JP5119989B2 - Storage method of solid-liquid separation membrane - Google Patents

Storage method of solid-liquid separation membrane Download PDF

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JP5119989B2
JP5119989B2 JP2008060609A JP2008060609A JP5119989B2 JP 5119989 B2 JP5119989 B2 JP 5119989B2 JP 2008060609 A JP2008060609 A JP 2008060609A JP 2008060609 A JP2008060609 A JP 2008060609A JP 5119989 B2 JP5119989 B2 JP 5119989B2
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separation membrane
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JP2009214023A5 (en
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敦 北中
和弥 杉田
寛生 高畠
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Toray Industries Inc
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    • 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
    • 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
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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  • Separation Using Semi-Permeable Membranes (AREA)
  • Activated Sludge Processes (AREA)

Description

本発明は、活性汚泥と処理水を固液膜分離する装置内に設置されて使用された分離膜を、運転休止後に保管する方法に関する。   The present invention relates to a method for storing a separation membrane used in an apparatus that separates activated sludge and treated water from a solid-liquid membrane after operation is stopped.

活性汚泥と処理水を膜により固液分離させる膜分離活性汚泥法は、下水や廃水を浄化処理する設備において使われてきている。このような膜分離活性汚泥法を行う設備は、年中稼働させる設備もあるが、リゾート地での廃水処理に使用される場合のように1年間のうちの特定期間に数ヶ月程度しか稼働させないといった設備もある。しかしながら、使用する分離膜の種類によっては、一度水中に設置させてしまうと、固液分離性能を保持するために、その後は湿潤状態で保つことが必要な場合がある。すなわち、このような分離膜の場合、乾燥状態にすることにより膜表面構造に悪影響を及ぼし、膜性能の低下などをおこす。従って、上記のような膜処理設備においては、設備の稼働しない時期には、膜に損傷等を与えないでかつ再稼働時には高い膜性能を発揮できるような状態で保管しておくことが望まれている。   The membrane separation activated sludge method in which activated sludge and treated water are separated into solid and liquid by a membrane has been used in facilities for purifying sewage and wastewater. Although facilities that perform such a membrane separation activated sludge process have facilities that operate throughout the year, they operate only for a few months during a specific period of the year, such as when used for wastewater treatment in resort areas. There are also such facilities. However, depending on the type of separation membrane to be used, once it is placed in water, it may be necessary to keep it in a wet state after that in order to maintain solid-liquid separation performance. That is, in the case of such a separation membrane, the membrane surface structure is adversely affected by making it dry, and membrane performance is degraded. Therefore, in the membrane treatment equipment as described above, it is desirable to store the membrane processing equipment in such a state that it does not damage the membrane or the like when the equipment is not in operation and can exhibit high membrane performance at the time of restart. ing.

そこで、実際の保管方法としては、運転休止した後にも槽内に水を貯めておき、その中に分離膜エレメントを保管することが考えられる。しかしながら、冬期には低温により槽内の水が凍結してしまい、凍結時の水膨張により分離膜自身に悪影響を及ぼす懸念がある。その他の保管方法としては、分離膜の膜面を乾燥させないように、膜エレメント全体を密閉した非透水性ポリマ袋などに入れて保管することも考えられる。しかし、密閉袋の準備や梱包作業などが煩雑であり、現実的ではない。   Therefore, as an actual storage method, it can be considered that water is stored in the tank even after the operation is stopped, and the separation membrane element is stored therein. However, in winter, the water in the tank freezes due to low temperatures, and there is a concern that the separation membrane itself may be adversely affected by water expansion during freezing. As another storage method, it is also conceivable to store the entire membrane element in a sealed non-permeable polymer bag or the like so as not to dry the membrane surface of the separation membrane. However, the preparation and packing of the sealed bag are complicated and not practical.

また、分離膜を湿潤状態で長期間保管するための保存液として、
安息香酸及び/又は安息香酸塩を0.05〜0.5質量%の範囲で含む水溶液が特許文献1で提案されている。この保存液は安全性が高く、細菌や黴に対する殺菌効果が高いものであるが、分離膜を浸漬させて保存することが必要であり、活性汚泥処理水の固液分離装置内に設置されて使用された分離膜の保管には適用困難である。
In addition, as a preservation solution for storing the separation membrane in a wet state for a long time,
Patent Document 1 proposes an aqueous solution containing benzoic acid and / or benzoate in a range of 0.05 to 0.5% by mass. This preservation solution is highly safe and has a high bactericidal effect against bacteria and sputum, but it must be stored by immersing the separation membrane, and it is installed in a solid-liquid separation device for activated sludge treated water. It is difficult to apply to storage of used separation membranes.

