / pond is used as a model for the increase in the supply amount, the conventional media filtration pond has 12,000 to 24,000 m 3 / day / pond, whereas the present invention has 12,000. -48,000m 3 / day / pond can be handled.

また、供給量の変動ばかりでなく、被処理水の水質変化に対しても、両者の処理量の比率を変化させることで要求される一定の水質の浄水を製造することが可能となる。   Moreover, it becomes possible not only to change the supply amount, but also to produce purified water having a constant water quality that is required by changing the ratio of the treatment amounts of both of the treated water.

しかも、本発明により、メディアろ過池の設置スペースで膜ろ過装置を一体的に組み込むことができるため、設置面積当りの水処理量(浄水量)を著しく向上させることが可能となり、コンパクトな設備で実施でき、設備全体の設置面積を小さくすることができ、これに伴って敷地の確保も容易となり、設備投資も少なくて済むことになる。特に、既設のメディアろ過池における供給量の増加に対しては、増設のための設置スペースを新たに確保する必要がなく膜ろ過装置をメディアろ過池に組み込むだけで対処できるので、実用性に富むものである。   In addition, according to the present invention, the membrane filtration device can be integrated in the installation space of the media filtration pond, so that the water treatment amount (purified water amount) per installation area can be remarkably improved, and compact equipment can be used. It can be implemented, and the installation area of the entire facility can be reduced. Accordingly, the site can be easily secured and the capital investment can be reduced. In particular, the increase in the supply volume of existing media filtration ponds can be dealt with by simply installing a membrane filtration device in the media filtration pond without the need for additional installation space for expansion. It is a waste.

さらに、膜ろ過装置単独に比べて、膜モジュールの目詰まりやその交換が軽減され、安定した運転、操業を継続でき、ランニングコストも減少することになる。
加えて、本発明によれば、膜ろ過装置(膜モジュール)の逆洗排水をそのままメディアろ過池でろ過することができ、膜ろ過の回収率を100%に維持することができる。
次に、本発明の複合ろ過設備について、他の実施形態により、逆洗などの処理方法を含めて、図4〜図7を参照してより詳しく開示する。
Furthermore, as compared with the membrane filtration device alone, clogging of the membrane module and its replacement are reduced, stable operation and operation can be continued, and running cost is also reduced.
In addition, according to the present invention, the backwash waste water from the membrane filtration device (membrane module) can be filtered as it is in the media filtration basin, and the membrane filtration recovery rate can be maintained at 100%.
Next, the composite filtration equipment of the present invention will be disclosed in more detail with reference to FIGS. 4 to 7 including a processing method such as backwashing according to another embodiment.

図4は、本設備の正面切欠き斜視図であり、メディアろ過池の槽11の下部にろ材層12が有り、その上部には膜ろ過装置の膜モジュール16が設けられている。そして、この実施形態では、4系列の膜モジュール16が、槽11の幅方向の中央部にその長手方向に伸びて配置されたガリット19の溝の中に収納された状態で並び、槽11内に供給された被処理水Hの水位よりも下に有り、その水中に浸漬して設けられている。つまり、本例はこのガリット19を膜モジュール16の浸漬槽として活用している形態である。ガリット19の両側にはこれに連通して直角方向に分岐したトラフ13がそれぞれ5個ずつ配設されている。20は被処理水Hを上記ガリット19に流入させるために槽11の一方の側壁上部に設けられた流入渠であり、21はろ材層12によってメディアろ過された浄水を槽11の外へ排出するために同側壁下部に設けられた流出渠である。また、22はろ材層12の逆洗後の排水を流出させるときなどのために、槽11の他方(反対側)の側壁下部に設置された排水渠である。17は同槽11の外側で排水渠22の上壁に載設された膜ろ過などの際に用いるポンプである。   FIG. 4 is a front cutaway perspective view of the present facility, in which a filter medium layer 12 is provided at the bottom of the tank 11 of the media filtration pond, and a membrane module 16 of a membrane filtration device is provided above the filter medium layer 12. In this embodiment, the four series of membrane modules 16 are arranged in a state of being housed in the groove of the galit 19 disposed in the center in the width direction of the tank 11 and extending in the longitudinal direction thereof. It is below the water level of the water to be treated H supplied to the water, and is immersed in the water. That is, this example is a form in which this galit 19 is utilized as an immersion tank for the membrane module 16. On each side of the galit 19, five troughs 13 communicating with this and branching in a right angle direction are arranged. 20 is an inflow trough provided on the upper side of one side wall of the tank 11 in order to allow the water H to be treated to flow into the galit 19, and 21 is for discharging the purified water media-filtered by the filter medium layer 12 out of the tank 11. Therefore, it is an outflow gutter provided at the bottom of the side wall. Reference numeral 22 denotes a drainage basin installed at the lower part of the other side (opposite side) of the tank 11 in order to drain the drainage of the filter medium layer 12 after backwashing. 17 is a pump used for membrane filtration or the like mounted on the upper wall of the drain 22 outside the tank 11.

