JP5380688B2 - Water treatment member, septic tank, and water treatment device - Google Patents

Water treatment member, septic tank, and water treatment device Download PDF

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JP5380688B2
JP5380688B2 JP2010011598A JP2010011598A JP5380688B2 JP 5380688 B2 JP5380688 B2 JP 5380688B2 JP 2010011598 A JP2010011598 A JP 2010011598A JP 2010011598 A JP2010011598 A JP 2010011598A JP 5380688 B2 JP5380688 B2 JP 5380688B2
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support
water treatment
tank
fiber
carrier
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JP2011147886A (en
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寛 亀井
直樹 木谷
幹夫 滝本
あゆみ 萩原
吉弘 和田
進 大沼
英二 櫻井
良子 池本
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Nikko Co Ltd
Kanazawa University NUC
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Kanazawa University NUC
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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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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

本発明は、水処理部材及び浄化槽に関する。   The present invention relates to a water treatment member and a septic tank.

例えば、特許文献1には、炭素繊維にて構成された複数の繊維状担体を束状にした繊維束の一端部を固定部にて互いに連結した繊維濾材が開示されている。
また、例えば、特許文献2には、排水処理装置に用いる微生物担体であって、微生物担体は複数の支持担体からなり、支持担体は支持部材と支持部材に上下方向に複数段配置した繊維束とを有し、繊維束は複数の繊維フィラメントからなり、一端又は途中を支持部材に束ねて固定し、他端又は端部が繊維フィラメントの自由端となっており、複数の支持担体を並設し、隣接する支持担体の繊維フィラメントの自由端が相互に一部重なり合うように配置したものである微生物担体が開示されている。
また、例えば、特許文献3には、水処理装置の曝気槽内に設置されて微生物を付着するため支持枠にほぼ垂直に取り付けられた多数のひも状接触濾材からなる生物接触濾材において、各ひも状接触濾材の生物担体部は不連続に設けられ、かつ生物担体部は隣接のひも状接触濾材の生物担体部に対し高さが不揃いになるように配置されている生物接触濾材。
また、例えば、特許文献4には、嫌気性生物処理槽において濾材としてひも状固定部材を中心軸に複数の可撓性揺動部材が放射状に設けられている浄化槽が開示されている。
For example, Patent Document 1 discloses a fiber filter medium in which one end portions of a fiber bundle obtained by bundling a plurality of fibrous carriers composed of carbon fibers are connected to each other at a fixing portion.
Further, for example, Patent Document 2 discloses a microbial carrier used in a wastewater treatment apparatus, wherein the microbial carrier includes a plurality of support carriers, and the support carrier includes a support member and a fiber bundle arranged in a plurality of stages in the vertical direction on the support member. The fiber bundle is composed of a plurality of fiber filaments, one end or the middle is bundled and fixed to a support member, the other end or the end is a free end of the fiber filament, and a plurality of support carriers are arranged in parallel. Also disclosed is a microbial carrier in which the free ends of the fiber filaments of adjacent support carriers are arranged so as to partially overlap each other.
In addition, for example, in Patent Document 3, in a biological contact filter medium comprising a large number of string contact filter media that are installed in an aeration tank of a water treatment device and attached to a support frame in order to adhere microorganisms, A biological contact filter medium in which the biological carrier parts of the contact filter medium are discontinuously provided, and the biological carrier parts are arranged so that their heights are uneven with respect to the biological carrier part of the adjacent string-like contact filter medium.
For example, Patent Document 4 discloses a septic tank in which a plurality of flexible rocking members are provided radially around a string-like fixing member as a filter medium in an anaerobic biological treatment tank.

特開2009−136737号公報JP 2009-136737 A 特開2008−29945号公報JP 2008-29945 A 特開平5−237490号公報JP-A-5-237490 特開2001−54796号公報JP 2001-54796 A

このように特許文献1、2、3、4それぞれに記載されたものでは繊維材を排水処理に用いて汚泥の捕集効率を高めているが、槽内水の排出時には繊維材に大量に付着した汚泥の荷重により、繊維材自体を痛めてしまう恐れがある他、繊維材の集合体を吊り下げた場合、吊り下げ部あるいは連結部が破損してしまう可能性もある。また補足率を高めるために繊維材量を増加させると、補足汚泥による濾床閉塞が起こる可能性がある。さらに、水処理用部材は、投入、交換が容易である必要もある。本発明は、簡便であり、嫌気性処理部において、懸濁固形物など汚泥の捕集効果に優れ、濾床閉塞を起しにくく、かつ槽内水排出時の荷重負荷に耐えうる水処理部材、及びこの水処理部材を設けた水処理装置、浄化槽を提供することを目的とする。   As described above, in each of Patent Documents 1, 2, 3, and 4, the fiber material is used for wastewater treatment to increase the sludge collection efficiency, but when the water in the tank is discharged, the fiber material adheres in large quantities. In addition to the risk of damaging the fiber material itself due to the sludge load, the suspended part or the connecting part may be damaged when the fiber material assembly is suspended. Moreover, if the amount of fiber material is increased in order to increase the supplement rate, the filter bed may be blocked by supplemental sludge. Further, the water treatment member needs to be easily charged and replaced. The present invention is simple and excellent in the effect of collecting sludge such as suspended solids in an anaerobic treatment section, hardly causes filter bed clogging, and can withstand the load load when draining water in the tank. And it aims at providing the water treatment apparatus and septic tank which provided this water treatment member.

本発明に係る水処理部材は、空中又は水中において一定の形態を保持できる程度の硬さを有する支持体と、前記支持体から斜め方向に張り出した複数の繊維部材とを有する。   The water treatment member according to the present invention includes a support body having a hardness capable of maintaining a certain form in the air or water, and a plurality of fiber members projecting obliquely from the support body.

好適には、前記支持体は、棒状であり、前記繊維部材の固定位置は、前記支持体表面に螺旋状に設けられてなる。   Suitably, the said support body is rod-shaped and the fixing position of the said fiber member is helically provided in the said support body surface.

好適には、紐状又は帯状の可撓性部材をさらに有し、複数の前記繊維部材は、前記可撓性部材に配列されており、前記前記可撓性部材が前記支持体の周囲に螺旋状に巻きつけられてなる。   Preferably, it further has a string-like or belt-like flexible member, and the plurality of fiber members are arranged in the flexible member, and the flexible member spirals around the support. Wrapped in a shape.

