JPH01228598A - Water treatment apparatus by aquatic plant - Google Patents

Water treatment apparatus by aquatic plant

Info

Publication number
JPH01228598A
JPH01228598A JP5270388A JP5270388A JPH01228598A JP H01228598 A JPH01228598 A JP H01228598A JP 5270388 A JP5270388 A JP 5270388A JP 5270388 A JP5270388 A JP 5270388A JP H01228598 A JPH01228598 A JP H01228598A
Authority
JP
Japan
Prior art keywords
water
flow
containers
aquatic plants
flow passage
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.)
Granted
Application number
JP5270388A
Other languages
Japanese (ja)
Other versions
JPH0427920B2 (en
Inventor
Tokuo Suzuki
登久雄 鈴木
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.)
BELL TECHNICAL CO KK
Original Assignee
BELL TECHNICAL CO KK
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 BELL TECHNICAL CO KK filed Critical BELL TECHNICAL CO KK
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

Links

Landscapes

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

Abstract

PURPOSE:To enhance the activity of rooting zone bacteria by effectively bonding nutriments in inflow raw water to the water roots of an aquatic plant by a method wherein a plurality of reticulated containers having the aquatic plate taking root thereinto are provided in a water flow passage so as to be set to one flow wall of said flow passage in a freely detachable manner and a main flow passage is formed between the flow walls on the opposite side of said flow passage to generate turblent flow between the containers. CONSTITUTION:When raw water is allowed to flow in a water flow passage 11, the flow of raw water viewed from the upper part of the water flow passage 11 passes through the main flow passage 41 formed between flow walls of the water flow passage opposed to the reticulated containers 15 of an aquatic plant 15 mounted to one flow wall 40 of the water flow passage and a part of the flow enters between the containers 15 to generate a vortex stream 27. Since this vortex stream falls gently, the colony of rooting zone bacteria already formed to the aquatic plant 16 is not released and nutriments in raw water are properly bonded to the water roots 17 of the aquatic plant 15 over the whole thereof. As a result, the activity of rooting zone bacteria is enhanced and the absorption of the nutriments in raw water is effectively promoted and water having transparency enough to permit the growth of fish can be obtained.

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l
z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ηに関するものである。
The present invention uses aquatic plants or other vascular plants that can grow on water to provide nutrients such as nitrogen and phosphorus to the water surface of the waterway.
The present invention relates to a water treatment system η for treating raw water such as water from rivers, lakes and marshes, or gray water that is eutrophicated with class Z substances.