さらにまた、ポリアミド、ポリイミド、ポリスルホンからなる湿潤半透膜を製造した後、乾燥させて保管するための方法として、グリセリン等の多価アルコールの水溶液で処理した後に乾燥して保管する方法が特許文献2で開示されている。しかし、この乾燥保管方法は、製造後の未使用の逆浸透膜を保管することを目的としたものであり、この方法をそのまま、使用済みの固液分離膜の乾燥保管に適用することは困難である。   Further, as a method for producing a wet semipermeable membrane made of polyamide, polyimide, polysulfone, and drying and storing it, a method of treating it with an aqueous solution of a polyhydric alcohol such as glycerin and then drying and storing the patent document. 2 is disclosed. However, this dry storage method is intended to store unused reverse osmosis membranes after production, and it is difficult to apply this method as it is to dry storage of used solid-liquid separation membranes. It is.

特開2007−63222号公報JP 2007-63222 A 特開昭58−156307号公報JP 58-156307 A

そこで、本発明は、活性汚泥と処理水を固液膜分離する装置内に設置されて使用された分離膜を、運転休止後に乾燥状態で保管するに際し、分離膜へ損傷を与えず、膜性能を低下させない、膜保管方法を提供することを目的とする。   Therefore, the present invention provides a membrane performance without damaging the separation membrane when storing the separation membrane used in the apparatus for separating the activated sludge and the treated water in a solid-liquid membrane, in a dry state after the operation is stopped. An object of the present invention is to provide a film storage method that does not lower the temperature.

かかる目的を達成するために、本発明の固液分離膜の保管方法は、次のとおり特定される。
1. 活性汚泥と処理水を固液膜分離する装置内に設置されて使用された分離膜を乾燥状態で保管する際、分離膜が設置されている固液膜分離装置の膜二次側から洗液を流入させて静置洗浄し、ついで、界面活性剤および多価アルコールからなる群から選ばれる少なくとも1つの親水化剤を含む水溶液を膜二次側から注入して膜面を親水化させた後、分離膜を乾燥し、保管することを特徴とする固液分離膜の保管方法
In order to achieve this object, the storage method of the solid-liquid separation membrane of the present invention is specified as follows.
1. When storing activated sludge and installed treated water to solid-liquid membrane separation to the device isolation film used in a dry state, washing the membrane secondary side of the solid-liquid membrane separation device separating film is placed Kiyoshi liquid was allowed to flow by static置洗 Kiyoshi and then a hydrophilic membrane surface by injecting aqueous solution from the membrane secondary side comprising at least one parent water agent selected from the group consisting of surfactant and a polyhydric alcohol A method for storing a solid-liquid separation membrane, wherein the separation membrane is dried and stored after conversion .

本発明法を適用すると、下水や工場廃水などの有機性汚水等の原水を生物処理槽内で活性汚泥処理し、活性汚泥を含む処理混合液を処理槽内で浸漬型分離膜により膜分離処理し、浸漬型分離膜の下部より曝気する形態をとる膜分離活性汚泥処理の設備を休止させる際に、活性汚泥処理水の固液膜分離装置内に設置されて使用されていた分離膜を乾燥状態で保管させることができ、かつ、乾燥保管時に分離膜表面に膜の乾燥に伴う損傷を与えることがなく、しかも再稼働時には高い膜性能を発揮することができる状態で保管することが可能となる。   When the method of the present invention is applied, raw water such as organic sewage such as sewage and factory wastewater is treated with activated sludge in a biological treatment tank, and a treatment liquid mixture containing activated sludge is subjected to membrane separation treatment with a submerged separation membrane in the treatment tank. Then, when suspending the membrane separation activated sludge treatment equipment that takes the form of aeration from the bottom of the submerged separation membrane, the separation membrane installed and used in the solid-liquid membrane separation device of activated sludge treated water is dried. It can be stored in a dry state, and it can be stored in a state that does not damage the surface of the separation membrane during drying storage and can exhibit high membrane performance during re-operation. Become.

