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JP3646537B2 - Method for operating microorganism-supported rotary flat membrane device - Google Patents
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JP3646537B2 - Method for operating microorganism-supported rotary flat membrane device - Google Patents

Method for operating microorganism-supported rotary flat membrane device Download PDF

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JP3646537B2
JP3646537B2 JP28025398A JP28025398A JP3646537B2 JP 3646537 B2 JP3646537 B2 JP 3646537B2 JP 28025398 A JP28025398 A JP 28025398A JP 28025398 A JP28025398 A JP 28025398A JP 3646537 B2 JP3646537 B2 JP 3646537B2
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flat membrane
microorganism
sponge
layer
water
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JP2000107784A (en
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義公 渡辺
克輝 木村
慎一 吉川
那夫紀 大熊
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Japan Science and Technology Agency
National Institute of Japan Science and Technology Agency
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Japan Science and Technology Agency
National Institute of Japan Science and Technology Agency
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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
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    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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Description

【0001】
【発明の属する技術分野】
本発明は、微生物担持型回転平膜装置の運転方法に係り、特に回転平膜に微生物を付着させて微生物層を形成し、この微生物層により用水、廃水の浄化処理を行う微生物担持型回転平膜装置の運転方法に関する。
【0002】
【従来の技術】
微生物担持型回転平膜装置は、回転平膜に微生物を付着させて微生物層を形成し、この微生物層により被処理水中のアンモニア性窒素等を生物学的に浄化処理を行い、合わせて被処理水中の濁質成分のろ過処理を行うことができる。
しかし、被処理水のろ過処理を続けるうちに被処理水中の微生物や固形物が微生物層の上に更に付着して微生物層の層厚が次第に厚くなる。微生物層の層厚が厚くなり過ぎると、ろ過性能が低下するだけでなく、生物学的な浄化処理性能も低下する。従って、微生物層の層厚が厚くなり過ぎた場合には、微生物層を剥離する必要がある。
【0003】
従来は、微生物層を剥離するために定期的に回転平膜を回転させたままろ過運転を停止、即ち吸引ポンプを停止することにより、回転平膜の回転で膜表面の微生物層を剥離していた。
【0004】
【発明が解決しようとする課題】
しかしながら、従来のように、回転平膜の微生物層を回転平膜の回転で剥離しようとすると、膜表面に乱流による一定以上の剪断力を与える必要があるため、ろ過運転時の回転平膜を高速回転させなくてはならない。従って、剥離操作のためだけに回転平膜を高速回転させる大出力のモータを設置しなくてはならないだけでなく、装置の構成部品も耐久性がよく、加工精度や組み付け精度のより部品を使用しなくてはならないので、装置コストが高価になるという欠点がある。
【0005】
更には、回転平膜の回転だけでの微生物層の剥離は、微生物層が高密度に付着した場合、剥離効率が悪く剥離操作に長時間を必要とするため、被処理水を浄化処理するための浄化処理運転時間が大幅に削減されてしまうという欠点がある。
本発明はこのような事情に鑑みてなされてもので、回転平膜に高密度で微生物層が形成されても、回転平膜を低回転数で回転させて微生物層を効果的に剥離することのできる微生物担持型回転平膜装置の運転方法を提供することを目的とする。
【0006】
課題を解決するための手段】