好適には、前記繊維部材は、炭素繊維であり、前記繊維部材の長軸方向は、前記可撓性部材の長軸方向に対して略直交する。   Preferably, the fiber member is carbon fiber, and the long axis direction of the fiber member is substantially orthogonal to the long axis direction of the flexible member.

また、本発明に係る浄化槽は、空中又は水中において一定の形態を保持できる程度の硬さを有する棒状の支持体と、前記支持体から斜め方向に張り出した複数の繊維部材を螺旋状に配置することで懸濁固形物など汚泥を効率的に捕集できる水処理部材と、前記支持体の長軸方向が処理水の流れる方向となるように形成された嫌気性処理槽とを有する。   Further, the septic tank according to the present invention spirally arranges a rod-like support having a hardness capable of maintaining a certain form in the air or in water and a plurality of fiber members projecting obliquely from the support. Thus, it has a water treatment member capable of efficiently collecting sludge such as suspended solids, and an anaerobic treatment tank formed so that the major axis direction of the support is the direction in which the treated water flows.

好適には、前記繊維部材は、炭素繊維であり、前記繊維部材の長軸方向は、前記可撓性部材の長軸方向に対して略直交する。   Preferably, the fiber member is carbon fiber, and the long axis direction of the fiber member is substantially orthogonal to the long axis direction of the flexible member.

また、本発明に係る水処理方法は、繊維部材が複数配列された紐状又は帯状の可撓性部材を、棒状の支持体の表面に螺旋状に巻き付け、前記可撓性部材が巻き付けられた支持体を、処理水中に設置する。   In the water treatment method according to the present invention, a string-like or belt-like flexible member in which a plurality of fiber members are arranged is spirally wound around the surface of a rod-like support, and the flexible member is wound around the surface. The support is installed in the treated water.

本発明に係る水処理部材は、懸濁固形物など汚泥を効率的に捕集でき、濾床閉塞しにくく、かつ槽内水排出時の荷重負荷に耐えることができる。   The water treatment member according to the present invention can efficiently collect sludge such as suspended solids, hardly clogs the filter bed, and can withstand the load applied when the water in the tank is discharged.

浄化槽1の全体構成を模式的に表す図である。It is a figure which represents typically the whole structure of the septic tank. 水処理部材120の全体構成を模式的に表す図である。It is a figure which represents typically the whole structure of the water treatment member. 各種水処理部材を設けられた嫌気濾床槽からの汚泥流出量を表す図である。It is a figure showing the sludge outflow amount from the anaerobic filter bed tank provided with various water treatment members. 各種水処理部材を設けられた嫌気濾床槽における汚泥保持量を表す図である。It is a figure showing the sludge retention amount in the anaerobic filter bed tank provided with various water treatment members. 浄化槽2の全体構成を模式的に表す図である。It is a figure which represents typically the whole structure of the septic tank. 浄化槽3の全体構成を模式的に表す図である。It is a figure which represents typically the whole structure of the septic tank. 水処理部材122の全体構成を模式的に表す図である。It is a figure which represents typically the whole structure of the water treatment member. 水処理部材124の全体構成を模式的に表す図である。It is a figure which represents typically the whole structure of the water treatment member. 水処理部材124の要部拡大図である。It is a principal part enlarged view of the water treatment member 124. FIG. 水処理装置400の全体構成を模式的に表す図である。It is a figure which represents typically the whole structure of the water treatment apparatus 400. FIG.

図1は、浄化槽1の全体構成を模式的に表す図である。
図1に例示するように、浄化槽1は、嫌気濾床槽第1室10と、可溶化槽20と、嫌気濾床槽第2室30と、接触曝気槽40と、処理水槽50と、消毒槽60とを有する。
FIG. 1 is a diagram schematically illustrating the entire configuration of the septic tank 1.
As illustrated in FIG. 1, the septic tank 1 includes an anaerobic filter bed first chamber 10, a solubilization tank 20, an anaerobic filter bed second chamber 30, a contact aeration tank 40, a treated water tank 50, and a disinfectant. And a tank 60.

嫌気濾床槽第1室10は、生活雑排水又はし尿などの汚水がまず最初に流入される場所である。流入した汚水は、嫌気濾床槽第1室10において上から下へと流れ、途中にある固形材110に、この汚水中に含まれる汚泥物質を付着させる。固形材110は、水処理部材の一種であり、表面には種々の微生物集団が膜状(以下「微生物膜」という)に形成されている。固形材110に付着した汚泥物質は、この微生物膜により、分解・浄化される。そして、汚泥物質を分解・浄化された汚水は、次に嫌気濾床槽第2室30へと送られる。また、固形材110に付着せず、嫌気濾床槽第1室10の底部に溜まった汚泥物質は、エアリフトポンプにより吸い上げられて、可溶化槽20へと送られる。   The anaerobic filter bed first chamber 10 is a place where sewage such as domestic wastewater or human waste is first introduced. The inflowing sewage flows from the top to the bottom in the anaerobic filter bed first chamber 10, and the sludge contained in the sewage is attached to the solid material 110 in the middle. The solid material 110 is a kind of water treatment member, and various microbial populations are formed in a film form (hereinafter referred to as “microbe membrane”) on the surface. The sludge substance adhering to the solid material 110 is decomposed and purified by this microbial film. Then, the sewage obtained by decomposing and purifying the sludge material is then sent to the anaerobic filter bed tank second chamber 30. The sludge substance that does not adhere to the solid material 110 and accumulates at the bottom of the anaerobic filter bed first chamber 10 is sucked up by the air lift pump and sent to the solubilization tank 20.