【従来技術] 家庭用211排水、下水、工場排水、田畑の農耕水等各
凱汚水が流入する河川や湖沼、池あるいは人工的な1也
、噴水池、排水1醪、貯水槽等において(:t1前記汚
水1月こ含まれる浮遊懸濁物ならびに有機物及び窒ぶ、
リン等の栄養塩類により、高栄養化され、水質が悪化1
7、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、前記汚水によって汚染された水(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
大証に発生し、水中の酸素不足によって死滅した魚類や
プランクトン等の遺体の沈降、堆積によって底泥の1M
質がヘドロ化し、死滅した魚類やプランクトンは酸素分
解されろため、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。 したがって、前記原水の富栄養化を停止させろためには
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1g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っ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m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8i城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Zま、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、両者ともに景観上も好まし
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った。 そこで、浮遊性または挺水生の水草、たとえばホティア
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
網状容器内に稙久込み、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。(例又は特公昭62−2
8720号参照) 前記水生植物の水中様の周辺に形成する根闇黴生物群の
活動を主体として原水を浄化する装置(息下本発明では
「水生植物)こよる処理装置J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様に有
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。 【発明が解決しようとする課題】 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様に有効に付着せしめろた
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
によって乱流の発生状態が変化することもあり、阻止体
J!e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った。 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
m架すると、前記乱流によっ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ってくるの
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ろ効果が低いという問題点があっ
た。 さらに、この手段では乱流を起こすための阻11:体を
水生植物の下面全体に渡って設置する必要があり、費用
も高いという問題点があった。 本発明は、面単な装置で原水の流水路に適度の乱流を発
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
んだ中水を得ろための水生植物による水処理装■を提供
することを目的とする。
[Prior art] In rivers, lakes, ponds, artificial ponds, fountain ponds, wastewater, water tanks, etc., into which wastewater such as household wastewater, sewage, industrial wastewater, and agricultural water from fields flows (:t1 The sewage contains suspended suspended solids and organic matter and nitrogen,
Nutrient salts such as phosphorus make the water highly nutritious and deteriorate water quality1
7. There is a problem that it becomes impossible for fish to live and further deteriorates the water quality. This is because the water contaminated by the above-mentioned sewage (hereinafter referred to as "raw water" in the present invention) becomes eutrophic, and plankton etc. are generated in OSE, and the bodies of fish and plankton etc. that die due to lack of oxygen in the water settle and accumulate. 1M of bottom mud
The water becomes sludge and the dead fish and plankton are decomposed by oxygen, so dissolved oxygen (DO) is consumed and becomes oxygen deficient. When this oxygen deficient condition occurs, H2S begins to be generated, and at the same time iron, manganese, and nitrogen are decomposed. This is because phosphorus is eluted. Therefore, in order to stop the eutrophication of the raw water, it is necessary to supply oxygen to the bottom of the water and prevent the leaching of nutrients, or to remove 1 g of nutrients leached from the bottom mud by some method. be. General 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 form a solid substance, and disposing of it, and sulfuric acid band. Chemical means are known, such as adding a flocculant such as to generate phosphorus and m-soluble compounds to inactivate the mixture, or sterilizing with chlorine or the like. However, the former type of treatment method requires large-scale equipment, and the latter type of chemical treatment method requires chemical treatment equipment and a large amount of flocculant, which can damage the habitat of fish and other living things. It is not suitable for Both are also undesirable from a landscape 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 lily, or other vascular plants that can grow on water, are placed in net containers placed below the water surface of ephemeral or circulating waterways, and submerged. Several devices have been disclosed that treat raw water mainly through the activities of rhizosphere microorganisms that form around roots that have developed. (Example or Special Public Service No. 62-2
(See No. 8720) In the device (hereinafter referred to as "aquatic plant treatment device J" in the present invention) that purifies raw water mainly through the activities of a group of dark fungal organisms that form around the aquatic plants, If nutrients such as nutrient salts in the inflowing raw water are effectively attached to plants, the activity of rhizosphere microorganisms will be increased and the absorption of nutrients in the raw water will be promoted, which will improve the treatment effect of the raw water. [Problems to be Solved by the Invention] In conventional water treatment devices using aquatic plants, in order to effectively attach nutrients in the inflowing raw water like water to plants, the bottom of the flow channel is Blockers such as gravel or blocking plates are installed to create moderate turbulence in the flowing water, allowing some of the turbulence to flow gently through the underwater root zone of plants.However, this method is not effective. In order for rhizosphere microbial colonies to develop, fairly intense turbulence must be created in order to effectively mix the raw water flowing down the roots of the plant up and down, thereby destroying the already formed rhizosphere microbial colonies. There is a risk of peeling off.Moreover, with this method,
The state of turbulence may change depending on the size of objects placed throughout the waterway that cause turbulence, the flow rate and velocity of raw water, and changes in the waterway area due to the growth of plant roots. eIt was difficult to arrange the system appropriately, and the effectiveness of water treatment was low. Furthermore, with this method, when underwater roots develop and hang directly under a net-like container that prevents plants that have grown in the upper part of the waterway from being submerged, the raw water mixed by the turbulence flows above and below the underwater roots. Since the state of penetration differs between the two parts, there is a problem that nutrients in the raw water do not adhere effectively, and as a result, the effect of absorption of nutrients is low. Furthermore, this method has the problem that it is necessary to install a barrier over the entire lower surface of the aquatic plant to create turbulent flow, and the cost is high. The present invention uses a simple device to generate moderate turbulence in a raw water channel, effectively attaching nutrients in the raw water to the underwater roots of aquatic plants, and effectively treating the raw water to support fish, etc. An object of the present invention is to provide a water treatment system using aquatic plants for obtaining clear greywater with a transparency of about 0.5 m, for example, that living organisms can live in.