本発明は、前記目的を達成するために、膜分離槽内に設けた回転平膜の膜表面に微生物を付着させて微生物層を形成し、該微生物層により被処理水を生物学的に浄化処理する微生物担持型回転平膜装置の運転方法において、前記回転平膜を回転させた状態で前記膜分離槽内に、前記被処理水の流れの速い前記回転平膜の周縁近傍から被処理水の流れが遅い前記回転平膜の中心近傍まで前記回転平膜の面全体に均等に分散されるように比重の異なる多数のスポンジ状部材を混合投入し、該スポンジ状部材と前記微生物層とを接触させることにより前記微生物層を剥離すると共に、前記スポンジ状部材で微生物層を剥離中は、前記回転平膜の回転数を浄化処理時の回転数よりも大きくすることを特徴とする。
【0007】
本発明によれば、回転平膜を回転させた状態で膜分離槽内にスポンジ状部材を投入することにより、スポンジ状部材と回転する回転平膜の微生物層とが接触するので、微生物層がスポンジ状部材により削り取られる。また、スポンジ状部材なので、回転平膜の膜面を傷つけることもない。
【0008】
【発明の実施の形態】
以下、添付図面により本発明の微生物担持型回転平膜装置の運転方法の好ましい実施の形態を詳説する。
図1は、本発明の微生物担持型回転平膜装置の運転方法を適用する回転平膜装置10の上面図である。
【0009】
図1に示すように、被処理水が供給される膜分離槽12内には、左右に平行な2本の中空回転軸14、14が回転自在に並設される。それぞれの中空回転軸14には、その軸方向に所定間隔をもって穿設された連通口(図示せず)を臨んで、円板状を有する複数の回転平膜16、16…が支持される。回転平膜16は、膜支持体上の不織布や網等のように通水性を有するスペーサに精密ろ過膜あるいは限外ろ過膜を被覆させて構成され、膜の材質としては、ポリスチレン系、ポリプロピレン系、ポリエチレン系、ポリオレフィン系等の高分子樹脂膜を用いることができる。並設された2本の中空回転軸14に支持された回転平膜16同士は、隣り合う回転平膜16同士の一部分がオーバラップするようになっている。中空回転軸14の両端は膜分離槽12外に延設されると供に、膜分離槽12と中空回転軸14とは軸封手段18により水密性が確保される。そして、中空回転軸14の一方閉塞端がモータ20、20にそれぞれ接続され、他方開放端が処理水配管22、22にそれぞれ接続され、中空回転軸14と回転平膜16とが一体的に回転される。処理水配管22は、2本の中空回転軸14にそれぞれ接続された枝管24、24と、枝管24が合流した幹管26で構成され、幹管26に吸引ポンプ28が設けられる。また、中空回転軸14と枝管24との接続は、中空回転軸14の回転を阻害しないための連結装置30、30を介して連結される。2本の中空回転軸14に支持された回転平膜16は、同方向に低速回転される。この場合、回転数も回転平膜16の径の大きさに応じて変えることが好ましい。この同方向の回転により、回転平膜16同士のオーバラップした部分では、回転方向が反対向きになり、乱流が発生する。
【0010】
そして、この回転平膜16に微生物を付着させて微生物層15を形成するには、吸引ポンプ28を作動させて回転平膜16内を負圧にすることにより、被処理水中に浮遊する微生物汚泥を膜表面に付着させる。或いは装置10の運転を行う前に、予め別途集積した硝化菌のような特定の微生物を膜分離槽12内に投入して全量ろ過することにより特定の微生物を回転平膜16の表面に高濃度に付着させるようにしてもよい。
【0011】
このように構成された微生物担持型回転平膜装置10による被処理水の浄化運転は、モータ30で回転平膜16を回転しながら吸引ポンプ28を作動することにより行なわれる。即ち、吸引ポンプ28の作動により、処理水配管22、中空回転軸14を介して回転平膜16内が負圧になり、膜分離槽12中の被処理水が回転平膜16内に吸引ろ過され、被処理水中の濁質成分が除去される。また、被処理水中の例えばアンモニアや有機物は、被処理水が回転平膜16の微生物層15を通過する際に、微生物層15の微生物により生物処理されて被処理水中から除去される。回転平膜16を通過した処理水は、中空回転軸14、処理水配管22を通って装置10外に引き抜かれる。これにより、被処理水中のアンモニアや有機物等の成分と濁質成分の両方を同時に処理することができる。
【0012】
次に、膜分離槽12に投入して回転平膜16に付着した微生物層15を剥離するスポンジ状部材32について説明する。
図2〜図7は、各種形状のスポンジ状部材32を示したものであり、図2はスポンジボール形状のもの、図3は立方体形状のもの、図4は紐状のもの、図5は雲丹状のもの、図6は糸玉状のものである。また、図7のように不定形状にしたスポンジ片を使用することもできる。スポンジ状部材32の大きさは、最小経の部分の寸法が1〜15mm程度のものを使用するのが適当である。この理由は、膜分離槽12に投入するスポンジ状部材32の投入量が一定の場合、スポンジ状部材32が小さいほど総表面積が大きくなるので、それだけ微生物層15との接触効率が良くなり剥離効率が向上するが、スポンジ状部材32が小さすぎると微生物層15を削り取る研削力が弱くなるためである。
【0013】
スポンジ状部材32の大きさと剥離性の関係は、回転平膜16の回転数にも影響されるので、回転平膜16の回転数に応じてスポンジ状部材32の大きさを変えることも剥離性を向上させる要因である。スポンジ状部材32の比重は、回転平膜16で攪拌させた時に被処理水中で分散し易いように被処理水の比重と略同等にすることが必要である。しかし、投入する多数のスポンジ状部材32の全ての比重を同一にする必要はなく、むしろ比重を変えることが好ましい。これは、回転平膜16を回転させた時に、回転平膜16の周縁近傍の被処理水の流れが速く、回転平膜16の中心近傍の被処理水は流れが遅くなるので、異なる比重のスポンジ状部材32を混合投入することにより、回転平膜16の面全体にスポンジ状部材32を均等に分散させ易いためである。スポンジ状部材32の材質としては、多孔質ウレタンフォーム、海綿等のように回転平膜16を傷つけない材質のもので研削力を発揮可能なものであれば、どのようなものでもよい。
【0014】
次に、上記のスポンジ部材32を使用して回転平膜16を膜表面に付着した微生物層15を剥離する剥離工程を備えた微生物担持型回転平膜装置10の運転方法について説明する。