図5は本実施形態のろ過設備により、膜ろ過とメディアろ過を同時に実施する通常の複合ろ過時のフローを示した正面切欠き斜視図であるが、これにより、本設備を用いた複合ろ過プロセスの概要を説明する。被処理水H(及びろ過後の浄水)の流れは矢印で示して
いる。
FIG. 5 is a front cutaway perspective view showing a flow during normal combined filtration in which membrane filtration and media filtration are simultaneously performed by the filtration facility of the present embodiment, whereby a combined filtration process using the facility is performed. The outline of will be described. The flow of the water to be treated H (and purified water after filtration) is indicated by arrows.

前処理設備により前処理された被処理水Hは本複合ろ過設備の流入渠20により、槽11内に流れ込み、ガリット19、トラフ13及びガリット19内の膜モジュール16などが完全に浸漬されるまで槽11内に満たされて、流入渠20の水位と同じ水位に達した時点で、メディアろ過池及び膜ろ過装置のバルブやポンプ起動手段を操作して稼動を開始する。両装置によるろ過速度は被処理水Hの供給量等に合わせて、予め、またはその稼動途中において適切な
範囲に設定または変更される。この稼動に伴って、ガリット19に連続的に流入した被処理水Hは、先ず、膜ろ過装置の複数の膜モジュール16にポンプ17により吸い込まれて膜ろ過され、これによって処理された浄水J1は槽11外に排出され前記浄水池15に送られる。また、流入した被処理水Hの一部は、メディアろ過池のろ材層12を通過してメディアろ過され、これによって処理された浄水J2は集水装置14を経て、順次、流出渠21に流出し、同様にして浄水池15に送られる。
The treated water H pretreated by the pretreatment facility flows into the tank 11 by the inflow tank 20 of the combined filtration facility until the galit 19, trough 13, and the membrane module 16 in the galit 19 are completely immersed. When the tank 11 is filled and reaches the same water level as that of the inflow trough 20, the operation is started by operating the valves and pump activation means of the media filtration pond and the membrane filtration device. The filtration rate by both apparatuses is set or changed in an appropriate range in advance or during its operation according to the supply amount of the water to be treated H or the like. With this operation, the treated water H continuously flowing into the galit 19 is first sucked by the pump 17 into the plurality of membrane modules 16 of the membrane filtration device and subjected to membrane filtration, and the purified water J1 treated thereby is It is discharged out of the tank 11 and sent to the water purification tank 15. In addition, a part of the treated water H that has flowed in passes through the filter medium layer 12 of the media filtration pond and is subjected to media filtration, and the purified water J2 treated thereby flows out to the outflow trough 21 sequentially through the water collecting device 14. In the same manner, it is sent to the water purification pond 15.

次に、本複合ろ過設備の逆洗時のフローについて同様なその正面切欠き正面図6及び同図7によって説明する。図6は膜ろ過装置の膜モジュール16の洗浄を、また図7はメディアろ過池のろ材層12の洗浄をそれぞれ実施している状態を表している。両図における矢印は逆洗時の洗浄水(及び洗浄後の逆洗排水)の流れを示している。
そこで、膜ろ過装置の膜モジュール16の洗浄をする場合は、先の図1に示した高架上に設けた洗浄水槽23から静圧を利用して配管を介して、その洗浄水Kが膜モジュール16に供給され、逆洗される。また、同時に、図1の洗浄用ブロア24によりでバブリング用の空気が膜モジュール16の下部に送り込まれ、膜に気泡を衝突させる。そして、ガリット19内に収容、浸漬された膜モジュール16に供給され洗浄水はろ過時とは逆向きに通過するとともに、気泡の作用により洗浄がなされる。膜モジュール16を通過して洗浄を終えた逆洗排水はろ材層12を通過して通常のろ過時と同様にメディアろ過され、浄水となって集水装置14、流出渠21を介して槽11の外に排出され、浄水池15に送られる。
Next, the flow at the time of backwashing of this composite filtration equipment will be described with reference to the same front cutaway front view 6 and FIG. FIG. 6 shows a state where the membrane module 16 of the membrane filtration device is cleaned, and FIG. 7 shows a state where the media layer 12 of the media filtration basin is cleaned. The arrows in both figures show the flow of cleaning water (and backwash drainage after cleaning) during backwashing.
Therefore, when the membrane module 16 of the membrane filtration device is washed, the washing water K is removed from the washing water tank 23 provided on the overhead shown in FIG. Supplied to 16 and backwashed. At the same time, bubbling air is sent to the lower part of the membrane module 16 by the cleaning blower 24 shown in FIG. 1, and air bubbles collide with the membrane. Then, the cleaning water supplied to the membrane module 16 accommodated and immersed in the galit 19 passes in the opposite direction to that during filtration and is cleaned by the action of bubbles. The backwash wastewater that has passed through the membrane module 16 and passed through the filter medium layer 12 passes through the filter medium layer 12 and is subjected to media filtration in the same manner as during normal filtration. It is discharged outside and sent to the water purification pond 15.

