JPH0947749A - Local water purification system and method, and purification device - Google Patents
Local water purification system and method, and purification deviceInfo
- Publication number
- JPH0947749A JPH0947749A JP7200840A JP20084095A JPH0947749A JP H0947749 A JPH0947749 A JP H0947749A JP 7200840 A JP7200840 A JP 7200840A JP 20084095 A JP20084095 A JP 20084095A JP H0947749 A JPH0947749 A JP H0947749A
- Authority
- JP
- Japan
- Prior art keywords
- water
- treated
- water area
- area
- purification
- 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.)
- Pending
Links
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- Filtration Of Liquid (AREA)
- Water Treatment By Sorption (AREA)
Abstract
(57)【要約】
【目的】本発明の目的は、浄水場の水源である湖沼、
池、ダム湖等の閉鎖性水域において汚染物質を分離除去
して水質の改善を図って良質の水を浄水場へ供給できる
ようにした局所水域浄化システムを提供することにあ
る。
【構成】本発明は、浄水場1の取水口2を含む閉鎖性水
域6の一部を処理水域7として仕切り装置14、14
t、14x、14yによって仕切り、少なくともこの処
理水域7の水を浄化装置11、11’、12で富栄養化
物質や藻類等の汚染物質を分離除去して浄化した後もと
の処理水域7に放出ように構成した局所水域浄化システ
ムである。また本発明は、通路35に沿ってフェンス2
4〜27を並べるだけの簡単な構成の汚染物除去装置4
1によって汚染物を分離除去するように構成したことに
ある。
(57) [Summary] [Objective] The object of the present invention is to provide a lake, which is the water source of the water purification plant,
It is an object of the present invention to provide a local water purification system capable of separating and removing pollutants in a closed water area such as a pond or a dam lake to improve water quality and supply high quality water to a water purification plant. [Constitution] In the present invention, a part of a closed water area 6 including a water intake 2 of a water purification plant 1 is divided into treated water areas 7 by partitioning devices 14, 14.
After partitioning by t, 14x, 14y, at least the water in this treated water area 7 is purified by separating and removing pollutants such as eutrophication substances and algae by the purifying devices 11, 11 ', 12 and returning to the original treated water area 7. It is a local water purification system configured to release. Further, the present invention is directed to the fence 2 along the passage 35.
Contaminant removal device 4 with a simple structure in which only 4 to 27 are lined up
1 is configured to separate and remove contaminants.
Description
【0001】[0001]
【産業上の利用分野】本発明は、湖沼、ダム湖などの閉
鎖性水域の浄化技術に係り、特に水道水源用閉鎖性水域
の浄化技術に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a technique for purifying closed water bodies such as lakes and dams, and more particularly to a technique for purifying closed water bodies for tap water sources.
【0002】[0002]
【従来の技術】近年、浄水場の水源である湖沼、ダム湖
などの閉鎖性水域において、窒素や燐等の富栄養物の流
入量が多くなり、藻類が大量発生する富栄養化現象が進
んでいる。このような閉鎖性水域の浄化技術は、数々の
ものが提案されているが、これらを大きく分類すると、
汚染物を機械的に除去する技術、微生物を活性化させる
ことにより処理する技術、薬品等により化学的に処理す
る技術、閉鎖性水域の一部の水を循環させることにより
処理する技術等に分類される。例えば、従来技術1とし
て、特開平2−95498号公報において、閉鎖性水域
の富栄養化に対する水処理方法及び装置であって、富栄
養化に伴って発生する藻類を除去する処理工程及び処理
装置と、嫌気性微生物による処理を施す処理工程及び処
理装置と、好気性微生物による処理を施す処理工程及び
処理装置と、化学的処理により残存する燐分を除去する
処理工程及び処理装置とを備えた水処理方法及び装置が
記載されている。また従来技術2として、特開平5−2
87号公報において、双胴型の台船の内側水面に、上部
が開口した凹状断面の樋の複数個を適宜な間隔をあけて
並設したフロート付の気泡回収用いかだを、各樋の側端
部がわずかに水面上にある吃水状態に調節可能に連結す
ると共に、その気泡回収用いかだの水中下方から気泡を
発生させる気泡造成装置を配設し、更に各樋内に進入し
た気泡の回収手段を設け、主に海や湖沼などの閉鎖性水
域の水中の懸濁物質を除去してその水域の水質浄化をは
かるために使用する汚濁水の浄化装置が記載されてい
る。2. Description of the Related Art In recent years, in the closed water areas such as lakes and dams, which are the water sources of water purification plants, the inflow of eutrophication such as nitrogen and phosphorus has increased, and eutrophication phenomenon in which a large amount of algae is generated has progressed. I'm out. There are many proposals for such purification technology for closed water areas.