可溶化槽20は、水処理部材120(図2を用いて後述)を設けられている。可溶化槽20に送られた汚水は、可溶化槽20の底部に設けられたポンプの作用により、可溶化槽20内部を上下に循環するようになっている。この循環により、可溶化槽20に送られた汚水に含まれる汚泥物質は、汚水への溶解が促進される。また、この循環により、水処理部材120には、汚水に含まれる汚泥物質が付着する。水処理部材120の表面には、嫌気性の微生物膜が形成されている。水処理部材120に付着した汚泥物質は、この微生物膜により、分解・浄化される。なお、水処理部材120は、固形材110と比べて表面積が大きく、一度に多くの汚泥物質を付着させ、分解・浄化することができる。特に炭素繊維である場合は、生物親和性が高く嫌気性の微生物膜が早期に形成されることが期待できる。そして、汚泥物質を分解・浄化された汚水は、次に嫌気濾床槽第2室30へと送られる。   The solubilization tank 20 is provided with a water treatment member 120 (described later with reference to FIG. 2). The sewage sent to the solubilization tank 20 is circulated up and down in the solubilization tank 20 by the action of a pump provided at the bottom of the solubilization tank 20. By this circulation, the sludge substance contained in the sewage sent to the solubilization tank 20 is promoted to dissolve in the sewage. Moreover, the sludge substance contained in sewage adheres to the water treatment member 120 by this circulation. An anaerobic microbial membrane is formed on the surface of the water treatment member 120. The sludge substance adhering to the water treatment member 120 is decomposed and purified by this microbial membrane. The water treatment member 120 has a surface area larger than that of the solid material 110, and can attach and disassemble and purify many sludge substances at a time. In particular, in the case of carbon fiber, it can be expected that an anaerobic microbial film having high bioaffinity is formed at an early stage. Then, the sewage obtained by decomposing and purifying the sludge material is then sent to the anaerobic filter bed tank second chamber 30.

嫌気濾床槽第2室30は、水処理部材120を設けられている。嫌気濾床槽第2室30に送られた汚水は、下から上へと流れ、途中にある水処理部材120に、この汚水中に含まれる汚泥物質を付着させる。水処理部材120は、可溶化槽20における場合と同様に、表面に形成された微生物膜により、付着した汚泥物質を分解・浄化する。そして、汚泥物質を分解・浄化された汚水は、次に接触曝気槽40へと送られる。   The anaerobic filter bed second chamber 30 is provided with a water treatment member 120. The sewage sent to the anaerobic filter bed second chamber 30 flows from the bottom to the top, and the sludge contained in the sewage is attached to the water treatment member 120 in the middle. As in the case of the solubilization tank 20, the water treatment member 120 decomposes and purifies the attached sludge substance by the microbial film formed on the surface. Then, the sewage obtained by decomposing and purifying the sludge substance is then sent to the contact aeration tank 40.

接触曝気槽40は、接触材130と、この接触材130に向けて絶えず空気の気泡を放出する散気装置140とを設けられている。接触材130の表面には、好気性の微生物膜が形成されている。汚水に含まれる汚濁物質は、この微生物膜による接触酸化作用により分解・浄化される。さらに、接触曝気槽40内は生物ろ過部135を有しており、その下部には逆洗用散気装置145を配している。この生物ろ過部135は、固形材115を有しており、汚水中に浮遊する固形物を物理的にろ過・捕捉するとともに表面に形成された微生物膜により、残存する汚濁物質を分解・浄化する。通常、逆洗用散気装置145は空気を放出しておらず、1日に1回〜数回の頻度で自動逆洗(空気の放出)が行われ、生物ろ過部135が捕捉した固形物により完全に閉塞してしまうことを防止している。そして、汚濁物質を分解・浄化された汚水は、処理水槽50、さらに消毒槽60へと送られる。   The contact aeration tank 40 is provided with a contact material 130 and an air diffuser 140 that constantly discharges air bubbles toward the contact material 130. An aerobic microbial film is formed on the surface of the contact material 130. The pollutant contained in the sewage is decomposed and purified by the catalytic oxidation action by the microbial membrane. Furthermore, the inside of the contact aeration tank 40 has a biological filtration part 135, and a backwashing air diffuser 145 is arranged in the lower part thereof. This biological filtration unit 135 has a solid material 115, and physically filters and captures solid matter floating in the sewage, and decomposes and purifies residual pollutants by a microbial film formed on the surface. . Normally, the backwashing diffuser 145 does not release air, and automatic backwashing (air release) is performed once to several times a day, and the solid matter captured by the biological filtration unit 135 is collected. To prevent complete blockage. Then, the sewage obtained by decomposing and purifying the pollutant is sent to the treated water tank 50 and further to the disinfection tank 60.

消毒槽60は、分解・浄化された汚水を最終的に消毒し、川などに放流する。また、処理水槽50は、接触曝気槽40から送られてきた汚水を、ポンプにより、循環水として嫌気濾床槽第1室10へ送る。場合によっては、嫌気濾床槽第2室30へ送ることもある。   The disinfection tank 60 finally disinfects the decomposed and purified sewage and discharges it to a river or the like. Moreover, the treated water tank 50 sends the sewage sent from the contact aeration tank 40 to the anaerobic filter bed tank first chamber 10 as circulating water by a pump. In some cases, it may be sent to the anaerobic filter bed tank second chamber 30.

以上説明したように、本実施例に係る水処理部材120は、浄化槽1に設けられ、汚水処理を行う。   As described above, the water treatment member 120 according to the present embodiment is provided in the septic tank 1 and performs sewage treatment.

図2は、水処理部材120の全体構成を模式的に表す図である。
図2に例示するように、水処理部材120は、支持体210と、担体部材220とを有する。本実施例では、水処理部材120は、さらに固定部材240を有する。
FIG. 2 is a diagram schematically illustrating the entire configuration of the water treatment member 120.
As illustrated in FIG. 2, the water treatment member 120 includes a support body 210 and a carrier member 220. In the present embodiment, the water treatment member 120 further includes a fixing member 240.

支持体210は、空中又は水中において一定の形態を保持できる硬さを有し、周囲に巻きつけられた担体部材220を支持する。支持体210の形状は、特に限定するものではなく、汚泥が保持された状態での担体部材220を構造体として最低限支えることができればよく、周囲に担体部材220を巻きつけられるものであればよい。例えば、支持体210は、略円柱型、略円錐型、略球型、略多角柱型、略錐体型などに形成されればよい。
本実施例では、支持体210は、略円柱型の棒状に形成されている。本実施例に係る支持体210の軸線に対する垂直断面の外径は、特に限定するものではないが、周囲に巻きつけられる担体部材220の繊維状担体320が適度に広がることで、水流を阻害しないように、5〜80mmであることが好ましい。
また、支持体210は、浄化槽1内の水流に耐え、耐腐食性のある素材で形成されることが好ましく、さらに支持体210の交換又はメンテナンス等を考慮し、軽量である素材で形成されることがより好ましい。例えば、支持体210は、塩化ビニルなどの素材で形成されるとよい。
The support 210 has a hardness capable of maintaining a certain form in the air or water, and supports the carrier member 220 wound around the support 210. The shape of the support 210 is not particularly limited as long as the support member 220 in a state where sludge is held can be supported at least as a structure, and can be wound around the support member 220. Good. For example, the support 210 may be formed in a substantially cylindrical shape, a substantially conical shape, a substantially spherical shape, a substantially polygonal column shape, a substantially cone shape, or the like.
In this embodiment, the support 210 is formed in a substantially cylindrical rod shape. The outer diameter of the vertical cross section with respect to the axis of the support 210 according to the present embodiment is not particularly limited, but the fibrous carrier 320 of the carrier member 220 that is wound around is moderately spread, so that the water flow is not hindered. Thus, it is preferable that it is 5-80 mm.
Further, the support 210 is preferably formed of a corrosion-resistant material that can withstand the water flow in the septic tank 1, and is formed of a lightweight material in consideration of replacement or maintenance of the support 210. It is more preferable. For example, the support 210 may be formed of a material such as vinyl chloride.