また、メディアろ過池のろ材層12を逆洗する場合は、被処理水Hの流入渠20からの供給を停止し、予め槽11内の水を排出渠22より排出させて水位Lを膜モジュール16の直下の位置まで下げておき、図1の高架上の洗浄水槽23から洗浄水Kを流出渠21を介してろ材層12の下部に供給し、通常のろ過とは逆向きに下方から上方に通過させて洗浄を行う。併せて、ろ材層12の下部に図1の洗浄用ブロア24によりでバブリング用の空気がその底部に送り込まれる。そして、ろ材層12を上向きに通過し発生した洗浄後の逆洗排水はろ材層12の上部からトラフ13を経由して排水渠22に向かって流れ、この排水渠22から槽11外に排出されることになる。   In addition, when the filter medium layer 12 of the media filtration basin is backwashed, the supply of the treated water H from the inflow tank 20 is stopped, and the water in the tank 11 is discharged from the discharge tank 22 in advance, and the water level L is changed to the membrane module. It is lowered to a position directly below 16, and the wash water K is supplied from the wash water tank 23 on the elevated line in FIG. Pass through to clean. At the same time, bubbling air is sent to the bottom of the filter medium layer 12 by the cleaning blower 24 of FIG. Then, the washed backwash drainage generated by passing upward through the filter medium layer 12 flows from the upper part of the filter medium layer 12 through the trough 13 toward the drainage basin 22 and is discharged out of the tank 11 from the drainage basin 22. Will be.

なお、膜モジュール16を薬品を用いて洗浄する場合は、目的とする薬液を可搬式の薬液移送ポンプによりガリット19内に供給して、これを満たし、膜モジュール16をこの薬液に浸漬する方法、すなわちガリット19を薬液の浸漬槽として利用する洗浄方法を採用すれば良い。   In the case where the membrane module 16 is cleaned using a chemical, the target chemical solution is supplied into the galit 19 by a portable chemical solution transfer pump, and this is satisfied, and the membrane module 16 is immersed in this chemical solution. That is, a cleaning method using the galit 19 as a chemical solution immersion tank may be employed.

実施形態の説明においては膜モジュール16としては中空糸膜を示したが、勿論、本発明はこれに限定されるものではなく、平膜、管状膜等ほかのタイプを用いても差し支えないものである。また、浄水を得る場合は、MF膜、UF膜などが好適に用いられる。メディアである粒状ろ材は、砂、アンスラサイト、粒状活性炭などを用いることができる。   In the description of the embodiment, a hollow fiber membrane is shown as the membrane module 16, but of course the present invention is not limited to this, and other types such as a flat membrane and a tubular membrane may be used. is there. Moreover, when obtaining purified water, MF membrane, UF membrane, etc. are used suitably. Sand, anthracite, granular activated carbon, etc. can be used for the granular filter medium which is a medium.

