JP4586147B2 - Water purification equipment - Google Patents

Water purification equipment Download PDF

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JP4586147B2
JP4586147B2 JP2007105517A JP2007105517A JP4586147B2 JP 4586147 B2 JP4586147 B2 JP 4586147B2 JP 2007105517 A JP2007105517 A JP 2007105517A JP 2007105517 A JP2007105517 A JP 2007105517A JP 4586147 B2 JP4586147 B2 JP 4586147B2
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water purification
backwashing
filter medium
purification apparatus
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JP2008100210A (en
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康夫 藤野
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桜井 信一
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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

Description

本発明は、河川や湖沼等から吸引した被処理水を濾過して濾物を生物処理することにより浄水する浄水処理装置に関する。 The present invention relates to a water purification apparatus that purifies water by filtering water to be treated sucked from rivers, lakes, and the like and biologically treating the filtrate.

市街地を流れる河川や湖沼等には、水の流れが停滞している場所がある。そこに市街地からの生活排水が流入することにより富栄養化が進み、アオコ等の藻類やヘドロ等の汚泥物質が蓄積され、更には悪臭が発生し、大きな環境問題となっている。この対策として、バクテリアの投入や水生植物の育成、貝の放流等が行われているが、顕著な効果は得られていない。   There are places where the flow of water is stagnant in rivers and lakes flowing through urban areas. Due to the inflow of domestic wastewater from the city area, eutrophication has progressed, and algae such as blue sea urchins and sludge substances such as sludge accumulate, and further foul odor is generated, which is a major environmental problem. As countermeasures, bacteria have been introduced, aquatic plants have been bred, shellfish have been released, etc., but no significant effect has been obtained.

かかる状況に鑑み、近年は、河川や湖沼等の水を生物処理して濾過することにより浄水する浄水処理装置が開発されている。例えば、下記特許文献1と2には、水中曝気ポンプにより揚水した揚水中に気泡化させた大気を混合させ、噴出落下させて波立作用を行う閉塞性水域の浄化装置が開示されている。この浄化装置は、いわゆる噴水装置であり噴水の際に大気を取り込むことで、閉塞性水域の溶存酸素量を増加させるものである。また、この浄化装置には、アクリル長繊維の濾過材が備わっている。下記特許文献3には、夾雑物除去漕と嫌気濾床槽と生物濾過槽とを備え、合成樹脂性中空濾過材を用いて、該濾過材の目詰まり防止のために、濾過材を曝気して付着した汚泥や余剰な微生物を取り除く逆洗が行われており、逆洗後の逆洗水には濾過材から剥離した汚泥や微生物が含まれるが、この逆洗水は浄水処理装置内の各槽を循環させることで浄水されるようになっている。
特許第2814349号公報 特開2003−340489号公報 特開2003−279536号公報
In view of such a situation, in recent years, a water purification apparatus for purifying water such as rivers and lakes by biological treatment and filtration has been developed. For example, Patent Documents 1 and 2 below disclose a purification device for an obstructive water area in which air bubbled is mixed in pumped water pumped by a submerged aeration pump and ejected and dropped to perform a ripple action. This purification device is a so-called fountain device, and increases the amount of dissolved oxygen in the obstructive water area by taking in the air during the fountain. Moreover, this purification apparatus is equipped with a filter material made of acrylic long fibers. The following Patent Document 3 is provided with a foreign substance removal tank, an anaerobic filter bed tank, and a biological filtration tank, and a synthetic resinous hollow filter medium is used to aerate the filter medium to prevent clogging of the filter medium. Backwash to remove sludge and excess microorganisms is performed, and the backwash water after backwash contains sludge and microorganisms that have peeled off the filter medium. Water is purified by circulating each tank.
Japanese Patent No. 2814349 Japanese Patent Laid-Open No. 2003-340489 JP 2003-279536 A

しかしながら、河川や湖沼等の水には有害物質や有害微生物を含んでいる場合があり、上記特許文献1と2記載の浄化装置では、例えばレジオネラ菌等の有害な雑菌が噴水にて、空中飛散されてしまい、付近の住民への健康に悪影響を及ぼすという問題がある。また、アクリル長繊維の濾過材は目詰まりしやすく、浄化装置の濾過材を頻繁に交換するなど浄化装置の品質維持に多大な労力を要する。上記特許文献3の浄化装置は、河川や湖沼等の水を浄水処理装置まで引いて浄水処理するため、設備が大掛かりとなり現実的でない。   However, water such as rivers and lakes may contain harmful substances and harmful microorganisms. In the purification devices described in Patent Documents 1 and 2, harmful germs such as Legionella bacteria are scattered in the fountain. This has the problem of adversely affecting the health of nearby residents. Moreover, the filter material of an acrylic long fiber is easy to be clogged, and much effort is required to maintain the quality of the purification device, such as frequently replacing the filtration material of the purification device. Since the purification device of Patent Document 3 draws water from a river or a lake to a water purification device and performs the water purification treatment, the equipment becomes large and is not realistic.

そこで本発明の目的は河川や湖沼等において従来よりも安全でかつ目詰まりせずに継続して高い浄水効果が得られる浄水処理装置を提案することにある。 Therefore, an object of the present invention is to propose a water purification apparatus that is safer than that in conventional rivers, lakes , and the like and that can continuously obtain a high water purification effect without clogging.

本発明の浄水処理装置は、河川や湖沼等の原水域に配された浄水槽から被処理水を吸引する吸引手段と、前記吸引手段により吸引した被処理水を濾過するとともに濾過材に保持された好気性生物により濾物を生物処理する濾過手段と、前記濾過手段により濾過された被処理水を排出する排出手段と、前記濾過材収納空間に配されて大気を取り込んで前記濾過手段の濾過材を逆洗する逆洗手段とを備え、前記濾過手段と排手段とが円筒形状の浄水槽に収納されており、前記排出手段は、前記濾過手段により濾過された被処理水の流路となる排水管が円筒形状の浄水槽の水平断面において放射線状に配置されており、前記原水域の被処理水が、前記浄水槽の側面に設けられた小孔から流入し、前記濾過手段で濾過された後に、収納容器の孔を通って収納容器内に流入し、収納容器内に設けられた吸引ポンプによって吸引されて、排水管によって原水域の水中に排出される構成とされ、前記逆洗手段による逆洗により前記濾過材から前記好気性生物を剥離させるとともに取り込んだ大気により前記好気性生物に酸素を与えて前記原水域に排出することを特徴とする。 The water purification apparatus of the present invention includes a suction means for sucking water to be treated from a water purification tank disposed in a raw water area such as a river or a lake, and the water to be treated sucked by the suction means is filtered and held by a filter medium. Filtration means for biologically treating the filtrate with aerobic organisms, discharge means for discharging the water to be treated filtered by the filtration means, and filtration of the filtration means arranged in the filter medium storage space to take in air and a backwashing means for backwashing the timber, the filtering means and has a discharge detecting means is housed in the water purification tank of cylindrical shape, said discharge means, the flow path of the treated water filtered by the filtering means The drainage pipes are arranged radially in a horizontal cross section of the cylindrical water purification tank, and the treated water in the raw water area flows from a small hole provided on the side surface of the water purification tank, and is filtered by the filtering means. After filtration, it passes through the hole in the storage container. Flows into the storage container Te is sucked by the suction pump provided on the receiving container, is configured to be discharged into the water of the original water by drainage pipe, said from the filtration material by backwashing by said backwashing means The aerobic organisms are exfoliated and oxygen is given to the aerobic organisms by the taken-in air and discharged into the raw water area.