Classified into technologies for mechanically removing contaminants, technologies for activating microorganisms, technologies for chemically treating with chemicals, and technologies for circulating a portion of water in closed water areas. To be done. For example, as prior art 1, in Japanese Patent Application Laid-Open No. 2-95498, a water treatment method and apparatus for eutrophication of a closed water area, which is a treatment step and treatment apparatus for removing algae generated with eutrophication And a treatment step and a treatment apparatus for performing treatment with an anaerobic microorganism, a treatment step and a treatment apparatus for performing treatment with an aerobic microorganism, and a treatment step and a treatment apparatus for removing residual phosphorus by chemical treatment. A water treatment method and apparatus is described. Further, as the prior art 2, Japanese Patent Laid-Open No. 5-2
In Japanese Patent Publication No. 87, a glove with a bubble collecting device, in which a plurality of gutters having a concave cross section with an open upper portion are juxtaposed at appropriate intervals on the inner water surface of a catamaran type boat, is provided on each gutter side. The ends are slightly above the water surface and adjustably connected to the water level, and the bubble recovery device is equipped with a bubble generating device to generate bubbles from under the water in the rack, and the recovery of the bubbles that have entered each trough. There is described a polluted water purifying device which is provided with a means and is mainly used for purifying the water quality of the water by removing suspended matter in the water of closed water such as the sea and lakes.
【0003】[0003]
【発明が解決しようとする課題】浄水場の水源である湖
沼、ダム湖などの閉鎖性水域において、富栄養化現象が
進むことにより、閉鎖性水域を水源としている水道水は
その浄化設備である浄水場を増強する必要がでてきた。
しかし、閉鎖性水域における富栄養化現象は今後も進む
ことが予想されており、浄水場の増強だけでは対応しき
れないのが現状であり、浄水場の水源である湖沼、ダム
湖などの閉鎖性水域の水質改善が望まれている。しかし
ながら、上記従来技術1、2では、浄水場の水源である
閉鎖性水域における富栄養化現象に対して十分を対処で
きるものでなく、従って浄水場における浄化処理量を大
幅に低減しえない課題を有するものである。[Problems to be Solved by the Invention] In a closed water area such as a lake, a dam, etc., which is the water source of a water purification plant, tap water whose source is the closed water area is a purification facility due to the progress of eutrophication phenomenon. There is a need to increase the water treatment plant.
However, it is expected that the eutrophication phenomenon in closed water areas will continue to progress in the future, and it is the current situation that it cannot be dealt with only by strengthening the water purification plant, and the water sources of the water purification plant such as lakes and dams are closed. It is desired to improve the water quality of natural waters. However, the above-mentioned prior arts 1 and 2 cannot sufficiently deal with the eutrophication phenomenon in the closed water area which is the water source of the water purification plant, and therefore the purification treatment amount in the water purification plant cannot be significantly reduced. Is to have.
【0004】また従来技術1においては、大がかりな設
備を設置しなければならないという課題も有するもので
ある。The prior art 1 also has a problem that large-scale equipment must be installed.
【0005】本発明の目的は、上記従来技術の課題を解
決すべく、浄水場の水源である湖沼、ダム湖などの閉鎖
性水域において、汚染物による富栄養化現象を解決して
水質を大幅に改善した多量の処理水を浄水場へ供給して
浄水場における浄化処理量を大幅に低減できるようにし
た局所水域浄化システム及びその方法を提供することに
ある。また本発明の他の目的は、浄水場の水源である湖
沼、ダム湖などの閉鎖性水域において、簡易な装置また
はシステムにより被処理水中の富栄養化物質や藻類等の
汚染物質を効率よく分離除去して浄化された処理水を浄
水場へ供給できるようにした局所水域浄化システム及び
その方法を提供することにある。また本発明の他の目的
は、簡易な装置により被処理水中の富栄養化物質や藻類
等の汚染物質を効率よく分離除去して浄化する浄化装置
及び汚染物質除去装置を提供することにある。In order to solve the above-mentioned problems of the prior art, an object of the present invention is to solve the eutrophication phenomenon due to pollutants in a closed water area such as a lake, dam lake, etc. (EN) Provided is a local water area purification system and method capable of supplying a large amount of improved treated water to a water purification plant to significantly reduce the amount of purification treatment in the water purification plant. Another object of the present invention is to efficiently separate contaminants such as eutrophication substances and algae in the water to be treated by a simple device or system in closed water areas such as lakes and dams that are the water source of the water purification plant. It is an object of the present invention to provide a local water area purification system and method capable of supplying treated water that has been removed and purified to a water purification plant. Another object of the present invention is to provide a purifying device and a pollutant removing device that efficiently separate and remove pollutants such as eutrophication substances and algae in the water to be treated with a simple device.