担体部材220は、紐状又は帯状に形成された基幹部材310に、繊維状担体320を複数固定したものである。繊維状担体320を基幹材310に固定する手段は、特に限定するものではない。例えば、繊維状担体320は、接着又は溶着などにより基幹材310に接合されてもよいし、又は繊維状担体320と基幹部材310とが一体的に形成されてもよい。また、繊維状担体320を基幹材310に固定したときの、繊維状担体320の基幹部材310の軸線方向に対する傾きは、特に限定するものではない。
本実施例では、繊維状担体320は、基幹部材310に略直交する状態で固定されている。また、繊維状担体320は、可撓性を有しており、重力により斜め下方に撓る。これにより、担体部材220は、槽内水排出時に鉛直下方にかかる荷重により繊維状担体320に作用する剪弾力を軽減させることができる。
基幹部材310及び繊維状担体320の素材は、特に限定するものではないが、例えば、炭素繊維、ナイロン繊維、ポリエステル繊維、ポリ塩化ビニリデン繊維、ポリプロピレン繊維などであればよい。なかでも、炭素繊維は、耐久性に優れ、軽量であり、かつ生物親和性にも優れるので好適である。
The carrier member 220 is obtained by fixing a plurality of fibrous carriers 320 to a base member 310 formed in a string shape or a belt shape. The means for fixing the fibrous carrier 320 to the base material 310 is not particularly limited. For example, the fibrous carrier 320 may be bonded to the basic material 310 by adhesion or welding, or the fibrous carrier 320 and the basic member 310 may be integrally formed. In addition, the inclination of the fibrous carrier 320 with respect to the axial direction of the basic member 310 when the fibrous carrier 320 is fixed to the basic material 310 is not particularly limited.
In this embodiment, the fibrous carrier 320 is fixed in a state of being substantially orthogonal to the basic member 310. The fibrous carrier 320 is flexible and bends obliquely downward due to gravity. Thereby, the carrier member 220 can reduce the shearing force which acts on the fibrous carrier 320 by the load applied vertically downward when the water in the tank is discharged.
The material of the basic member 310 and the fibrous carrier 320 is not particularly limited, and may be, for example, carbon fiber, nylon fiber, polyester fiber, polyvinylidene chloride fiber, polypropylene fiber, or the like. Among these, carbon fibers are preferable because they are excellent in durability, light in weight, and excellent in biocompatibility.

また、担体部材220は、支持体210の周囲に巻き付けられ、支持体210に固定される。担体部材220を支持体210に固定する手段は、特に限定するものではない。例えば、担体部材220は、支持体210に設けられたフック状の部材に引っ掛けられる、又は帯状の部材で緊締される等により、支持体210に固定されればよい。また、担体部材220は、支持体210の複数箇所で固定されることが好ましい。これにより、担体部材220は、槽内水排出時に鉛直下方にかかる荷重を、支持体210に固定されている複数箇所に分散させることができる。
本実施例では、担体部材220は、緊締部材230により支持体210に複数箇所で固定されている。緊締部材230は、担体部材230を支持体210に緊締することができるものであれば、何でもよい。例えば、緊締部材230は、ゴムバンド又はベルトなどである。
Further, the carrier member 220 is wound around the support 210 and fixed to the support 210. The means for fixing the carrier member 220 to the support 210 is not particularly limited. For example, the carrier member 220 may be fixed to the support 210 by being hooked on a hook-shaped member provided on the support 210 or tightened by a belt-shaped member. Further, the carrier member 220 is preferably fixed at a plurality of locations of the support 210. Thereby, the carrier member 220 can disperse the load applied vertically downward when the water in the tank is discharged to a plurality of locations fixed to the support 210.
In the present embodiment, the carrier member 220 is fixed to the support body 210 at a plurality of locations by fastening members 230. The fastening member 230 may be anything as long as it can fasten the carrier member 230 to the support 210. For example, the tightening member 230 is a rubber band or a belt.

また、担体部材220が支持体210の周囲に巻き付く形状は、特に限定するものではないが、図2に例示するように螺旋状であることが好ましい。担体部材220が支持体210の周囲に螺旋状に巻き付けられ、固定されることにより、担体部材220の間を通る上下方向の水流は、螺旋状に渦を巻くようになる。これにより、処理水は短絡することなく繊維状担体320と繰り返し接触することから、水処理部材120は、効率的に汚泥を繊維状担体320に付着させることができる。また、担体部材220が支持体210の周囲に螺旋状に巻き付けられることにより、支持体210の配置間隔を短くしても、隣接する担体部材220のラップ接合部分が少なく、上下方向の水流の通路が必ず確保されるので、汚泥の増殖による濾床閉塞が起こりにくい。なお、この場合における支持体210の軸線方向は、水流方向に平行であることが好ましい。   Moreover, the shape in which the carrier member 220 wraps around the support 210 is not particularly limited, but is preferably a spiral shape as illustrated in FIG. When the carrier member 220 is spirally wound and fixed around the support 210, the water flow in the vertical direction passing between the carrier members 220 is spirally spiraled. Thereby, since treated water repeatedly contacts with the fibrous carrier 320 without short-circuiting, the water treatment member 120 can efficiently attach sludge to the fibrous carrier 320. Further, since the carrier member 220 is spirally wound around the support 210, even if the arrangement interval of the support 210 is shortened, there are few lap joint portions of the adjacent carrier members 220, and the water flow path in the vertical direction. Therefore, filter bed blockage due to sludge growth is unlikely to occur. In this case, the axial direction of the support 210 is preferably parallel to the water flow direction.