この発明によれば、吸引手段により河川や湖沼等の原水域から吸引された被処理水は濾過手段により濾過された後に排手段により排水され、濾物は濾過材に保持される生物により生物処理される。逆洗時には、濾過材から生物が剥離されて河川や湖沼等の原水域に排出される。これにより、浄水処理装置内では濾過手段による浄水処理が行われ、浄水処理装置外では逆洗により排出された生物による生物処理が行われ、浄水処理装置内外の処理が相俟って高い浄水効果が得られる。更に、原水域中に沈殿している汚泥等は、逆洗により原水域に排出された生物によって生物処理され、粘着力が衰えて水中に浮遊する。浮遊した汚泥等は吸引手段により浄水処理装置に吸引されやすく、浄水効率が高まる。吸引された汚泥等は浄水処理装置内の生物の餌となって増殖を促進させ、その結果、逆洗により排出される生物も増加し、この一連のサイクルにより浄水処理装置内外で非常に高い浄水効果が得られる。ここで、生物は細菌・原生動物・藻類などの微生物(バクテリア)であることが好ましい。 According to the present invention, the water to be treated is sucked from the original body of water such as rivers and lakes by the suction means is drained by the discharge detection means after being filtered by the filtering means, filtrate organisms by organisms to be held in the filtering material It is processed. At the time of backwashing, organisms are peeled off from the filter medium and discharged into raw water areas such as rivers and lakes. As a result, the water purification treatment by the filtering means is performed inside the water purification treatment apparatus, the biological treatment by the organisms discharged by backwashing is carried out outside the water purification treatment apparatus, and the high water purification effect combined with the treatment inside and outside the water purification treatment apparatus Is obtained. Furthermore, sludge and the like precipitated in the raw water area are biologically treated by the organisms discharged into the raw water area by backwashing, and the adhesive force is weakened and floats in the water. The suspended sludge and the like are easily sucked into the water purification apparatus by the suction means, and the water purification efficiency is increased. The sucked sludge, etc. becomes the food for the organism in the water treatment system and promotes its growth. As a result, the number of organisms discharged by backwashing also increases, and this series of cycles results in extremely high purified water inside and outside the water treatment system. An effect is obtained. Here, the organism is preferably a microorganism such as a bacterium, protozoan, or algae.

本発明の浄水処理装置は、前記濾過手段と排手段は円筒形状の浄水槽に収納されており、前記排出手段は、前記濾過手段により濾過された被処理水の流路となる排水管が円筒形状の浄水槽の水平断面において放射線状に配置されていることを特徴とする。この発明によれば、排手段の排水管は円筒形状の浄水槽の水平断面において放射線状に配置されているため、水中において浄水処理装置の姿勢を安定させることができる。被処理水は放射線状に排出されるため、被処理水の排出によってもバランスが崩されることはなく、安定姿勢が維持される。浄水処理装置は、上部に円形状の浮き(フロート部)が取り付けられ、河川や湖沼等の原水域に配置されて浮かばせて使用することが好ましい。河川や湖沼等の原水域では、水底がぬかるんでいるが、当該浄水処理装置を浮かばせて使用することで、水底の状態によらず、当該浄水処理装置を水平に保つことができる。また、当該浄水処理装置を浮かばせることで、目的の場所に移動させやすい。 Water treatment apparatus of the present invention, the filtering means and emissions means is housed in the water purification tank of cylindrical shape, said discharge means, drainage tube to be a flow path of the treated water filtered by the filtering means It arrange | positions radially at the horizontal cross section of a cylindrical water purification tank, It is characterized by the above-mentioned. According to the invention, the drainage pipe emissions means because it is located radially in a horizontal cross section of the purified water tank cylindrical, it is possible to stabilize the attitude of the water treatment device in water. Since the water to be treated is discharged radially, the balance is not lost by the discharge of the water to be treated, and a stable posture is maintained. It is preferable that the water purification apparatus has a circular float (float part) attached to the upper part and is placed and floated in a raw water area such as a river or a lake. In raw water areas such as rivers and lakes, the bottom of the water is muddy. By floating and using the water purification apparatus, the water purification apparatus can be kept horizontal regardless of the state of the water bottom. Moreover, it is easy to move to the target place by making the said water purification apparatus float.

前記生物は好気性生物であり、前記逆洗手段は大気を取り込んで前記濾過材を逆洗することが好ましい。大気は通常の空気であれば足りるが、好気性生物の生息や増殖に適するように調整された調整ガスでもよい。この発明によれば、濾過材に保持される生物は好気性生物であり、逆洗手段により大気が排出されるため、逆洗により濾過材の目詰まりを防止すると同時に浄水処理装置内の溶存酸素を増加させて生物の生息環境を整えることができる。浄水処理装置外にも酸素が供給され、原水域中での生物処理も促進される。   Preferably, the organism is an aerobic organism, and the backwashing means takes in air and backwashes the filter medium. As long as the air is normal air, it is sufficient to use a conditioned gas adjusted to suit the habitat and growth of aerobic organisms. According to the present invention, the organism held in the filter medium is an aerobic organism, and the air is discharged by the backwashing means, so that the filter medium is prevented from being clogged by backwashing and at the same time dissolved oxygen in the water purification apparatus The living habitat of living things can be adjusted by increasing Oxygen is also supplied outside the water purification system, facilitating biological treatment in the raw water area.

前記濾過材は、表面にひだを有する粒状体であることが好ましい。この発明によれば、濾過材が互いに接触しても、ひだの間に保持された生物は濾過手段から剥離することがなく、生物が安定して保持され、ひだの間にて生物の増殖が促進される。逆洗時には逆洗のために排出される空気等がひだに沿って流れるため、増殖した生物を濾過材から効率よく剥離・排出させることができる。排出した後はひだの間にて生物の増殖が促進されて、浄水処理装置内での生物処理能力が早急に回復し、このサイクルにより高い浄水効果を得ることができる。   The filter medium is preferably a granular body having pleats on the surface. According to the present invention, even if the filter media come into contact with each other, the organisms held between the folds do not peel off from the filtering means, the organisms are stably held, and the organisms grow between the folds. Promoted. At the time of backwashing, air or the like discharged for backwashing flows along the pleats, so that the grown organism can be efficiently peeled and discharged from the filter medium. After discharging, the growth of organisms is promoted between the pleats, and the biological treatment capacity in the water purification apparatus is quickly restored, and a high water purification effect can be obtained by this cycle.

この発明によれば、原水域から吸引した被処理水を濾過手段により濾過して排出するとともに、濾過材に保持される生物により濾物を生物処理する一連の処理の間の所定のタイミングで濾過手段を逆洗する。逆洗に際しては、濾過材から生物を剥離させ、原水域に排出する。これにより、浄水処理装置内では濾過手段により浄水処理が行われ、浄水処理装置外では逆洗時に排出された生物によって浄水処理が行われ、高い浄水効果が得られる。さらに、原水域の汚泥等は排出された生物の生物処理により粘着力が衰えて浮遊し、浄水処理装置に吸引されやすくなり、浄水効率が高められる。   According to the present invention, the water to be treated sucked from the raw water area is filtered and discharged by the filtering means, and is filtered at a predetermined timing between a series of treatments in which the filtrate is biologically treated by the organisms held by the filter medium. Backwash means. At the time of backwashing, organisms are peeled off from the filter medium and discharged into the raw water area. Thereby, the water purification process is performed by the filtering means in the water purification apparatus, and the water purification process is performed by the organism discharged at the time of backwashing outside the water purification apparatus, thereby obtaining a high water purification effect. Furthermore, the sludge and the like in the raw water area will float due to the loss of adhesive strength due to the biological treatment of the discharged organisms, and will be easily sucked into the water purification apparatus, thereby improving the water purification efficiency.