図8は、被処理水を生物処理及びろ過処理する浄化運転と、スポンジ状部材32による微生物層15の剥離運転を組み合わせたもので、浄化運転を一定時間行ったら剥離運転を行い、再び処理運転を行うように運転サイクルを構成したものである。この運転方法は、微生物層15の層厚が早く厚くなるような固形物濃度の大きな被処理水の水質の場合に適している。
【0015】
図9は、前記浄化運転と、回転平膜16を回転させたまま吸引ポンプ28を停止するセルフクリーニング運転を基本サイクルとし、この基本サイクルの途中にスポンジ状部材32による剥離運転をバイパスサイクルとして組み入れるように構成したものである。セルフクリーニングは、回転平膜16内の負圧を解除した状態で回転平膜16の遠心力により微生物層15を剥離するものである。このセルフクリーニングのみでは、微生物層15の十分な剥離を行うことは難しい。従って、この運転方法は、微生物層15の層厚がゆっくりと厚くなるような固形物濃度の小さな被処理水の水質の場合に適している。
【0016】
図8及び図9の運転方法の場合にも、スポンジ状部材32による剥離運転を行うタイミングとしては、浄化処理運転中のろ過圧力を検出して検出値が所定圧力以上になったら剥離運転を行うか、又は被処理水の固形物濃度を検出して検出値に基づいて剥離運転のタイミング、換言すると浄化運転時間を設定してもよい。図10は、膜分離槽12内にスポンジ状部材32を投入して回転平膜に形成された微生物層15を剥離している状態図である。
【0017】
膜分離槽12内に投入された多数のスポンジ状部材32は、回転平膜16の回転による攪拌作用により膜分離槽12内全体に分散されると共に、回転平膜16によって発生する被処理水の旋回流にのって被処理水中を動き回る。これにより、スポンジ状部材32は、回転平膜16の微生物層15に接触し、微生物層15を削り取ることにより短時間で微生物層15を剥離していく。この時、吸引ポンプ28は停止しておくと剥離性をより向上させることができる。そして、この剥離運転時間、即ちスポンジ状部材32を膜分離槽内に投入している時間を制御することにより、微生物層15の層厚を略一定に維持することができる。また、剥離効率は、回転平膜16の回転数を大きくすると向上するので、剥離運転時間と回転平膜の回転数を制御することにより微生物層15の層厚を所望の層厚にする維持することも可能である。この場合、従来のように回転平膜16を高速回転させる必要はなく、被処理水の処理運転時における回転数よりも、例えば1.5倍から2倍程度で充分である。即ち、この剥離運転においては、回転平膜16の回転速度は、スポンジ状部材32を被処理水中で膜分離槽12内全体に分散させる程度の速度であればよく、小さな回転速度でも微生物層15の剥離を充分に行うことができる。従って、回転平膜16を回転するモータに大出力のものを使用する必要がないと共に、その他の回転に係わる部品の加工精度や組み付け精度も特別精度の良いものを使用する必要ないので、装置コストを低減できる。
【0018】
また、スポンジ状部材32と回転平膜16同士のオーバラップとを組み合わせることにより、スポンジ状部材32がオーバラップした回転平膜16同士の間に入り込むので、微生物層15にスポンジ状部材32を圧接した状態で微生物層15を削り取る。従って、単にスポンジ状部材32と微生物層15とを接触させるよりも、微生物層15の剥離性をより高めることができる。
【0019】
更に、剥離運転と並行して膜分離槽12内の低部から上方に向かってエアバブリングを行うと、気泡による剪断力で微生物層15が剥離されるので、スポンジ状部材32での剥離と相まって剥離効果を更に向上させることができる。
図11は、被処理水として固形物濃度が10000mg/Lの鉄系の凝集液を用いて、ろ過圧力と運転時間との関係を調べたものである。
【0020】
本発明の運転方法は、図9で説明した浄化運転とセルフクリーニング運転を基本サイクルとし、この基本サイクルの途中にスポンジ状部材32による剥離運転をバイパスサイクルとして入れるように構成した運転方法で行い、スポンジ状部材32の投入は3時間の浄化運転ごとに1回行うようにした。
一方、従来の運転方法としては、図9の運転サイクルからスポンジ状部材32による剥離運転を除いたもので、浄化運転とセルフクリーニング運転との組み合わせによる運転方法で行った。図11において、太線は本発明の運転方法であり、細線は従来の運転方法である。また、本発明と従来ともに、ろ過圧力が40kPaに達したら薬液洗浄を行ってろ過圧力を約6kPaにまで復活させた。
【0021】
図11から分かるように、従来の運転方法の場合には、約300時間に1回の割合で薬剤洗浄を行う必要があったが、本発明の運転方法では、1000時間に1回の割合で薬剤洗浄をすればよく、薬剤洗浄の間隔を従来の運転方法の3倍以上長くすることができた。また、鉄系の凝集液の固形物が回転平膜に高密度で付着していたが、本発明によれば微生物層15を効率的に剥離することができた。
【0022】
尚、本実施の形態では、スポンジ状部材32を間欠的に投入することで説明したが、微生物層をすべて剥離したければ、スポンジ状部材32を膜分離槽12に常時投入しておくことも可能である。また、中空回転軸を2本で説明したが、1本でも2本以上でもよい。
【0023】
【発明の効果】
以上説明したように、本発明の微生物担持型回転平膜装置の運転方法によれば、回転平膜に高密度で微生物層が形成されても、回転平膜を低回転数で回転させて微生物層を効果的に剥離することができる。
従って、微生物層を剥離する剥離運転のための時間を大幅に短縮することができるので、被処理水の処理を行う処理運転を効率的に行うことができる。また、従来のように、微生物層の剥離のために回転平膜を高速回転させる必要がないので、装置コストを削減することができる。
【図面の簡単な説明】
【図1】回転平膜装置の上面図
【図2】スポンジボール形状のスポンジ状部材の斜視図