本発明の分離膜の乾燥保管方法は、下水や工場廃水などの有機性汚水等の原水を生物処理槽内で活性汚泥処理し、活性汚泥を含む処理混合液を処理槽内で浸漬型分離膜により膜分離処理し、浸漬型分離膜の下部より曝気する形態をとる膜分離活性汚泥処理の設備において水中に浸漬されて使用されていた分離膜に対し適用される。   The separation membrane dry storage method of the present invention is to treat raw water such as organic sewage such as sewage and factory wastewater in the biological treatment tank, and treat the mixed liquid containing the activated sludge in the treatment tank. This is applied to a separation membrane that has been used by being immersed in water in a facility for membrane separation activated sludge treatment in which the membrane is subjected to a membrane separation treatment and aerated from the lower part of the submerged separation membrane.

本発明法を適用することができる廃水処理装置の一例を図1に示す。この廃水処理装置は、活性汚泥を投入し生物処理を行う曝気槽(生物処理槽)2と、その曝気槽2に原水(廃水)1を供給する原水供給ポンプ3と、生物処理された活性汚泥混合液を固液分離する膜分離装置4と、膜分離装置で固液分離された膜透過液を吸引する吸引ポンプ5と、曝気槽内の余剰汚泥を引き抜く汚泥引き抜きポンプ6が設けられている。膜分離装置4は曝気槽2内の液中に浸漬されており、その膜分離装置の下方には、空気を供給し、好気処理を進行させるとともに、膜面の洗浄を行うための微細気泡を発生させる散気装置8が設けられ、この散気装置には空気供給装置7により空気が供給されている。   An example of a wastewater treatment apparatus to which the method of the present invention can be applied is shown in FIG. This waste water treatment apparatus includes an aeration tank (biological treatment tank) 2 for performing biological treatment by introducing activated sludge, a raw water supply pump 3 for supplying raw water (waste water) 1 to the aeration tank 2, and biologically treated activated sludge. There are provided a membrane separation device 4 for solid-liquid separation of the mixed liquid, a suction pump 5 for sucking the membrane permeate separated by the membrane separation device, and a sludge extraction pump 6 for extracting excess sludge in the aeration tank. . The membrane separation device 4 is immersed in the liquid in the aeration tank 2, and air is supplied below the membrane separation device to advance the aerobic treatment and fine bubbles for cleaning the membrane surface. An air diffuser 8 is provided, and air is supplied to the air diffuser by an air supply device 7.

曝気槽2としては、活性汚泥を貯え、膜分離装置4を被処理水と活性汚泥の混合液に浸漬することができれば、大きさや材質等は特に制限されるものではなく、例えば、コンクリート槽、繊維強化プラスチック槽などが好ましく用いられる。また、曝気槽の内部が複数に分割された槽構造でもよいし、その複数に分割されている槽のうちの一部の槽内に膜分離装置4を浸漬することにしてもよい。   As the aeration tank 2, if the activated sludge is stored and the membrane separation device 4 can be immersed in the mixed liquid of the water to be treated and the activated sludge, the size and material are not particularly limited. For example, a concrete tank, A fiber reinforced plastic tank or the like is preferably used. Moreover, the tank structure by which the inside of the aeration tank was divided | segmented into plurality may be sufficient, and you may decide to immerse the membrane separation apparatus 4 in the one part tank among the tank divided | segmented into the plurality.

原水供給ポンプ3は、原水(廃水)1を曝気槽2に送液することができるポンプであれば特に制限されるものではなく、渦巻ポンプ、ディフューザーポンプ、渦巻斜流ポンプ、斜流ポンプ、ピストンポンプ、プランジャポンプ、ダイアフラムポンプ、歯車ポンプ、スクリューポンプ、ベーンポンプ、カスケードポンプ、ジェットポンプなどを用いることができる。   The raw water supply pump 3 is not particularly limited as long as the raw water (waste water) 1 can be fed to the aeration tank 2, and is not limited to a vortex pump, a diffuser pump, a vortex mixed flow pump, a mixed flow pump, a piston. A pump, plunger pump, diaphragm pump, gear pump, screw pump, vane pump, cascade pump, jet pump, or the like can be used.

