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JPH0427920B2 - - Google Patents
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JPH0427920B2 - - Google Patents

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Publication number
JPH0427920B2
JPH0427920B2 JP63052703A JP5270388A JPH0427920B2 JP H0427920 B2 JPH0427920 B2 JP H0427920B2 JP 63052703 A JP63052703 A JP 63052703A JP 5270388 A JP5270388 A JP 5270388A JP H0427920 B2 JPH0427920 B2 JP H0427920B2
Authority
JP
Japan
Prior art keywords
water
flow channel
flow
aquatic plants
channel
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 - Lifetime
Application number
JP63052703A
Other languages
Japanese (ja)
Other versions
JPH01228598A (en
Inventor
Tokuo Suzuki
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
BERU TEKUNIKARU KANPANII JUGEN
Original Assignee
BERU TEKUNIKARU KANPANII JUGEN
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by BERU TEKUNIKARU KANPANII JUGEN filed Critical BERU TEKUNIKARU KANPANII JUGEN
Priority to JP5270388A priority Critical patent/JPH01228598A/en
Publication of JPH01228598A publication Critical patent/JPH01228598A/en
Publication of JPH0427920B2 publication Critical patent/JPH0427920B2/ja
Granted legal-status Critical Current

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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention] 【産業上の利用分野】[Industrial application field]

本発明は、流水路の水面に水生植物または水上
で生育可能な他の維管束植物を用いて、窒素、リ
ンなどの栄養塩類で富栄養化された河川、湖沼な
どの水又は雑排水などの原水を処理する水処理装
置に関するものである。
The present invention uses aquatic plants or other vascular plants that can grow on water on the water surface of a waterway to remove water from rivers, lakes, etc. or gray water that is eutrophic with nutrients such as nitrogen and phosphorus. The present invention relates to a water treatment device that processes raw water.

【従来技術】[Prior art]

家庭用雑排水、下水、工場排水、田畑の農耕水
等各種汚水が流入する河川や湖沼、池あるいは人
工的な池、噴水池、排水溝、貯水槽等において
は、前記汚水中に含まれる浮遊懸濁物ならびに有
機物及び窒素、リン等の栄養塩類により、富栄養
化され、水質が悪化し、魚類の生息が不可能にな
り、さらにその水質を悪化させるという問題があ
る。 なぜなら、前記汚水によつて汚染された水(以
下本発明では「原水」という)は富栄養化してプ
ランクトン等が大量に発生し、水中の酸素不足に
よつて死滅した魚類やプランクトン類の遺体の沈
降、堆積によつて底泥の泥質がヘドロ化し、死滅
した魚類やプランクトンは酸素分解されるため、
溶存酸素(DO)は消費され酸素不足の状態とな
り、この酸欠状態が起きるとH2Sが発生しはじ
め、同時に鉄、マンガン、窒素、リンが溶出する
からである。 したがつて、前記原水の富栄養化を停止させる
ためには水底に酸素を供給し、栄養塩類等の溶出
を防止すること、あるいは底泥から溶出した栄養
塩類を何らかの方法で除去することが必要であ
る。 溶出した栄養塩類を除去する一般的な手段とし
ては、底泥をかき寄せ集め、ポンプ等にて吸い上
げ、吸い上げた汚泥を濃縮して固形物を作つて廃
棄するなどの機械的な手段と、硫酸バンド等の凝
集剤を投入してリンと難溶性化合物を生成し不活
性化したり、あるいは塩素等による滅菌による化
学的手段が知られている。 しかし、前者の機械的な処理手段では大規模な
装置を必要とし、後者の化学的な処理手段では、
化学的処理装置や多量の凝集剤が必要となり、魚
類や他の生物の生息に不向きである。そして、両
者ともに最観上も好ましくない。 さらに、富栄養化現象が起きると植物の三大栄
養素と光合成の作用により藻が発生し、透明度を
悪くするが、発生した藻は微生物であるので濾過
しても完全に除去できないという問題があつた。 そこで、浮遊性または挺水生の水草、たとえば
ホテイアオイやオランダガラシ、または水上で生
育可能な他の維管束植物を一過性または循環する
水路の水面下に設けた網状容器内に植え込み、水
中に発達した根の周辺に形成する根圏微生物群の
活動を主体として原水を処理する装置がいくつか
開示されている。(例えば特公昭62−28720号参
照) 前記水生植物の水中根の周辺に形成する根圏微
生物群の活動を主体として原水を浄化する装置
(以下本発明では「水生植物による処理装置」と
いう)においては、流入した原水中の栄養塩類等
の栄養物を植物の水中根に有効に付着せしめれ
ば、根圏微生物の活性を高め、原水中の栄養物の
吸収が促進されるので、原水の処理効果を高める
ことができる。