【図3】立方体形状のスポンジ状部材の斜視図
【図4】紐状のスポンジ状部材の斜視図
【図5】雲丹状のスポンジ状部材の斜視図
【図6】糸玉状のスポンジ状部材の斜視図
【図7】不定形状のスポンジ状部材の斜視図
【図8】本発明の微生物担持型回転平膜装置の運転方法の一例を示した図
【図9】本発明の微生物担持型回転平膜装置の運転方法の別の例を示した図
【図10】スポンジ状部材で回転平膜に付着した微生物層を剥離している状態図
【図11】本発明の運転方法と従来の運転方法とによる微生物層の剥離効果を比較したグラフ
【符号の説明】
10…回転平膜装置
12…膜分離槽
14…中空回転軸
15…微生物層
16…回転平膜
20…モータ
22…処理水配管
28…吸引ポンプ
32…スポンジ状部材
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for operating a microorganism-supporting rotary membrane device, and in particular, a microorganism layer is formed by adhering microorganisms to the rotary membrane, and the microorganism layer is used to purify water and wastewater. The present invention relates to a method for operating a membrane device.
[0002]
[Prior art]
The microorganism-supported rotary flat membrane device forms a microbial layer by attaching microorganisms to the rotary flat membrane, and biologically purifies ammonia nitrogen in the water to be treated by this microbial layer, and also performs the treatment. Filtration of turbid components in water can be performed.
However, as filtration of the water to be treated continues, microorganisms and solids in the water to be treated further adhere on the microorganism layer, and the layer thickness of the microorganism layer gradually increases. When the layer thickness of the microorganism layer becomes too thick, not only the filtration performance is lowered, but also the biological purification treatment performance is lowered. Therefore, when the layer thickness of the microorganism layer becomes too thick, it is necessary to peel off the microorganism layer.
[0003]
Conventionally, in order to remove the microbial layer, the filtration operation is stopped while the rotating flat membrane is periodically rotated, that is, the suction pump is stopped, so that the microbial layer on the membrane surface is peeled off by the rotation of the rotating flat membrane. It was.
[0004]
[Problems to be solved by the invention]
However, as in the past, when the microbial layer of the rotating flat membrane is to be peeled off by rotating the rotating flat membrane, it is necessary to apply a certain level of shearing force due to turbulent flow to the membrane surface. Must be rotated at high speed. Therefore, it is necessary not only to install a high-power motor that rotates the rotating flat membrane at high speed just for the peeling operation, but also the component parts of the device have good durability, and use parts with higher processing accuracy and assembly accuracy. Therefore, there is a disadvantage that the apparatus cost becomes high.