膜分離装置4は、固液分離膜が配設されている装置であり、その分離膜としては、中空糸膜タイプ、平膜タイプのものがある。ろ過膜(分離膜)の取り扱い性や物理的耐久性を向上させるためには、例えば、フレームの両面にろ過水流路材を挟んで平膜を接着した構造の平膜エレメントを備えていることが望ましい。平膜エレメントの構造は上記に限定されるものではない。   The membrane separation device 4 is a device in which a solid-liquid separation membrane is disposed, and the separation membrane includes a hollow fiber membrane type and a flat membrane type. In order to improve the handleability and physical durability of the filtration membrane (separation membrane), for example, a flat membrane element having a structure in which a flat membrane is adhered to both sides of the frame with a filtrate channel material sandwiched between them is provided. desirable. The structure of the flat membrane element is not limited to the above.

吸引ポンプ5は、膜分離装置4による膜ろ過固液分離に必要な吸引力を与えるために、膜ろ過透過水を吸引するポンプであり、特に形状を制限されるものではないが、通常は減圧状態から300kPa以下で運転されるポンプが使用される。また、吸引ポンプの代わりに、自然水頭差を駆動力として膜ろ過を行うことも可能である。   The suction pump 5 is a pump that sucks the membrane permeated permeated water in order to give a suction force necessary for the membrane filtration solid-liquid separation by the membrane separation device 4 and is not particularly limited in shape, but is usually decompressed. A pump that is operated at 300 kPa or less from the state is used. Further, instead of the suction pump, it is also possible to perform membrane filtration using the natural water head difference as a driving force.

汚泥引き抜きポンプ6は、曝気槽内のMLSS濃度を一定に保つために、余剰な汚泥を定期的に引き抜くためのポンプである。粘性の高い汚泥を送液できるものであれば、特に制限されるものではない。膜分離活性汚泥法におけるMLSS濃度は3,000〜20,000mg/L程度であるが、より安定した膜ろ過流束を保つためのMLSS濃度は5,000〜15,000mg/L程度である。   The sludge extraction pump 6 is a pump for periodically extracting excess sludge in order to keep the MLSS concentration in the aeration tank constant. There is no particular limitation as long as sludge with high viscosity can be fed. The MLSS concentration in the membrane separation activated sludge method is about 3,000 to 20,000 mg / L, but the MLSS concentration for maintaining a more stable membrane filtration flux is about 5,000 to 15,000 mg / L.

空気供給装置7は、圧縮空気を送風する装置のことであり、一般にはブロア、コンプレッサ等が用いられる。送風された空気は散気装置8から槽内に気泡として送出され、この気泡により、膜分離装置の分離膜面洗浄が行なわれるとともに、生物処理(好気処理)に必要な酸素が液中に供給される。散気装置8としては、膜面上を洗浄するための気泡を発生させることができる散気管であれば特に限定されるものではないが、塩ビやステンレス配管に空気吐出孔を開けた散気管が通常使用される。その他、多孔性のゴム、セラミック、メンブレンを用いた散気管なども使用することができる。   The air supply device 7 is a device that blows compressed air, and generally a blower, a compressor, or the like is used. The blown air is sent out as bubbles from the diffuser 8 into the tank, and the bubbles clean the separation membrane surface of the membrane separator, and oxygen necessary for biological treatment (aerobic treatment) in the liquid. Supplied. The air diffuser 8 is not particularly limited as long as the air diffuser can generate bubbles for cleaning the membrane surface, but an air diffuser having an air discharge hole in a PVC or stainless steel pipe is used. Usually used. In addition, a porous rubber, ceramic, a diffuser tube using a membrane, and the like can be used.

洗浄剤貯留タンク9は、分離膜を洗浄するための薬剤を貯めておくタンクであり、使用する薬剤に対して耐性があるのであれば、特に材質が規定されるものではない。たとえば、ポリエチレン等のプラスチック製のものが使用できる。   The cleaning agent storage tank 9 is a tank for storing a medicine for cleaning the separation membrane, and the material is not particularly defined as long as it is resistant to the medicine to be used. For example, plastics such as polyethylene can be used.

親水化剤貯留タンク10は、分離膜の膜面を親水化させるための薬剤を貯めておくタンクであり、使用する薬剤に対して耐性があるのであれば、特に材質が規定されるものではない。たとえば、ポリエチレン等のプラスチック製のものが使用できる。   The hydrophilizing agent storage tank 10 is a tank for storing a chemical for hydrophilizing the membrane surface of the separation membrane, and the material is not particularly defined as long as it is resistant to the chemical used. . For example, plastics such as polyethylene can be used.