In rivers, lakes, ponds, artificial ponds, fountain ponds, drainage ditches, water storage tanks, etc., into which various types of wastewater such as domestic gray water, sewage, industrial wastewater, and agricultural water from fields flow, the suspended solids contained in the wastewater are Turbid matter, organic matter, and nutrient salts such as nitrogen and phosphorus cause eutrophication, deteriorating water quality, making it impossible for fish to live there, and further deteriorating the water quality. This is because the water contaminated by the sewage (hereinafter referred to as "raw water" in the present invention) becomes eutrophic and generates a large amount of plankton, etc., and the remains of fish and plankton that die due to lack of oxygen in the water. Due to sedimentation and sedimentation, the muddy bottom mud turns into sludge, and dead fish and plankton are decomposed with oxygen.
This is because dissolved oxygen (DO) is consumed, resulting in an oxygen-deficient state, and when this oxygen-deficient state occurs, H 2 S begins to be generated, and at the same time, iron, manganese, nitrogen, and phosphorus are eluted. Therefore, in order to stop the eutrophication of the raw water, it is necessary to supply oxygen to the bottom of the water to prevent the leaching of nutrients, etc., or to remove the nutrient salts eluted from the bottom mud by some method. It is. Common methods for removing eluted nutrient salts include mechanical means such as scraping and collecting bottom sludge, sucking it up with a pump, etc., concentrating the sucked up sludge to create a solid substance, and disposing of it, and sulfuric acid band. Chemical methods are known, such as adding a flocculant such as to generate phosphorus and a poorly soluble compound to inactivate it, or sterilizing with chlorine or the like. However, the former mechanical treatment method requires large-scale equipment, and the latter chemical treatment method requires
It requires chemical treatment equipment and large amounts of flocculants, making it unsuitable for fish and other organisms. And both are undesirable from a superficial perspective. Furthermore, when eutrophication occurs, algae grow due to the action of the three major plant nutrients and photosynthesis, impairing transparency, but since the algae that grow are microorganisms, there is a problem that they cannot be completely removed even by filtration. Ta. Therefore, floating or aquatic aquatic plants, such as water hyacinth and water hyacinth, or other vascular plants that can grow on water, are planted in mesh containers placed below the water surface of ephemeral or circulating waterways, allowing them to develop underwater. Several devices have been disclosed that treat raw water mainly through the activities of rhizosphere microorganisms that form around the roots. (For example, see Japanese Patent Publication No. 62-28720.) In an apparatus for purifying raw water mainly through the activities of rhizosphere microorganisms formed around the underwater roots of aquatic plants (hereinafter referred to as "aquatic plant treatment apparatus" in the present invention). If nutrients such as nutrient salts in the inflowing raw water are effectively attached to the underwater roots of plants, the activity of rhizosphere microorganisms will be increased and the absorption of nutrients in the raw water will be promoted. The effect can be increased.