【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
物を稙え付けた網状容器を複数間、前記流水路の流量を
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ろと共に、前記各容器と対向す
る流水路の他方の側壁間に主流路を形成して、前記容器
間に乱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量を成す一又は
複数の隔壁を設けて該−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量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
ろと共に、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、前記各容器間に乱流を発生するよう
にしたことを特徴とするものである。 また主流路を、対向する流量すなわち、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、乱流が前記主流路の両側で発生し、効果的な水
処理ができろ。 そして、前記流水路の底面に排泥手段を設けろと水処理
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ックを設
け、該フックを介して前記容器を前記流水路又は分、!
′II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 each having aquatic plants attached thereto are placed in the water channel in opposite directions that form the flow rate of the water channel. A main channel is formed between the other side wall of the flow channel facing each container to generate turbulent flow between the containers. It is characterized by the following. Furthermore, one or more partition walls are provided to form a flow rate in the flow direction in the flow channel, and a divided flow channel is formed between the partition wall and the side wall of the flow channel, or between the plurality of partition walls, A plurality of net-like containers planted with aquatic plants are removably provided in the divided flow channel at appropriate intervals on at least one of the side walls or partition walls that form the flow rate of the divided flow channel, and are arranged opposite to each of the containers. A main channel is formed between the side walls of the divided flow channel to generate turbulent flow between the containers. In addition, if the main flow path is formed between containers with opposing flow rates, that is, opposite to both the side walls and/or partition walls, turbulent flow will occur on both sides of the main flow path, resulting in effective water flow. Be able to process it. It is effective for water treatment to provide a means for draining sludge at the bottom of the water channel. Furthermore, a hook is provided on the net-like container in which the aquatic plants are planted, and the container is connected to the watercourse or the water passage through the hook.
'II It is preferable to hang it on the upper end of the side wall of the flow channel.

【作用】[Effect]

流水路に原水を流入させろと、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も一方
の前記流量に取り付けた前記水生植物を櫃丸付けた網状
容器と対向する流水路ないしは分割流水路の流量との間
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。ntJ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1頭などの栄養物は的記水中根に付着し、根
圏微生物のコロニーが形成され、語生物によって汚水中
の有機物が分子’+1され、前記水中浪から吸収される
。この時発生する渦流は緩やかに渦をひきながら降下す
るので、すでに形成した根圏(敞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って
、はどよく何重することになり、根団徹生物の活性は高
められ、原水の栄養物の吸収が効果的に促進されろ。 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、他の生物が生じてき、且つこれを水−
ヒから観察できるほどの約0 、5mの透明度の澄んだ
中水を得ろことができろっ流水路を流下中に生物の作用
によって凝集し粗大化した原水中の懸濁物は、@記水生
植物の水中根に付着せず、底面に落下すると、往面をゆ
っ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
排出されろ。 また前記容器に−I Htりを設け、該フックを前記(
l′i11壁及び隔壁から成ろ流量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hi替又司用面なり、又培養土の取り替又も、
根を除去することも簡単である。
When raw water flows into a flow channel, the flow of raw water seen from the upper part of the flow channel is a flow channel facing a net-like container with the aquatic plants attached to the flow rate of at least one of the flow channel or the divided flow channel. When the flow passes through the main flow path between the flow rate and the flow rate 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 turbulent flow. Occur. The underwater roots of aquatic plants develop directly under and around the net-like container, and nutrients such as one nutrient in the raw water attach to the net-like underwater roots, and a colony of rhizosphere microorganisms is formed. The organic matter inside is converted into molecules '+1' and absorbed from the water. The vortex generated at this time descends while drawing a gentle vortex, so the nutrients in the raw water are distributed over the entire upper and lower parts of the underwater roots in multiple layers without causing the already formed rhizosphere (colonies of insects to separate). As a result, the activity of the root group organisms will be enhanced, and the absorption of nutrients in the raw water will be effectively promoted. Since a plurality of net-like containers planted with the above-mentioned aquatic plants are installed in the area, the raw water that flows down is gradually treated, fish and other organisms are generated, and this is used as a water source.
It is possible to obtain clear gray water with a transparency of about 0.5 m that can be observed from water. If the plants do not attach to the underwater roots and fall to the bottom, they will be slowly washed away, but the slurry drainage means installed at the bottom of the flow channel effectively removes the coarse fallen suspended matter. Be it. Additionally, a -I Ht hook is provided on the container, and the hook is attached to the (
When the container is suspended at the upper end of the flow rate consisting of a wall and a partition wall, the container can be easily removed from the side wall, so that it is easy to remove thick or dead aquatic plants. Whether it's the surface or replacing the culture soil,
It is also easy to remove the roots.