本発明法によって、活性汚泥と処理水を固液膜分離する装置内に設置されて使用された分離膜を乾燥状態で保管する際、分離膜を洗浄液により洗浄し、ついで、親水化剤を含む水溶液により膜面を親水化させた後、分離膜を乾燥し、保管する。   According to the method of the present invention, when the separation membrane installed and used in an apparatus for separating activated sludge and treated water into a solid-liquid membrane is stored in a dry state, the separation membrane is washed with a washing liquid, and then contains a hydrophilizing agent. After hydrophilizing the membrane surface with an aqueous solution, the separation membrane is dried and stored.

その分離膜の洗浄、親水化処理とは、具体的には、分離膜が設置されている固液分離装置の膜二次側から洗浄液を流入させて静置洗浄し、ついで、親水化剤を含む水溶液を膜二次側から注入して膜面を親水化させる方法により行えばよい。この方法を図1の装置において実施する場合、浸漬槽内に活性汚泥混合液が残留したままの状態で、洗浄剤貯留タンク9から、洗浄剤を、分離膜が設置されている固液膜分離装置4の膜二次側に注入し、膜の二次側および膜の表面に付着する汚れを洗浄、除去する。この洗浄は、たとえば有機性物質の汚染に対しては、次亜塩素酸ナトリウムを1,000mg/L〜5,000mg/L程度の濃度で含む水溶液にて洗浄を行えばよい。また、無機性物質の汚染に対しては、シュウ酸を0.1%〜10%程度の濃度で含む水溶液で洗浄を行えばよい。洗浄は、通常、洗浄液を膜二次側に流入させた状態で2〜3時間静置することにより行えばよい。なお、洗浄の方法については、上記以外の方法を採用してもよい。洗浄液中に含有させる洗浄剤の種類、濃度、温度等は、膜に付着している汚れの程度や種類や分離膜の材質等を考慮して選定することが好ましい。洗浄剤含有水による浸漬洗浄をおこなった後に、必要に応じて、水ですすいで洗浄剤を除去してもよい。   Specifically, the separation membrane cleaning and hydrophilization treatment are performed by allowing the cleaning liquid to flow from the membrane secondary side of the solid-liquid separation apparatus in which the separation membrane is installed, and then allowing the hydrophilizing agent to flow. What is necessary is just to carry out by the method of inject | pouring the aqueous solution containing from the film | membrane secondary side and hydrophilizing a film surface. When this method is carried out in the apparatus shown in FIG. 1, the cleaning liquid is separated from the cleaning agent storage tank 9 while the activated sludge mixed liquid remains in the immersion tank. It inject | pours into the film | membrane secondary side of the apparatus 4, and the stain | pollution | contamination adhering to the film | membrane secondary side and the film | membrane surface is wash | cleaned and removed. This cleaning may be performed, for example, with an aqueous solution containing sodium hypochlorite at a concentration of about 1,000 mg / L to 5,000 mg / L for contamination of organic substances. In addition, for contamination with inorganic substances, washing may be performed with an aqueous solution containing oxalic acid at a concentration of about 0.1% to 10%. Washing may be usually performed by leaving the solution for 2 to 3 hours in a state where the cleaning liquid is allowed to flow into the membrane secondary side. In addition, you may employ | adopt methods other than the above about the washing | cleaning method. The type, concentration, temperature, and the like of the cleaning agent contained in the cleaning liquid are preferably selected in consideration of the degree and type of dirt adhering to the membrane, the material of the separation membrane, and the like. After immersion cleaning with cleaning agent-containing water, if necessary, the cleaning agent may be removed by rinsing with water.

ついで、親水化剤貯留タンク10から、親水化剤を含む水溶液を分離膜の二次側に注入し、分離膜の親水化処理を行う。親水化処理に用いる薬剤としては、界面活性剤(たとえば、脂肪酸エステル溶液や製品:TRITON X-100(ダウケミカル)など)や多価アルコール(たとえばグリセリン溶液)を使用すればよい。使用している分離膜の材質に対して最適なもの、最適な濃度を選択化することが好ましい。そして親水化処理後は、自然乾燥などにより乾燥させ、その後に保管する。   Next, an aqueous solution containing a hydrophilizing agent is injected from the hydrophilizing agent storage tank 10 to the secondary side of the separation membrane, and the separation membrane is hydrophilized. As a chemical | medical agent used for a hydrophilization process, surfactant (for example, fatty acid ester solution and a product: TRITON X-100 (Dow Chemical) etc.) and a polyhydric alcohol (for example, glycerol solution) should just be used. It is preferable to select an optimum concentration and an optimum concentration for the material of the separation membrane used. Then, after the hydrophilic treatment, it is dried by natural drying or the like and then stored.