[0005]
Furthermore, since the microbial layer is peeled off only by rotating the rotating flat membrane, when the microbial layer adheres at a high density, the peeling efficiency is poor and a long time is required for the peeling operation. There is a disadvantage that the operation time of the purification process is greatly reduced.
Since the present invention is made in view of such circumstances, even if a microorganism layer is formed at a high density on the rotating flat membrane, the rotating flat membrane is rotated at a low rotation number to effectively separate the microorganism layer. It is an object of the present invention to provide a method for operating a microorganism-supporting rotary flat membrane device capable of performing the above.
[0006]
[Means for Solving the Problems ]
In order to achieve the above object, the present invention forms a microbial layer by attaching microorganisms to the surface of a rotating flat membrane provided in a membrane separation tank, and biologically purifies the water to be treated by the microbial layer. In the operation method of the microorganism-supporting rotary flat membrane device to be treated, the water to be treated is introduced into the membrane separation tank in a state where the rotary flat membrane is rotated from the vicinity of the periphery of the rotating flat membrane where the flow of the water to be treated is fast. A large number of sponge-like members having different specific gravities are mixed and introduced so as to be evenly distributed over the entire surface of the rotating flat membrane until the vicinity of the center of the rotating flat membrane is slow , and the sponge-like member and the microorganism layer are mixed. The microbial layer is peeled off by contact, and while the microbial layer is being peeled off by the sponge-like member, the rotational speed of the rotating flat membrane is made larger than the rotational speed at the time of purification treatment.
[0007]
According to the present invention, the sponge-like member and the microbial layer of the rotating rotating membrane are brought into contact with each other by introducing the sponge-like member into the membrane separation tank while the rotating flat membrane is rotated. It is scraped off by a sponge-like member. Moreover, since it is a sponge-like member, the film surface of the rotating flat membrane is not damaged.
[0008]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, a preferred embodiment of a method for operating a microorganism-supporting rotary flat membrane device of the present invention will be described in detail with reference to the accompanying drawings.
FIG. 1 is a top view of a rotary flat membrane device 10 to which the operation method of the microorganism-supported rotary flat membrane device of the present invention is applied.
[0009]
As shown in FIG. 1, two hollow rotating shafts 14 and 14 parallel to the left and right are rotatably arranged in parallel in a membrane separation tank 12 to which water to be treated is supplied. Each of the hollow rotating shafts 14 supports a plurality of rotating flat membranes 16, 16... Having a disk shape so as to face a communication port (not shown) drilled at a predetermined interval in the axial direction. The rotating flat membrane 16 is constituted by coating a microfiltration membrane or an ultrafiltration membrane on a water-permeable spacer such as a nonwoven fabric or a net on a membrane support, and the material of the membrane is polystyrene or polypropylene. A polymer resin film such as polyethylene or polyolefin can be used. The rotating flat membranes 16 supported by the two hollow rotating shafts 14 arranged side by side are configured such that parts of the adjacent rotating flat membranes 16 overlap each other. Both ends of the hollow rotary shaft 14 are extended outside the membrane separation tank 12, and the membrane separation tank 12 and the hollow rotary shaft 14 are secured to the water tightness by the shaft sealing means 18. The one closed end of the hollow rotary shaft 14 is connected to the motors 20 and 20, respectively, and the other open end is connected to the treated water pipes 22 and 22, respectively. The hollow rotary shaft 14 and the rotary flat membrane 16 rotate integrally. Is done. The treated water pipe 22 is composed of branch pipes 24 and 24 respectively connected to the two hollow rotary shafts 14 and a trunk pipe 26 where the branch pipes 24 are joined, and the trunk pipe 26 is provided with a suction pump 28. Further, the connection between the hollow rotary shaft 14 and the branch pipe 24 is connected via connecting devices 30 and 30 for preventing the rotation of the hollow rotary shaft 14. The rotating flat membrane 16 supported by the two hollow rotating shafts 14 is rotated at a low speed in the same direction. In this case, it is preferable to change the number of rotations according to the size of the diameter of the rotating flat membrane 16. Due to the rotation in the same direction, in the overlapping portion of the rotating flat membranes 16, the rotation direction is opposite and turbulence is generated.
[0010]
And in order to make microorganisms adhere to this rotation flat membrane 16 and form the microorganism layer 15, the suction pump 28 is operated and the inside of the rotation flat membrane 16 is made into a negative pressure, The microorganism sludge which floats in to-be-processed water Is attached to the membrane surface. Alternatively, before the operation of the apparatus 10, specific microorganisms such as nitrifying bacteria accumulated separately in advance are put into the membrane separation tank 12 and filtered in a total amount so that the specific microorganisms are concentrated on the surface of the rotating flat membrane 16. You may make it adhere to.