【発明が解決しようとする課題】[Problem to be solved by the invention]

従来の水生植物による水処理装置においては、
流入した原水中の栄養物を植物の水中根に有効に
付着せしめるために、流水路の底部の流水に適度
の乱流を起こすための阻止体、たとえば砂利や阻
止板を設け、乱流の一部が植物の水中根域を緩や
かに流れるようにしている。 しかし、この手段では、有効な根圏微生物のコ
ロニーを発達させるためには、植物の根を流下す
る原水を有効に上下に混合させるためにかなり激
しい乱流を起こさなければならず、そのためにす
でに形成した根圏微生物のコロニーが剥離する危
険がある。しかも、この手段では、水路の随所に
配置した乱流を起こす物体の大きさ、原水の流
量、流速、植物の根の発育による水路面積の変化
等によつて乱流の発生状態が変化することもあ
り、阻止体を適性に配置することは難しく、水処
理の効果性も低いという問題点があつた。 さらに、この手段では、水路の上部に繁殖した
植物が水没するのを防止する網状容器の直下に水
中根が発達して密集すると、前記乱流によつて混
合された原水は、前記水中根の上と下の部分とで
は侵入状態が異なつてくるので、原水中の栄養物
の付着が効果的に行われず、結果的には栄養物の
吸収される効果が低いという問題点があつた。 さらに、この手段では乱流を起こすための阻止
体を水生植物の下面全体に渡つて設置する必要が
あり、費用も高いという問題点があつた。 本発明は、簡単な装置で原水の流水路に適度の
渦流を発生せしめ、原水中の栄養物を水生植物の
水中根に有効に付着せしめ、原水を効果的に処理
し、魚類、他生物が住むことができる程度の例え
ば、約0.5mの透明度の澄んだ中水を得るための
水生植物による水処理装置を提供することを目的
とする。
In conventional water treatment equipment using aquatic plants,
In order to effectively attach nutrients in the inflowing raw water to the underwater roots of plants, a barrier such as gravel or a blocking plate is installed to create appropriate turbulence in the flowing water at the bottom of the flow channel. This allows the water to flow gently through the underwater root zone of the plant. However, with this measure, in order to develop an effective rhizosphere microbial colony, fairly intense turbulence must be created to effectively mix the raw water flowing down the roots of the plant up and down, which is already There is a risk that the formed rhizosphere microbial colonies will peel off. Moreover, with this method, the state of turbulence may change depending on the size of objects that cause turbulence placed throughout the waterway, the flow rate and velocity of raw water, changes in the waterway area due to the growth of plant roots, etc. Therefore, there were problems in that it was difficult to properly arrange the blocking body, and the effectiveness of water treatment was low. Furthermore, with this method, when underwater roots develop and become densely concentrated directly under the mesh container that prevents the plants that have grown in the upper part of the waterway from being submerged, the raw water mixed by the turbulence flows through the underwater roots. Since the penetration conditions are different between the upper and lower parts, there is a problem that the nutrients in the raw water do not adhere effectively, and as a result, the effectiveness of nutrients being absorbed is low. Furthermore, this method requires a blocker to be installed over the entire lower surface of the aquatic plants to create turbulent flow, and is expensive. The present invention uses a simple device to generate an appropriate eddy current in a raw water channel, effectively attaching nutrients in the raw water to the underwater roots of aquatic plants, effectively treating the raw water, and preventing fish and other organisms from growing. The purpose of the present invention is to provide a water treatment device using aquatic plants for obtaining clear gray water with a transparency of about 0.5 m, which is livable.