固定部材240は、支持体210を固定する。固定部材240は上部と下部の一方のみあっても良いし、図2のように両方あっても良い。固定部材240が支持体210を固定する手段は、特に限定するものではない。例えば、固定部材240は、支持体210に嵌合する、又は支持体210の周囲を支持すること等により、支持体210を固定すればよい。なお、固定部材240は、水処理部材120が設けられる浄化槽と別個に形成され、浄化槽に固定されてもよいし、又は浄化槽と一体的に形成されてもよい。
本実施例では、固定部材240は、支持体210の外径よりもやや大き目の穴を複数設けられた板である。固定部材240は、支持体210の両端部に位置するように、2枚平行に浄化槽内に設けられている。支持体210は、この平行に設けられた固定部材240の穴に挿入されることにより、両端部において固定される。
なお、固定部材240が固定する支持体210の数は、水処理部材120が設けられる浄化槽の容量又は浄化能力などに応じて、適宜変更されればよい。
The fixing member 240 fixes the support body 210. The fixing member 240 may be only one of the upper part and the lower part, or may be both as shown in FIG. The means by which the fixing member 240 fixes the support 210 is not particularly limited. For example, the fixing member 240 may be fixed to the support 210 by fitting to the support 210 or supporting the periphery of the support 210. The fixing member 240 may be formed separately from the septic tank in which the water treatment member 120 is provided, and may be fixed to the septic tank, or may be formed integrally with the septic tank.
In this embodiment, the fixing member 240 is a plate provided with a plurality of holes slightly larger than the outer diameter of the support 210. Two fixing members 240 are provided in the septic tank in parallel so as to be positioned at both ends of the support 210. The support 210 is fixed at both ends by being inserted into the holes of the fixing member 240 provided in parallel.
In addition, the number of the support bodies 210 to which the fixing member 240 is fixed may be appropriately changed according to the capacity of the septic tank in which the water treatment member 120 is provided or the purification capacity.

以上説明したような構成により、水処理部材120は、槽内水排出時又は不定期な流量変化による担体部材220への荷重負荷を軽減し、付着した汚泥により基幹材310が破断する等の担体部材220の損傷を防止している。また、繊維状担体320が、曲げに弱い炭素繊維である場合でも、繊維状担体310が支持体210から斜め方向に張り出しているため、繊維状担体320が槽内水排出後に自重で下方に垂れ下がったときに、支持体210に対する繊維状担体320の屈曲角度が小さくなり、破断防止が期待できる。
また、水処理部材120は、担体部材220を支持体210に螺旋状に巻き付けることにより、螺旋状の整流効果と、繊維状担体320の十分な広がりとを実現し、浄化能力の向上が期待できる。さらに、水処理部材120は、固定部材240により、支持体210ごとの交換を容易にしている。
With the configuration as described above, the water treatment member 120 reduces the load applied to the carrier member 220 when the water in the tank is discharged or irregularly changes in the flow rate, and the base material 310 is broken by the attached sludge. The member 220 is prevented from being damaged. Even when the fibrous carrier 320 is a carbon fiber that is weak against bending, the fibrous carrier 310 projects obliquely from the support 210, so that the fibrous carrier 320 hangs down by its own weight after draining the water in the tank. The bending angle of the fibrous carrier 320 with respect to the support 210 is reduced, and breakage prevention can be expected.
Further, the water treatment member 120 spirally winds the carrier member 220 around the support 210 to realize a spiral rectification effect and a sufficient spread of the fibrous carrier 320, and an improvement in purification capability can be expected. . Further, the water treatment member 120 facilitates replacement of each support 210 by the fixing member 240.

図3は、50Lの小型槽にて嫌気性処理実験をおこなった結果であり、懸濁固形物(SS)3000mg/Lの汚泥5L/日を流入させたときの流出汚泥のSS濃度を測定した。グラフでの「炭素繊維ムカデ型」は炭素繊維を担体部材220として、支持体210に巻き付けて固定することなく設置したものであり、「ひも状繊維材」はポリエステル系の繊維材を担体部材220として、支持体210に巻きつけて固定することなく設置したものである。また「炭素繊維螺旋タイプ」は炭素繊維を担体部材として、支持体210に螺旋状に巻き付けて固定した状態で設置したものである。なお炭素繊維量は同量とした。   FIG. 3 shows the results of an anaerobic treatment experiment in a 50 L small tank, and the SS concentration of the spilled sludge was measured when 5 L / day of sludge of suspended solids (SS) 3000 mg / L was flowed. . The “carbon fiber centipede type” in the graph is a carbon fiber that is installed as a carrier member 220 without being wrapped around and fixed to the support 210, and the “string-like fiber material” is a polyester fiber material that is supported by the carrier member 220. As described above, it is installed without being wrapped around the support 210 and fixed. The “carbon fiber spiral type” is a carbon fiber as a carrier member and is installed in a state of being wound around and fixed to the support 210 in a spiral manner. The amount of carbon fiber was the same.

図3に例示するように「炭素繊維ムカデ型」は「ひも状繊維材」と比較し流出SSが増加するまでの日数が長く、「炭素繊維螺旋タイプ」では測定期間中流出SS量が非常に少ない結果となった。   As illustrated in FIG. 3, the “carbon fiber centipede type” has a longer number of days until the outflow SS increases than the “string fiber material”, and the “carbon fiber spiral type” has a very large amount of outflow SS during the measurement period. There were few results.

図4は、前述の図3で示した嫌気性処理実験について、流入汚泥量と流出汚泥量の差異から、実験槽内に保持されている累積汚泥量を求めたものである。グラフでの「炭素繊維ムカデ型」は炭素繊維を担体部材220として、支持体210に巻き付けて固定することなく設置したものであり、「ひも状繊維材」はポリエステル系の繊維材を担体部材220として、支持体210に巻きつけて固定することなく設置したものである。また「炭素繊維螺旋タイプ」は炭素繊維を担体部材として、支持体210に螺旋状に巻き付けて固定した状態で設置したものである。   FIG. 4 shows the cumulative amount of sludge retained in the experimental tank, based on the difference between the inflow sludge amount and the outflow sludge amount, in the anaerobic treatment experiment shown in FIG. The “carbon fiber centipede type” in the graph is a carbon fiber that is installed as a carrier member 220 without being wrapped around and fixed to the support 210, and the “string-like fiber material” is a polyester fiber material that is supported by the carrier member 220. As described above, it is installed without being wrapped around the support 210 and fixed. The “carbon fiber spiral type” is a carbon fiber as a carrier member and is installed in a state of being wound around and fixed to the support 210 in a spiral manner.