[0011]
The purification operation of the water to be treated by the microorganism-supporting rotary flat membrane device 10 configured as described above is performed by operating the suction pump 28 while rotating the rotary flat membrane 16 by the motor 30. That is, when the suction pump 28 is operated, the inside of the rotary flat membrane 16 becomes negative pressure via the treated water pipe 22 and the hollow rotary shaft 14, and the water to be treated in the membrane separation tank 12 is suction filtered into the rotary flat membrane 16. Then, the turbid component in the for-treatment water is removed. Further, for example, ammonia or organic matter in the water to be treated is biologically treated by the microorganisms in the microbial layer 15 and removed from the water to be treated when the water to be treated passes through the microorganism layer 15 of the rotating flat membrane 16. The treated water that has passed through the rotating flat membrane 16 is drawn out of the apparatus 10 through the hollow rotating shaft 14 and the treated water pipe 22. Thereby, both components, such as ammonia and organic substance, and a turbid component in to-be-processed water can be processed simultaneously.
[0012]
Next, the sponge-like member 32 that is put into the membrane separation tank 12 and peels off the microorganism layer 15 attached to the rotating flat membrane 16 will be described.
2 to 7 show sponge-shaped members 32 having various shapes, FIG. 2 is a sponge ball shape, FIG. 3 is a cube shape, FIG. 4 is a string shape, and FIG. FIG. 6 shows a threadball shape. Moreover, the sponge piece made indefinite shape like FIG. 7 can also be used. As for the size of the sponge-like member 32, it is appropriate to use a member having a minimum dimension of about 1 to 15 mm. The reason for this is that when the amount of sponge-like member 32 introduced into the membrane separation tank 12 is constant, the smaller the sponge-like member 32 is, the larger the total surface area is. However, if the sponge-like member 32 is too small, the grinding force for scraping the microorganism layer 15 is weakened.
[0013]
Since the relationship between the size of the sponge-like member 32 and the peelability is also affected by the number of rotations of the rotating flat membrane 16, it is possible to change the size of the sponge-like member 32 according to the number of revolutions of the rotating flat membrane 16. It is a factor to improve. The specific gravity of the sponge-like member 32 needs to be substantially equal to the specific gravity of the water to be treated so that it can be easily dispersed in the water to be treated when the rotating flat membrane 16 is stirred. However, it is not necessary to make all the specific gravity of the many sponge-like members 32 to be supplied the same, but it is preferable to change the specific gravity. This is because when the rotating flat membrane 16 is rotated, the flow of water to be treated near the periphery of the rotating flat membrane 16 is fast, and the water to be treated near the center of the rotating flat membrane 16 has a slow flow. This is because mixing the sponge-like member 32 makes it easy to uniformly disperse the sponge-like member 32 over the entire surface of the rotating flat film 16. As the material of the sponge-like member 32, any material that does not damage the rotating flat membrane 16, such as porous urethane foam, sponge, etc., can exhibit any grinding force.
[0014]
Next, an operation method of the microorganism-supporting rotary flat membrane device 10 including a peeling process for peeling the microorganism layer 15 having the rotary flat membrane 16 attached to the membrane surface using the sponge member 32 will be described.
FIG. 8 shows a combination of a purification operation for biologically treating and filtering water to be treated and a separation operation for removing the microbial layer 15 by the sponge-like member 32. After the purification operation is performed for a certain period of time, the separation operation is performed and the treatment operation is performed again. The operation cycle is configured to perform the following. This operation method is suitable for the case of the quality of the water to be treated having a large solid concentration such that the layer thickness of the microorganism layer 15 is increased quickly.
[0015]
FIG. 9 shows a basic cycle of the purification operation and a self-cleaning operation in which the suction pump 28 is stopped while the rotating flat membrane 16 is rotated, and a peeling operation by the sponge-like member 32 is incorporated as a bypass cycle in the middle of the basic cycle. It is comprised as follows. In the self-cleaning, the microorganism layer 15 is peeled off by the centrifugal force of the rotating flat membrane 16 in a state where the negative pressure in the rotating flat membrane 16 is released. It is difficult to sufficiently remove the microorganism layer 15 only by this self-cleaning. Therefore, this operation method is suitable for the case of the quality of water to be treated having a low solid matter concentration so that the layer thickness of the microorganism layer 15 gradually increases.