【課題を解決するための手段】[Means to solve the problem]

上記目的を解決するために、流水路に水生植物
を生育させて成る水処理装置において、前記流水
路内に、水生植物を植え付けた網状容器を複数
個、前記流水路の流壁を成す対向する両側壁の少
なくとも一方の側壁に適宜間隔を介して着脱自在
に設けると共に、前記各容器と対向する流水路の
他方の側壁との間に主流路を形成して、前記隣接
する容器間に渦流を発生するようにしたことを特
徴とするものである。 さらに、前記流水路内の流れの方向に流壁を成
す一又は複数の隔壁を設けて該一の隔壁及び前記
流水路の側壁間に、または前記複数の隔壁間に分
割流水路を形成すると共に、該分割流水路内に、
水生植物を植付けた網状容器を複数個、前記分割
流水路の流壁を成す少なくとも一方の前記側壁又
は隔壁に適宜間隔を介して着脱自在に設けると共
に、前記各容器と対向する分割流水路の側壁間に
主流路を形成して、前記隣接する容器間に渦流を
発生するようにしたことを特徴とするものであ
る。 また主流路を、対向する流壁すなわち、側壁及
び又は隔壁の両方に相対向して設けた各容器間に
形成するようにすれば、渦流が前記主流路の両側
で発生し、効果的な水処理ができる。 そして、前記流水路の底面に排泥手段を設ける
と水処理が効果的である。 さらに、前記水生植物を植付けた網状容器にフ
ツクを設け、該フツクを介して前記容器を前記流
水路又は分割流水路の側壁の上端に懸吊するとよ
い。
In order to solve the above object, in a water treatment device in which aquatic plants are grown in a water channel, a plurality of net-like containers in which aquatic plants are planted are placed in the water channel, and are arranged in opposing directions forming the flow walls of the water channel. A main channel is formed between each container and the other side wall of the opposing flow channel, and a vortex flow is generated between the adjacent containers. This feature is characterized in that it is made to occur. Further, one or more partition walls forming a flow wall in the direction of flow in the flow channel are provided to form a divided flow channel between the one partition wall and a side wall of the flow channel, or between the plurality of partition walls, and , in the divided flow channel,
A plurality of net-like containers planted with aquatic plants are removably installed at appropriate intervals on at least one of the side walls or partition walls forming the flow wall of the divided flow channel, and a side wall of the divided flow channel that faces each of the containers is provided. It is characterized in that a main flow path is formed between the containers to generate a vortex between the adjacent containers. In addition, if the main flow path is formed between containers that are provided oppositely to opposite flow walls, that is, both side walls and/or partition walls, vortices will be generated on both sides of the main flow path, and effective water flow will be achieved. Can be processed. Water treatment is effective when a mud draining means is provided at the bottom of the flow channel. Furthermore, it is preferable that a hook is provided on the net-like container in which the aquatic plants are planted, and the container is suspended from the upper end of the side wall of the flow channel or the divided flow channel via the hook.

【作用】[Effect]

流水路に原水を流入させると、流水路の上部か
ら見た原水の流れは流水路あるいは分割流水路の
少なくととも一方の前記流壁に取り付けた前記水
生植物を植え付けた網状容器と対向する流水路な
いしは分割流水路の流壁との間の主流路を通過す
ると、その流れの一部は前記容器を適宜間隔を介
して下流に取り付けている前記容器との間に流れ
込み、緩やかな渦状の乱流が発生する。前記水生
植物の水中根は網状容器の直下及び周囲に発達
し、原水中の栄養塩類などの栄養物は前記水中根
に付着し、根圏微生物のコロニーが形成され、微
生物によつて汚水中の有機物が分解され、前記水
中根から吸収される。この時発生する渦流は緩や
かに渦を巻きながら降下するので、すでに形成し
た根圏微生物のコロニーが剥離することなく原水
の栄養物は水中根の上下全体に渡つて、ほどよく
付着することになり、根圏微生物の活性は高めら
れ、原水の栄養物の吸収が効果的に促進される。 このようにして、前記流水路あるいは分割流水
路内の側壁または隔壁から成る流壁に前記水生植
物を植付けた網状容器を複数個設けているので、
流下した原水は次第に処理され、魚類、他の生物
が生息でき、且つこれを水上から観察できるほど
の約0.5mの透明度の澄んだ中水を得ることがで
きる。流水路を流下中に生物の作用によつて凝集
し粗大化した原水中の懸濁物は、前記水生植物の
水中根に付着せず、底面に落下すると、底面をゆ
つくりと押し流されることになるが、流水路の底
面に設けた排泥手段により、粗大化した落下懸濁
物は効果的に排出される。 また前記容器にフツクを設け、該フツクを前記
側壁及び隔壁から成る流壁の上端に懸吊すると、
前記容器を前記側壁から簡単に取り外すことが可
能となるので、繁茂した水生植物あるいは枯死し
た水生植物を容易に植替え可能となり、又倍養土
の取り替えも、根を除去することも簡単である。
When raw water flows into the flow channel, the flow of raw water seen from the upper part of the flow channel is such that the flow of raw water is opposite to the net-like container in which the aquatic plants are planted, which is attached to the flow wall of at least one of the flow channel or the divided flow channel. When the flow passes through the main channel between the channel or the flow wall of the divided flow channel, a portion of the flow flows between the container and the container attached downstream at an appropriate interval, creating a gentle vortex-like turbulence. A flow occurs. The underwater roots of the aquatic plants develop directly under and around the mesh container, and nutrients such as nutrient salts in the raw water adhere to the underwater roots, and a colony of rhizosphere microorganisms is formed, and the microorganisms Organic matter is decomposed and absorbed through the underwater roots. The vortex that is generated at this time descends in a gentle swirl, so the nutrients in the raw water are properly adhered to the entire upper and lower parts of the underwater roots, without causing the colonies of rhizosphere microorganisms that have already formed to separate. , the activity of rhizosphere microorganisms is enhanced, and the absorption of nutrients in raw water is effectively promoted. In this way, a plurality of net-like containers in which the aquatic plants are planted are provided on the flow wall consisting of the side wall or partition wall in the flow channel or divided flow channel.
The raw water that flows down is gradually treated, making it possible to obtain clear gray water with a transparency of about 0.5 m that allows fish and other organisms to live and to be observed from above. Suspended matter in the raw water that aggregates and becomes coarse due to the action of living things while flowing down the water channel does not attach to the underwater roots of the aquatic plants, and when it falls to the bottom, it is slowly washed away down the bottom. However, the coarse fallen suspended solids are effectively discharged by the mud draining means provided at the bottom of the flow channel. Further, when a hook is provided on the container and the hook is suspended from the upper end of the flow wall consisting of the side wall and the partition wall,
Since the container can be easily removed from the side wall, overgrown or dead aquatic plants can be easily replanted, and it is also easy to replace the doubling soil and remove roots. .