【実施例] 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!排水などの原水が流
れろ流水路11の水1r11に、浮遊性または挺水性の
水草、たとえばホティアオイやイ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イ4
二物訂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]1の側壁35を流量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の全断面に渡って設け、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1
4′の下流側には各分割流水路12で処理された水の集
合ン也23を設けである。 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、1)7I記m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#512内には、前記水生植物16を石
、スポンジ、ロックウールなど(土ではなく、又、植物
の種類によって異なる)の培養土18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の上端に設けたフック19を介して複数個、
前記分割流水路12の流量たろ一方の前記側壁35に適
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間に乱流を発生ずるように設けてい
る。 なお、前記容器15を複数個、前記分割流水路12の両
方の流量たろ前記側壁35および隔壁13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間に乱流を発生するよ
うに設ける。 なお、前記網状容器15は上部UI面略円形状を成すカ
ゴ状のものであってもよい。さらに、前記網状容器15
の上端に前記−ノック19を設けずに、網状容器15を
同様に配列して前記流量40に取外し可能に固着しても
よし)。 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t
コ落下懸濁物を集合せしめ排出できるようにしている5
、 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って整流さ
れ、各分割流水路12へ分流される。分!′11流水路
12に流入された原水中の栄養塩類などの栄養物1ま前
記側壁35及び隔壁13から成ろ流量40に取付けられ
た網状容器15に植又付けられた水生植物16の水中根
17に付着し、根I!! 微生物のコロニーが形成され
、根圏微生物によって原水中の有機物が分解されて前記
水中択17から吸収される。そこで、分割流水路12に
流入された原水は、水生植物16を植え付けた網状容器
16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i1の一部:ま前記網
状容器15を適宜間隙を介して下流に取付けでいる前記
網状8器15との間に流れ込み、緩やかな渦状の乱流、
すなわち9流27が発生する。この渦流27は砂やかに
烏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
根の上下全体に渡っ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を植付けた綿状容器15を複数個設け
ているので、流Fした原水は次第に処理され、整流板1
4′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
用によって凝集し、粗大化した原水中の懸濁物は前記水
生IIII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、かつ下流にゆっ
(りと押し流されて移動し、随所に設けた排@925の
バルブ26を開けると、排泥管25を通過して外部へ排
出されろ。 第4図(81,(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2
5から排出するようにしてもよ(、又第5図に示すよう
に集合/li!23の底面に沈澱11130を設け、流
水路11の底面をゆっ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ば網状容器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、フック19を設けた網状容器15を前記隔壁
13の上端に前記7ツク19を介して懸吊す乙ので、前
記網状容器15をVAAlB2ら簡単に変換可能となり
、繁茂した水生植物16、あるいは枯死した水生植物1
6を容易に槙替え可能となる。又培養土の取り替丈、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#81
1を設は該流水路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ろ
。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てき
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ろ、3【発明の効
果】 ゛ 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量に適宜間隔を介
して着脱自在に設けると共に、前記各容器と対向する流
水路の他方の流量間に主流路を形成して、前記容U間に
乱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
に発生する馬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ろことなく、原水
中の栄養物は水中根の上下全体に渡ってほどよく付着す
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t!中水
を得ろことができろ。 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よれているの
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
けろことにより、非常に効果的に水処理を行うことがで
きろ。 さらに、流水路の底面に排泥手段を設けることにより、
流水路を流水中に生物の作用によっ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ろ。 また、前記水生植物を植込んだ網状容器にフックを設け
、該フックを介して前記網状容器を流水路あるいは分割
流水路の流量を成す隔壁の上端にも吊することによって
、i′i′lI記網状容器金網状容器から簡単に交換可
能となるので、繁茂した水生植物あろいは枯死した水生
植物を容易に植替又可能となり、また培養土の取り替又
、根の除去作業も簡mに行うことができ、管理が容易で
ある。
[Example] Hereinafter, an example of the present invention will be described with reference to the drawings. In Figure 2, water from rivers, lakes, etc. that is eutrophic with nutrients such as nitrogen and phosphorus or! In the water 1r11 in which raw water such as drainage water flows, floating or floating aquatic plants 16 such as water hyacinth, orchid or other vascular plants that can grow on water are grown and developed in the water. The microscopic rhizosphere that forms around the roots 4
In the water treatment device 10 for treating the raw water, the water treatment device 10 is mainly used for the activities of 2nd revision, in which a partition wall 13 is provided in the flow channel 11, and the partition wall 13 and the side wall 35 of the flow channel]1 are divided flow channels with a flow rate of 40. form 12. At the upstream and downstream ends of the partition wall 13, flow regulating plates 14 and 14' are provided, respectively, over the entire cross section of the flow channel 11 to support and fix the partition wall 13. A distribution pond 22 for distributing the raw water to each of the divided flow channels 12 is provided on the upstream side of the rectifying plate 14.
A collecting tank 23 for water treated in each divided flow channel 12 is provided on the downstream side of 4'. An introduction pipe 20 for conveying the raw water to the distribution pond 22
1) A water pipe 21 for transporting the treated water is arranged in the joint pond 23 via a pump 24. In each divided flowing water #512, the aquatic plants 16 are placed in an upper section along with a culture medium 18 made of stone, sponge, rock wool, etc. (not soil, and varies depending on the type of plant);
A plurality of plants are implanted in a basket-shaped mesh container 15 having a square shape, and connected via hooks 19 provided at the upper end of the mesh container 15.
The flow rate of the divided flow channel 12 is suspended from one side wall 35 at an appropriate interval, and a main flow channel 41 is formed between each container 15 and the opposing side wall 35 of the divided flow channel. The containers 15 are provided so as to generate turbulent flow between them. In addition, when a plurality of containers 15 are removably provided on both the side walls 35 and the partition wall 13 of the divided flow channel 12 at appropriate intervals, each container 15 provided on both the side walls 35 is are arranged at opposing positions, and a main flow path 41 is formed between each of the opposing containers 15,
The containers 15 are arranged so as to generate turbulent flow between the containers 15 arranged in parallel in the water flow direction. Note that the net-like container 15 may be a basket-like container having a substantially circular shape on the upper UI surface. Furthermore, the mesh container 15
The mesh containers 15 may be similarly arranged and removably fixed to the flow rate 40 without providing the knock 19 at the upper end of the mesh container 15). The bottom surface of the flow channel 11 is inclined in the width direction, and a mud draining pipe 25 is provided at the lowest position via a valve 26 to make the flow channel 11 coarser.