本発明の浄水処理装置によれば、浄水処理装置内で濾過手段による浄水処理が行われ、浄水処理装置外では排出された生物(バクテリア)により汚泥等が生物処理され、浄水処理装置内外の処理が相俟って高い浄水効果が得られる。さらに、排出された生物の生物処理により原水域に付着する汚泥等は粘着力が弱まって浮遊し、浄水処理装置に吸引されやすくなり、高い浄水効率が得られる。吸引した汚泥等により浄水処理装置内の生物が増殖し、増殖した生物は逆洗により原水域に排出されて生物処理に供され、このサイクルにより河川や沼等の原水域において非常に高い浄水効果が得られる。つまり、本発明は、単なる浄水処理装置に留まらず、生物(バクテリア)の培養装置を兼ねており、いわば自然界の貝と同様の働きをすることで、従来よりも安全でかつ目詰まりせずに継続して高い浄水効果が得られる。 According to the water purification apparatus of the present invention, water purification treatment is performed by filtration means in the water purification apparatus, and sludge and the like are biologically treated by discharged organisms (bacteria) outside the water purification apparatus, and treatment inside and outside the water purification apparatus. High water purification effect is obtained in combination. Furthermore, sludge and the like adhering to the raw water area due to the biological treatment of the discharged organisms will float with weak adhesive force, and will be easily sucked into the water purification apparatus, resulting in high water purification efficiency. Living organisms in the water treatment system grow by the sludge sucked, and the grown organisms are discharged into the raw water area by backwashing and used for biological treatment. Is obtained. In other words, the present invention is not limited to a simple water treatment device, but also serves as a living organism (bacteria) culture device, so to speak, it functions in the same way as a natural shellfish, and is safer and less clogged than before. High water purification effect can be obtained continuously.

以下、本発明に係る浄水処理装置Sについて詳細に説明する。図1は、浄水処理装置Sの内部構造を示す正面図であり、図2はその上面図であり、図3はその斜視図である。浄水処理装置Sは、河川や湖沼等の原水域の水を浄水する浄水処理装置である。この浄水処理装置Sは、原水域にて水中に一部又は全体が沈められるように使用されるものであり、浄水処理を行う浄水部Cと、浄水部Cの上方に配置されて浄水処理装置Sに浮力を与えるフロート部Fを備える。   Hereinafter, the water purification apparatus S according to the present invention will be described in detail. FIG. 1 is a front view showing an internal structure of the water purification apparatus S, FIG. 2 is a top view thereof, and FIG. 3 is a perspective view thereof. The water purification apparatus S is a water purification apparatus that purifies water in raw water areas such as rivers and lakes. This water purification apparatus S is used so that a part or the whole is submerged in water in the original water area, and is disposed above the water purification section C and the water purification section C for water purification treatment. The float part F which gives buoyancy to S is provided.

浄水部Cは、吸引手段2、濾過手段3、排出手段4、逆洗手段5を備え、これらが浄水槽1に収納されている。   The water purification unit C includes a suction unit 2, a filtration unit 3, a discharge unit 4, and a backwash unit 5, which are stored in the water purification tank 1.

浄水槽1は、底部1aと側部1bとを備える円筒形状の容器であり、側部1bには複数の小孔1cが設けられている。   The water purification tank 1 is a cylindrical container provided with the bottom part 1a and the side part 1b, and the several small hole 1c is provided in the side part 1b.

吸引手段2は、原水域から被処理水を吸引する機能を備える。吸引手段2としては、浄水槽1内に収納して使用する観点から、水中でも稼動可能な水中ポンプPが好ましい。吸手段2は、複数の小孔6aが設けられた円筒形状の収納容器6内に収められて浄水槽1内に配置され、浄水槽1の小孔1cと収納容器6の小孔6aを介して原水域から被処理水を吸引可能となっている。吸手段2の配置ポジションは任意であるが、浄水槽1の底部1aの略中央付近として、浄水処理装置Sを水中に設置したときにバランスを維持することが好ましい。なお、水中ポンプPを用いない場合は、水の外にポンプ本体を配置し、ポンプと接続される配管の吸引口を浄水槽1内に設置して、被処理水を吸引するようにすることができる。 The suction means 2 has a function of sucking water to be treated from the raw water area. As the suction means 2, a submersible pump P that can be operated in water is preferable from the viewpoint of being housed in the water purification tank 1 and used. Aspirate unit 2 is housed in a plurality of small holes 6a is a container 6 of a cylindrical shape provided disposed purified water tank 1, a small hole 1c water purification tank 1 a small hole 6a of the container 6 The treated water can be sucked from the raw water area. Although placement position Aspirate means 2 is optional, as substantially near the center of the bottom 1a of the water purification tank 1, it is preferable to keep the balance when installed water treatment apparatus S in water. In addition, when not using the submersible pump P, arrange | position a pump main body out of water, install the suction port of the piping connected with a pump in the water-purifying tank 1, and suck in to-be-processed water. Can do.

濾過手段3は、吸引手段2により吸引した被処理水を濾過材3aにより濾過するとともに、濾過材に保持された生物により濾物を生物処理する機能を備える。本実施の形態では、濾過手段3は、浄水槽1内部、詳しくは浄水槽1と収納容器6との間隙によって形成される濾過材収納空間7に充填された粒状の複数の濾過材3a,,,3aにより構成されている。濾過材3aは被処理水を濾過可能な程度の密度で濾過材収納空間7に充填されており、被処理水が濾過材3aの間隙を通過することにより濾物が濾過されるようになっている。   The filtering unit 3 has a function of filtering the water to be treated sucked by the suction unit 2 with the filtering material 3a and biologically treating the filtered material with the organism held by the filtering material. In the present embodiment, the filtering means 3 includes a plurality of granular filter media 3 a, filled in a filter medium storage space 7 formed inside the water purification tank 1, specifically, a gap between the water purification tank 1 and the storage container 6. , 3a. The filter medium 3a is filled in the filter medium storage space 7 with a density sufficient to filter the water to be treated, and the filtered material is filtered by passing through the gap between the filter medium 3a. Yes.

粒状の濾過材3aは、生物を保持可能であれば、生物を担持可能な空孔を有する担体であっても良いし、生物を表面に吸着保持する吸着体であっても良い。また、濾過材3aの材料としては、材料密度が大きくて比表面積を大きくできるものであれば、合成樹脂、木炭、サンゴ砂等の何れでも良く、その形状は、円柱状、円筒状、球状、多孔質形状等の何れの形状でも良い。   The particulate filter medium 3a may be a carrier having pores capable of supporting living organisms or an adsorbent that adsorbs and holds living organisms on the surface as long as it can hold living organisms. The material of the filter medium 3a may be any of synthetic resin, charcoal, coral sand, etc. as long as the material density is large and the specific surface area can be increased. Any shape such as a porous shape may be used.

図4は、濾過材3aを示す図である。濾過材3aの形状として、好ましくは、保持する生物の定着性や剥離性を両立可能な観点から、粒状体の表面に褶曲したひだ3bを有する粒状体であることが好ましい。このひだ3bは合成樹脂からなる濾過材3aを螺旋状に形成することで形成されているので、頑丈でありながら比表面積を大きくすることができる。   FIG. 4 is a diagram showing the filter medium 3a. The shape of the filter medium 3a is preferably a granule having pleats 3b bent on the surface of the granule from the viewpoint of achieving both the fixability and the peelability of the organism to be held. Since the pleat 3b is formed by forming the filter medium 3a made of synthetic resin in a spiral shape, the specific surface area can be increased while being strong.