保管に際しては、直射日光を避けて冷暗所に保管する等、分離膜にできる限り損傷を与えないような環境下で保管することが望ましい。   When storing, it is desirable to store it in an environment that does not damage the separation membrane as much as possible, such as storing it in a cool and dark place avoiding direct sunlight.

上記形態では膜の二次側から、洗浄剤を注入し、さらに、親水化剤を注入する方法を説明したが、他の方法によって洗浄や親水化処理を行ってもよい。   In the above embodiment, the method of injecting the cleaning agent from the secondary side of the film and further injecting the hydrophilizing agent has been described. However, cleaning and hydrophilization treatment may be performed by other methods.

例えば、運転休止後に固液膜分離装置から取出された分離膜エレメントを、洗浄液に浸漬させて洗浄を行い、ついで、親水化液を含む水溶液に浸漬させて親水化処理を行うことでもよい。具体的には、分離膜による固液膜分離装置が設置されていた曝気槽内の活性汚泥処理水を排出した後の槽内に洗浄剤を含む水溶液を貯水して洗浄を行い、次いで、槽内を、親水化剤を含む水溶液に置き換えて親水化処理することでもよい。また、別に、洗浄液を貯留させた槽と、親水化剤の液を貯留させた槽とを準備しておき、固液分離装置から取り外した分離膜エレメントをその中に順次浸漬することにより、膜の洗浄、膜の親水化処理を行ってもよい。   For example, the separation membrane element taken out from the solid-liquid membrane separation apparatus after the operation stop may be immersed in a cleaning solution for cleaning, and then immersed in an aqueous solution containing a hydrophilicizing solution to perform a hydrophilic treatment. Specifically, an aqueous solution containing a cleaning agent is stored in the tank after discharging the activated sludge treated water in the aeration tank in which the solid-liquid membrane separation apparatus using the separation membrane was installed, and then the tank is washed. The inside may be replaced with an aqueous solution containing a hydrophilizing agent and subjected to a hydrophilic treatment. Separately, a tank in which the cleaning liquid is stored and a tank in which the liquid of the hydrophilizing agent is stored are prepared, and the separation membrane element removed from the solid-liquid separation device is sequentially immersed therein to thereby form a membrane. The membrane may be washed and the membrane may be hydrophilized.

以下では、本発明について、実施例を用いてさらに具体的に説明する。なお、本発明は実施例に記載の態様に限定されるものではない。
本実施例では、膜分離活性汚泥処理に用いた固液膜分離装置から分離膜エレメントを取り出し、以下の3条件について実施し、比較検討を行なった。
Hereinafter, the present invention will be described more specifically with reference to examples. In addition, this invention is not limited to the aspect as described in an Example.
In this example, the separation membrane element was taken out from the solid-liquid membrane separation apparatus used for the membrane separation activated sludge treatment, and the following three conditions were carried out for comparison.

(条件1) 薬品による洗浄(2時間)→親水化処理(2時間)→乾燥保管(6ヶ月)→運転再開
(条件2) 薬品による洗浄(2時間)→乾燥保管(6ヶ月)→運転再開
(条件3) 薬品により洗浄(2時間)→乾燥保管(6ヶ月)→親水化処理(2時間)→運転再開
(Condition 1) Cleaning with chemicals (2 hours) → Hydrophilization (2 hours) → Dry storage (6 months) → Operation restart (Condition 2) Cleaning with chemicals (2 hours) → Dry storage (6 months) → Operation restart (Condition 3) Cleaning with chemicals (2 hours) → Dry storage (6 months) → Hydrophilization treatment (2 hours) → Resumption of operation

条件1を実施した際の具体的な操作手順を、図2のフロー図に示す。また、その際の仕様を表1に示す。   The specific operation procedure when Condition 1 is implemented is shown in the flowchart of FIG. The specifications at that time are shown in Table 1.