図4に例示するように「炭素繊維ムカデ型」および「炭素繊維螺旋タイプ」は「ひも状繊維材」と比較し非常に汚泥保持量が高くなっている。また経過日数が経ったところでは「炭素繊維螺旋タイプ」と「炭素繊維ムカデ型」の差が出始め、「炭素繊維螺旋タイプ」がより多くの汚泥を保持できると言うことができる。   As illustrated in FIG. 4, the “carbon fiber centipede type” and the “carbon fiber spiral type” have a very high sludge retention amount compared to the “string fiber material”. Further, when the elapsed days have passed, the difference between the “carbon fiber spiral type” and the “carbon fiber spiral type” begins to appear, and it can be said that the “carbon fiber spiral type” can hold more sludge.

以上説明したグラフから、水処理部材120は、効率的に汚泥を保持し、かつ分解・浄化していることが分かる。   From the graph demonstrated above, it turns out that the water treatment member 120 hold | maintains sludge efficiently, and decomposes | disassembles and purifies.

[変形例1]
図5は、浄化槽2の全体構成を模式的に表す図である。
図5に例示するように、浄化槽2は、分離腐敗槽12と、可溶化槽20と、嫌気濾床槽32と、接触曝気槽40と、処理水槽50と、消毒槽60とを有する。なお、本図に示される各構成のうち、図1に示された各構成と実質的に同一のものには同一の符号が付されている。
以下、本図に示される各構成のうち、図1に示された構成と異なるものについて説明する。
[Modification 1]
FIG. 5 is a diagram schematically illustrating the entire configuration of the septic tank 2.
As illustrated in FIG. 5, the septic tank 2 includes a separation septic tank 12, a solubilization tank 20, an anaerobic filter bed tank 32, a contact aeration tank 40, a treated water tank 50, and a disinfection tank 60. Note that, among the components shown in this figure, the same reference numerals are given to the components substantially the same as those shown in FIG.
In the following, the components different from those shown in FIG. 1 will be described among the components shown in FIG.

分離腐敗槽12は、生活雑排水又はし尿などの汚水がまず最初に流入される場所である。流入した汚水は、分離腐敗槽12において汚泥物質を沈澱させる。沈澱した汚泥物質は、嫌気性の微生物により、分解・浄化される。そして、汚泥物質を沈澱させた汚水の上澄みが、嫌気濾床槽32へと送られる。   The separation septic tank 12 is a place where sewage such as domestic wastewater or human waste is first introduced. The inflowing sewage precipitates sludge in the separation septic tank 12. The precipitated sludge material is decomposed and purified by anaerobic microorganisms. Then, the supernatant of the sewage in which the sludge substance is precipitated is sent to the anaerobic filter bed tank 32.

嫌気濾床槽32は、固形材110を設けられている。嫌気濾床槽32に送られた汚水は、上から下へと流れ、途中にある固形材110に、この汚水中に含まれる汚泥物質を付着させる。固形材110は、表面に形成された嫌気性の微生物膜により、付着した汚泥物質を分解・浄化する。そして、汚泥物質を分解・浄化された汚水は、次に接触曝気槽40へと送られる。また、固形材110に付着せず、嫌気濾床槽32の底部に溜まった汚泥物質は、エアリフトポンプにより吸い上げられて、可溶化槽20へと送られる。   The anaerobic filter bed tank 32 is provided with a solid material 110. The sewage sent to the anaerobic filter bed 32 flows from the top to the bottom, and the sludge substance contained in the sewage is attached to the solid material 110 in the middle. The solid material 110 decomposes and purifies the attached sludge substance by an anaerobic microbial film formed on the surface. Then, the sewage obtained by decomposing and purifying the sludge substance is then sent to the contact aeration tank 40. In addition, the sludge substance that does not adhere to the solid material 110 and accumulates at the bottom of the anaerobic filter bed tank 32 is sucked up by the air lift pump and sent to the solubilization tank 20.

以上説明したような浄化槽2に、上記実施例に係る水処理部材120が設けられてもよい。   The water treatment member 120 according to the above embodiment may be provided in the septic tank 2 as described above.

[変形例2]
図6は、浄化槽3の全体構成を模式的に表す図である。
図6に例示するように、浄化槽3は、嫌気濾床槽第1室14と、嫌気濾床槽第2室34と、接触曝気槽40と、処理水槽50と、消毒槽60とを有する。なお、本図に示される各構成のうち、図1に示された各構成と実質的に同一のものには同一の符号が付されている。
以下、本図に示される各構成のうち、図1に示された構成と異なるものについて説明する。
[Modification 2]
FIG. 6 is a diagram schematically illustrating the entire configuration of the septic tank 3.
As illustrated in FIG. 6, the septic tank 3 includes an anaerobic filter bed tank first chamber 14, an anaerobic filter bed tank second chamber 34, a contact aeration tank 40, a treated water tank 50, and a disinfection tank 60. Note that, among the components shown in this figure, the same reference numerals are given to the components substantially the same as those shown in FIG.
In the following, the components different from those shown in FIG. 1 will be described among the components shown in FIG.

嫌気濾床槽第1室14は、生活雑排水又はし尿などの汚水がまず最初に流入される場所であり、水処理部材120を設けられている。嫌気濾床槽第1室14に流入した汚水は、嫌気濾床槽第1室14において、下から上へと流れ、途中にある水処理部材120に、この汚水中に含まれる汚泥物質を付着させる。水処理部材120は、表面に形成された嫌気性の微生物膜により、付着した汚泥物質を分解・浄化する。そして、汚泥物質を分解・浄化された汚水は、次に嫌気濾床槽第2室34へと送られる。   The anaerobic filter bed first chamber 14 is a place where sewage such as daily wastewater or human waste is first introduced, and is provided with a water treatment member 120. The sewage that has flowed into the first chamber 14 of the anaerobic filter bed flows from the bottom to the top in the first chamber 14 of the anaerobic filter bed, and the sludge contained in the sewage adheres to the water treatment member 120 in the middle. Let The water treatment member 120 decomposes and purifies the attached sludge substance by an anaerobic microbial film formed on the surface. Then, the sewage obtained by decomposing and purifying the sludge substance is then sent to the anaerobic filter bed tank second chamber 34.

嫌気濾床槽第2室34は、水処理部材120を設けられている。嫌気濾床槽第2室34に流入した汚水は、嫌気濾床槽第2室34において、下から上へと流れ、途中にある水処理部材120に、この汚水中に含まれる汚泥物質を付着させる。水処理部材120は、表面に形成された嫌気性の微生物膜により、付着した汚泥物質を分解・浄化する。そして、汚泥物質を分解・浄化された汚水は、次に接触曝気槽40へと送られる。また、水処理部材120に付着せず、嫌気濾床槽第2室34の底部に溜まった汚泥物質は、エアリフトポンプにより吸い上げられて、嫌気濾床槽第1室14へと送られる。   The anaerobic filter bed second chamber 34 is provided with a water treatment member 120. The sewage that has flowed into the second chamber 34 of the anaerobic filter bed flows from the bottom to the top in the second chamber 34 of the anaerobic filter bed, and the sludge contained in the sewage adheres to the water treatment member 120 in the middle. Let The water treatment member 120 decomposes and purifies the attached sludge substance by an anaerobic microbial film formed on the surface. Then, the sewage obtained by decomposing and purifying the sludge substance is then sent to the contact aeration tank 40. The sludge substance that does not adhere to the water treatment member 120 and accumulates at the bottom of the anaerobic filter bed tank second chamber 34 is sucked up by the air lift pump and sent to the anaerobic filter bed tank first chamber 14.

以上説明したような浄化槽3に、上記実施例に係る水処理部材120が設けられてもよい。   The water treatment member 120 according to the above embodiment may be provided in the septic tank 3 as described above.

[変形例3]
図7は、水処理部材122の全体構成を模式的に表す図である。
図7に例示するように、水処理部材122は、繊維状担体320が基幹材310の片側一方向
にのみ略直交する状態で固定された担体部材222を有する。このように繊維状担体320を基幹材310に固定することにより、繊維状担体320は、図2に例示した水処理部材120の繊維状担体320に比べ、平均して、より下方を向くことになる。これにより、水処理部材122は、槽内水排出時に鉛直下方にかかる荷重をさらに軽減させることができる。
[Modification 3]
FIG. 7 is a diagram schematically illustrating the entire configuration of the water treatment member 122.
As illustrated in FIG. 7, the water treatment member 122 includes a carrier member 222 that is fixed in a state in which the fibrous carrier 320 is substantially orthogonal to only one direction on one side of the base material 310. By fixing the fibrous carrier 320 to the base material 310 in this way, the fibrous carrier 320 is on the lower side on average, compared to the fibrous carrier 320 of the water treatment member 120 illustrated in FIG. Become. Thereby, the water treatment member 122 can further reduce the load applied vertically downward when the water in the tank is discharged.

図8は、水処理部材124の全体構成を模式的に表す図である。
図8に例示するように、水処理部材124は、支持体210と、担体部材224とを有する。本実施例では、水処理部材124は、さらに固定材240を有する。なお、本図に示される各構成のうち、図2に示された各構成と実質的に同一のものには同一の符号が付されている。
以下、本図に示される各構成のうち、図2に示された構成と異なるものについて説明する。
FIG. 8 is a diagram schematically illustrating the overall configuration of the water treatment member 124.
As illustrated in FIG. 8, the water treatment member 124 includes a support body 210 and a carrier member 224. In the present embodiment, the water treatment member 124 further includes a fixing member 240. It should be noted that among the components shown in this figure, those substantially the same as those shown in FIG.
In the following, the configuration different from the configuration shown in FIG. 2 will be described among the configurations shown in FIG.

担体部材224は、図9に例示するように、紐状又は帯状に形成された基幹材310に、実施例1における繊維状担体320を束状にしたもの(繊維束322)を複数固定したものである。繊維束322を基幹材310に固定する手段は、特に限定するものではない。例えば、繊維束322は、接着又は溶着などにより基幹材310に接合されてもよいし、又は繊維束322と基幹部材310とが一体的に形成されてもよい。また、繊維束322を基幹材310に固定したときの、繊維束322の基幹部材310の軸線方向に対する傾きは、特に限定するものではない。
本実施例では、繊維束320は、基幹部材310に略直交する状態で固定されている。また、繊維束322は、可撓性を有しており、重力により下方に撓る。これにより、担体部材224は、槽内水排出時に鉛直下方にかかる荷重を軽減させることができる。さらに、担体部材224は、繊維束322を固定することにより、図2に例示した水処理部材120に比べ、表面積を増大させ、より多量の汚泥物質を保持することができる。
As illustrated in FIG. 9, the carrier member 224 is obtained by fixing a plurality of bundles (fiber bundles 322) of the fibrous carriers 320 in Example 1 to the base material 310 formed in a string shape or a band shape. It is. The means for fixing the fiber bundle 322 to the base material 310 is not particularly limited. For example, the fiber bundle 322 may be joined to the base material 310 by adhesion or welding, or the fiber bundle 322 and the base member 310 may be integrally formed. In addition, the inclination of the fiber bundle 322 with respect to the axial direction of the base member 310 when the fiber bundle 322 is fixed to the base material 310 is not particularly limited.
In this embodiment, the fiber bundle 320 is fixed in a state substantially orthogonal to the basic member 310. Further, the fiber bundle 322 has flexibility and bends downward due to gravity. Thereby, the carrier member 224 can reduce the load applied vertically downward when the water in the tank is discharged. Furthermore, the carrier member 224 can increase the surface area and retain a larger amount of sludge substance by fixing the fiber bundle 322 as compared with the water treatment member 120 illustrated in FIG.

図10は、水処理装置400の全体構成を模式的に表す図である。
図10に例示するように、水処理装置400は、給水管410と、水処理部材124と、排水管412とを有する。給水管410から流入した液体(原水)は、水処理装置400において下から上へと水処理部材124の間を流れる。このとき、水処理部材124は、微生物を表面に担持し、この担持している微生物の働きにより、液体を処理する。このように処理された液体は、排水管412により、外部に流出される。また、液体を処理する過程で放出されたガスは、水処理装置400の上部から収集される。
なお、水処理装置400は、微生物を用いて液体を処理するものであれば何でもよい。従って、浄化槽は、水処理装置400の一例である。
FIG. 10 is a diagram schematically illustrating the overall configuration of the water treatment apparatus 400.
As illustrated in FIG. 10, the water treatment apparatus 400 includes a water supply pipe 410, a water treatment member 124, and a drain pipe 412. The liquid (raw water) flowing in from the water supply pipe 410 flows between the water treatment members 124 from the bottom to the top in the water treatment apparatus 400. At this time, the water treatment member 124 carries the microorganisms on the surface and treats the liquid by the action of the carried microorganisms. The liquid thus treated is discharged to the outside through the drain pipe 412. Further, the gas released in the process of processing the liquid is collected from the upper part of the water treatment device 400.
The water treatment apparatus 400 may be anything as long as it can process a liquid using microorganisms. Therefore, the septic tank is an example of the water treatment device 400.