A:前処理設備 B:複合ろ過設備 H:被処理水 M:メディアろ過池 S:膜ろ過装置 J1、J 2:浄水 K:洗浄水11:ろ過槽 12:ろ材層 13:トラフ 14:集水装置 15:浄水池 16:膜モジュール 17:ポンプ 18:流量計 19:ガリット 20:流入渠 21:流出渠 22:排出渠 23:洗浄水槽 24:洗浄用ブロア   A: Pretreatment equipment B: Combined filtration equipment H: Treated water M: Media filtration pond S: Membrane filtration device J1, J2: Clean water K: Wash water 11: Filtration tank 12: Filter media layer 13: Trough 14: Water collection Equipment 15: Water purification tank 16: Membrane module 17: Pump 18: Flow meter 19: Galit 20: Inflow tank 21: Outflow tank 22: Discharge tank 23: Washing water tank 24: Cleaning blower

Claims (5)

メディアろ過池と、該メディアろ過池のろ過槽に、ろ過時における被処理水の水位よりも下方となる位置に複数の膜モジュールを配設した膜ろ過装置とからなり、前記ろ過槽に供給された被処理水を、前記メディアろ過池と前記膜ろ過装置の双方によって同時にろ過処理して前記メディアろ過池と前記膜ろ過装置の双方からろ過後の浄水を同時に得るように構成したことを特徴とするメディア及び膜ろ過複合ろ過設備。   A medium filtration pond, and a membrane filtration device in which a plurality of membrane modules are arranged at a position below the water level of the water to be treated at the time of filtration, and supplied to the filtration tank. The treated water is filtered at the same time by both the media filtration basin and the membrane filtration device, and purified water is obtained at the same time from both the media filtration pond and the membrane filtration device. Media and membrane filtration combined filtration equipment. 膜ろ過装置の膜モジュールの配設位置がメディアろ過池のろ過槽の内部上方である請求項1に記載のメディア及び膜ろ過複合ろ過設備。   The media and membrane filtration combined filtration equipment according to claim 1, wherein the position of the membrane module of the membrane filtration device is located above the inside of the filtration tank of the media filtration pond. メディアろ過池には被処理水が流入するガリットを有し、膜モジュールがガリットの溝の中に収容された状態で配置される請求項1または2に記載のメディア及び膜ろ過複合ろ過設備。   The media and membrane filtration combined filtration facility according to claim 1 or 2, wherein the media filtration pond has a galit into which treated water flows, and the membrane module is disposed in a state where the membrane module is accommodated in a groove of the galit. 前記ガリットにはその直角方向に分岐したトラフが配設されている請求項3に記載のメディア及び膜ろ過複合ろ過設備。   The media and membrane filtration combined filtration equipment according to claim 3, wherein a trough branched in a direction perpendicular to the galit is disposed. 請求項1に記載のメディア及び膜ろ過複合ろ過設備を用いた運転方法において、被処理水の供給量の変動、要求浄水量の変動または被処理水の水質変化に対して、メディアろ過と膜ろ過の処理量の比率を変化させて浄水を製造するメディア及び膜ろ過複合ろ過設備の運転方法。
In the operation method using the media and membrane filtration combined filtration equipment according to claim 1, media filtration and membrane filtration with respect to fluctuations in the supply amount of the treated water, fluctuations in the required purified water amount or changes in the quality of the treated water The method of operating a medium and a membrane filtration combined filtration facility for producing purified water by changing the ratio of the amount of treatment.
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Publication number Priority date Publication date Assignee Title
CN105688501A (en) * 2016-03-01 2016-06-22 昆山东大智汇技术咨询有限公司 Membrane method concentration process for aloe juice gel
CN105688497A (en) * 2016-03-03 2016-06-22 中国市政工程西北设计研究院有限公司天津分院 Anti-floating filter plate of upward flow suspension filter material filter pool and preparation and installation method thereof

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JPH07124407A (en) * 1993-11-01 1995-05-16 Maezawa Ind Inc Sedimentation and filtration equipment
JPH07275887A (en) * 1994-04-06 1995-10-24 Toto Ltd Purifying tank
JPH0833834A (en) * 1994-07-22 1996-02-06 Ishigaki Mech Ind Co Washing of composite filter

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JPH07124407A (en) * 1993-11-01 1995-05-16 Maezawa Ind Inc Sedimentation and filtration equipment
JPH07275887A (en) * 1994-04-06 1995-10-24 Toto Ltd Purifying tank
JPH0833834A (en) * 1994-07-22 1996-02-06 Ishigaki Mech Ind Co Washing of composite filter

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105688501A (en) * 2016-03-01 2016-06-22 昆山东大智汇技术咨询有限公司 Membrane method concentration process for aloe juice gel
CN105688497A (en) * 2016-03-03 2016-06-22 中国市政工程西北设计研究院有限公司天津分院 Anti-floating filter plate of upward flow suspension filter material filter pool and preparation and installation method thereof

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