It collects the falling suspended matter and allows it to be discharged.5
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. The water is divided into each divided flow channel 12. Minute! '11 Nutrients such as nutrient salts in the raw water flowing into the flow channel 12; and submerged roots of aquatic plants 16 planted in the mesh container 15 attached to the flow rate 40 made up of the side wall 35 and the partition wall 13; Attach to 17 and root I! ! A colony of microorganisms is formed, and the organic matter in the raw water is decomposed by the rhizosphere microorganisms and absorbed from the water solution 17. Therefore, when the raw water flowing into the divided flow channel 12 passes through the main channel 41 between the mesh container 16 in which the aquatic plants 16 are planted and the partition wall 13 of the opposing divided flow channel 12, part of the flow i1 : A gentle vortex-like turbulent flow flows between the mesh container 15 and the mesh container 15 installed downstream through an appropriate gap,
In other words, 9 flows 27 occur. Since this vortex 27 descends in a sandy manner, the nutrients in the raw water adhere 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, the divided flow channel 12
Since a plurality of flocculent containers 15 with aquatic plants 16 planted therein are provided, the raw water flowing F is gradually treated, and the rectifying plate 1
4' and reaches the collection pond 23. In this way, it is possible to obtain clear gray water with a transparency of 0.5 m 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 adhere to the underwater roots 17 of the aquatic III species 16 and falls to the bottom of the water channel 11, and this fallen suspended matter The sludge pipe 29 moves to a low position on the bottom surface of the flow channel 11 which is inclined in the width direction, and is slowly pushed downstream. As shown in FIG. 4 (81, (C)), a sedimentation tank 28 is provided on the bottom surface around the position where the mud removal pipe 25 is installed, and the fallen suspended matter 29 is discharged to the outside. The sludge is deposited in the sedimentation tank 28 and the sludge is removed from the drainage pipe 2 as needed.
Alternatively, as shown in FIG. 5, a sediment 11130 may be provided on the bottom of the collection/li! 23 to collect the fallen suspended solids 29 that have been slowly flowing down the bottom of the flow channel 11. The accumulated fallen suspended solids 29 may be discharged from a sludge pipe 31 extending to a settling tank 30 by a pump 32 provided in the sludge pipe 31. A mesh container 15 in which the aquatic plants 16 are planted. Since they are cage-shaped, the underwater roots 17 develop directly under and around the net-like container 15, making it easier for nutrient suspensions in the raw water to be captured around the underwater roots 17, making it easier for rhizosphere microorganism colonies to form. Since the mesh container 15 provided with the hooks 19 is suspended from the upper end of the partition wall 13 via the seven hooks 19, the mesh container 15 can be easily converted to VAAlB2, and can be used to store flourishing aquatic plants 16 or dead aquatic plants. Aquatic plants 1
6 can be easily replaced. Also, it is easy to replace the culture soil and remove the roots. As shown in FIG.
1, the water treatment device 10 of the present invention can be installed in the flow channel 11, and the treated water can be used by being sent to the pond through a circulation pipe 34 equipped with a pump 33 for pumping up the water. Further, 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 flow channel itself if there is a flow channel.3 [Effects of the Invention] Since the present invention is configured as described above, This produces the effects described below. In a water treatment device in which aquatic plants are grown in a flow channel, a plurality of net-like containers in which aquatic plants are planted are removably provided in the flow channel at appropriate intervals depending on the flow rate of at least one of the flow channels. At the same time, a main flow path is formed between each of the containers and the other flow channel of the flow channel facing each other to generate turbulent flow between the volumes U, so the device is very simple and inexpensive. Since the flow that occurs between each of the net-like containers planted with the aquatic plants falls slowly, the already formed rhizosphere microbial colonies are not detached, and the nutrients in the raw water are distributed all over the upper and lower parts of the underwater roots. As a result, the activity of rhizosphere microorganisms is increased,
The absorption of nutrients in the raw water is effectively promoted, and the transparency is 0.5m, which is enough for fish and other organisms to grow! You can get gray water. 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 or the like, it will be possible to improve the aquatic environment by planting various ornamental plants. It will be a botanical garden, so above the water it will be a landscape, and below the water it will be a raw water treatment facility. 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 installing 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 mud removal means on the bottom of the flow channel,
The suspended solids in the raw water that aggregate and become coarse due to the action of living things in the flowing water can be effectively discharged, and water treatment can be carried out even more effectively. In addition, by providing a hook on the net-like container in which the aquatic plants are planted, and hanging the net-like container via the hook on the upper end of the partition wall forming the flow rate of the flow channel or the divided flow channel, i'i'lI Since the wire mesh container can be easily replaced, it is possible to easily replant overgrown aquatic plants or withered aquatic plants, and it is also easy to replace the culture soil and remove roots. It is easy to manage.