濾過材3aは、濾過手段3に吸引された被処理水が接触するように、浄水槽1の小孔1cと収納容器6の小孔6aの間、すなわち吸引された被処理水の流路途中に配される。   The filter medium 3a is disposed between the small hole 1c of the water purification tank 1 and the small hole 6a of the storage container 6, that is, in the middle of the flow path of the sucked water to be treated so that the water to be treated sucked into the filtering means 3 is in contact with it. Arranged.

濾過材3aには、原水に対して好適な浄水作用を発揮する生物が保持されている。この生物は、例えば、細菌・酵母・原生動物・菌類・藻類等の微生物であり、あらかじめ、浄水の対象となる原水が採取・分析され、原水に好適な生物処理を行う生物が適宜選択されている。生物は、浄水作用を有するものであればよく、後述する逆洗が通常の空気により行われる場合は好気性であることが好ましい。   The filter medium 3a holds a living organism that exhibits a water purification action suitable for raw water. This organism is, for example, a microorganism such as a bacterium, yeast, protozoan, fungus, or algae. The raw water that is the target of water purification is collected and analyzed in advance, and an organism that performs biological treatment suitable for the raw water is appropriately selected. Yes. The living body only needs to have a water purifying action, and is preferably aerobic when backwashing described below is performed with ordinary air.

排出手段4は、濾過手段3により濾過された被処理水を原水域に排出する機能を備える。排出手段4は、吸引手段2と共用の水中ポンプPと排水管4aを備える。排水管4aは、一端が水中ポンプPの排出側と接続され、他端が浄水槽1の外部に引き出され、被処理水を浄水処理装置S外に排出可能としている。排出手段4は、浄水処理装置Sが水中でも安定姿勢を保ち、又、被処理水を排水したときにもその姿勢を崩すことがないように配置され、バランス調整の機能も果たしている。その配置は浄水処理装置Sの構成に応じて適宜設計すれば良い。例えば、本実施の形態の浄水処理装置Sのように他の構成によってほぼ均衡がとれている場合、水中ポンプPは浄水槽1の底部1aの略中央付近に配置し、排水管4aは水中ポンプPから垂直に引き出し、途中で複数本に分岐させ、分岐先は水平断面において放射線状に配することが好ましい。本実施の形態では、排水管4aは二つに分岐しており、被処理水は二方向に排出されるようになっているが、分岐先を三本やそれ以上としても良い。   The discharging means 4 has a function of discharging the water to be treated filtered by the filtering means 3 to the raw water area. The discharge means 4 includes a submersible pump P and a drain pipe 4a shared with the suction means 2. One end of the drainage pipe 4a is connected to the discharge side of the submersible pump P, and the other end is drawn to the outside of the water purification tank 1 so that the water to be treated can be discharged out of the water purification apparatus S. The discharge means 4 is disposed so that the water purification apparatus S maintains a stable posture even in water, and the posture of the water treatment apparatus S is not destroyed even when the water to be treated is drained, and also functions as a balance adjustment. The arrangement may be appropriately designed according to the configuration of the water purification apparatus S. For example, when the water purification treatment apparatus S of the present embodiment is almost balanced by another configuration, the submersible pump P is disposed near the center of the bottom 1a of the water purification tank 1, and the drain pipe 4a is a submersible pump. It is preferable to pull out vertically from P, branch into a plurality of parts in the middle, and arrange the branch destinations radially in a horizontal section. In this embodiment, the drain pipe 4a is branched into two, and the water to be treated is discharged in two directions, but the number of branch destinations may be three or more.

逆洗手段5は、気体や液体を排出することにより濾過材3aを逆洗する機能を備える。本実施の形態の逆洗手段5は、気体を排出するものであり、エアポンプ5aと、エアポンプ5aの吸引側に接続される吸引側配管5bと、エアポンプ5aの排出側に接続される排出側配管5cとを備える。吸引側配管5bの吸引口は浄水槽1外に引き出され、排出側配管5cの排出口は濾過材収納空間7の任意の箇所に配置されている。エアポンプ5aを駆動すると、吸引側配管5bの吸引口から気体が吸引され、排出側配管5cの排出口から排出され、濾過材3aが曝気されて逆洗される。排出された気体は上方に向かうため、排出口は濾過材収納空間7の下方側に配することが好ましい。排出口を複数配置して濾過材3aを満遍なく逆洗するようにしても良い。   The backwashing means 5 has a function of backwashing the filter medium 3a by discharging gas or liquid. The backwashing means 5 of the present embodiment discharges gas, and includes an air pump 5a, a suction side pipe 5b connected to the suction side of the air pump 5a, and a discharge side pipe connected to the discharge side of the air pump 5a. 5c. The suction port of the suction side pipe 5 b is drawn out of the water purification tank 1, and the discharge port of the discharge side pipe 5 c is arranged at an arbitrary location in the filter medium storage space 7. When the air pump 5a is driven, gas is sucked from the suction port of the suction side pipe 5b, discharged from the discharge port of the discharge side pipe 5c, and the filter medium 3a is aerated and backwashed. Since the discharged gas is directed upward, the discharge port is preferably disposed on the lower side of the filter medium storage space 7. A plurality of outlets may be arranged to backwash the filter medium 3a evenly.

濾過材3aに保持される生物が好気性である場合は、逆洗手段5から排出される気体は通常の空気であることが好ましい。吸引側配管5bの吸引口を大気中に配置して大気を取り込んで用いる。大気は通常の空気であれば足りるが、生物に好適となるように調整された調整ガスを準備し、その調整ガスを入れたガスボンベに吸引口を接続して調整ガスを用いる構成でも良い。これにより、逆洗するとともに好気性生物に酸素を与えることができる。   When the organism held in the filter medium 3a is aerobic, the gas discharged from the backwashing means 5 is preferably normal air. The suction port of the suction side pipe 5b is arranged in the atmosphere and used by taking in the atmosphere. It is sufficient if the atmosphere is normal air, but a configuration may be used in which a regulation gas adjusted to be suitable for a living organism is prepared, and the suction gas is connected to a gas cylinder containing the regulation gas and the regulation gas is used. Thereby, oxygen can be given to an aerobic organism while backwashing.

これらの構成を備える浄水部Cの上側にはフロート部Fが設けられている。フロート部Fは、内側の空間に空気が溜められて浄水処理装置Sに浮力を与える機能を果たすとともに、浄水部Cのキャップの機能も果たす。このフロート部Fは、一方に開口する略半球状の枠体であり、浄水槽1の開口側に嵌合させて取り付けられている。フロート部Fは着脱自在であり、取り外すと浄水部C内部の修理や交換時を容易に行うことができ、取り付けると浄水部Cの上方開口を塞ぐとともに内側の空間の大気により浄水処理装置Sに浮力を与えることができる。   A float part F is provided on the upper side of the water purification part C having these configurations. The float part F functions as a cap of the water purification unit C while air is stored in the inner space to provide buoyancy to the water purification apparatus S. This float part F is a substantially hemispherical frame that opens on one side, and is fitted and attached to the opening side of the water purification tank 1. The float part F is detachable, and when it is removed, it can be easily repaired or replaced inside the water purification part C. When attached, the upper part of the water purification part C is closed and the atmosphere in the inner space allows the water purification treatment apparatus S to close. Can give buoyancy.

