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JP3062883B2 - Water purification method and water purification device - Google Patents
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JP3062883B2 - Water purification method and water purification device - Google Patents

Water purification method and water purification device

Info

Publication number
JP3062883B2
JP3062883B2 JP10260463A JP26046398A JP3062883B2 JP 3062883 B2 JP3062883 B2 JP 3062883B2 JP 10260463 A JP10260463 A JP 10260463A JP 26046398 A JP26046398 A JP 26046398A JP 3062883 B2 JP3062883 B2 JP 3062883B2
Authority
JP
Japan
Prior art keywords
water
partition wall
space
sediment
container
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP10260463A
Other languages
Japanese (ja)
Other versions
JP2000084308A (en
Inventor
正 山田
Original Assignee
北新工業株式会社
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Filing date
Publication date
Application filed by 北新工業株式会社 filed Critical 北新工業株式会社
Priority to JP10260463A priority Critical patent/JP3062883B2/en
Publication of JP2000084308A publication Critical patent/JP2000084308A/en
Application granted granted Critical
Publication of JP3062883B2 publication Critical patent/JP3062883B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • 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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  • Biological Treatment Of Waste Water (AREA)
  • Filtration Of Liquid (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、粘土やシルト、砂
質土、ヘドロ、軟弱土等の土系材料を主成分とする多孔
質体であるろ材をし尿浄化装置の水路等に用いてその水
質を継続的に向上することができる水質浄化方法及び水
質浄化装置に関する。
The present invention relates to a filter medium which is a porous material mainly composed of an earth-based material such as clay, silt, sandy soil, sludge, soft soil and the like, and is used for a water channel of a urine purification apparatus. The present invention relates to a water purification method and a water purification device that can continuously improve water quality.

【0002】[0002]

【従来の技術】従来より河川や農業用の用水路、家庭
用、学校用、食品事業場用、畜産事業施設用、海水等の
廃水処理施設の流路等の水質浄化に、各種のろ材、例え
ば空隙を有するコンクリート固化体、プラスチック製ろ
材、木炭、石材、レキ等を敷設する試みがなされてい
る。また、近年では、ろ材を金属メッシュ材などからな
る透水性カゴに充填した状態で敷設する方法も実施され
ている。これらの方法では、ろ材間に流水中に含まれる
汚損物質を捕捉し、凝集、沈澱させて水質を浄化するこ
とができる。また、ろ材の表面やろ材間に微生物膜層を
形成させ、この微生物により水中の有機物を酸化分解す
ることによっても水質は浄化される。さらに、最近では
軽石などの多孔質骨材を用いて流水との接触面積を向上
した多孔質ろ材の提案もなされている。
2. Description of the Related Art Conventionally, various filter media, such as water channels for rivers and agriculture, households, schools, food establishments, livestock business facilities, and water purification of seawater and other wastewater treatment facilities, have been used. Attempts have been made to lay concrete solids having voids, filter media made of plastic, charcoal, stone, rubble, and the like. In recent years, a method of laying a filter medium in a state of being filled in a water-permeable basket made of a metal mesh material or the like has also been implemented. In these methods, the pollutants contained in the flowing water between the filter media can be captured, aggregated and precipitated, and the water quality can be purified. Further, the water quality is also purified by forming a microbial membrane layer on the surface of the filter medium or between the filter materials, and oxidatively decomposing organic substances in the water by the microorganisms. Further, recently, a porous filter medium having improved contact area with running water using a porous aggregate such as pumice has been proposed.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、前記従
来の水質浄化方法は、河川等の底部(河床)にろ材を層
状に敷設するので、河床に近い下層側のろ材間には上方
から沈殿物が沈降し、そのまま滞留するため、下層側か
ら順にろ材間が沈殿物で半ば閉塞され、ろ過作用が失わ
れてしまう。多孔質の骨材の表面も沈殿物で覆われてし
まう。そのため、一定期間の後にはろ過作用が失われ、
水質浄化効率が著しく低下してしまう。また、ろ材表面
に形成される微生物膜層も水流と接触できなくなるた
め、この点でも水質浄化効率は低下する。したがって、
一定期間の後には、ろ材を河川等から取り出し、新たな
ろ材を設置する交換作業が必要となる。特に流水中に汚
損物質を多量に含有するし尿浄化処理の場合には極めて
短期間にろ材を交換しなければならない。しかも、取り
出したろ材の廃棄については再利用の用途が少ないとい
う現状がある。
However, in the above-mentioned conventional water purification method, a filter medium is laid in a layer at the bottom (river bed) of a river or the like. Since the sediment settles and stays as it is, the space between the filter media is partially blocked by the sediment in order from the lower layer side, and the filtering action is lost. The surface of the porous aggregate is also covered with sediment. Therefore, after a certain period, the filtration action is lost,
Water purification efficiency is significantly reduced. In addition, the microbial membrane layer formed on the surface of the filter medium cannot contact the water stream, so that the water purification efficiency also decreases in this respect. Therefore,
After a certain period of time, it is necessary to take out the filter media from a river or the like and replace it with a new one. In particular, in the case of human urine purification treatment containing a large amount of fouling substances in running water, the filter medium must be replaced in a very short time. In addition, there is a current situation in which there is little use for reuse of the removed filter media.

【0004】[0004]

【課題を解決するための手段】本発明は前記に鑑み提案
されたもので、粘土、シルト、砂質土、ヘドロ、軟弱
土、或いはこれらを組み合わせた土系材料100重量部
と、セメントと固化剤又はセメント系固化剤から選ばれ
る一種以上の材料10〜35重量部とからなる多数のろ
材を透水性収容体に充填した状態で、その下方に空間部
が形成されるように流水路中に設置し、且つ透水性収容
体を長さ方向に並列させることにより上方に長さ方向に
連続するろ材の充填層を形成すると共に下方に長さ方向
に連続する空間部を形成し、空間部の水下側に開閉可能
な仕切り壁を設け、流水中に含まれる汚損物質をろ材に
より捕捉、沈澱させ、前記透水性収容体内から空間部に
沈降した沈殿物を仕切り壁を閉塞した状態で沈殿物を仕
切り壁の水上側近傍に集積させ、その水下側に回収容器
を設置した状態で仕切り壁を開放して回収容器に沈殿物
を導入して回収することを特徴とする水質浄化方法に関
するものである。
DISCLOSURE OF THE INVENTION The present invention has been proposed in view of the above, and it has been proposed that clay, silt, sandy soil, sludge, soft soil, or 100 parts by weight of an earth-based material obtained by combining these, cement and solidification In a state in which a large number of filter media comprising 10 to 35 parts by weight of one or more materials selected from the group consisting of an agent and a cement-based solidifying agent are filled in a water-permeable container, By installing and arranging the water-permeable containers in the length direction, a filled layer of the filter medium that is continuous in the length direction is formed upward, and a space portion that is continuous in the length direction is formed below, and the space portion is formed. An openable and closable partition wall is provided below the water, and the fouling substances contained in the running water are captured and settled by the filter medium, and the sediment that has settled out of the water-permeable container into the space is sedimented with the partition wall closed. Near the water side of the partition wall It was integrated, to a water purification method characterized by its water lower collection vessel at the installation state by introducing the precipitate into the recovery vessel by opening the partition wall recovery.

【0005】また、本発明は、粘土、シルト、砂質土、
ヘドロ、軟弱土、或いはこれらを組み合わせた土系材料
100重量部と、セメントと固化剤又はセメント系固化
剤から選ばれる一種以上の材料10〜35重量部とから
なる多数のろ材と、該ろ材を充填すると共に長さ方向に
並列させる透水性収容体と、該透水性収容体を流水路に
設置した際に上方に長さ方向に連続するろ材の充填層を
形成すると共に下方に長さ方向に連続する空間部を形成
されるための空間部形成手段とを備えて流水路中に常設
される浄化機構、及び空間部の水下側に開閉可能な仕切
り壁を設け、前記空間部の沈殿物を仕切り壁を閉塞した
状態で沈殿物を仕切り壁の水上側近傍に集積させ、その
水下側に回収容器を設置した状態で仕切り壁を開放して
回収容器に沈殿物を導入して回収する排出機構からなる
ことを特徴とする水質浄化装置をも提案する。
[0005] The present invention also relates to clay, silt, sandy soil,
Sludge, soft soil, or 100 parts by weight of an earth-based material obtained by combining them, a large number of filter media comprising 10 to 35 parts by weight of one or more materials selected from cement and a solidifying agent or a cement-based solidifying agent, A water-permeable container to be filled and arranged in the length direction, and when the water-permeable container is installed in a flowing water channel, a filling layer of a filter medium continuous in the length direction is formed upward and the length is lowered in the length direction. A purifying mechanism which is provided in the flowing water channel with a space forming means for forming a continuous space, and an openable / closable partition wall is provided below the water in the space, and the sediment in the space is provided. The sediment is collected near the upper side of the partition wall with the partition wall closed, and the partition wall is opened with the collecting container installed under the water, and the sediment is introduced into the collecting container and collected. Characterized by comprising a discharge mechanism Also it proposes a quality purifying device.

【0006】[0006]

【発明の実施の形態】まず、前記本発明に用いるろ材に
ついて説明する。ろ材としては、土系材料100重量
部、及びセメントと固化剤又はセメント系固化剤から選
ばれる一種以上の材料10〜35重量部からなるものを
用いる。尚、以下の説明において、「ろ材」は前記土系
材料を固化させたものを指す。
DESCRIPTION OF THE PREFERRED EMBODIMENTS First, a filter medium used in the present invention will be described. As the filter material, a material composed of 100 parts by weight of an earth-based material and 10 to 35 parts by weight of one or more materials selected from cement and a solidifying agent or a cement-based solidifying agent is used. In the following description, "filter medium" indicates a solidified version of the above-mentioned earth-based material.

【0007】ろ材の主成分である土系材料としては、粘
土、シルト、砂質土、ヘドロ、軟弱土等を挙げることが
でき、或いはこれらを適宜に組み合わせて使用しても良
い。例えば施工現場付近にて容易に調達するようにして
も良く、そのため、従来の細骨材や粗骨材を用いるコン
クリート固化体に比べ、原材料費が安価である。特に前
記のように施工現場付近にて土系材料を調達する場合に
は、施工現場まで運搬する資材(セメント及び固化剤)
が少ないので、この点でも有利である。尚、ヘドロはそ
のままでは環境汚染を引き起こすが、後述するセメント
及び固化剤により固化、改質されるので、本発明におけ
るろ材中の土系材料として用いることができ、しかも不
要となった後には粉砕して道路基礎等の盛土材や埋立土
として利用することができる。また、栄養分が多く肥料
としても使われる。軟弱土も同様である。
[0007] Examples of the soil-based material that is a main component of the filter medium include clay, silt, sandy soil, sludge, soft soil, and the like, or may be used in an appropriate combination. For example, it may be easily procured in the vicinity of the construction site, and therefore, the cost of raw materials is lower than that of a conventional solidified concrete using fine aggregate or coarse aggregate. Especially when procuring earth-based materials near the construction site as described above, materials (cement and solidifying agent) transported to the construction site
Is also advantageous in this respect. In addition, sludge causes environmental pollution as it is, but is solidified and modified by a cement and a solidifying agent described later, so that it can be used as an earth-based material in the filter medium of the present invention. It can be used as embankment material or landfill for road foundations. It is also rich in nutrients and is used as fertilizer. The same applies to soft soil.

【0008】また、セメントとしては、どのようなもの
でもよく、例えばポルトランドセメント、高炉セメン
ト、シリカセメント、フライアッシュセメント、アルミ
ナセメント、膨張セメントなどから選ばれる1種又は2
種以上の混合物を使用することができる。
[0008] The cement may be any cement, for example, one or two selected from Portland cement, blast furnace cement, silica cement, fly ash cement, alumina cement, expanded cement and the like.
Mixtures of more than one species can be used.

【0009】固化剤としては、既に多くの市販品が市場
に提供され、一般的には高含水粘土、高有機質土などの
軟弱地盤の改良及びヘドロ、下水汚泥、有害重金属など
を含有する産業廃棄物の固化処理などに使用されてい
る。このように多くの市販品があるため、その配合量を
狭い範囲で特定することは困難であり、所望の強度等の
特性に応じて添加量を設定すればよい。例えば、この固
化剤は、前記土系材料及びセメント(100重量部)に
対して0.1〜30重量部添加することが望ましい。セ
メント系固化剤としても、既に市販されているどのよう
なものを用いても良い。
As the solidifying agent, many commercially available products have already been provided on the market. Generally, improvement of soft ground such as high hydrous clay and high organic soil and industrial waste containing sludge, sewage sludge, harmful heavy metals, etc. It is used for solidification of objects. Since there are many commercially available products, it is difficult to specify the compounding amount in a narrow range, and the amount to be added may be set in accordance with desired properties such as strength. For example, it is desirable to add 0.1 to 30 parts by weight of the solidifying agent to the earth-based material and cement (100 parts by weight). Any commercially available cement-based solidifying agent may be used.

【0010】ろ材における前記各成分の混合割合は、土
系材料100重量部に対してセメントと固化剤又はセメ
ント系固化剤から選ばれる一種以上の材料(=以下、総
じて固化材料という)を10〜35重量部添加する。こ
の混合割合よりも固化材料の量が少ない(土系材料が多
い)場合には、ろ材を後述する透水性収容体に多層に積
み重ねて充填した際に最下層部分が圧壊したり、或いは
流水路中に配設した場合に水流(水圧)によって破壊
(破損)されるおそれがある。一方、上記混合割合より
も固化材料の量が多い(土系材料が少ない)場合には、
土粒子間の空隙形成が損なわれ、しかも交換した後に破
砕する作業が困難となる。
[0010] The mixing ratio of each of the above components in the filter medium is 10 to 1 part by weight of one or more materials selected from cement and a solidifying agent or a cement-based solidifying agent per 100 parts by weight of the earth-based material (hereinafter referred to as a solidified material). 35 parts by weight are added. When the amount of the solidified material is smaller than the mixing ratio (the amount of the earth-based material is large), the lowermost layer portion is crushed when the filter medium is stacked and filled in a water-permeable container described later, If it is installed inside, there is a possibility that it will be broken (damaged) by water flow (water pressure). On the other hand, when the amount of the solidified material is larger than the above mixing ratio (the amount of the earth-based material is small),
The formation of voids between the soil particles is impaired, and the work of crushing after replacement becomes difficult.

【0011】さらに、前記配合に砂、砕石、フライアッ
シュ等の各種の骨材を併用するようにしても良い。例え
ば径が数十mmのレキ状骨材を添加するようにしても良
い。また、各種混和材(剤)を添加するようにしても良
い。
Further, various kinds of aggregates such as sand, crushed stone, fly ash and the like may be used in combination with the above-mentioned composition. For example, a reticulated aggregate having a diameter of several tens of mm may be added. Further, various admixtures (agents) may be added.

【0012】そして、ろ材の作成(成形)に際しては、
前記各成分からなる配合に適量の水を加え、専用練り混
ぜ機等で混練する。混練物は、見掛け上、生コンと同様
であり、適度の流動性を有する。この混練物を用いて各
種形状に成形する方法については、公知のどのような方
法を用いても良い。
[0012] Then, when preparing (forming) the filter medium,
An appropriate amount of water is added to the mixture of the above components, and the mixture is kneaded with a dedicated kneading machine or the like. The kneaded material is apparently similar to ready-mixed concrete, and has appropriate fluidity. Any known method may be used for molding the kneaded material into various shapes.

【0013】また、このろ材はレキ状(小塊状)に成形
されるが、具体的な形状、寸法についても特に限定する
ものではなく、どのような形状、寸法に成形しても良
い。一般的には取扱性やろ過作用等を考慮して径40〜
100mm程度の球状に形成することが望ましい。さら
に、径が数十mmのレキ状骨材を併用し、このレキ状骨
材の周囲に前記土系材料を主成分とする組成物をまぶ
し、径100mm程度のレキ状複合体に成形しても良
い。この場合、併用するレキ状骨材として、例えばゼオ
ライト等の吸着性能を有するものを使用すれば、浮遊懸
濁物質の除去効率がより高いものとなる。
[0013] The filter medium is formed in a rek shape (small lump shape), but the specific shape and size are not particularly limited, and may be formed in any shape and size. Generally, a diameter of 40 to 40
It is desirable to form it into a spherical shape of about 100 mm. Further, a combination of a recre-like aggregate having a diameter of several tens of mm is used, and a composition containing the earth-based material as a main component is coated around the recre-like aggregate to form a reticulate composite having a diameter of about 100 mm. Is also good. In this case, if a reticulated aggregate to be used in combination with, for example, zeolite or the like having an adsorbing performance is used, the efficiency of removing suspended suspended substances becomes higher.

【0014】次に、前記ろ材を充填する透水性収容体に
ついて説明する。この透水性収容体は、その内部に前記
ろ材を収容することができ、収容したろ材に流水が十分
に接触できるものであればよく、特にその素材や形状、
寸法等について限定するものではない。一般的には底面
及び側面がろ材が落下しない程度の空隙を多数有するカ
ゴ状のものが用いられ、強度の高い金属製メッシュ、金
属製網材、パンチングメタル等を上方が開放するカゴ
状、箱状に成形したもの、棒状木材をカゴ状、箱状に組
み立てたものなどが用いられる。また、ろ材の径よりも
大きな(粗い)空隙を有する枠状に形成しても、多数の
ろ材をネット状の袋材などに収納し、これを袋材ごと収
容した場合にろ材が落下しなければ、何等支障はない。
Next, the water-permeable container filled with the filter medium will be described. The water-permeable container may be any one as long as the filter medium can be accommodated therein, and the running water can sufficiently contact the accommodated filter medium.
The size and the like are not limited. In general, a cage-shaped box with a large number of voids on the bottom and side surfaces that does not allow the filter material to fall is used, and a basket-shaped box with a high strength metal mesh, metal mesh, punched metal, etc. For example, those formed into a shape, those formed by assembling bar-shaped wood into a cage or a box, and the like are used. Further, even if the filter is formed in a frame shape having a void (coarse) larger than the diameter of the filter, a large number of filter media are stored in a net-shaped bag, and if the bag is stored together with the bag, the filter must fall. If there is no problem.

【0015】前記ろ材を充填した透水性収容体を、その
下方に空間部が形成されるように流水路中に設置する手
段(空間部形成手段)としては、例えば前記透水性収容
体に脚部を設ければよい。また、流水の流れ方向に沿っ
て溝状の空間部が形成されるように複数の載置台を設け
るようにしてもよい。この空間部形成手段は特に前記の
例に限定するものではなく、どのように構成してもよ
い。空間部の高さは、設置する空間部形成手段の高さに
より決定されるが、数cmから数十cmまで適宜に設定
すればよい。
As means for installing the water-permeable container filled with the filter medium in a flowing water channel so that a space is formed below the space (space forming means), for example, a leg portion may be attached to the water-permeable container. May be provided. Further, a plurality of mounting tables may be provided so that a groove-shaped space is formed along the flow direction of the flowing water. This space portion forming means is not particularly limited to the above-described example, and may be configured in any manner. The height of the space is determined by the height of the space forming means to be installed, but may be set appropriately from several cm to several tens of cm.

【0016】そして、前述のようにろ材を透水性収容体
に充填した状態で、その下方に空間部が形成されるよう
に流水路中に設置するので、流水中に含まれる各種の汚
損物質は、ろ材表面及びろ材間に捕捉され、凝集、沈澱
し、透水性収容体内からその下方の空間部に沈降する。
そして、この空間部に沈降した汚損物質の沈殿物を適宜
方法で流水路外へ排出する。
As described above, since the filter medium is filled in the water-permeable container and installed in the flowing water channel so as to form a space below the container, various pollutants contained in the flowing water can be reduced. The water is trapped on the surface of the filter medium and between the filter media, aggregates and precipitates, and settles out of the water-permeable container into a space thereunder.
Then, the sediment of the fouling substance settled in the space is discharged out of the flowing water channel by an appropriate method.

【0017】前記空間部に沈降した沈殿物を流水路外へ
排出するための手段(排出機構)としては、どのような
構成を採用してもよく、以下に好適な3例を示すが、こ
れらのうち本発明では(3)の排出手段を選択する。
As a means (discharge mechanism) for discharging the sediment settled in the space to the outside of the flowing water channel, any structure may be adopted, and three preferred examples are shown below. Among them, in the present invention, the discharging means (3) is selected.

【0018】(1) 空間部の水下側を仕切り壁で閉塞
することにより、汚損物質の沈殿物を仕切り壁の水上側
近傍に集積させる。この仕切り壁としては、一般的にコ
ンクリート板、木板、金属板等の板材が用いられるが、
特にその素材を限定するものではなく、その上端が水面
から露出しない程度に立設させる。この仕切り壁により
集積させた沈殿物は、水中ポンプ又はバキュームポンプ
等の吸引ポンプで吸引、排出してもよいし、目の細かな
網材ですくい上げるようにしても良い。この仕切り壁
は、ろ材を充填した透水性収容体に密接状に設置しても
よいし、やや離反した水下側に設置してもよいが、網材
ですくい上げる場合は上方からの作業に限定されるので
後者の設置位置でなければならない。しかも後者の場
合、吸引ポンプで吸引する場合にも流水路近傍に設備を
常設しておく必要がなく、適当な周期間隔で設備を流水
路近傍に持ち運び、上方から吸引パイプの先端を空間部
に挿入して排出することができる。また、前記の仕切り
壁は、空間部の最水下側に設置するが、加えて、空間部
の長さ方向の適宜位置に同様な仕切り壁を設置するよう
にしてもよい。
(1) By closing the lower side of the space with the partition wall, sediment of the fouling substance is accumulated near the upper side of the partition wall. As the partition wall, a plate material such as a concrete plate, a wooden plate, and a metal plate is generally used.
The material is not particularly limited, and it is erected so that the upper end is not exposed from the water surface. The sediment accumulated by the partition wall may be sucked and discharged by a suction pump such as a submersible pump or a vacuum pump, or may be scooped up by a fine mesh material. This partition wall may be installed close to the water-permeable container filled with the filter medium, or may be installed under the water that is slightly separated, but when picking up with a net material, it is limited to work from above Must be in the latter location. In addition, in the latter case, even when suction is performed by the suction pump, there is no need to permanently install equipment near the water channel, and the equipment is carried near the water channel at appropriate periodic intervals, and the tip of the suction pipe is inserted into the space from above. Can be inserted and ejected. Further, the above-mentioned partition wall is installed at the lowermost water side of the space portion. In addition, a similar partition wall may be installed at an appropriate position in the length direction of the space portion.

【0019】この(1)の方法は、特にその適用を制限
するものではないが水流が比較的速い場合に好適であ
る。また、この仕切り壁は外部(水下側)に沈殿物を流
出させない機能も果たす。浄水成分(流水中の沈殿物を
除く成分)は仕切り壁を乗り越えて流下する。尚、前記
仕切り壁に代えて目の細かな網材等を配設し、より微細
で沈降しきれずに浮遊しているような沈殿物(浮遊物)
を除去するようにしてもよいが、この除去効果は、網材
の微細空隙が浮遊物により閉塞されると共に失われてし
まうので、頻繁に交換する必要がある。
The method (1) is not particularly limited, but is suitable when the water flow is relatively fast. The partition wall also has a function of preventing the sediment from flowing out (under the water). Water purification components (components excluding sediment in running water) flow down over the partition wall. It should be noted that a fine mesh material or the like is provided in place of the partition wall, and the sediment (floating matter) which is finer and floats without being settled completely.
May be removed, but this removal effect needs to be replaced frequently because the fine voids of the netting material are closed and lost by the suspended matter.

【0020】(2) 透水性収容体自体、又は隣接する
透水性収容体間に、下方の空間部に達する貫通孔を形成
する。形成した貫通孔には、上方から吸引ポンプに接続
した吸引パイプを挿入し、沈殿物を排出する。この吸引
パイプの先端が空間部に位置すると、その近傍に浮遊す
る沈殿物が吸引され、吸引パイプの先端を貫通孔に位置
させると、その周囲のろ材間に滞留する沈殿物が吸引さ
れる。この貫通孔は、透水性収容体の側面に凹部を形成
し、隣接する2つの透水性収容体の凹部どうしを対向さ
せて形成させるものでもよいし、直方体状に形成した透
水性収容体の隅部に凹部を形成し、隣接する4つの透水
性収容体の凹部どうしを突き合わせるようにして形成さ
せるものでもよい。
(2) A through hole reaching the lower space portion is formed between the water-permeable container itself and the adjacent water-permeable container. A suction pipe connected to a suction pump is inserted from above into the formed through hole, and the sediment is discharged. When the tip of the suction pipe is located in the space, the sediment floating in the vicinity is sucked, and when the tip of the suction pipe is located in the through hole, the sediment remaining between the filter media around the suction pipe is sucked. The through-hole may be formed by forming a concave portion on the side surface of the water-permeable container so that the concave portions of two adjacent water-permeable containers are opposed to each other, or a corner of the water-permeable container formed in a rectangular parallelepiped shape. A concave portion may be formed in the portion, and the concave portions of four adjacent water-permeable containers may be formed to abut each other.

【0021】この(2)の方法は、特にその適用を制限
するものではないが水流が比較的遅く、沈殿物が仕切り
壁まで流れないような場合に好適である。尤も、継続的
に吸引ポンプで吸引していなければ沈殿物が外部に流出
してしまうので、前記仕切り壁を設置する(1)の方法
と併用することが望ましい。
The method (2) is not particularly limited, but is suitable for the case where the water flow is relatively slow and the sediment does not flow to the partition wall. However, if the suction is not continuously performed by the suction pump, the sediment flows out. Therefore, it is desirable to use the method together with the method (1) of installing the partition wall.

【0022】(3) 空間部の水下側に開閉可能な仕切
り壁(以下、前記固定式の仕切り壁と区別するためにス
ライド式仕切り壁という)を設ける。このスライド式仕
切り壁をを閉塞した状態で沈殿物をスライド式仕切り壁
の水上側近傍に集積させる点では前記固定式の仕切り壁
と同様であるが、このスライド式仕切り壁の水下側に回
収容器を設置した状態でスライド式仕切り壁を開放し、
回収容器に沈殿物を導入して回収する。この回収容器と
しては、一般的に目の細かな網材からなるものが用いら
れる。
(3) A partition wall that can be opened and closed (hereinafter, referred to as a sliding partition wall to distinguish it from the fixed partition wall) is provided below the space below the water. This is similar to the fixed partition wall in that the sediment is collected near the upper side of the slide partition wall in a state where the slide partition wall is closed, but is collected below the slide partition wall. With the container installed, open the sliding partition wall,
The precipitate is introduced into the collection container and collected. As the collection container, a container made of fine mesh material is generally used.

【0023】この(3)の方法は、特にその適用を制限
するものではないが流水中に汚損物質を多量に含有する
し尿浄化処理などに好適である。例えば前記スライド式
仕切り壁を設置せずに空間部の水下側に回収容器を常設
しておいた場合には、回収容器を構成する網材の微細空
隙が流水中に含まれる沈殿物で速やかに閉塞され、流水
自体を閉塞してしまうことになる。しかし、前述のよう
に開閉可能なスライド式仕切り壁を設け、沈殿物を集積
させた後、回収容器を設置してスライド式仕切り壁を開
放すると、回収容器には流水と共に多量の沈殿物が導入
されるので、前記と同様に回収容器を構成する網材の微
細空隙が沈殿物で閉塞されるものの回収容器を取り外し
て多量の沈殿物を回収することができる。
The method (3) is not particularly limited in its application, but is suitable for the purification of human waste containing a large amount of fouling substances in running water. For example, when the collection container is permanently installed below the space without installing the sliding partition wall, the fine voids of the mesh material constituting the collection container are quickly formed by sediment contained in the running water. And the running water itself will be blocked. However, as described above, a sliding partition that can be opened and closed is provided, and after collecting sediment, a collection container is installed and the sliding partition is opened, and a large amount of sediment is introduced into the collection container along with running water. Therefore, although the fine voids of the mesh material constituting the collection container are closed by the precipitate in the same manner as described above, a large amount of precipitate can be collected by removing the collection container.

【0024】このように本発明の水質浄化方法では、汚
損物質の沈殿物を空間部に沈降させてこの空間部から流
水路外へ排出するので、ろ材間に沈殿物を滞留させるこ
とがなく、ろ過作用が短期間に失われることがない。し
たがって、継続的に水質浄化が行われるものとなる。ま
た、ろ材の表面、ろ材間には微生物が生息し、微生物増
殖の場となるが、適当に水流が緩められ、且つ流水が滞
留して澱むことがなく新鮮な水流が供給されるので、微
生物による水質浄化も活発に行われる。特にろ材として
土系材料を主成分とする多孔質体を用いたので、吸着性
に優れ、その表面、ろ材間ばかりでなく、ろ材の内部も
微生物の棲家となり、この微生物が有機物を酸化分解さ
せる。さらに、ろ材を構成する土系材料中には、当初又
は形成後から微生物が生息していて、流水中の有機物を
酸化分解する。そのため、流水中に含まれる浮遊懸濁物
質(SS)、生物的酸素要求量(BOD)、化学的酸素
要求量(COD)、全リン(T−P)、全窒素(T−
N)の各数値を低下させ、水質を改善することができ
る。
As described above, in the water purification method of the present invention, the sediment of the fouling substance is settled in the space and discharged from the space out of the flowing water channel, so that the sediment does not stay between the filter media. Filtration is not lost in a short time. Therefore, water purification is performed continuously. In addition, microorganisms inhabit the surface of the filter medium and between the filter media, and provide a place for microbial growth.However, the water flow is appropriately relaxed, and the fresh water flow is supplied without stagnant due to stagnant running water. Water purification is also actively carried out. In particular, since a porous material containing an earth-based material as the main component is used as a filter material, it has excellent adsorptivity, and not only the surface and between the filter materials, but also the inside of the filter material becomes a home for microorganisms, and these microorganisms oxidize and decompose organic substances. . Furthermore, microorganisms inhabit the soil-based material constituting the filter medium from the beginning or after the formation, and oxidatively decompose organic substances in running water. Therefore, suspended suspended solids (SS), biological oxygen demand (BOD), chemical oxygen demand (COD), total phosphorus (TP), total nitrogen (T-
N) can be reduced to improve the water quality.

【0025】さらに、本発明の水質浄化方法では、前述
のようにろ過作用が継続的に維持されて水質浄化が行わ
れるので、従来のようにろ材を頻繁に交換する必要がな
い。特にろ材として土系材料を主成分とする多孔質体を
用いたので、交換したろ材は重機等で容易に粉砕するこ
とができ、土にかえしたり、盛り土等の建築現場に再利
用することもできる。加えて、粉砕物中にはセメント含
有量が少なく、しかも土系材料中にはリン、窒素が含ま
れているので、肥料として再利用することもできる。さ
らに、前述のように土系材料としてヘドロや軟弱土を用
いることができ、粉砕後には道路基礎等に適用すること
ができるので、この場合、地盤改良や環境問題にも貢献
するものとなる。
Further, according to the water purification method of the present invention, since the water purification is carried out while the filtration action is continuously maintained as described above, it is not necessary to frequently replace the filter medium as in the conventional case. In particular, since a porous material mainly composed of an earth-based material was used as the filter medium, the replaced filter medium can be easily crushed by heavy equipment, etc., and can be returned to soil or reused at construction sites such as embankment. it can. In addition, since the pulverized material has a low cement content and the soil material contains phosphorus and nitrogen, it can be reused as fertilizer. Furthermore, as described above, sludge or soft soil can be used as an earth-based material, and can be applied to a road foundation or the like after pulverization. In this case, it also contributes to ground improvement and environmental problems.

【0026】また、本発明の水質浄化装置は、流水路中
に常設する浄化機構と、排出機構とからなり、排出機構
は、適宜時期に取り付けるものでもよいし、浄化機構と
同様に常設するものでもよく、両者を組み合わせてなる
ものでもよい。浄化機構を構成するろ材、透水性収容
体、空間部形成手段(脚部や載置台など)については前
述の通りである。排出機構は、前記(1)の方法では
(固定式)仕切り壁及び吸引ポンプ(吸引パイプ等を含
む)であり、前記(2)の方法では貫通孔及び吸引ポン
プ(吸引パイプ等を含む)であり、本発明の前記(3)
の方法ではスライド式仕切り壁及び回収容器である。
尚、(固定式)仕切り壁、貫通孔、スライド式仕切り壁
は、それ自体には沈殿物を排出する作用はないが、排出
を補助或いは効率化するものであるから、排出機構に含
める。このように本発明の水質浄化装置は、極めて簡易
な設備構成で水質浄化を図ることができる。
Further, the water purification apparatus of the present invention comprises a purifying mechanism permanently installed in a flowing water channel and a discharging mechanism, and the discharging mechanism may be attached at an appropriate time, or may be permanently installed similarly to the purifying mechanism. Or a combination of the two. The filter medium, the water-permeable container, and the space section forming means (legs, mounting table, etc.) constituting the purification mechanism are as described above. The discharge mechanism includes a (fixed) partition wall and a suction pump (including a suction pipe) in the method (1), and a through hole and a suction pump (including a suction pipe and the like) in the method (2). Yes, said (3) of the present invention
In the method (1), a sliding partition wall and a collecting container are used.
The (fixed) partition wall, the through hole, and the slide partition wall have no function of discharging the sediment by themselves, but they are included in the discharging mechanism because they assist or discharge the sediment. As described above, the water purification device of the present invention can purify water with an extremely simple facility configuration.

【0027】また、本発明の水質浄化方法及び水質浄化
装置を適用する流水路としては、河川や農業用の用水
路、家庭用、学校用、食品事業場用、畜産事業施設用、
海水等の廃水処理施設の流路等がある。例えば狭幅の河
川(小川)や各種施設の人工水路等の比較的幅が狭い流
水路では、透水性収容体の寸法等を調整して流水路の幅
一杯に透水性収容体を配設してもよい。また、一般的な
河川等の比較的幅が広い流水路では、流水の流れ方向に
沿う長尺な側壁を適当な間隔で左右に配設し、該側壁間
に透水性収容体が位置するように配設してもよい。尚、
この側壁は前記仕切り壁と同様な材料で形成されるが、
透水性収容体の横方向からの沈殿物の漏出を防止するた
め、一般的には配設した透水性収容体の上端より高くな
るように設置する。
The running water channel to which the water purification method and the water purification device of the present invention are applied includes rivers, agricultural waterways, homes, schools, food establishments, livestock establishments, and the like.
There is a channel for wastewater treatment facilities such as seawater. For example, in relatively narrow waterways such as narrow rivers (rivers) and artificial waterways of various facilities, the size of the water-permeable container is adjusted, and the water-permeable containers are arranged to fill the width of the waterway. You may. Also, in a relatively wide flowing water channel such as a general river, long side walls along the flow direction of flowing water are disposed on the left and right at appropriate intervals, and the permeable container is positioned between the side walls. May be arranged. still,
This side wall is formed of the same material as the partition wall,
In order to prevent the sediment from leaking from the lateral direction of the water-permeable container, the water-permeable container is generally installed so as to be higher than the upper end of the disposed water-permeable container.

【0028】尚、水流が激しい河川等に敷設する場合な
どには、上流側に水圧を抑制する壁材やその他の構成を
追加、設置するようにしても良い。
In the case of laying in a river or the like where the water flow is strong, a wall material for suppressing water pressure and other components may be additionally provided on the upstream side.

【0029】[0029]

【実施例】以下に、図面の実施例に基づいて本発明を説
明する。透水性収容体2は、図1に示すように4本の脚
部5を有して自立できる構成であるため、配設時にはそ
の下方に空間部6が形成される。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below with reference to the embodiments shown in the drawings. As shown in FIG. 1, the water-permeable container 2 has four legs 5 and can stand on its own, so that a space portion 6 is formed below the water-permeable container 2 at the time of disposition.

【0030】尚、ろ材1は、砂質土1kgに対してセメ
ント系固化剤『ジオライト』(秩父小野田(株)製固化
剤)0.2kg、水200ccを配合し、混練して径5
0mmの球形に成形した。また、透水性収容体2は、図
1に示すようにアングル材(柵材)を枠状に組み立てて
4側面及び底面に金網を張設した構成である。
The filter medium 1 was prepared by mixing 0.2 kg of cement-based solidifying agent "Geolite" (solidifying agent manufactured by Chichibu Onoda Co., Ltd.) and 200 cc of water with 1 kg of sandy soil, and kneading the mixture to a diameter of 5 kg.
It was formed into a spherical shape of 0 mm. Further, as shown in FIG. 1, the permeable container 2 has a configuration in which an angle member (fence member) is assembled in a frame shape and wire meshes are stretched on four side surfaces and a bottom surface.

【0031】図2及び図3は、し尿浄化装置(循環型曝
気処理装置)に本発明の水質浄化方法及び水質浄化装置
を適用した例を示すものであり、Bはし尿受け入れ槽、
Cは水路、Dは曝気層、Eはポンプ、Fは循環ポンプ装
置である。この例では、水路Cの幅と一致する幅寸法の
透水性収容体2”を用い、空間部6の最先端側及び最終
端側にスライド式仕切り壁12を設けた。このスライド
式仕切り壁12は、ここでは上下方向にスライド可能な
構成とした。また、常設せずに沈殿物の回収時に取り付
ける回収容器13は、図4に示すようにアングル材と金
網とを組み合わせて形成され、水路Cの横幅より広幅に
形成される。この回収容器13は、上方に設けた取付部
14によって曝気槽Dの水上側壁面の上端に容易に着脱
することができ、最下方に設けた堆積部15に、上方前
面側に形成した導入口16から沈殿物を含む流水を導入
して沈殿物を堆積させる。また、堆積部15の背面側に
は開閉可能な扉17が設けられ、取り外した後に堆積し
た沈澱物を堆積部15から取り出すことができる。
FIGS. 2 and 3 show an example in which the water purification method and the water purification apparatus of the present invention are applied to a human waste purification apparatus (circulation type aeration processing apparatus).
C is a water channel, D is an aeration layer, E is a pump, and F is a circulation pump device. In this example, a water-permeable container 2 ″ having a width corresponding to the width of the water channel C is used, and a sliding partition wall 12 is provided on the most distal end side and the last end side of the space 6. This sliding partition wall 12 is provided. In this case, the collection container 13 which is slidable up and down without being permanently installed is formed by combining an angle material and a wire mesh as shown in FIG. The collection container 13 can be easily attached to and detached from the upper end of the water-side wall surface of the aeration tank D by the mounting portion 14 provided above, and is attached to the lowermost deposition portion 15. The sediment is deposited by introducing running water containing the sediment from the inlet 16 formed on the upper front side, and a door 17 that can be opened and closed is provided on the back side of the depositing section 15, and is deposited after being removed. The precipitate is removed from the depositing section 15 It can be issued.

【0032】この図2及び図3の例において、スライド
式仕切り壁12を閉塞した状態でし尿受け入れ槽Bから
曝気槽Dへ向けて水路Cに被処理水を流すと、流水中に
含まれる汚損物質が沈殿物となって透水性収容体2”か
ら空間部6に入り、水流と共に流下し、スライド式仕切
り壁12に堰き止められ、集積される。十分に沈殿物が
集積したら、前記回収容器13を取り付け、スライド式
仕切り壁12を上方にスライド移動させて開放する。こ
のスライド式仕切り壁12の開放により、沈殿物を高濃
度に含有する流水が導入口16から堆積部15に入り、
捕獲される。この回収容器13は前述のように系外に取
り外して扉17を開放することにより、沈殿物を取り出
すことができる。
In the example shown in FIGS. 2 and 3, when the water to be treated flows from the urine receiving tank B to the aeration tank D in the water channel C with the sliding partition wall 12 closed, the contamination included in the running water is reduced. The substance as a precipitate enters the space 6 from the water-permeable container 2 ″, flows down with the water flow, is blocked by the sliding partition wall 12, and is accumulated. The slide type partition wall 12 is slid upward to open the slide type partition wall 12. With the opening of the slide type partition wall 12, running water containing a high concentration of sediment enters the accumulation part 15 from the inlet 16 through the inlet 16.
Captured. The sediment can be taken out by removing the collecting container 13 outside the system and opening the door 17 as described above.

【0033】沈殿物が除去された流水は、スライド式仕
切り壁12を乗り越えて曝気槽Dに落下し、その際、空
気を巻き込むので、曝気槽D内の被処理水に空気(酸
素)を供給する。そして、曝気槽Dに設置されたポンプ
Eから循環ポンプ装置Fを通してし尿受け入れ槽Bに被
処理水を還流することにより、循環、曝気、水質浄化が
繰り返される。
The running water from which the sediment has been removed climbs over the sliding partition wall 12 and falls into the aeration tank D. At this time, the air is entrained, so that air (oxygen) is supplied to the water to be treated in the aeration tank D. I do. Then, by circulating the water to be treated from the pump E installed in the aeration tank D to the human waste receiving tank B through the circulation pump device F, the circulation, aeration and water purification are repeated.

【0034】[浄化試験1] 試験に用いた浄化水路は、循環型のし尿浄化装置と略同
様であり、細長の水路にろ材を充填した透水性収容体
(脚部付き)を、その下方に空間部が形成されるように
配置した。そして水中ポンプにより、水流を調節できる
ようにした。また、ろ材は、砂質土1kgに対してセメ
ント系固化剤『ジオライト』(秩父小野田(株)製固化
剤)0.2kg、水200ccを配合し、混練して径5
0mmの球形に成形した「球形ろ材」と、40〜60m
mの砕石からなる「レキ状ろ材」の2種を用いた。そし
て、予め調製した原水を浄化処理し、2週間後のss、
COD、T−N、T−Pの変化を測定した。その結果を
表1に示した。
[Purification Test 1] The purification water channel used for the test is substantially the same as that of a circulation type night soil purification device, and a permeable container (with legs) in which an elongate water channel is filled with a filter medium is placed underneath. They were arranged so that a space was formed. The water flow could be adjusted by a submersible pump. The filter medium was prepared by mixing 0.2 kg of cement-based solidifying agent “Geolite” (solidifying agent manufactured by Chichibu Onoda Co., Ltd.) and 200 cc of water with 1 kg of sandy soil, and kneading the mixture to a diameter of 5 kg.
"Spherical filter media" molded into a spherical shape of 0 mm, 40-60 m
Two types of “Reki-like filter media” consisting of m crushed stones were used. Then, the raw water prepared in advance is purified, and ss after 2 weeks,
Changes in COD, TN, and TP were measured. The results are shown in Table 1.

【表1】 [Table 1]

【0035】表1より明らかなように、ろ材が土系材料
を固化した球形ろ材であっても、砕石からなるレキ状ろ
材であっても、水質が改善され、一般河川に放流可能な
値となることが確認された。また、土系材料を固化した
球形ろ材を用いた方が、砕石からなるレキ状ろ材よりも
浄化効果が高いことが確認された。また、別途ろ材を水
路上に直接敷設、堆積して同様の試験を行ったところ、
ろ材表面及びろ材間に沈殿物が滞留し、2〜4週間程度
で浄化効果が失われてしまうことが確認された。
As is clear from Table 1, whether the filter medium is a spherical filter medium obtained by solidifying an earth-based material or a reciprocating filter medium made of crushed stone, the water quality is improved and the value that can be discharged to a general river is determined. It was confirmed that it became. It was also confirmed that the use of a spherical filter medium obtained by solidifying an earth-based material had a higher purification effect than the use of a crushed stone filter medium. In addition, when a separate filter medium was laid directly on the water channel and deposited, and a similar test was performed,
It was confirmed that sediment stayed on the surface of the filter medium and between the filter media, and the purification effect was lost in about 2 to 4 weeks.

【0036】[浄化試験2] 原水としてし尿を用い、前記図2及び図3の循環型し尿
処理装置(曝気処理装置)をそのまま用いて浄化試験を
実施した。そして、1週間ごとに6週後までBODの変
化を測定すると共に6週間後のpH、ss、T−N、T
−Pの変化を測定した。その結果を表2に示した。
[Purification Test 2] Purification test was performed using human waste as raw water and using the circulation type human waste treatment apparatus (aeration treatment apparatus) shown in FIGS. 2 and 3 as it is. The change in BOD was measured every week until 6 weeks later, and the pH, ss, TN, T
The change in -P was measured. The results are shown in Table 2.

【表2】 [Table 2]

【0037】表2より明らかなように、本発明をし尿の
浄化に適用しても良好な結果が得られることが確認され
た。また、別途ろ材を水路上に直接敷設、堆積して同様
の試験を行ったところ、ろ材表面及びろ材間に多量の沈
殿物が滞留し、1〜2週間程度で浄化効果が失われてし
まうことが確認された。
As is clear from Table 2, it was confirmed that good results were obtained even when the present invention was applied to purification of human urine. In addition, when the same test was performed by separately laying and depositing a filter medium directly on the water channel, a large amount of sediment stayed between the filter medium surface and the filter medium, and the purification effect was lost in about 1 to 2 weeks. Was confirmed.

【0038】以上本発明を実施例に基づいて説明した
が、本発明は前記した実施例に限定されるものではな
く、特許請求の範囲に記載した構成を変更しない限りど
のようにでも実施することができる。
Although the present invention has been described based on the embodiments, the present invention is not limited to the above-described embodiments, and may be implemented in any way unless the configuration described in the claims is changed. Can be.

【0039】[0039]

【発明の効果】以上要するに本発明の水質浄化方法で
は、汚損物質の沈殿物を空間部に沈降させてこの空間部
から流水路外へ排出するので、ろ材間に沈殿物を滞留さ
せることがなく、ろ過作用が短期間に失われることがな
い。したがって、継続的に水質浄化が行われるものとな
る。また、ろ材の表面、ろ材間には微生物が生息し、微
生物増殖の場となるが、適当に水流が緩められ、且つ流
水が滞留して澱むことがなく新鮮な水流が供給されるの
で、微生物による水質浄化も活発に行われる。さらに、
本発明の水質浄化方法では、ろ過作用が継続的に維持さ
れて水質浄化が行われるので、従来のようにろ材を頻繁
に交換する必要がない。
In summary, in the water purification method of the present invention, the sediment of the fouling substance is settled in the space and discharged from the space out of the flowing water channel, so that the sediment is not retained between the filter media. The filtration action is not lost in a short time. Therefore, water purification is performed continuously. In addition, microorganisms inhabit the surface of the filter medium and between the filter media, and provide a place for microbial growth.However, the water flow is appropriately relaxed, and the fresh water flow is supplied without stagnant due to stagnant running water. Water purification is also actively carried out. further,
In the water purification method of the present invention, since the water purification is performed while the filtering action is continuously maintained, it is not necessary to frequently replace the filter medium as in the related art.

【0040】特にろ材として土系材料を主成分とする多
孔質体を用いたので、吸着性に優れ、その表面、ろ材間
ばかりでなく、ろ材の内部も微生物の棲家となり、この
微生物が有機物を酸化分解させる。さらに、ろ材を構成
する土系材料中には、当初又は形成後から微生物が生息
していて、流水中の有機物を酸化分解する。そのため、
流水中に含まれる浮遊懸濁物質(SS)、生物的酸素要
求量(BOD)、化学的酸素要求量(COD)、全リン
(T−P)、全窒素(T−N)の各数値を低下させ、水
質を改善することができる。さらに、一定期間使用して
交換したろ材は重機等で容易に粉砕することができ、土
にかえしたり、盛り土等の建築現場に再利用することも
できる。加えて、粉砕物中にはセメント含有量が少な
く、しかも土系材料中にはリン、窒素が含まれているの
で、肥料として再利用することもできる。さらに、前述
のように土系材料としてヘドロや軟弱土を用いることが
でき、粉砕後には道路基礎等に適用することができるの
で、この場合、地盤改良や環境問題にも貢献するものと
なる。
In particular, since a porous material mainly composed of an earth-based material is used as a filter material, it has excellent adsorptivity, and not only the surface and between the filter materials, but also the inside of the filter material becomes a home for microorganisms, and the microorganisms remove organic matter. Oxidatively decomposes. Furthermore, microorganisms inhabit the soil-based material constituting the filter medium from the beginning or after the formation, and oxidatively decompose organic substances in running water. for that reason,
Suspended suspended solids (SS), biological oxygen demand (BOD), chemical oxygen demand (COD), total phosphorus (TP), total nitrogen (TN) contained in running water Water quality can be reduced. Further, the filter medium used and exchanged after being used for a certain period can be easily crushed by a heavy machine or the like, and can be returned to soil or reused at a construction site such as embankment. In addition, since the pulverized material has a low cement content and the soil material contains phosphorus and nitrogen, it can be reused as fertilizer. Furthermore, as described above, sludge or soft soil can be used as an earth-based material, and can be applied to a road foundation or the like after pulverization. In this case, it also contributes to ground improvement and environmental problems.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明に用いる透水性収容体の一例を示す斜視
図である。
FIG. 1 is a perspective view showing an example of a water-permeable container used in the present invention.

【図2】循環型曝気処理装置への適用例を示す平面図で
ある。
FIG. 2 is a plan view showing an example of application to a circulation type aeration apparatus.

【図3】図2の側面図である。FIG. 3 is a side view of FIG. 2;

【図4】(a)図2の装置に取り付ける着脱式の回収装
置を示す斜視図、(b)その側面図である。
4 (a) is a perspective view showing a detachable collection device attached to the device of FIG. 2, and FIG. 4 (b) is a side view thereof.

【符号の説明】[Explanation of symbols]

1 ろ材 2 透水性収容体 5 脚部(空間部形成手段) 6 空間部 DESCRIPTION OF SYMBOLS 1 Filter medium 2 Permeable container 5 Leg part (space part formation means) 6 Space part

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B01D 24/02 - 24/26 B01D 39/00 - 39/20 C02F 3/02 - 3/10 ──────────────────────────────────────────────────の Continued on the front page (58) Field surveyed (Int. Cl. 7 , DB name) B01D 24/02-24/26 B01D 39/00-39/20 C02F 3/02-3/10

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 粘土、シルト、砂質土、ヘドロ、軟弱
土、或いはこれらを組み合わせた土系材料100重量部
と、セメントと固化剤又はセメント系固化剤から選ばれ
る一種以上の材料10〜35重量部とからなる多数のろ
材を透水性収容体に充填した状態で、その下方に空間部
が形成されるように流水路中に設置し、且つ透水性収容
体を長さ方向に並列させることにより上方に長さ方向に
連続するろ材の充填層を形成すると共に下方に長さ方向
に連続する空間部を形成し、空間部の水下側に開閉可能
な仕切り壁を設け、流水中に含まれる汚損物質をろ材に
より捕捉、沈澱させ、前記透水性収容体内から空間部に
沈降した沈殿物を仕切り壁を閉塞した状態で沈殿物を仕
切り壁の水上側近傍に集積させ、その水下側に回収容器
を設置した状態で仕切り壁を開放して回収容器に沈殿物
を導入して回収することを特徴とする水質浄化方法。
1. Clay, silt, sandy soil, sludge, softness
100 parts by weight of earth or earth-based material combining these
And, selected from cement and solidifying agent or cement-based solidifying agent
In a state in which a large number of filter media composed of 10 to 35 parts by weight of one or more materials are filled in a water-permeable container, the water-permeable container is installed in a flowing water channel so that a space is formed below the medium, and Are formed in parallel in the length direction to form a packed layer of filter media that is continuous in the length direction at the top and a space that is continuous in the length direction below, and can be opened and closed under the water below the space
A separate partition wall is provided, and fouling substances contained in running water are captured and settled by a filter medium, and sediment that has settled out of the water-permeable container into the space is separated from the sediment with the partition wall closed.
It is collected near the upper side of the cut wall and the collection container is located below the lower side of the water.
Open the partition wall with
A water purification method characterized by introducing and recovering water.
【請求項2】 粘土、シルト、砂質土、ヘドロ、軟弱
土、或いはこれらを組み合わせた土系材料100重量部
と、セメントと固化剤又はセメント系固化剤から選ばれ
る一種以上の材料10〜35重量部とからなる多数のろ
材と、該ろ材を充填すると共に長さ方向に並列させる透
水性収容体と、該透水性収容体を流水路に設置した際に
上方に長さ方向に連続するろ材の充填層を形成すると共
に下方に長さ方向に連続する空間部を形成されるための
空間部形成手段とを備えて流水路中に常設される浄化機
構、及び空間部の水下側に開閉可能な仕切り壁を設け、
前記空間部の沈殿物を仕切り壁を閉塞した状態で沈殿物
を仕切り壁の水上側近傍に集積させ、その水下側に回収
容器を設置した状態で仕切り壁を開放して回収容器に沈
殿物を導入して回収する排出機構からなることを特徴と
する水質浄化装置
2. Clay, silt, sandy soil, sludge, softness
100 parts by weight of earth or earth-based material combining these
And, selected from cement and solidifying agent or cement-based solidifying agent
Numerous filters consisting of 10 to 35 parts by weight of one or more materials
Media and a filter which is filled with the filter media and arranged in parallel in the longitudinal direction.
When the aqueous container and the permeable container are installed in a flowing water channel,
When a packed bed of filter media that is continuous in the length direction is formed
To form a continuous space in the length direction downward
Purifier permanently provided in the running water channel with space forming means
Provide a partition wall that can be opened and closed on the underside of the structure and space,
The sediment in the space portion with the partition wall closed
Is collected near the upper side of the partition wall and collected below the lower side.
With the container installed, open the partition wall and settle in the collection container.
It has a discharge mechanism that introduces and collects artifacts.
Water purification equipment .
JP10260463A 1998-09-14 1998-09-14 Water purification method and water purification device Expired - Fee Related JP3062883B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Application Number Priority Date Filing Date Title
JP10260463A JP3062883B2 (en) 1998-09-14 1998-09-14 Water purification method and water purification device

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Publication Number Publication Date
JP2000084308A JP2000084308A (en) 2000-03-28
JP3062883B2 true JP3062883B2 (en) 2000-07-12

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ID=17348306

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Country Link
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5049475B2 (en) * 2005-08-29 2012-10-17 株式会社総合開発 Water purification equipment

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