以上説明したように、本実施例に係る水処理部材124は、水処理装置400に設けられ、液体を処理する。   As described above, the water treatment member 124 according to the present embodiment is provided in the water treatment apparatus 400 and treats a liquid.

その他の変形例を説明する。
上記実施形態では、支持体210に担体部材220を巻きつける形態を説明したが、これに限定されるものではなく、例えば、支持体210の表面に対して斜め方向に繊維状担体320を埋め込むようにしてもよいし、支持体210と繊維状担体320とを一体的に成型した後で、支持体210をねじってもよいし、長細い袋の表面に繊維状担体を接着又は縫着し、この袋を支持体210に被せるようにしてもよい。
Other modifications will be described.
In the above embodiment, the mode in which the carrier member 220 is wound around the support 210 has been described. However, the present invention is not limited to this. For example, the fibrous carrier 320 is embedded obliquely with respect to the surface of the support 210. Alternatively, after integrally forming the support 210 and the fibrous carrier 320, the support 210 may be twisted, or the fibrous carrier may be bonded or sewn to the surface of a long thin bag, You may make it cover this support body 210 with this bag.

1 浄化槽
2 浄化槽(変形例1)
3 浄化槽(変形例2)
10 嫌気濾床槽第1室
12 分解腐敗槽
14 嫌気濾床槽第1室(変形例2)
20 可溶化槽
30 嫌気濾床槽第2室
32 嫌気濾床槽(変形例1)
34 嫌気濾床槽第2室(変形例2)
40 接触曝気槽
50 処理水槽
60 消毒槽
110 固形材
115 固形材
120 水処理部材
122 水処理部材(変形例3)
124 水処理部材(実施例2)
130 接触材
135 生物ろ過部
140 散気装置
145 逆洗用散気装置
210 支持体
220 担体部材
222 担体部材(変形例3)
224 担体部材(実施例2)
230 緊締部材
240 固定部材
310 基幹材
320 繊維状担体
322 繊維束
400 水処理装置
410 給水管
412 排水管
1 Septic Tank 2 Septic Tank (Modification 1)
3 Septic tank (Modification 2)
10 Anaerobic filter bed 1st chamber 12 Decomposition septic tank 14 Anaerobic filter bed 1st chamber (Modification 2)
20 Solubilization tank 30 Anaerobic filter bed 2nd chamber 32 Anaerobic filter bed (Modification 1)
34 Anaerobic filter bed second chamber (Modification 2)
40 Contact aeration tank 50 Treated water tank 60 Disinfection tank 110 Solid material 115 Solid material 120 Water treatment member 122 Water treatment member (Modification 3)
124 Water treatment member (Example 2)
DESCRIPTION OF SYMBOLS 130 Contact material 135 Biological filtration part 140 Air diffuser 145 Air diffuser for backwash 210 Support body 220 Carrier member 222 Carrier member (modification 3)
224 Carrier member (Example 2)
230 Tightening member 240 Fixing member 310 Base material 320 Fibrous carrier 322 Fiber bundle 400 Water treatment device 410 Water supply pipe 412 Drainage pipe

Claims (3)

処理水の水流方向に平行に配置された、棒状の支持体と、
炭素繊維からなる繊維部材と、
紐状又は帯状の可撓性部材と
を有し、
複数の前記繊維部材は、前記繊維部材の長軸方向が前記可撓性部材の長軸方向に対して略直交するように、前記可撓性部材に配列されており、
前記可撓性部材が前記支持体の周囲に螺旋状に巻きつけられて、前記繊維部材が前記支持体から斜め方向に張り出してなる水処理部材。
A rod-like support disposed in parallel with the direction of the treated water flow ;
A fiber member made of carbon fiber ;
A string-like or belt-like flexible member;
Have
The plurality of fiber members are arranged in the flexible member such that the long axis direction of the fiber member is substantially orthogonal to the long axis direction of the flexible member,
A water treatment member in which the flexible member is spirally wound around the support and the fiber member protrudes obliquely from the support .
水処理部材と、
嫌気性処理槽と
を有し、
前記水処理部材は、
棒状の支持体と、
炭素繊維からなる繊維部材と、
紐状又は帯状の可撓性部材と
を含み、
複数の前記繊維部材は、前記繊維部材の長軸方向が前記可撓性部材の長軸方向に対して略直交するように、前記可撓性部材に配列されており、
前記可撓性部材が前記支持体の周囲に螺旋状に巻きつけられて、前記繊維部材が前記支持体から斜め方向に張り出しており、
前記嫌気性処理槽は、前記支持体の長軸方向が処理水の流れる方向となるように形成されている
浄化槽。
A water treatment member;
Anaerobic treatment tank and
Have
The water treatment member is
A rod-shaped support;
A fiber member made of carbon fiber;
A string-like or belt-like flexible member;
Including
The plurality of fiber members are arranged in the flexible member such that the long axis direction of the fiber member is substantially orthogonal to the long axis direction of the flexible member,
The flexible member is spirally wound around the support, and the fiber member protrudes obliquely from the support;
The anaerobic treatment tank is a purification tank formed such that the major axis direction of the support is the direction in which treated water flows .
炭素繊維からなる繊維部材が複数配列された紐状又は帯状の可撓性部材を、棒状の支持体の表面に螺旋状に巻き付け、
前記支持体の長軸方向が処理水の流れる方向となるように、前記可撓性部材が巻き付けられた支持体を、嫌気性処理槽内に設置する
水処理方法。
A string-like or belt-like flexible member in which a plurality of fiber members made of carbon fiber are arranged is spirally wound around the surface of a rod-like support,
A water treatment method in which the support on which the flexible member is wound is installed in an anaerobic treatment tank so that the major axis direction of the support is a direction in which treated water flows .
JP2010011598A 2010-01-22 2010-01-22 Water treatment member, septic tank, and water treatment device Expired - Fee Related JP5380688B2 (en)

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