(使用態様)
この浄水処理装置Sは、次のように使用される。図5は、浄水処理装置Sの使用態様を説明する説明図である。浄水処理装置Sは、河川や湖沼等の原水域において水中に浮かべて使用される。浄水処理装置Sを原水域に投入すると、浄水処理装置Sは、フロート部Fの浮力により、水面Wより下に浄水部Cが位置する程度の水深で浮かんだ状態となり、水底Kより上に浮かぶ。浄水処理装置S全体が水中に沈むようにしても良く、水底K近くまで沈めても良く、どの程度の水深に位置させるかは、原水域の状況に応じて調整すれば良い。水面W付近に浮かべて水深の浅い領域から序々に水深の深い領域へ浄水作用を促して、空気中に臭気を発したり水面Wを汚泥で汚したりすることなく穏やかに浄水処理を進めるようにしても良い。また、浄水処理装置Sは、水中に浮かべることで、容易に目的の場所に移動させることができ、例えばワイヤー(綱)などにより係留させることができる(図示せず)。
(Usage mode)
This water purification apparatus S is used as follows. FIG. 5 is an explanatory diagram for explaining a usage mode of the water purification apparatus S. The water purification apparatus S is used floating in water in raw water areas such as rivers and lakes. When the water purification apparatus S is introduced into the raw water area, the water purification apparatus S floats at a depth that allows the water purification section C to be located below the water surface W due to the buoyancy of the float section F, and floats above the bottom K. . The entire water purification apparatus S may be submerged in water, or may be submerged to near the bottom K, and what level of water depth is positioned may be adjusted according to the condition of the raw water area. Float near the water surface W and gradually promote the water purification action from the shallow water area to the deep water area, so that the water purification process can proceed gently without causing odor in the air or polluting the water surface W with sludge. Also good. Moreover, the water purification apparatus S can be easily moved to the target place by floating in water, for example, can be moored with a wire (not shown).

吸引手段2を駆動すると、浄水槽1の小孔1cから被処理水が吸引される。吸引手段2として水中で使用可能な水中ポンプPを用いると、原水域の外にポンプを配置して被処理水を原水域外に汲み上げる場合と比較して、吸引力が小さくて済み、低消費電力化が図られる。原水域から吸引された被処理水は濾過材収納空間7に流入し、濾過材3aにより濾過され、水中ポンプPにより排水管4aに送られ原水域に排水される。水中では、排水の減衰が少ないため、従来の噴水方式に比べて広範囲に排水することができる。排水管4aは浄水処理装置Sの安定姿勢を維持するように放射線状に配置されているため、排水による水圧によっても浄水処理装置Sが傾斜したり揺動したりして姿勢を崩すことがなく、濾過材3aの偏りや、逆洗手段5の吸気管5bの配置の乱れが防止される。濾過により濾過材収納空間7に残存した濾物は濾過材3aに保持される生物により生物処理されて分解される。生物は濾物中の有機物を分解しながら増殖を続ける。   When the suction means 2 is driven, the water to be treated is sucked from the small hole 1 c of the water purification tank 1. When the submersible pump P that can be used underwater is used as the suction means 2, the suction power is smaller and the power consumption is lower than when the pump is placed outside the raw water area and the treated water is pumped outside the raw water area. Is achieved. The water to be treated sucked from the raw water area flows into the filter medium storage space 7, is filtered by the filter medium 3a, is sent to the drain pipe 4a by the submersible pump P, and is drained to the raw water area. In water, since the attenuation of drainage is small, it can be drained in a wide range compared to the conventional fountain system. Since the drain pipe 4a is radially arranged so as to maintain the stable posture of the water purification apparatus S, the posture of the water purification apparatus S is not tilted or swung even by water pressure due to drainage. Further, the bias of the filter medium 3a and the disorder of the arrangement of the intake pipe 5b of the backwashing means 5 are prevented. Filtrate remaining in the filter medium storage space 7 by filtration is biologically processed and decomposed by organisms held in the filter medium 3a. Living organisms continue to grow while decomposing organic matter in the filtrate.

浄水処理装置Sは、所定のタイミングで逆洗手段5により逆洗を行う。逆洗のタイミングは、原水域の状況に応じて適宜設定すればよいが、おおよそ1日数回から十数回程度である。本実施の形態では、エアポンプ5aの稼働により、大気が吸引側配管5bの吸引口から吸引されて排出側配管5cの排出口から排出される。排出された大気は濾過材3aを曝気して逆洗する。逆洗により、濾過材3aから過剰な生物や付着物が剥離され、濾過材3aの目詰まりが防止されるとともに、剥離された生物が浄水槽1の小孔1cから浄水処理装置Sの外、すなわち原水域に排出される。   The water purification apparatus S performs backwashing by the backwashing means 5 at a predetermined timing. The timing of backwashing may be set as appropriate according to the conditions of the raw water area, but is approximately several times to a dozen times a day. In the present embodiment, the air is sucked from the suction port of the suction side pipe 5b and discharged from the discharge port of the discharge side pipe 5c by the operation of the air pump 5a. The exhausted air is back-washed by aeration of the filter medium 3a. By backwashing, excess organisms and deposits are separated from the filter medium 3a, and the filter medium 3a is prevented from being clogged, and the peeled organism is removed from the small hole 1c of the water purification tank 1 outside the water purification apparatus S, That is, it is discharged into the raw water area.

原水域の水中では、逆洗により排出された生物により汚泥等が生物処理される。これにより水中の有機物が分解され、原水域の水中における浄水処理が促進される。浄水処理装置S内での浄水処理に加え、原水域では浄水処理装置Sから排出された生物によって浄水処理がなされ、浄水処理装置S内外の処理が相俟って高い浄水効果が得られる。また、汚泥等は粘着質であり原水域に付着しているため、このままでは浄水処理装置Sに吸引されにくい。浄水処理装置Sによれば、排出された生物の生物処理により原水域中に付着する汚泥等の分解が進むと、汚泥等は粘着力が弱まって水中に浮遊し、浄水処理装置Sに吸入されやすくなる。このサイクルにより相乗効果が生じ、非常に高い浄水効果が得られる。   In the raw water, sludge is biologically treated by the organisms discharged by backwashing. Thereby, the organic substance in water is decomposed | disassembled and the water purification process in the water of a raw | natural water area is accelerated | stimulated. In addition to the water purification treatment in the water purification apparatus S, the raw water area is subjected to water purification treatment by living organisms discharged from the water purification apparatus S, and a high water purification effect is obtained in combination with the treatment inside and outside the water purification treatment apparatus S. Moreover, since sludge etc. are sticky and have adhered to the raw | natural water area, it is hard to be attracted | sucked by the water purification apparatus S as it is. According to the water purification apparatus S, when the sludge adhering to the raw water area progresses due to the biological treatment of the discharged organisms, the sludge is weakened in the adhesive force and floats in the water and is sucked into the water purification apparatus S. It becomes easy. This cycle produces a synergistic effect and provides a very high water purification effect.

生物が好気性の場合、逆洗手段5は、濾過材3aに保持される生物に酸素を供給するエアレーションの機能も果たす。濾過材3aに保持される生物は逆洗により排出されて乏しくなるが、同時に酸素が供給されて増殖が促進され、浄水能力の回復が早められる。原水域中では、逆洗により酸素が供給されて生物の生息環境も改善されて、更に浄水効果が高められる。排出される気体は大気に限定するものではなく、生物に適するように調整された酸素含有ガスとしても良い。この場合は、予め調整した酸素含有ガスや酸素含有溶液が入ったボンベを準備し、逆洗手段5の吸気口を接続する。なお、逆洗手段5は、気体を排出するものに限らず、例えば酸素を溶融させた酸素含有液体を排出することにより逆洗するものでも良い。   When the organism is aerobic, the backwashing means 5 also functions as aeration for supplying oxygen to the organism held in the filter medium 3a. The organisms held in the filter medium 3a are exhausted by backwashing and become scarce, but at the same time, oxygen is supplied to promote the growth and the recovery of the water purification ability is accelerated. In the raw water area, oxygen is supplied by backwashing, the habitat of the organism is improved, and the water purification effect is further enhanced. The gas to be discharged is not limited to the atmosphere, and may be an oxygen-containing gas adjusted to be suitable for living organisms. In this case, a cylinder containing a preliminarily prepared oxygen-containing gas or oxygen-containing solution is prepared, and the intake port of the backwashing means 5 is connected. Note that the backwashing means 5 is not limited to discharging gas, and may be backwashed by discharging an oxygen-containing liquid in which oxygen is melted, for example.