[0016]
Also in the case of the operation method of FIG. 8 and FIG. 9, as the timing of performing the peeling operation by the sponge-like member 32, the separation pressure is detected when the filtration pressure during the purification treatment operation is detected and the detected value becomes equal to or higher than a predetermined pressure. Alternatively, the solids concentration of the water to be treated may be detected, and the timing of the peeling operation, in other words, the purification operation time may be set based on the detected value. FIG. 10 is a state diagram in which the sponge-like member 32 is introduced into the membrane separation tank 12 and the microorganism layer 15 formed on the rotating flat membrane is peeled off.
[0017]
A large number of sponge-like members 32 charged into the membrane separation tank 12 are dispersed throughout the membrane separation tank 12 by the stirring action caused by the rotation of the rotary flat membrane 16, and the water to be treated generated by the rotary flat membrane 16 is also dispersed. Move around the treated water in a swirling flow. As a result, the sponge-like member 32 comes into contact with the microbial layer 15 of the rotating flat membrane 16, and the microbial layer 15 is peeled off in a short time by scraping the microbial layer 15. At this time, if the suction pump 28 is stopped, the peelability can be further improved. Then, by controlling the peeling operation time, that is, the time during which the sponge-like member 32 is put into the membrane separation tank, the layer thickness of the microorganism layer 15 can be maintained substantially constant. Further, the peeling efficiency is improved by increasing the number of rotations of the rotating flat membrane 16, so that the layer thickness of the microorganism layer 15 is maintained at a desired layer thickness by controlling the peeling operation time and the rotating number of the rotating flat membrane. It is also possible. In this case, it is not necessary to rotate the rotating flat membrane 16 at a high speed as in the prior art, and for example, about 1.5 to 2 times the rotation speed during the treatment operation of the water to be treated is sufficient. That is, in this peeling operation, the rotation speed of the rotating flat membrane 16 may be a speed that allows the sponge-like member 32 to be dispersed throughout the membrane separation tank 12 in the water to be treated. Can be sufficiently peeled off. Therefore, it is not necessary to use a motor that rotates the rotating flat membrane 16 with a high output, and it is not necessary to use a machine with high accuracy of machining and assembly of other parts related to rotation. Can be reduced.
[0018]
Further, by combining the sponge-like member 32 and the overlap between the rotating flat membranes 16, the sponge-like member 32 enters between the overlapping rotating flat membranes 16, so that the sponge-like member 32 is pressed against the microorganism layer 15. In this state, the microbial layer 15 is scraped off. Therefore, the detachability of the microbial layer 15 can be improved more than simply bringing the sponge-like member 32 and the microbial layer 15 into contact with each other.
[0019]
Further, when air bubbling is performed upward from the lower part in the membrane separation tank 12 in parallel with the peeling operation, the microbial layer 15 is peeled off by the shearing force due to the bubbles, which is coupled with the peeling at the sponge-like member 32. The peeling effect can be further improved.
FIG. 11 shows the relationship between the filtration pressure and the operation time using an iron-based coagulated liquid having a solid concentration of 10,000 mg / L as water to be treated.
[0020]
The operation method of the present invention is performed by an operation method configured such that the purification operation and the self-cleaning operation described in FIG. 9 are set as basic cycles, and the peeling operation by the sponge member 32 is included as a bypass cycle in the middle of the basic cycle, The sponge-like member 32 was charged once every 3 hours of purification operation.
On the other hand, as a conventional operation method, the operation cycle of FIG. 9 is excluded from the peeling operation by the sponge-like member 32, and the operation method is a combination of the purification operation and the self-cleaning operation. In FIG. 11, the thick line is the operation method of the present invention, and the thin line is the conventional operation method. In both the present invention and the prior art, when the filtration pressure reached 40 kPa, chemical cleaning was performed to restore the filtration pressure to about 6 kPa.
[0021]
As can be seen from FIG. 11, in the case of the conventional operation method, it was necessary to perform chemical cleaning once every 300 hours, but in the operation method of the present invention, once every 1000 hours. It was only necessary to perform chemical cleaning, and the chemical cleaning interval could be increased by three times or more than the conventional operation method. Moreover, although the solid substance of the iron-based agglomerated liquid adhered to the rotating flat membrane at a high density, the microbial layer 15 could be efficiently peeled according to the present invention.
[0022]
In the present embodiment, the sponge-like member 32 is intermittently charged. However, if the microorganism layer is to be completely removed, the sponge-like member 32 may be constantly charged in the membrane separation tank 12. Is possible. Moreover, although the two hollow rotating shafts have been described, the number may be one or two or more.
[0023]
【The invention's effect】
As described above, according to the method of operating the microorganism-supporting rotating flat membrane device of the present invention, even if a microorganism layer is formed at a high density on the rotating flat membrane, the rotating flat membrane is rotated at a low rotational speed to The layer can be effectively peeled off.
Therefore, since the time for the peeling operation for peeling the microorganism layer can be greatly shortened, the treatment operation for treating the water to be treated can be efficiently performed. Further, unlike the prior art, it is not necessary to rotate the rotating flat membrane at a high speed for the separation of the microorganism layer, so that the apparatus cost can be reduced.
[Brief description of the drawings]
FIG. 1 is a top view of a rotating flat membrane device. FIG. 2 is a perspective view of a sponge-like member having a sponge ball shape. FIG. 3 is a perspective view of a sponge-like member having a cubic shape. FIG. 5 is a perspective view of a cloud-like sponge-like member. FIG. 6 is a perspective view of a thread-like sponge-like member. FIG. 7 is a perspective view of an irregular-shaped sponge-like member. FIG. 9 is a diagram showing an example of the operation method of the rotating flat membrane apparatus of the mold type. FIG. 9 is a diagram showing another example of the operating method of the microorganism-supporting rotating flat membrane apparatus of the present invention. Fig. 11 is a state diagram in which the microbial layer adhering to the surface is peeled. Fig. 11 is a graph comparing the microbial layer peeling effect between the operation method of the present invention and the conventional operation method.
DESCRIPTION OF SYMBOLS 10 ... Rotating flat membrane apparatus 12 ... Membrane separation tank 14 ... Hollow rotating shaft 15 ... Microorganism layer 16 ... Rotating flat membrane 20 ... Motor 22 ... Treated water piping 28 ... Suction pump 32 ... Sponge-like member

Claims (3)

膜分離槽内に設けた回転平膜の膜表面に微生物を付着させて微生物層を形成し、該微生物層により被処理水を生物学的に浄化処理する微生物担持型回転平膜装置の運転方法において、
前記回転平膜を回転させた状態で前記膜分離槽内に、前記被処理水の流れの速い前記回転平膜の周縁近傍から被処理水の流れが遅い前記回転平膜の中心近傍まで前記回転平膜の面全体に均等に分散されるように比重の異なる多数のスポンジ状部材を混合投入し、該スポンジ状部材と前記微生物層とを接触させることにより前記微生物層を剥離すると共に、前記スポンジ状部材で微生物層を剥離中は、前記回転平膜の回転数を浄化処理時の回転数よりも大きくすることを特徴とする微生物担持型回転平膜装置の運転方法。
A method for operating a microorganism-supported rotary flat membrane apparatus, wherein a microorganism layer is formed by attaching microorganisms to the surface of a rotary flat membrane provided in a membrane separation tank, and the treated water is biologically purified by the microorganism layer. In
In the state where the rotating flat membrane is rotated, the rotation from the vicinity of the periphery of the rotating flat membrane where the flow of the water to be processed is fast to the vicinity of the center of the rotating flat membrane where the flow of the water to be processed is slow A plurality of sponge-like members having different specific gravities are mixed and introduced so as to be evenly distributed over the entire surface of the flat membrane , and the sponge layer and the microorganism layer are brought into contact with each other to peel off the microorganism layer, and the sponge A method for operating a microorganism-supporting rotary flat membrane device, wherein the rotational speed of the rotating flat membrane is set to be larger than the rotational speed at the time of purification treatment while the microbial layer is being peeled off by the shaped member.
前記被処理水の固形物濃度を検出し、その検出した値に応じて前記スポンジ状部材を間欠投入する時間の間隔を調整することを特徴とする請求項1の微生物担持型回転平膜装置の運転方法。2. The microorganism-supported rotary flat membrane device according to claim 1, wherein the solid content concentration of the water to be treated is detected, and an interval of time for intermittently inserting the sponge-like member is adjusted according to the detected value. how to drive. 前記回転平膜のろ過圧力を検出し、その検出値に応じて前記スポンジ状部材を間欠投入する時間の間隔を調整することを特徴とする請求項1の微生物担持型回転平膜装置の運転方法。The method for operating a microorganism-supporting rotary flat membrane device according to claim 1, wherein the filtration pressure of the rotary flat membrane is detected, and the time interval for intermittently inserting the sponge-like member is adjusted according to the detected value. .
JP28025398A 1998-10-01 1998-10-01 Method for operating microorganism-supported rotary flat membrane device Expired - Fee Related JP3646537B2 (en)

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