Figure 0005119989
Figure 0005119989

薬品による洗浄直後と、各条件で運転再開直後とについて、分離膜の透水量を測定した。
透水量の測定: 浸漬槽内の水中に分離膜エレメントを浸漬し、ろ過水取り出し口に一定の水頭差を与えることにより分離膜表面に一定の水圧をかけ、所定時間における透水量を測定する。
The water permeability of the separation membrane was measured immediately after cleaning with chemicals and immediately after restarting operation under each condition.
Measurement of water permeability: The separation membrane element is immersed in the water in the immersion tank, and a constant water pressure is applied to the surface of the separation membrane by giving a constant water head difference to the filtered water outlet, and the water permeability at a predetermined time is measured.

得られた透水量の値を、薬品洗浄後の透水量に対する比でもって表し、透水性能を比較した。その結果を図3に示す。   The obtained water permeation value was expressed as a ratio to the water permeation amount after chemical cleaning, and the water permeation performance was compared. The results are shown in FIG.

図3に示す結果のとおり、条件2のように薬品洗浄後にそのまま乾燥保管すると、運転再開後の透水性はもとの半分程度にまで低下してしまった。条件3のように乾燥保管後、再び親水化処理を行ったとしても透水性能は80%程度までしか回復しなかった。一方、本発明法による条件1の操作を行うことにより、透水性能は95%と、ほぼもとの状態にまで回復することができた。   As shown in FIG. 3, when the product was dried and stored as it was after chemical cleaning as in Condition 2, the water permeability after restarting the operation was reduced to about half of the original. Even if the hydrophilization treatment was performed again after dry storage as in Condition 3, the water permeation performance recovered only to about 80%. On the other hand, by performing the operation under Condition 1 according to the method of the present invention, the water permeation performance was 95%, which was almost restored to the original state.

本発明法は、下水等の汚水を生物処理槽内で活性汚泥処理し、活性汚泥を含む処理混合液を処理槽内で浸漬型分離膜により膜分離処理する膜分離活性汚泥法の膜設備を、季節的に若しくは定期的に運転休止状態とする際に、分離膜の乾燥保管するために適用することができる。   The method of the present invention is a membrane separation activated sludge method that treats sewage such as sewage in a biological treatment tank and performs membrane separation treatment with a submerged separation membrane in a treatment tank. It can be applied to store the separation membrane in a dry state when the operation is suspended seasonally or periodically.

固液分離膜を用いた膜分離活性汚泥処理法を実施するための装置の一例を示す装置概略図である。It is an apparatus schematic diagram which shows an example of the apparatus for implementing the membrane separation activated sludge processing method using a solid-liquid separation membrane. 実施例における操作手順を示したフロー図である。It is the flowchart which showed the operation procedure in an Example. 実施例における分離膜の透水性能比を示す図である。It is a figure which shows the water-permeable performance ratio of the separation membrane in an Example.

符号の説明Explanation of symbols

1:原水(廃水)
2:曝気槽(生物処理槽)
3:原水供給ポンプ
4:膜分離装置
5:吸引ポンプ
6:汚泥引き抜きポンプ
7:空気供給装置
8:散気装置
9:洗浄剤貯留タンク
10:親水化剤貯留タンク
1: Raw water (waste water)
2: Aeration tank (biological treatment tank)
3: Raw water supply pump 4: Membrane separation device 5: Suction pump 6: Sludge extraction pump 7: Air supply device 8: Air diffuser 9: Cleaning agent storage tank 10: Hydrophilizing agent storage tank

Claims (1)

活性汚泥と処理水を固液膜分離する装置内に設置されて使用された分離膜を乾燥状態で保管する際、分離膜が設置されている固液膜分離装置の膜二次側から洗液を流入させて静置洗浄し、ついで、界面活性剤および多価アルコールからなる群から選ばれる少なくとも1つの親水化剤を含む水溶液を膜二次側から注入して膜面を親水化させた後、分離膜を乾燥し、保管することを特徴とする固液分離膜の保管方法。 When storing activated sludge and installed treated water to solid-liquid membrane separation to the device isolation film used in a dry state, washing the membrane secondary side of the solid-liquid membrane separation device separating film is placed Kiyoshi liquid was allowed to flow by static置洗 Kiyoshi and then a hydrophilic membrane surface by injecting aqueous solution from the membrane secondary side comprising at least one parent water agent selected from the group consisting of surfactant and a polyhydric alcohol A method for storing a solid-liquid separation membrane, wherein the separation membrane is dried and stored after conversion.
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