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

第1図は本発明に係る水性植物に、Lる水処理装置の部
分斜視図、第2図(A)は平面図、第2図tB)は矢視
A−A断面図、第2図(C)は矢視B −B断翻図、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CB)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紹槽を設けた要部
断面図、第6図、第7図は、本発明の装置9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1jlJ流水絡 13 隔壁 14・・整流板
15 M3状容器 16・水生植物 17 水中根 18 ・培養土 19 ランク2〇−導
入管 21・送水管22・分配位置23−実き池 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 34 wj環パイプ3
5 流水路側壁 40 流量 41 ・主流路特許出願
人 有限会社ベルテクニカルカンパニー代工事人 所理
士 小倉正明 第3図 第6凹
FIG. 1 is a partial perspective view of a water treatment device for water plants according to the present invention, FIG. 2 (A) is a plan view, FIG. C) is a cross-sectional view taken along arrow B-B, FIG. 3 is a perspective view of a net-like container planted with aquatic plants attached to the side wall, and FIG. 4(A) is a plan view of the device according to the present invention.
Figure CB) is a sectional view taken along arrow C-C, and Figure 4 (C) is taken along arrow D-
D sectional view, FIG. 5 is a sectional view of essential parts in which a settling tank is provided at the bottom of a collecting pond, and FIGS. 6 and 7 are explanatory diagrams of an application example using the device 9 of the present invention. 10 Water treatment equipment 11・Flow channel 12 Minute 1JlJ water flow junction 13 Partition wall 14・・Rectifying plate 15 M3-shaped container 16・Aquatic plant 17 Underwater roots 18・Cultivating soil 19 Rank 2〇-Introduction pipe 21・Water pipe 22・Distribution position 23-Fruit Pond 24
・Pump 25・°Sludge drainage pipe 26 Valve 27 Whirlpool
28 Sedimentation tank 29 Fallen suspended matter 30 Sedimentation tank 31
・Sludge drainage pipe 32.33 Pump 34 wj ring pipe 3
5 Flow channel side wall 40 Flow rate 41 ・Main channel patent applicant: Bell Technical Company Ltd. Contractor/Investor: Masaaki Ogura Figure 3, 6th recess