また、濾過材3aとして表面にひだ3bを有する粒状ものを用いた場合、生物の保持及び剥離の両方の面で有効である。すなわち、逆洗時には逆洗手段5から排出される気体や液体がひだに沿って流れ、繁殖した生物を濾過材3aから効率良く剥離させることができる。そして、逆洗以外のときは濾過材3aが互いに接触してもひだの間に保持される生物は濾過材3aから剥離することがなく、生物が安定して保持される。これにより、逆洗時には生物が効率よく原水域に排出されて、浄水処理装置S外での浄水処理効果が高められ、排出した後はひだの間にて生物の増殖が促進されて、浄水処理装置S内での生物処理能力が早急に回復し、このサイクルにより高い浄水効果を得ることができる。このひだ3bは合成樹脂からなる濾過材3aを螺旋状に形成することで形成されているので、頑丈でありながら比表面積を大きくすることができる。   Moreover, when the granular material which has the pleat 3b on the surface is used as the filter medium 3a, it is effective in both the surface of biological holding and peeling. That is, at the time of backwashing, the gas or liquid discharged from the backwashing means 5 flows along the folds, and the propagated organisms can be efficiently separated from the filter medium 3a. In cases other than backwashing, even if the filter media 3a come into contact with each other, the organisms held between the pleats are not separated from the filter media 3a, and the organisms are stably held. Thereby, at the time of backwashing, the organism is efficiently discharged into the raw water area, the effect of the water purification treatment outside the water purification apparatus S is enhanced, and after the discharge, the growth of the organism is promoted between the folds, and the water purification treatment The biological treatment capacity in the apparatus S is quickly recovered, and a high water purification effect can be obtained by this cycle. Since the pleat 3b is formed by forming the filter medium 3a made of synthetic resin in a spiral shape, the specific surface area can be increased while being strong.

(実施例1)
一昨年夏頃、大阪市内の人工河川A(掘割)に、試験的に本発明の浄水処理装置S1を設置して水質改善の様子を観察した。図6は、浄水処理装置S1の外観写真である。この浄水処理装置S1の本体は強化プラスチック(FRP)製であり、直径1.4m、高さ0.9mである。図7は、浄水処理装置S1を人工河川(掘割)に浮かべて配置した写真である。この人工河川(掘割)の水深は、平均2.5m、堆積したヘドロの深さは、平均0.3mを超えている。
Example 1
Around the summer of last year, the water purification device S1 of the present invention was experimentally installed in an artificial river A (digging) in Osaka city to observe the state of water quality improvement. FIG. 6 is an appearance photograph of the water purification apparatus S1. The main body of this water purification apparatus S1 is made of reinforced plastic (FRP) and has a diameter of 1.4 m and a height of 0.9 m. FIG. 7 is a photograph in which the water purification apparatus S1 is placed on an artificial river (digging). The average depth of this artificial river (digging) is 2.5 m, and the depth of the accumulated sludge exceeds 0.3 m on average.

この浄水処理装置S1では、水中ポンプPによる吸水と排水は24時間連続運転を行い、大気を取り込む逆洗は2時間毎に0.5時間運転を行なった。逆洗の頻度と逆洗時間は、原水域の汚れ具合や水源の大きさなどにより適宜設計(設定)するものであるが、今回は、生ゴミ処理装置での経験を参考にして上記設計値とした。この水中ポンプPによる排水は、約15m先まで水を運ぶことができるので、浄水処理装置S1を人工河川(掘割)の片側に設置すれば、反対側の岸まで水を循環させることも可能である。   In this water purifier S1, water absorption and drainage by the submersible pump P was continuously operated for 24 hours, and backwashing for taking in air was performed every 2 hours for 0.5 hours. The frequency of backwashing and the time of backwashing are designed (set) as appropriate depending on the degree of contamination in the raw water area and the size of the water source, but this time, the above design values are based on experience with garbage processing equipment. It was. Since the drainage by this submersible pump P can carry water up to about 15m ahead, if the water purification device S1 is installed on one side of an artificial river (digging), it is possible to circulate the water to the opposite shore. is there.

図8は、浄水処理装置S1の付近の水質を観察した写真である。図8(a)は設置直後の写真であり、アオコにより遮光され河川が深緑色となり水中が全く見えない。図8(b),(c)は、設置から45日後の写真であり、浄水がすすみ、河川が澄んでいるので、図8(b)では水中にある浄水処理装置S1の底部が見えており、また、図8(c)では水中を泳ぐ魚の姿がはっきり見える。この状態で堆積したヘドロの深さは、平均0.1m程度となり、1/3以下に改善された。   FIG. 8 is a photograph of the water quality in the vicinity of the water purification apparatus S1. FIG. 8 (a) is a photograph immediately after the installation, where the river is dark green and the river is dark green and the water is completely invisible. 8 (b) and 8 (c) are photographs 45 days after the installation, and since the purified water has progressed and the river is clear, in FIG. 8 (b), the bottom of the purified water treatment device S1 in water is visible. In addition, in FIG. 8C, the figure of the fish swimming in the water is clearly visible. The depth of sludge deposited in this state was about 0.1 m on average, which was improved to 1/3 or less.

(実施例2)
一昨年末から昨年初めにかけて、大阪市内の人工河川B(掘割)に、試験的に本発明の浄水処理装置S1を3台設置して、水底地形の変化を調査した。便宜上、これら浄水処理装置をS1,S2,S3として以下に説明する。図9は、浄水処理装置S1,S2,S3を人工河川Bに設置した状態を示す上面図である。人工河川Bは、両側に護岸Wa,Wbを備えており、進行方向yの方向に(図9では左側から右側に向かって)河川水Wが流れている。人工河川Bには、高架道路の橋脚h11〜h32が並んでおり河川水Wの淀みが生じやすい。浄水処理装置S1とS2とS3は護岸Waから河川の中央に向かって約1mの位置に係留されており、フロート部Fにより浄水処理装置の一部が浮かんでいる(図示せず)。浄水処理装置S1とS2,S2とS3の間隔Lは、約7mである。護岸Waから1m内側に配置された浄水処理装置S1とS2とS3を結ぶライン(図9に一点鎖線で示すライン)A1−A1線断面での水底地形を測定して断面観察した(図10)。また、A1−A1線と平行、かつ、護岸Waから2m内側のA2−A2断面での水底地形を測定して断面観察した(図11)。さらに、A1−A1線と平行、かつ、護岸Waから3m内側のA3−A3断面での水底地形を測定して断面観察した(図11)。図10は、図9のA1−A1線断面での水底地形を測定して断面観察した水底地形断面図であり、図10(a)は装置設置前の水底地形断面図であり、図10(b)は設置直後の水底地形断面図であり、図10(c)は設置から1週間後の水底地形断面図であり、図10(d)は設置から3週間後の水底地形断面図であり、図10(e)は設置から7週間後の水底地形断面図であり、図10(f)は装置撤去から3週間後の水底地形断面図である。図11は、図9のA2−A2線断面での水底地形を図10と同時期に測定して断面観察した水底地形断面図である。図12は、図9のA3−A3線断面での水底地形を図10と同時期に測定して断面観察した水底地形断面図である。
(Example 2)
From the end of the year before to the beginning of last year, three water purification treatment devices S1 of the present invention were experimentally installed on the artificial river B (digging) in Osaka city, and the change in the bottom topography was investigated. For convenience, these water purifiers will be described below as S1, S2, and S3. FIG. 9 is a top view showing a state where the water purification apparatuses S1, S2, and S3 are installed in the artificial river B. FIG. The artificial river B has revetments Wa and Wb on both sides, and the river water W flows in the direction of travel y (from the left side to the right side in FIG. 9). In the artificial river B, the bridge piers h11 to h32 of the elevated road are arranged, and the stagnation of the river water W is likely to occur. The water purification apparatuses S1, S2 and S3 are moored at a position of about 1 m from the revetment Wa toward the center of the river, and a part of the water purification apparatus is floated by the float part F (not shown). The distance L between the water purification devices S1 and S2, S2 and S3 is about 7 m. A line connecting water purification devices S1, S2 and S3 placed 1m inside from the revetment Wa (line shown by a one-dot chain line in FIG. 9) A1-A1 line cross section was measured and the cross section was observed (FIG. 10). . In addition, the bottom surface of the A2-A2 cross section parallel to the A1-A1 line and 2 m inside from the revetment Wa was measured to observe the cross section (FIG. 11). Furthermore, the water bottom topography in the A3-A3 cross section parallel to the A1-A1 line and 3 m inside from the revetment Wa was measured, and the cross section was observed (FIG. 11). FIG. 10 is a cross-sectional view of the bottom terrain obtained by measuring the cross-section of the bottom of the A1-A1 line in FIG. 9 and observing the cross section. FIG. 10 (a) is a cross-sectional view of the bottom terrain before the installation of the apparatus. b) is a bottom terrain sectional view immediately after installation, FIG. 10 (c) is a bottom terrain sectional view one week after installation, and FIG. 10 (d) is a bottom terrain sectional view three weeks after installation. FIG. 10 (e) is a sectional view of the bottom of the bottom 7 weeks after installation, and FIG. 10 (f) is a sectional view of the bottom of the bottom 3 weeks after the device is removed. FIG. 11 is a cross-sectional view of the water bottom topography obtained by measuring the water bottom topography in the cross section along line A2-A2 of FIG. 12 is a cross-sectional view of the water bottom topography obtained by measuring the water bottom topography in the cross section along line A3-A3 in FIG. 9 and observing the cross section at the same time as FIG.

図10(a)は装置設置前の水底地形断面図である。水底地形断面図の縦軸は水深を表しており、横軸はA1−A1線を表している。横軸の上端の目盛は1m間隔に付けている。図中に橋脚h21を位置の目安として、点線で示している。水底地形断面図は、上から順に、河川水W、スラリー状の流動性泥(ヘドロ)K1(濃色で表示)、堆積泥K2(淡色で表示)の順に表示されている。流動性泥(ヘドロ)K1は、密度ρが1.2〜1.4(g/cm)の泥層であり、堆積泥K2は、密度ρが1.4以上(g/cm)の層である。 FIG. 10A is a sectional view of the bottom of the water before the device is installed. The vertical axis of the bottom terrain sectional view represents the water depth, and the horizontal axis represents the A1-A1 line. The scale at the top of the horizontal axis is set at 1 m intervals. In the figure, the pier h21 is indicated by a dotted line as a position guide. The bottom topographic cross-sectional views are displayed in order of river water W, slurry-like fluid mud (sludge) K1 (displayed in dark color), and sedimented mud K2 (displayed in light color) from the top. Liquidity mud (sludge) K1 is a mud layer of density ρ is 1.2~1.4 (g / cm 3), sediments K2 has a density ρ of 1.4 or more (g / cm 3) Is a layer.

水底地形断面図を表すために、RIコーン(Radio Isotope Cone)により水底質密度測定を行い、その測定結果にもとづき作製した探索重錘に付けた糸の繰り出し量にて、堆積泥K2の位置を測定した。また、周波数200kHzの音響測深機により、流動性泥(ヘドロ)K1の位置を測定した。   In order to show the topographical profile of the bottom, the bottom sediment density is measured with an RI cone (Radio Isotope Cone), and the position of the deposited mud K2 is determined by the amount of thread fed to the search weight created based on the measurement result. It was measured. Moreover, the position of fluid mud (sludge) K1 was measured with the acoustic sounding instrument of frequency 200kHz.

浄水処理装置S1,S2,S3設置前の水底地形断面図(図10(a))では、流動性泥(ヘドロ)K1の層の厚みは、およそ1mあるが、浄水処理装置S1,S2,S3設置から1週間後の水底地形断面図(図10(c))では、流動性泥(ヘドロ)K1の層の厚みは、当初の1/2から1/3に減少し、さらに、時間経過とともに流動性泥(ヘドロ)K1の層の厚みの減少が見られる(図10(d),図10(e))。図10での流動性泥(ヘドロ)K1の層の厚みの減少傾向は、図11と図12でも同様である。いっぽう、浄水処理装置S1,S2,S3撤去から3週間後の水底地形断面図では、流動性泥(ヘドロ)K1の層の厚みが装置撤去前に比べて、若干増加しているように見える(図10(f)等)。このことから、浄水処理装置S1,S2,S3の浄水作用により、広い範囲で流動性泥(ヘドロ)K1の層の厚みが減少することが確認できた。   In the bottom topographical sectional view (FIG. 10 (a)) before the water purification apparatus S1, S2, S3 is installed, the thickness of the fluid mud (sludge) K1 is about 1 m, but the water purification apparatuses S1, S2, S3. In the bottom topographic cross-sectional view one week after installation (Fig. 10 (c)), the thickness of the fluid mud (sludge) K1 is reduced from 1/2 to 1/3 of the initial level, and further, as time passes. A decrease in the thickness of the fluid mud (sludge) K1 layer is observed (FIG. 10 (d), FIG. 10 (e)). The decreasing tendency of the thickness of the fluid mud (sludge) K1 in FIG. 10 is the same in FIG. 11 and FIG. On the other hand, in the bottom topographic cross-sectional view after 3 weeks from the removal of the water purification devices S1, S2, S3, it seems that the thickness of the fluid mud (sludge) K1 layer is slightly increased compared to before the removal of the device ( FIG. 10 (f) and the like). From this, it has confirmed that the thickness of the layer of fluid mud (sludge) K1 decreased in the wide range by the water purification effect | action of water purification apparatus S1, S2, S3.

本発明の浄水処理装置は、河川や湖沼等での使用が好適であるが、観賞魚や養殖魚の飼育槽等の人工的環境や、様々な環境の浄水に適用可能である。また、本発明は、バクテリアの培養装置としての応用も可能である。このように、本発明は、その趣旨を逸脱しない範囲で適宜変更が可能であることは言うまでもない。   The water purification apparatus of the present invention is suitable for use in rivers, lakes and the like, but is applicable to artificial environments such as aquarium fish and aquaculture fish breeding tanks, and water purification in various environments. The present invention can also be applied as a bacterial culture apparatus. Thus, it goes without saying that the present invention can be modified as appropriate without departing from the spirit of the present invention.

本発明の一実施の形態の浄水処理装置の内部構造を示す正面図である。It is a front view which shows the internal structure of the water purification apparatus of one embodiment of this invention. 上記実施の形態の浄水処理装置の内部構造を示す上面図である。It is a top view which shows the internal structure of the water purification apparatus of the said embodiment. 上記実施の形態の浄水処理装置の内部構造を示す斜視図である。It is a perspective view which shows the internal structure of the water purification apparatus of the said embodiment. 表面にひだを有する濾過材の斜視図である。It is a perspective view of the filter medium which has a pleat on the surface. 本発明の一実施の形態の浄水処理装置の使用態様を説明する説明図である。It is explanatory drawing explaining the usage condition of the water purification apparatus of one embodiment of this invention. 本発明の一実施の形態の浄水処理装置の外観を示す外観写真である。It is an external appearance photograph which shows the external appearance of the water purification apparatus of one embodiment of this invention. 上記実施の形態の浄水処理装置を人工河川Aに設置した状態を示す外観写真である。It is an external appearance photograph which shows the state which installed the water purifier of the said embodiment in the artificial river A. 上記実施の形態の浄水処理装置付近の水質を観察した外観写真であり、図8(a)は、設置直後の外観写真であり、図8(b),(c)は、設置から45日後の外観写真である。It is the external appearance photograph which observed the water quality of the water purification treatment apparatus vicinity of the said embodiment, FIG.8 (a) is an external appearance photograph immediately after installation, FIG.8 (b), (c) is 45 days after installation. It is an appearance photograph. 上記実施の形態の浄水処理装置を人工河川Bに設置した状態を示す上面図である。It is a top view which shows the state which installed the water purification apparatus of the said embodiment in the artificial river B. 図9のA1−A1線断面での水底地形を測定して断面観察した水底地形断面図であり、図10(a)は装置設置前の水底地形断面図であり、図10(b)は設置直後の水底地形断面図であり、図10(c)は設置から1週間後の水底地形断面図であり、図10(d)は設置から3週間後の水底地形断面図であり、図10(e)は設置から7週間後の水底地形断面図であり、図10(f)は装置撤去から3週間後の水底地形断面図である。FIG. 10A is a cross-sectional view of the water bottom topography obtained by measuring the cross-section of the water bottom at the A1-A1 line cross section of FIG. 9; FIG. 10A is a cross-sectional view of the water bottom topography before the device is installed; FIG. FIG. 10C is a cross-sectional view of the water bottom terrain immediately after the installation, FIG. 10D is a cross-sectional view of the water terrain after 3 weeks from the installation, and FIG. e) is a sectional view of the bottom of the bottom 7 weeks after the installation, and FIG. 10 (f) is a sectional view of the bottom of the bottom 3 weeks after the device is removed. 図11は、図9のA2−A2線断面での水底地形を図10と同時期に測定して断面観察した水底地形断面図である。FIG. 11 is a cross-sectional view of the water bottom topography obtained by measuring the water bottom topography in the cross section along line A2-A2 of FIG. 図12は、図9のA3−A3線断面での水底地形を図10と同時期に測定して断面観察した水底地形断面図である。12 is a cross-sectional view of the water bottom topography obtained by measuring the water bottom topography in the cross section along line A3-A3 in FIG. 9 and observing the cross section at the same time as FIG.

符号の説明Explanation of symbols

S S1 S2 S3 浄水処理装置、C 浄水部、F フロート部、
1 浄水槽、1a 浄水槽の底部、1b 浄水槽の側部、1c 浄水槽の孔、
2 吸引手段、P 水中ポンプ、
3 濾過手段、3a 濾過材、3b 濾過材表面のひだ、
4 排出手段、4a 排水管、
5 逆洗手段、5a エアポンプ、5b 吸引側配管、5c 排出側配管、
6 収納容器、6a 収納容器の孔、
7 濾過材収納空間、
W 河川水、Wa Wb 護岸、W1 水面、
K 水底、K1 流動性泥(ヘドロ)、K2 堆積泥、
S S1 S2 S3 Water purification device, C water purification unit, F float unit,
DESCRIPTION OF SYMBOLS 1 Water purification tank, 1a Bottom part of water purification tank, 1b Side part of water purification tank, 1c Hole of water purification tank,
2 suction means, P submersible pump,
3 Filtration means, 3a filter material, 3b pleats on the surface of the filter material,
4 Discharge means, 4a Drain pipe,
5 Backwashing means, 5a Air pump, 5b Suction side piping, 5c Discharge side piping,
6 storage container, 6a hole of storage container,
7 Filter material storage space,
W river water, Wa Wb revetment, W1 water surface,
K water bottom, K1 fluid mud (sludge), K2 sediment mud,

Claims (4)

河川や湖沼等の原水域に配された浄水槽から被処理水を吸引する吸引手段と、前記吸引手段により吸引した被処理水を濾過するとともに濾過材に保持された好気性生物により濾物を生物処理する濾過手段と、前記濾過手段により濾過された被処理水を排出する排出手段と、前記濾過材収納空間に配されて大気を取り込んで前記濾過手段の濾過材を逆洗する逆洗手段とを備え、
前記濾過手段と排手段とが円筒形状の浄水槽に収納されており、前記排出手段は、前記濾過手段により濾過された被処理水の流路となる排水管が円筒形状の浄水槽の水平断面において放射線状に配置されており、前記原水域の被処理水が、前記浄水槽の側面に設けられた小孔から流入し、前記濾過手段で濾過された後に、収納容器の孔を通って収納容器内に流入し、収納容器内に設けられた前記吸引手段によって吸引されて、排水管によって原水域の水中に排出される構成とされ、前記逆洗手段による逆洗により前記濾過材から前記好気性生物を剥離させるとともに取り込んだ大気により前記好気性生物に酸素を与えて前記原水域に排出することを特徴とする浄水処理装置。
A suction means for sucking water to be treated from a water purification tank disposed in a raw water area such as a river or a lake, and a filter for filtering the water to be treated sucked by the suction means and aerobic organisms held on the filter medium. A filtering means for biological treatment; a discharging means for discharging the water to be treated filtered by the filtering means; and a backwashing means for backwashing the filtering material of the filtering means that is disposed in the filtering material storage space and takes in the atmosphere. And
Said filtering means and the discharge detecting means is housed in the water purification tank of cylindrical shape, said discharge means, horizontal water purification tank drain pipe cylindrical shape having a flow path for treated water filtered by the filtering means It is arranged radially in cross section, and the treated water in the raw water area flows from a small hole provided in the side surface of the water purification tank, is filtered by the filtering means, and then passes through the hole of the storage container. It flows into the storage container, is sucked by the suction means provided in the storage container, and is discharged into the water of the raw water area by the drain pipe, and from the filter medium by backwashing by the backwashing means A water purification apparatus, which exfoliates aerobic organisms and supplies oxygen to the aerobic organisms and discharges them into the raw water area.
前記逆洗手段による逆洗のタイミングが、1日数回から十数回に設定されることを特徴とする請求項1記載の浄水処理装置。   The water purification apparatus according to claim 1, wherein the timing of backwashing by the backwashing means is set from several times to a dozen times a day. 前記逆洗手段に備わったエアポンプの排出口が、前記濾過材が収納された収納空間の下方側に複数配されており、かつ、前記濾過材が、表面にひだを有する粒状体が複数配されたものであることを特徴とする請求項2記載の浄水処理装置。 A plurality of outlets of an air pump provided in the backwashing means are arranged below the storage space in which the filter medium is stored, and the filter medium is provided with a plurality of granules having pleats on the surface. The water purification apparatus according to claim 2, wherein 河川や湖沼等で浮かばせて使用するための半球状のフロート部が着脱自在に前記浄水槽の上部に嵌合されており、かつ、前記吸引手段に備わった水中ポンプが、前記浄水槽の底部の中央付近に配されていることを特徴とする請求項1記載の浄水処理装置。 A hemispherical float for use in floating in a river or lake is detachably fitted to the upper part of the water purification tank, and a submersible pump provided in the suction means is provided at the bottom of the water purification tank. The water purification apparatus according to claim 1, wherein the water purification apparatus is disposed near the center of the water.
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