【実施例】【Example】

以下本発明の実施例について図面を参照して説
明すると、第2図において、窒素、リンなどの栄
養塩類で富栄養化された河川、湖沼などの水又は
雑排水などの原水が流れる流水路11の水面に、
浮遊性または挺水性の水草、たとえばホテイアオ
イやオランダガラシ又は水上で生育可能な他の維
管束植物などの水生植物16を生育させて、水中
に発達した根の周辺に形成する根圏微生物群の活
動を主体として、前記原水を処理する水処理装置
10において、前記流水路11に隔壁13を設け
て該隔壁13及び前記流水路11の側壁35を流
壁40とする分割流水路12を形成する。前記隔
壁13の上流側端と下流側端にはそれぞれ整流板
14,14′を流水路11の全断面に渡つて設け、
前記隔壁13を支持固定する。前記整流板14の
上流側には前記原水を前記各分割流水路12に分
配する分配池22を設け、前記整流板14′の下
流側には各分割流水路12で処理された水の集合
池23を設けてある。 前記分配池22に前記原水を送水するための導
入管20を配管し、前記集合池23内には前記処
理水を送水するための送水管21がポンプ24を
介して配置されている。 前記各分割流水路12内には、前記水生植物1
6を石、スポンジ、ロツクウールなど(土ではな
く、又、植物の種類によつて異なる)の培養土1
8と共に上部断面、四角形状を成すカゴ状の網状
容器15に植え込み、該網状容器15の上端に設
けたフツク19を介して複数個、前記分割流水路
12の流壁たる一方の前記側壁35を適宜間隔を
介して懸吊すると共に、前記各容器15と対向す
る分割流水路の側壁35との間に主流路41を形
成して、前記各容器15間に渦流を発生するよう
に設けている。 なお、前記容器15を複数個、前記分割流水路
12の両方の流壁たる前記側壁35および隔壁1
3に適宜間隔を介して着脱自在に設ける場合は、
前記両方の側壁35に設けた各容器15をそれぞ
れ対向する位置に配設すると共に、対向する各容
器15間に主流路41を形成して、水流方向に並
設した前記容器15間に渦流を発生するように設
ける。 なお、前記網状容器15は上部断面略円形状を
成すカゴ状のものであつてもよい。さらに、前記
網状容器15の上端に前記フツク19を設けず
に、網状容器15を同様に配列して前記流壁40
に取外し可能に固着してもよい。 前記流水路11の底面は幅方向に傾斜させ、そ
の最低位置にバルブ26を介して排泥管25を設
け、粗大化した落下懸濁物を集合せしめ排出でき
るようにしている。 次に、本発明の実施例の作用を説明すると、富
栄養化された原水は導入管20から流水路11の
分配池22へ送水されると、整流板14を通過す
ることによつて整流され、各分割流水路12へ分
流される。分割流水路12に流入された原水中の
栄養塩類などの栄養物は前記側壁35及び隔壁1
3から成る流壁40に取付けられた網状容器15
に植え付けられた水生植物16の水中根17に付
着し、根圏微生物のコロニーが形成され、根圏微
生物によつて原水中の有機物が分解されて前記水
中根17から吸収される。そこで、分割流水路1
2に流入された原水は、水生植物16を植え付け
た網状容器15と対向する分割流水路12の前記
隔壁13との間の主流路41を通過すると、その
流れの一部は前記網状容器15を適宜間隙を介し
て下流に取付けている前記網状容器15との間に
流れ込み、緩やかな渦状の乱流、すなわち渦流2
7が発生する。この渦流27は緩やかに渦を巻き
ながら降下するので、すでに形成した根圏微生物
のコロニーが剥離することなく原水中の栄養物は
水中根の上下全体に渡つてほどよく付着すること
になり、根圏微生物の活性は高められ、原水中の
栄養物の吸収が効果的に促進される。このように
して前記分割流水路12内に水生植物16を植付
けた網状容器15を複数個設けているので、流下
した原水は次第に処理され、整流板14′を通過
して集合池23に到達する。このようにして魚類
や他生物が生育できるほどの0.5mの透明度の澄
んだ中水を得ることができる。流水路を流下中に
生物作用によつて凝集し、粗大化した原水中の懸
濁物は前記水生植物16の水中根17に付着せず
流水路11の底部に落下し、この落下した懸濁物
29は幅方向に傾斜している流水路11の底面を
低位置に、かつ下流にゆつくりと押し流されて移
動し、随所に設けた排泥管25のバルブ26を開
けると、排泥管25を通過して外部へ排出され
る。 第4図B,Cに示すように前記排泥管25を設
けた位置周辺の底面に堆積槽28を設け、前記落
下懸濁物29を前記堆積槽28に堆積させて随時
前記排泥管25から排出するようにしてもよく、
又第5図に示すように集合池23の底面に沈澱槽
30を設け、流水路11の底面をゆつくり流され
てきた前記落下懸濁物29を堆積させ、この堆積
された落下懸濁物29を沈澱槽30まで延長した
排泥管31から、排泥管31に備えたポンプ32
により排出してもよい。 前記水生植物16を植え込む網状容器15はカ
ゴ状なので水中根17は網状容器15の直下およ
び周囲に発達し、水中根17の周辺に原水中の栄
養懸濁物が捕捉されやすくなり、根圏微生物のコ
ロニーが形成されやすくなる。さらに、フツク1
9を設けた網状容器15を前記隔壁13の上端に
前記フツク19を介して懸吊するので、前記網状
容器15を隔壁13から簡単に交換可能となり、
繁茂した水生植物16、あるいは枯死した水生植
物16を容易に植替え可能となる。又培養土の取
り替え、根の除去作業も簡単である。 本発明の装置は、第6図に示すように、池に流
水路11を設け該流水路11に本発明の水処理装
置10を設置し、処理された水を汲み上げるポン
プ33を備えた循環パイプ34にて前記池に送水
するようにして利用できる。さらに、第7図に示
すように、自然あるいは人工の河川にバイパスの
流水路11を設け、該流水路11に本発明の水処
理装置10を設置して水処理を行うこともでき
る。とにかく、本発明の水処理装置は流水路があ
ればその流水路自体に簡単に設置することができ
る。
Hereinafter, embodiments of the present invention will be described with reference to the drawings. In Fig. 2, a water channel 11 through which raw water such as water from rivers, lakes, or gray water that is eutrophic with nutrients such as nitrogen and phosphorus flows. on the surface of the water,
Activities of rhizosphere microorganisms formed around roots developed in water by growing floating or waterborne aquatic plants, such as water hyacinth, water hyacinth, or other vascular plants that can grow on water. In the water treatment apparatus 10 for treating the raw water, a partition wall 13 is provided in the flow channel 11 to form a divided flow channel 12 in which the partition wall 13 and the side wall 35 of the flow channel 11 serve as flow walls 40. Rectifier plates 14 and 14' are provided at the upstream and downstream ends of the partition wall 13, respectively, over the entire cross section of the flow channel 11,
The partition wall 13 is supported and fixed. A distribution pond 22 for distributing the raw water to each of the divided water channels 12 is provided on the upstream side of the current plate 14, and a collection pond for water treated in each of the separate water channels 12 is provided on the downstream side of the current plate 14'. 23 are provided. An introduction pipe 20 for sending the raw water is installed in the distribution pond 22, and a water pipe 21 for sending the treated water is arranged in the collecting pond 23 via a pump 24. In each of the divided flow channels 12, the aquatic plants 1
6. Stone, sponge, rock wool, etc. (not soil, and it varies depending on the type of plant) 1.
8 into a basket-shaped mesh container 15 having a square upper cross section, and via hooks 19 provided at the upper end of the mesh container 15, a plurality of the side walls 35, which are the flow walls of the divided flow channel 12, are implanted. The containers 15 are suspended at appropriate intervals, and a main channel 41 is formed between each container 15 and the opposing side wall 35 of the divided flow channel to generate a vortex between the containers 15. . Note that a plurality of containers 15 are provided, and the side wall 35 and the partition wall 1, which are both flow walls of the divided flow channel 12, are connected to each other.
3, if it is detachably provided at appropriate intervals,
The containers 15 provided on both side walls 35 are disposed at opposing positions, and a main flow path 41 is formed between the opposing containers 15 to create a vortex between the containers 15 arranged in parallel in the water flow direction. Set it so that it occurs. Note that the net-like container 15 may be a basket-like container having a substantially circular upper section. Furthermore, without providing the hook 19 on the upper end of the mesh container 15, the mesh containers 15 are arranged in the same manner so that the flow wall 40
It may be removably affixed to. The bottom surface of the flow channel 11 is inclined in the width direction, and a mud drain pipe 25 is provided at the lowest position via a valve 26 to collect and discharge coarse fallen suspended solids. Next, to explain the operation of the embodiment of the present invention, when the eutrophic raw water is sent from the introduction pipe 20 to the distribution pond 22 of the flow channel 11, it is rectified by passing through the rectifying plate 14. , and are divided into each divided flow channel 12. Nutrients such as nutrient salts in the raw water flowing into the divided flow channel 12 are transferred to the side wall 35 and the partition wall 1.
A mesh container 15 attached to a flow wall 40 consisting of 3
A colony of rhizosphere microorganisms is formed by the rhizosphere microorganisms, and organic matter in the raw water is decomposed by the rhizosphere microorganisms and absorbed from the underwater roots 17. Therefore, the divided flow channel 1
2 passes through the main channel 41 between the mesh container 15 in which the aquatic plants 16 are planted and the partition wall 13 of the opposing divided flow channel 12 , a part of the flow passes through the mesh container 15 . A gentle vortex-like turbulent flow, that is, a vortex flow 2, flows into the mesh container 15 installed downstream through an appropriate gap.
7 occurs. Since this vortex flow 27 descends while swirling gently, the nutrients in the raw water are properly adhered to the entire upper and lower parts of the underwater roots without peeling off the colonies of rhizosphere microorganisms that have already formed. The activity of microorganisms in the sphere is enhanced, and the absorption of nutrients in raw water is effectively promoted. In this way, since a plurality of mesh containers 15 in which aquatic plants 16 are planted are provided in the divided flow channel 12, the flowing raw water is gradually treated, passes through the rectifying plate 14', and reaches the collecting pond 23. . In this way, it is possible to obtain clear gray water with a transparency of 0.5 meters that allows fish and other organisms to grow. The suspended matter in the raw water that aggregates and becomes coarse due to biological action while flowing down the water channel does not attach to the underwater roots 17 of the aquatic plants 16 and falls to the bottom of the water channel 11, and this fallen suspended matter The object 29 is slowly pushed down the bottom of the flow channel 11, which is inclined in the width direction, to a low position and downstream, and when the valves 26 of the sludge drain pipes 25 installed at various locations are opened, the sludge drain pipes are opened. 25 and is discharged to the outside. As shown in FIGS. 4B and 4C, a sedimentation tank 28 is provided on the bottom surface around the position where the sludge drainage pipe 25 is provided, and the fallen suspended matter 29 is deposited in the sedimentation tank 28, and the sludge drainage pipe 25 is deposited as needed. It may also be discharged from
Further, as shown in FIG. 5, a sedimentation tank 30 is provided at the bottom of the collecting pond 23 to deposit the fallen suspended solids 29 that have been slowly flowing down the bottom of the flow channel 11. From the sludge pipe 31 extending from 29 to the sedimentation tank 30, the pump 32 provided in the sludge pipe 31
It may be discharged by Since the mesh container 15 in which the aquatic plants 16 are planted is cage-shaped, the underwater roots 17 develop directly under and around the mesh container 15, and the nutrient suspension in the raw water is easily captured around the underwater roots 17, and the rhizosphere microorganisms. colonies are more likely to form. In addition, hook 1
9 is suspended from the upper end of the partition wall 13 via the hook 19, the mesh container 15 can be easily replaced from the partition wall 13,
A flourishing aquatic plant 16 or a dead aquatic plant 16 can be easily replanted. It is also easy to replace the culture soil and remove the roots. As shown in FIG. 6, the device of the present invention includes a water treatment device 10 of the present invention provided in a pond with a flow channel 11, and a circulation pipe equipped with a pump 33 for pumping the treated water. It can be used by supplying water to the pond at 34. Furthermore, as shown in FIG. 7, a bypass waterway 11 may be provided in a natural or artificial river, and the water treatment device 10 of the present invention may be installed in the waterway 11 to perform water treatment. In any case, the water treatment device of the present invention can be easily installed in the water channel itself if there is a water channel.

【発明の効果】【Effect of the invention】

本発明は、以上説明したように構成されている
ので、以下に記載されるような効果を奏する。 流水路に水生植物を生育させて成る水処理装置
において、前記流水路内に、水生植物を植付けた
網状容器を複数個、前記流水路の少なくとも一方
の流壁に適宜間隔を介して着脱自在に設けると共
に、前記各容器と対向する流水路の他方の側壁と
の間に主流路を形成して、前記隣接する容器間に
渦流を発生するようにしたので、非常に簡単な装
置であり、費用が安く、前記水生植物を植付けた
各網状容器間に発生する渦流は緩やかに降下する
ために、すでに形成した根圏微生物のコロニーが
剥離されることなく、原水中の栄養物は水中根の
上下全体に渡つてほどよく付着することになり、
その結果根圏微生物の活性は高められ、原水中の
栄養物の吸収が効果的に促進され、魚類や他生物
が生育できるほどの0.5mの透明度の澄んだ中水
を得ることができる。 さらに、本発明の装置は全て自然な水処理装置
であるので、魚類や他の生物に対して無害で安全
な処理を行うことができ、他の水処理装置と組合
せるに際し、前処理あるいは後処理装置として用
いることができる。 そして、人工的な流れにおいては流れの中間に
本発明の水生植物による水処理装置を簡単に設置
することが可能であり、公園などに設置すれば
様々な観賞に耐える植物を植え込むことにより、
水生植物園的な見本園になるので、水の上では景
観になり、水の下では原水処理装置となる。 さらに、各水生植物は各網状容器毎に植込まれ
ているので、各網状容器毎に維持管理することが
できる。 また、流水路に隔壁を設けて分割流水路を形成
し、該分割流水路内に、本発明の水生植物による
水処理装置を設けることにより、非常に効果的に
水処理を行うことができる。 さらに、流水路の底面に排泥手段を設けること
により、流水路を流下中に生物の作用によつて凝
集し粗大化した原水中の落下懸濁物は効果的に排
出され、水処理がなお一層効果的に行われる。 また、前記水生植物を植込んだ網状容器にフツ
クを設け、該フツクを介して前記網状容器を流水
路あるいは分割流水路の流壁を成す隔壁の上端に
懸吊することによつて、前記網状容器を前記側壁
から簡単に交換可能となるので、繁茂した水生植
物あるいは枯死した水生植物を容易に植替え可能
となり、また培養土の取り替え、根の除去作業も
簡単に行ううことができ、管理が容易である。
Since the present invention is configured as described above, it produces the effects described below. In a water treatment device in which aquatic plants are grown in a water channel, a plurality of net-like containers in which aquatic plants are planted are detachably attached to at least one flow wall of the water channel at appropriate intervals. In addition, a main flow path is formed between each of the containers and the other side wall of the opposing flow channel to generate a vortex between the adjacent containers, so the device is very simple and inexpensive. Since the vortex generated between each mesh container in which the aquatic plants are planted descends slowly, the already formed colonies of rhizosphere microorganisms are not detached, and the nutrients in the raw water are distributed above and below the underwater roots. It will adhere well throughout,
As a result, the activity of rhizosphere microorganisms is increased, the absorption of nutrients in the raw water is effectively promoted, and it is possible to obtain clear gray water with a transparency of 0.5 m that allows fish and other organisms to grow. Furthermore, since the device of the present invention is an all-natural water treatment device, it can perform treatment that is harmless and safe for fish and other living things, and when combined with other water treatment devices, it can be used for pre-treatment or post-treatment. It can be used as a processing device. In addition, in an artificial stream, it is possible to easily install the water treatment device using aquatic plants of the present invention in the middle of the stream, and if installed in a park etc., by planting various ornamental plants,
It will be a sample garden similar to an aquatic plant garden, so above the water it becomes a landscape, and below the water it becomes a raw water treatment device. Furthermore, since each aquatic plant is planted in each net-like container, it is possible to maintain and manage each net-like container separately. Further, by providing a partition wall in the water channel to form a divided water channel, and providing the water treatment device using the aquatic plants of the present invention in the divided water channel, water treatment can be carried out very effectively. Furthermore, by providing a means for draining sludge at the bottom of the water channel, suspended solids in the raw water that aggregate and become coarse due to the action of living organisms while flowing down the water channel can be effectively discharged, allowing water treatment to continue. This will be done more effectively. Furthermore, by providing a hook on the net-like container in which the aquatic plants are planted, and suspending the net-like container via the hook from the upper end of the partition wall forming the flow wall of the flow channel or the divided flow channel, Since the container can be easily replaced from the side wall, overgrown or dead aquatic plants can be easily replanted, and the cultivation soil can be replaced and roots can be easily removed, making management easier. is easy.

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

第1図は本発明に係る水性植物による水処理装
置の部分斜視図、第2図Aは平面図、第2図Bは
矢視A−A断面図、第2図Cは矢視B−B断面
図、第3図は水性植物を植付けた網状容器を側壁
に取付けた斜視図、第4図Aは本発明に係る装置
の平面図、第4図Bは矢視C−C断面図、第4図
Cは矢視D−D断面図、第5図は集合池の底面に
沈澱槽を設けた要部断面図、第6図、第7図は、
本発明の装置を用いた応用例の説明図を示す。 10……水処理装置、11……流水路、12…
…分割流水路、13……隔壁、14……整流板、
15……網状容器、16……水生植物、17……
水中根、18……培養土、19……フツク、20
……導入管、21……送水管、22……分配位
置、23……集合池、24……ポンプ、25……
排泥管、26……バルブ、27……渦流、28…
…堆積槽、29……落下懸濁物、30……沈澱
槽、31……排泥管、32,33……ポンプ、3
4……循環パイプ、35……流水路側壁、40…
…流壁、41……主流路。
Fig. 1 is a partial perspective view of a water treatment device using aquatic plants according to the present invention, Fig. 2A is a plan view, Fig. 2B is a sectional view taken along arrow A-A, and Fig. 2C is shown as arrow B-B. 3 is a perspective view of a mesh container planted with aquatic plants attached to the side wall, FIG. 4A is a plan view of the device according to the present invention, FIG. Figure 4C is a sectional view taken along arrow D-D, Figure 5 is a sectional view of the main part with a sedimentation tank provided on the bottom of the collecting pond, and Figures 6 and 7 are:
An explanatory diagram of an application example using the device of the present invention is shown. 10...Water treatment device, 11...Flow channel, 12...
... Divided flow channel, 13 ... Partition wall, 14 ... Straightening plate,
15... Net-like container, 16... Aquatic plant, 17...
Underwater roots, 18...Culture soil, 19...Futsuku, 20
...Introduction pipe, 21 ... Water pipe, 22 ... Distribution position, 23 ... Collection pond, 24 ... Pump, 25 ...
Sludge drain pipe, 26... Valve, 27... Vortex, 28...
... Sedimentation tank, 29 ... Fallen suspended matter, 30 ... Sedimentation tank, 31 ... Sludge removal pipe, 32, 33 ... Pump, 3
4...Circulation pipe, 35...Flow channel side wall, 40...
...Flow wall, 41...Main channel.