Claims (5)

【特許請求の範囲】[Claims] (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間に主流路
を形成して、前記容器間に乱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。
(1) 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 at least one of opposing both side walls forming the flow wall of the water channel is provided. The container is detachably provided on the side wall of the container at appropriate intervals, and a main flow path is formed between the other side wall of the flow channel facing each of the containers to generate turbulent flow between the containers. Water treatment equipment using aquatic plants.
(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、前記各容器間に乱流を発生する
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) 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 water flow direction in the water channel are provided between the one partition wall and the side wall of the water channel. , or a divided flow channel is formed between the plurality of partition walls, and a plurality of net-like containers in which aquatic plants are planted in the divided flow channel,
At least one of the side walls or partition walls forming the flow wall of the divided flow channel is removably provided at an appropriate interval, and
A water treatment device using aquatic plants, characterized in that a main flow path is formed between the other side wall or partition of the divided flow channel facing each of the containers to generate turbulent flow between each of the containers.
(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。
(3) Each of the containers is removably provided at an appropriate interval so as to face the opposite side walls forming the flow walls of the flow channel or the divided flow channel, or the partition wall facing one side wall, or both partition walls, and 3. The water treatment device using aquatic plants according to claim 1, wherein a main flow path is formed between both side walls, a partition wall facing one side wall, or each container facing each other on both partition walls.
(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
(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)前記容器にフックを設け、該フックを介して前記
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。
(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 true JPH01228598A (en) 1989-09-12
JPH0427920B2 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)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0870427A3 (en) * 1997-04-07 1999-09-08 Hermann Hugel Planting bed for a sewage 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 type water cleaning device
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

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58199099A (en) * 1982-05-17 1983-11-19 Toshiba Corp Device for treating water in water channel

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58199099A (en) * 1982-05-17 1983-11-19 Toshiba Corp Device for treating water in water channel

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0870427A3 (en) * 1997-04-07 1999-09-08 Hermann Hugel Planting bed for a sewage 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 type water cleaning device
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

Also Published As

Publication number Publication date
JPH0427920B2 (en) 1992-05-13

Similar Documents

Publication Publication Date Title
CN101548655B (en) Ecological closed cycle water fish-cultivating method
CN107279022B (en) A kind of aquatic products circulating water culture system and method based on biological flocculation and biomembrane
CN104705238B (en) A kind of aquatic animal cultivating system
CN108439711A (en) A kind of marine culture waste water integrated treatment purification system and method
CN105724304B (en) Stacked fishes and shrimps recirculated water raises together system
CN105621794B (en) A kind of processing system and its processing method of intensive marine culture wastewater
CN108862854A (en) Sea pond circulating water culture system
CN107018941B (en) Ecological farming systems of circulation and flotation tank
CN106857363A (en) A kind of light-transmission type bio-decontamination cycle water fish farming system
CN113213710A (en) Seawater factory greenhouse aquaculture penaeus vannamei tail water treatment system and method
CN108467162A (en) Rural domestic sewage treating device
CN112335596B (en) Pond engineering circulating water zero-discharge culture system
CN210076358U (en) Land-based semi-buried rotational flow recirculating aquaculture system
CN108423926A (en) A kind of pond inner recirculation flow water breeding pollution object emission-reducing system
CN107711684A (en) Multifunctional aquatic product cultivates the water purification circulatory system
CN107459226A (en) Inland sea farming system and its cultural method
JPH01228598A (en) Water treatment apparatus by aquatic plant
CN110036967B (en) Double-fishpond circulating water ecological fish culture system
CN207811495U (en) A kind of simple fishpond sewage disposal system
CN109287538A (en) A kind of crab cultivation water pollution control system and its application
CN109122545A (en) A kind of pond bottom blowdown water quality improvement system
CN108684598B (en) Intelligent seawater pond leisure landscape ecological breeding system
CN210120854U (en) Double-fishpond circulating water ecological breeding system
CN1183827C (en) Marine product environment-protecting cultivation process and its cultivation equipment
CN207435252U (en) The natural catalytic oxidation pool

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees