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JP5824960B2 - Microbe attachment carrier - Google Patents
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JP5824960B2 - Microbe attachment carrier - Google Patents

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JP5824960B2
JP5824960B2 JP2011178864A JP2011178864A JP5824960B2 JP 5824960 B2 JP5824960 B2 JP 5824960B2 JP 2011178864 A JP2011178864 A JP 2011178864A JP 2011178864 A JP2011178864 A JP 2011178864A JP 5824960 B2 JP5824960 B2 JP 5824960B2
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carrier
nonwoven fabric
activated sludge
microorganisms
water tank
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JP2013039536A (en
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谷崎 美江
美江 谷崎
朋樹 川岸
朋樹 川岸
中原 禎仁
禎仁 中原
小林 秀章
小林  秀章
正博 大坪
正博 大坪
透雄 小野原
透雄 小野原
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Mitsubishi Chemical Corp
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Mitsubishi Chemical Corp
Mitsubishi Rayon Co Ltd
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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

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Description

本発明は、有機性排水などを生物処理する微生物を付着させる微生物付着用担体に関する。   The present invention relates to a microorganism adhesion carrier to which microorganisms for biological treatment of organic wastewater or the like are adhered.

従来から、家庭排水、工場廃水などの有機性排水の処理方法として、生物処理が有効であることが知られている。なかでも、活性汚泥法は最も広く採用されている。
活性汚泥法には、活性汚泥が投入された処理水槽中に担体が浸漬配置され、該担体の表面に活性汚泥に含まれる微生物を付着させ、付着した微生物により排水中の有機物などを分解する方法がある。ここで担体としては、繊維製品を利用したものが知られており、例えば特許文献1には、経糸と横糸とから基幹を構成し、さらにこの基幹に対して多数のU字形ループ状の横糸が設けられた形態の担体が記載されている。また、特許文献2には、経糸と横糸からなる織物を房状に加工した担体が記載されている。また、特許文献3には、ネット状の芯材に汚泥付着糸を沿わせて配した立体形状のものが記載されている。
Conventionally, it is known that biological treatment is effective as a treatment method for organic wastewater such as household wastewater and factory wastewater. Among them, the activated sludge method is most widely adopted.
In the activated sludge method, a carrier is immersed and disposed in a treated water tank into which activated sludge has been charged, microorganisms contained in the activated sludge are adhered to the surface of the carrier, and organic matter in waste water is decomposed by the adhered microorganisms. There is. Here, as a carrier, one using a fiber product is known. For example, in Patent Document 1, a backbone is composed of a warp and a weft, and a number of U-shaped loop wefts are formed on the backbone. A provided form of carrier is described. Patent Document 2 describes a carrier obtained by processing a woven fabric made of warp and weft into a tuft. Patent Document 3 describes a three-dimensional shape in which a sludge-attached yarn is arranged along a net-like core material.

特許第3242363号公報Japanese Patent No. 3242363 特許第3167151号公報Japanese Patent No. 3167151 特許第3471310号公報Japanese Patent No. 3471310

しかしながら、特許文献1および2に記載された形態の担体は、製造に手間がかかる。また、処理水槽に浸漬した場合における単位体積当りの繊維量が少なく、そのため付着する微生物量も限られ、効率的な生物処理が難しい。
また、特許文献3に記載のものは、特許文献1や2の担体に比較すると、単位体積当たりの繊維量は多いものの、その製造に非常に手間がかかる。
However, the carrier of the form described in Patent Documents 1 and 2 takes time to manufacture. In addition, when immersed in a treated water tank, the amount of fibers per unit volume is small, so the amount of attached microorganisms is limited, and efficient biological treatment is difficult.
Moreover, although the thing of patent document 3 has much fiber amount per unit volume compared with the support | carrier of patent document 1 and 2, its manufacture takes very much effort.

本発明は上記事情に鑑みてなされたもので、簡単に製造でき、単位体積当りの繊維量が多く効率的な生物処理が可能な微生物付着用担体の提供を目的とする。   The present invention has been made in view of the above circumstances, and an object of the present invention is to provide a carrier for attaching microorganisms that can be easily manufactured, has a large amount of fibers per unit volume, and enables efficient biological treatment.

本発明の微生物付着用担体は、膜分離活性汚泥処理装置における活性汚泥が投入された処理水槽内に浸漬配置され、前記活性汚泥中の微生物を付着させる微生物付着用担体であって、アクリロニトリル単位を50質量%以上有するアクリル系重合体の繊維で構成された乾式不織布からなる。
前記不織布は、目付けが60〜1000g/mであることが好ましい。
前記不織布は、厚みが0.5〜30mmであることが好ましい。
The carrier for attaching microorganisms of the present invention is a carrier for attaching microorganisms, which is immersed in a treated water tank into which activated sludge is charged in a membrane separation activated sludge treatment apparatus , and attaches microorganisms in the activated sludge. It consists of a dry-type nonwoven fabric comprised with the fiber of the acrylic polymer which has 50 mass% or more.
The nonwoven fabric preferably has a basis weight of 60 to 1000 g / m 2 .
The nonwoven fabric preferably has a thickness of 0.5 to 30 mm.

本発明によれば、簡単に製造でき、単位体積当りの繊維量が多く効率的な生物処理が可能な微生物付着用担体を提供できる。   ADVANTAGE OF THE INVENTION According to this invention, the support | carrier for microorganisms adhesion which can be manufactured simply and has many fibers per unit volume and can perform an efficient biological treatment can be provided.

本発明の微生物付着用担体を具備した担体ユニットの一例を示す平面図である。It is a top view which shows an example of the support | carrier unit which comprised the support | carrier for microorganisms adhesion of this invention. 図1の担体ユニットを備えた膜分離活性汚泥処理装置の一例を示す構成図である。It is a block diagram which shows an example of the membrane separation activated sludge processing apparatus provided with the support | carrier unit of FIG. 実施例において微生物付着用担体を処理水槽に浸漬した経過日数と、その際の質量増加との関係を示すグラフである。It is a graph which shows the relationship between the elapsed days which immersed the support | carrier for microorganisms adhesion in the processing water tank in the Example, and the mass increase in that case.

以下、本発明を詳細に説明する。
本発明の微生物付着用担体は、アクリル系重合体の繊維で構成された不織布からなるシート状のものであって、有機性排水などを生物処理する活性汚泥が投入された処理水槽内に浸漬配置され、活性汚泥中の微生物を付着させるものである。処理水槽としては、活性汚泥による生物処理のみが行われる活性汚泥槽の他、中空糸膜などの分離膜も浸漬され、生物処理とともに分離膜による膜処理も行われる膜分離活性汚泥槽などが挙げられる。
Hereinafter, the present invention will be described in detail.
The carrier for attaching microorganisms of the present invention is a sheet-like material composed of a nonwoven fabric composed of acrylic polymer fibers, and is immersed in a treated water tank into which activated sludge for biologically treating organic wastewater is placed. And attaches microorganisms in activated sludge. Examples of the treated water tank include an activated sludge tank in which only biological treatment with activated sludge is performed, and a membrane separation activated sludge tank in which a separation membrane such as a hollow fiber membrane is also immersed, and membrane treatment with a separation membrane is performed together with biological treatment. It is done.

アクリル系重合体としては、アクリロニトリル単位を50質量%以上有するものが用いられる。このようなアクリル系重合体からなる繊維(アクリル繊維)は、他の繊維と比較して微生物付着性に優れているため、微生物付着用担体の材料として適している。   As the acrylic polymer, one having 50% by mass or more of acrylonitrile units is used. Fibers (acrylic fibers) made of such an acrylic polymer are suitable as a material for a carrier for attaching microorganisms because they are superior in adhesion to microorganisms compared to other fibers.

なお、「アクリロニトリル単位を50質量%以上有する」とは、アクリル系重合体を製造する単量体中のアクリロニトリルの割合が50質量%以上であることを言う。
また、アクリロニトリル単位の好ましい上限は、97質量%である。
“Having 50% by mass or more of acrylonitrile units” means that the ratio of acrylonitrile in the monomer for producing the acrylic polymer is 50% by mass or more.
Moreover, the preferable upper limit of an acrylonitrile unit is 97 mass%.

アクリル系重合体は、アクリロニトリル単位を50質量%以上有するとともに、アクリロニトリルと共重合可能な不飽和単量体からなる単位を50質量%以下の範囲で有することができる。
アクリロニトリルと共重合可能な不飽和単量体としては、特に限定されないが、例えばアクリル酸、メタクリル酸、これらの誘導体、酢酸ビニル、アクリルアミド、塩化ビニル、塩化ビニリデンなどが挙げられる。また、目的によっては、ビニルベンゼンスルホン酸ソーダ、メタクリルスルホン酸ソーダ、アクリルアミドメチルプロパンスルホン酸ソーダなどのイオン性不飽和単量体をアクリロニトリルと共重合可能な不飽和単量体として用いることができる。
The acrylic polymer has 50% by mass or more of acrylonitrile units, and can have a unit composed of an unsaturated monomer copolymerizable with acrylonitrile in a range of 50% by mass or less.
The unsaturated monomer copolymerizable with acrylonitrile is not particularly limited, and examples thereof include acrylic acid, methacrylic acid, derivatives thereof, vinyl acetate, acrylamide, vinyl chloride, and vinylidene chloride. Depending on the purpose, ionic unsaturated monomers such as vinylbenzene sulfonic acid soda, methacrylic sulfonic acid soda, and acrylamidomethylpropane sulfonic acid soda can be used as unsaturated monomers copolymerizable with acrylonitrile.

アクリル系重合体の重合法は、特に限定されないが、例えば通常の懸濁重合法または溶液重合法を採用できる。   The polymerization method of the acrylic polymer is not particularly limited, and for example, a usual suspension polymerization method or solution polymerization method can be adopted.

不織布は、このようなアクリル系重合体の繊維により構成されるものであれば特に制限はないが、不織布には、微生物付着用担体としての処理水槽中での耐久性が求められるため、乾式法を経て製造された乾式不織布が好ましい。
乾式不織布は、巻縮のあるステープル繊維をカーディングおよび積層してウェブを形成し、このウェブを結着させたものである。ウェブの結着方法としては、繊維を不織布の表面になるべく多く露出させ得ることから、スパンレース法、ニードルパンチ法、ステッチボンド法のなかから選択される方法が好ましい。
The nonwoven fabric is not particularly limited as long as it is composed of such acrylic polymer fibers, but the nonwoven fabric is required to have durability in a treated water tank as a microorganism-adhering carrier. A dry nonwoven fabric produced through the process is preferred.
A dry nonwoven fabric is obtained by carding and laminating staple fibers having a crimped shape to form a web and binding the web. As the method for binding the web, a method selected from the spunlace method, the needle punch method, and the stitch bond method is preferable because the fiber can be exposed as much as possible on the surface of the nonwoven fabric.

製造された不織布には、必要に応じて、カレンダー加工、エンボス加工、起毛加工、熱プレスなどの任意の加工を施してもよい。   The manufactured nonwoven fabric may be subjected to arbitrary processing such as calendering, embossing, raising, and hot pressing as necessary.

不織布の目付けおよび厚みは、微生物付着用担体として浸漬した際の微生物の付着量や、強度、耐久性などと関係があり、処理水槽内の排水の水質、処理条件などに応じて調整できるが、目付けは、1m当たり60g以上であることが好ましい。目付けが60g以上であると、微生物付着用担体として膜分離活性汚泥槽に浸漬されて曝気などの物理的負荷が加わった場合などにも、充分な強度、耐久性を発揮することができるとともに、微生物を充分に付着させることができる。
一方、微生物は、不織布の表面に多く付着して保持されやすいため、目付けが高すぎると、不織布内部の繊維は微生物の付着には充分には利用されない。また、目付けが高すぎると、不織布に付着した汚泥や水分により、不織布の重量が増す。このような観点からは、1m当たりの目付けは1000g以下であることが好ましく、さらに不織布の加工性、微生物の付着の効率性の観点などを考慮すると、300g以下がより好ましい。
The basis weight and thickness of the nonwoven fabric are related to the amount of microorganisms when immersed as a carrier for microorganism adhesion, strength, durability, etc., and can be adjusted according to the quality of the wastewater in the treatment water tank, treatment conditions, The basis weight is preferably 60 g or more per 1 m 2 . When the basis weight is 60 g or more, it is possible to exhibit sufficient strength and durability even when a physical load such as aeration is applied by being immersed in a membrane separation activated sludge tank as a carrier for attaching microorganisms, Microorganisms can be sufficiently adhered.
On the other hand, since many microorganisms are easily attached and held on the surface of the nonwoven fabric, if the basis weight is too high, the fibers inside the nonwoven fabric are not sufficiently utilized for the adhesion of microorganisms. If the basis weight is too high, the weight of the nonwoven fabric increases due to sludge and moisture adhering to the nonwoven fabric. From such a viewpoint, the basis weight per 1 m 2 is preferably 1000 g or less, and more preferably 300 g or less in consideration of the processability of the nonwoven fabric and the efficiency of adhesion of microorganisms.

不織布の厚みは、薄すぎると強度、耐久性が弱くなるとともに、微生物の付着量が不充分となる場合がある。また、厚すぎると加工性が低下し、例えば後述のように担体ユニットを製造する際などの加工がしにくくなる場合がある。よって、不織布の厚みは、0.5mm以上30mm以下が好ましく、加工性の観点からは、20mm以下がより好ましい。   If the thickness of the nonwoven fabric is too thin, the strength and durability may be reduced, and the amount of microorganisms attached may be insufficient. Moreover, when too thick, workability will fall, for example, when manufacturing a carrier unit like the after-mentioned, it may become difficult to process. Therefore, the thickness of the nonwoven fabric is preferably 0.5 mm or more and 30 mm or less, and more preferably 20 mm or less from the viewpoint of workability.

最も好ましい不織布は、1m当たりの目付けが100〜500g/mで、厚みが1〜10mmのものである。このような不織布であれば、充分に微生物を付着させることができ、強度、耐久性、加工性にも優れる。 The most preferred nonwoven is a basis weight 100 to 500 g / m 2 per 1 m 2, is intended thickness of 1 to 10 mm. If it is such a nonwoven fabric, microorganisms can fully adhere and it is excellent also in intensity | strength, durability, and workability.

不織布の目付けを調整するためには、例えば、ローラーカードにて繊維のカーディングを行い、得られたカードウェブをパラレル状に所定の目付けになるまで折りたたんで積層すればよい。
また、不織布の厚みを調整するためには、上述のように積層されたものに対して、パンチ針によるニードルパンチを行うことにより、所定の厚みとなるようにすればよい。また、必要に応じて、得られた不織布を熱プレスするなどして、所定の厚みとなるようにさらに調整してもよい。
In order to adjust the basis weight of the nonwoven fabric, for example, fiber carding may be performed with a roller card, and the obtained card web may be folded and laminated in parallel until a predetermined basis weight is obtained.
In addition, in order to adjust the thickness of the nonwoven fabric, a predetermined thickness may be obtained by performing needle punching with a punch needle on the laminated layers as described above. Moreover, you may further adjust so that it may become predetermined thickness by hot-pressing the obtained nonwoven fabric as needed.

このような不織布は、そのままシート状の微生物付着用担体として、活性汚泥槽、膜分離活性汚泥槽などの処理水槽に浸漬してもよいが、強度、耐久性を高めるために、基布と組み合わせた積層体の形態で浸漬してもよい。また、このように基布と積層する場合には、以上説明してきた不織布が表面に位置することが微生物付着の観点から好ましいため、2枚の不織布で基布を挟持した構成が好ましい。   Such a non-woven fabric may be immersed in a treated water tank such as an activated sludge tank or a membrane-separated activated sludge tank as a sheet-like microorganism adhesion carrier as it is, but is combined with a base cloth in order to increase strength and durability. It may be immersed in the form of a laminated body. Moreover, when laminating | stacking with a base fabric in this way, since it is preferable from a viewpoint of microorganisms adhesion that the nonwoven fabric demonstrated above is located in the surface, the structure which clamped the base fabric with two nonwoven fabrics is preferable.

2枚の不織布に基布が挟持された積層体を製造する方法としては、まず、ローラーカードにより繊維のカーディングを行い、得られたカードウェブをパラレル状に折りたたみ積層させ、所望の目付けのウェブを得る。このようにして得られたウェブを2枚用意しこれらの間に基布を挟んだものに対して、パンチ針によるニードルパンチを行って、所望の厚みとすればよい。
基布としては、ポリエステル繊維、ポリプロピレン繊維、ポリアミド繊維、アクリル繊維など、水や生物に対して難分解性な繊維を材質としたスパンボンド不織布や織物などが挙げられる。
As a method of manufacturing a laminate in which a base fabric is sandwiched between two nonwoven fabrics, first, fiber carding is performed with a roller card, and the obtained card web is folded and laminated in parallel to obtain a web having a desired basis weight. Get. What is necessary is just to perform needle punching with a punch needle with respect to what prepared two sheets of webs obtained in this way, and pinched | interposed the base fabric between them, and should just make it a desired thickness.
Examples of the base fabric include spunbonded nonwoven fabrics and woven fabrics made of fibers that are hardly decomposable to water and organisms, such as polyester fibers, polypropylene fibers, polyamide fibers, and acrylic fibers.

また、不織布からなる微生物付着用担体に対して、微生物付着用担体を支持する支持体を組み合わせた担体ユニットの形態として、微生物付着用担体を処理水槽内に浸漬配置してもよい。
担体ユニットとしては、例えば図1に示すように、四角形の不織布からなる微生物付着用担体1と、該微生物付着用担体1を処理水槽に浸漬配置した場合に、上端および下端となる端部に設けられた一対の長尺な支持体2とからなる担体ユニット3が挙げられる。また、不織布からなる微生物付着用担体に上述の基布を積層した積層体に対して、同様の支持体を設けて、担体ユニットとしてもよい。
Alternatively, the microorganism-adhering carrier may be immersed in the treatment water tank in the form of a carrier unit in which a microorganism-adhering carrier comprising a nonwoven fabric is combined with a support that supports the microorganism-adhering carrier.
As the carrier unit, for example, as shown in FIG. 1, when the microorganism-adhering carrier 1 made of a rectangular non-woven fabric and the microorganism-adhering carrier 1 are immersed in the treatment water tank, they are provided at the ends that are the upper end and the lower end. A carrier unit 3 composed of a pair of elongated supports 2 is mentioned. Further, a similar support may be provided on the laminate in which the above-mentioned base fabric is laminated on a carrier for attaching microorganisms made of nonwoven fabric to form a carrier unit.

以上説明した微生物付着用担体は不織布からなるため、簡単に製造できる。また、単位体積当りの繊維量が多いため、処理水槽に浸漬配置した際の微生物の付着量も高くなり、効率的な生物処理を行うことができる。   Since the carrier for attaching microorganisms described above is made of a nonwoven fabric, it can be easily manufactured. Moreover, since the amount of fibers per unit volume is large, the amount of microorganisms attached when immersed in a treated water tank is increased, and an efficient biological treatment can be performed.

以下、本発明について、実施例を挙げて具体的に説明する。
[実施例1〜3]
アクリル繊維として、三菱レイヨン社製のボンネル「H815BRE2.2T51」を使用し、この繊維に対してローラーカードにてカーディングを行い、得られたカードウェブをパラレル状に折りたたんで積層した。ついで、得られたウェブに対してパンチ針によるニードルパンチを行った。さらに、厚みを抑えるために、実施例3では熱プレスを施し、表1に示す目付け、厚みの各不織布を得た。
なお、不織布の目付けは、カードウェブをパラレル状に折りたたんで積層する際の層数により調整し、厚みは、ニードルパンチの条件と熱プレスの有無により調整した。
Hereinafter, the present invention will be specifically described with reference to examples.
[Examples 1 to 3]
As the acrylic fiber, Bonnell “H815BRE2.2T51” manufactured by Mitsubishi Rayon Co., Ltd. was used. Carding was performed on this fiber with a roller card, and the resulting card web was folded in parallel and laminated. Next, needle punching with a punch needle was performed on the obtained web. Furthermore, in order to suppress the thickness, in Example 3, hot pressing was performed to obtain nonwoven fabrics having the basis weight and thickness shown in Table 1.
The basis weight of the nonwoven fabric was adjusted by the number of layers when the card webs were folded in parallel and laminated, and the thickness was adjusted by the conditions of needle punching and the presence or absence of hot pressing.

Figure 0005824960
Figure 0005824960

ついで、図1に示すように、不織布からなる微生物付着用担体1に一対の支持体2を設けて担体ユニット3とし、この担体ユニット3を図2に示すように膜分離活性汚泥処理装置中の処理水槽(活性汚泥槽)10中に浸漬し、固定具4で固定した。   Next, as shown in FIG. 1, a pair of supports 2 is provided on a microorganism-adhering carrier 1 made of nonwoven fabric to form a carrier unit 3, and this carrier unit 3 is placed in a membrane separation activated sludge treatment apparatus as shown in FIG. It was immersed in the treated water tank (activated sludge tank) 10 and fixed with the fixture 4.

図2に示す膜分離活性汚泥処理装置は、処理水槽10と、処理水槽10内に浸漬配置された膜ユニット20と、膜ユニット20に対して散気する散気装置30と、膜ユニット20に接続された濾過ポンプ40と、濾過ポンプ40および散気装置30の運転をコントロールする制御装置50と、被処理原水を処理水槽10に供給する供給ライン60とを備えている。
処理水槽10の活性汚泥濃度は、固形分濃度MLSSが8,000〜10,000mg/Lの間になるように制御した。また、処理水槽10中の溶存酸素濃度(DO)は、0.5〜1.0mg/Lの間になるように散気量を制御した。被処理原水としては、生物学的酸素要求量(BOD)の濃度が、150〜200mg/Lである生活排水を用い、この原水を、処理水槽10内の水力学的滞留時間が3時間となるように供給し、上記条件にて3ヶ月間馴致した。
その後、馴致した処理水槽10の活性汚泥中に、担体ユニット3を浸漬し、上述のように固定した。
The membrane separation activated sludge treatment apparatus shown in FIG. 2 includes a treatment water tank 10, a membrane unit 20 immersed in the treatment water tank 10, an air diffuser 30 that diffuses into the membrane unit 20, and a membrane unit 20. A connected filtration pump 40, a control device 50 that controls the operation of the filtration pump 40 and the air diffuser 30, and a supply line 60 that supplies raw water to be treated to the treated water tank 10 are provided.
The activated sludge concentration in the treated water tank 10 was controlled so that the solid content concentration MLSS was between 8,000 and 10,000 mg / L. Moreover, the amount of diffused air was controlled so that the dissolved oxygen concentration (DO) in the treated water tank 10 was between 0.5 and 1.0 mg / L. As raw water to be treated, domestic wastewater having a biological oxygen demand (BOD) concentration of 150 to 200 mg / L is used, and this raw water is subjected to a hydrodynamic residence time of 3 hours in the treated water tank 10. And acclimated for 3 months under the above conditions.
Then, the support | carrier unit 3 was immersed in the activated sludge of the treated water tank 10 which was adapted, and it fixed as mentioned above.

浸漬後、所定日数の経過毎に、担体ユニット3を処理水槽10から取り出し、その質量を測定した。図3のグラフに、経過日数と、質量増加との関係を示す。
質量増加は、浸漬後の担体ユニット3の質量から、浸漬前の担体ユニット3の質量を引いて得られた値を微生物付着用担体(不織布)1の面積で割り、単位面積当たり(1cm当たり)の値に換算したものである。質量増加は、活性汚泥の付着量に相当する。
After the immersion, the carrier unit 3 was taken out of the treated water tank 10 every predetermined number of days, and its mass was measured. The graph of FIG. 3 shows the relationship between elapsed days and mass increase.
The mass increase is obtained by dividing the value obtained by subtracting the mass of the carrier unit 3 before the immersion from the mass of the carrier unit 3 after the immersion by the area of the carrier (nonwoven fabric) 1 for attaching microorganisms, and per unit area (per 1 cm 2 ) Value. The increase in mass corresponds to the amount of activated sludge attached.

図3に示すように、各例の微生物付着用担体は、経過日数とともに質量が増加し、良好に微生物が付着していることが理解できた。
また、不織布の目付けを60g/m以上とした実施例1および2においては、さらに質量増加、すなわち微生物の付着量も増加した。
As shown in FIG. 3, it was understood that the microorganism-adhering carrier of each example increased in mass with the elapsed days, and the microorganisms adhered well.
Further, in Examples 1 and 2 in which the basis weight of the nonwoven fabric was 60 g / m 2 or more, the mass increased, that is, the amount of attached microorganisms also increased.

1 微生物付着用担体(不織布)   1 Microorganism attachment carrier (nonwoven fabric)

Claims (3)

膜分離活性汚泥処理装置における活性汚泥が投入された処理水槽内に浸漬配置され、前記活性汚泥中の微生物を付着させる微生物付着用担体であって、
アクリロニトリル単位を50質量%以上有するアクリル系重合体の繊維で構成された乾式不織布からなる微生物付着用担体。
A microbial attachment carrier that is immersed in a treated water tank into which activated sludge is charged in a membrane separation activated sludge treatment apparatus , and adheres microorganisms in the activated sludge,
A microorganism-adhering carrier comprising a dry nonwoven fabric composed of acrylic polymer fibers having 50% by mass or more of acrylonitrile units.
前記不織布は、目付けが60〜1000g/mである、請求項1に記載の微生物付着用担体。 The non-woven fabric, basis weight is 60~1000g / m 2, microbial attachment carrier according to claim 1. 前記不織布は、厚みが0.5〜30mmである、請求項1または2に記載の微生物付着用担体。   The microorganism-adhering carrier according to claim 1 or 2, wherein the nonwoven fabric has a thickness of 0.5 to 30 mm.
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