Claims (1)

【特許請求の範囲】 1 流水路に水生植物を生育させて成る水処理装
置において、 前記流水路内に、水生植物を植付けた網状容器
を複数個、前記流水路の流壁を成す対向する両側
壁の少なくとも一方の側壁に適宜間隔を介して着
脱自在に設けると共に、前記各容器と、対向する
流水路の他方の側壁との間に主流路を形成して、
前記隣接する容器間に渦流を発生するようにした
ことを特徴とする水生植物による水処理装置。 2 流水路に水生植物を生育させて成る水処理装
置において、 前記流水路内の流水方向に流壁を成す一又は複
数の隔壁を設けて該一の隔壁及び前記流水路の側
壁間に、または前記複数の隔壁間に分割流水路を
形成すると共に、該分割流水路内に、水生植物を
植付けた網状容器を複数個、前記分割流水路の流
壁を成す少なくとも一方の前記側壁又は隔壁に適
宜間隔を介して着脱自在に設けると共に、前記各
容器と対向する分割流水路の他方の側壁又は隔壁
間に主流路を形成して、前記隣接する容器間に渦
流を発生するようにしたことを特徴とする水生植
物による水処理装置。 3 前記流水路又は分割流水路の流壁を成す対向
する両側壁、又は一方の側壁と対向する隔壁又は
両隔壁に前記各容器を対向させて適宜間隔を介し
て着脱自在に設け、前記両側壁、又は一方の側壁
と対向する隔壁又は両隔壁の対向する各容器間に
主流路を形成した請求項1又は2記載の水生植物
による水処理装置。 4 前記流水路の底面に排泥手段を設けることを
特徴とする請求項1又は2記載の水生植物による
水処理装置。 5 前記容器にフツクを設け、該フツクを介して
前記容器を前記側壁の上端に懸吊する請求項1又
は2記載の水生植物による水処理装置。
[Scope of Claims] 1. A water treatment device in which aquatic plants are grown in a flow channel, wherein a plurality of net-like containers in which aquatic plants are planted are placed in the flow channel on opposite sides forming the flow walls of the flow channel. At least one side wall of the wall is removably provided at an appropriate interval, and a main flow path is formed between each container and the other side wall of the opposing flow channel,
A water treatment device using aquatic plants, characterized in that a vortex is generated between the adjacent containers. 2. In a water treatment device in which aquatic plants are grown in a water channel, one or more partition walls forming a flow wall in the direction of water flow are provided in the water channel, and a partition wall is provided between the partition wall and a side wall of the water channel, or A divided flow channel is formed between the plurality of partition walls, and within the divided flow channel, a plurality of net-like containers in which aquatic plants are planted are appropriately attached to at least one of the side walls or partition walls forming the flow wall of the divided flow channel. A main channel is formed between the other side wall or partition wall of the divided flow channel facing each of the containers, so that a vortex is generated between the adjacent containers. Water treatment equipment using aquatic plants. 3. Each of the containers is removably provided at an appropriate interval so as to face opposite side walls forming the flow walls of the flow channel or the divided flow channel, or a partition wall facing one side wall, or both partition walls, and 3. The water treatment device using aquatic plants according to claim 1 or 2, wherein a main flow path is formed between the containers facing each other, or between one side wall and the opposing partition wall, or between the opposing containers of both partition walls. 4. The water treatment device using aquatic plants according to claim 1 or 2, characterized in that a sludge drainage means is provided on the bottom surface of the flow channel. 5. The water treatment device using aquatic plants according to claim 1 or 2, wherein the container is provided with a hook, and the container is suspended from the upper end of the side wall via the hook.
JP5270388A 1988-03-08 1988-03-08 Water treatment apparatus by aquatic plant Granted JPH01228598A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5270388A JPH01228598A (en) 1988-03-08 1988-03-08 Water treatment apparatus by aquatic plant

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5270388A JPH01228598A (en) 1988-03-08 1988-03-08 Water treatment apparatus by aquatic plant

Publications (2)

Publication Number Publication Date
JPH01228598A JPH01228598A (en) 1989-09-12
JPH0427920B2 true JPH0427920B2 (en) 1992-05-13

Family

ID=12922250

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5270388A Granted JPH01228598A (en) 1988-03-08 1988-03-08 Water treatment apparatus by aquatic plant

Country Status (1)

Country Link
JP (1) JPH01228598A (en)

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Publication number Priority date Publication date Assignee Title
DE19714097A1 (en) * 1997-04-07 1998-10-08 Hermann Hugel Plant bed for a plant bed sewage treatment plant
KR20020041728A (en) * 2000-12-06 2002-06-03 박영국 Autogenesis device for purifying water
JP2003005626A (en) * 2001-06-20 2003-01-08 Kato Construction Co Ltd Biotope kit for environment study
KR100443314B1 (en) * 2002-08-09 2004-08-09 학교법인 인제학원 Structure for artificial marshy land and sewage treatment device using thereof
JP2004237141A (en) * 2003-02-03 2004-08-26 Tomoharu Takashima Floating island water purification system
CN101962227B (en) 2009-07-23 2012-09-05 上海海洋大学 Method for removing water eutrophication
CN102001753A (en) * 2010-10-20 2011-04-06 环境保护部南京环境科学研究所 Ecological corridor for removing nitrogen and phosphorus of micro-polluted river water and construction method thereof
CN102951737A (en) * 2011-08-26 2013-03-06 广西科学院 Treatment system for treating eutrophic water body by duckweed

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JPS58199099A (en) * 1982-05-17 1983-11-19 Toshiba Corp Device for treating water in water channel

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