【0006】[0006]
【課題を解決するための手段】上記目的を達成するため
に、本発明は、水源である湖沼、ダム湖などの閉鎖性水
域の少なくとも一部を囲むように深さ方向に仕切って処
理水域を形成する仕切り物体または仕切り装置と、前記
閉鎖性水域または処理水域の水を取水してこの水に存在
する汚染物を分離除去し、この分離除去された処理水を
前記処理水域に放出する浄化装置とを備え、該浄化装置
で浄化された前記処理水域内の水を浄水場へ取水するよ
うに構成したことを特徴とする局所水域浄化システムで
ある。In order to achieve the above object, the present invention divides a treated water area by partitioning it in the depth direction so as to surround at least a part of a closed water area such as a lake, a dam lake or the like which is a water source. A partition object or partition device to be formed, and a purifying device that takes in water in the closed water area or treated water area to separate and remove contaminants existing in the water, and discharges the separated and removed treated water to the treated water area. A local water area purification system comprising: a water purifying apparatus for collecting water in the treated water area that has been purified by the purification apparatus to a water purification plant.
【0007】また本発明は、前記局所水域浄化システム
における前記浄化装置において、分離除去する汚染物と
して富栄養物質または藻類を含むことを特徴とする。ま
た本発明は、前記局所水域浄化システムにおける前記浄
化装置を、前記閉鎖性水域または処理水域内に設置した
ことを特徴とする。また本発明は、前記局所水域浄化シ
ステムにおいて、前記浄化装置は、前記閉鎖性水域また
は処理水域の水を取水するためのポンプと、このポンプ
の働きによって取水された水を瀘材と接触させて浄化し
て処理水を放出する濾過槽と、該濾過槽から放出された
処理水に存在する浮遊物質を沈降させる沈殿槽とを備え
たことを特徴とする。また本発明は、前記局所水域浄化
システムにおいて、前記浄化装置には、前記ポンプを駆
動する電源を備えたことを特徴とする。また本発明は、
前記電源として、ソ−ラ発電パネルと該ソ−ラ発電パネ
ルから得られる電気を蓄電する蓄電器とで構成したこと
を特徴とする。また本発明は、前記局所水域浄化システ
ムにおいて、前記仕切り物体または仕切り装置の上部
に、前記浄化装置で処理した汚染物を流す補助通路を形
成したことを特徴とする。また本発明は、前記局所水域
浄化システムにおいて、前記浄化装置を、前記閉鎖性水
域内に浮漂させたことを特徴とする。Further, the present invention is characterized in that, in the above-mentioned purification device in the above-mentioned local water purification system, a rich nutrient or algae is contained as a contaminant to be separated and removed. Further, the present invention is characterized in that the purification device in the local water purification system is installed in the closed water area or the treated water area. Further, the present invention is, in the local water purification system, the purification device, a pump for taking in water of the closed water region or the treated water region, the water taken by the action of this pump is brought into contact with the filter. It is characterized by comprising a filter tank for purifying and discharging treated water, and a settling tank for settling suspended substances existing in the treated water discharged from the filter tank. Further, according to the present invention, in the local water area purification system, the purification apparatus includes a power source for driving the pump. The present invention also provides
The power source includes a solar power generation panel and a power storage device that stores electricity obtained from the solar power generation panel. Further, the present invention is characterized in that, in the local water purification system, an auxiliary passage is formed in an upper portion of the partition object or the partition device, through which contaminants processed by the purification device flow. Further, the present invention is characterized in that, in the local water purification system, the purification device is floated in the closed water area.
【0008】また本発明は、水源である湖沼、ダム湖な
どの閉鎖性水域の少なくとも一部を囲むように深さ方向
に仕切って処理水域の少なくとも一部を形成する仕切り
物体または仕切り装置と、前記閉鎖性水域または処理水
域の水を取水するための取水手段と該取水手段によって
取水された被処理水を瀘材と接触させて浄化して放出ま
たは流出する濾過手段と該濾過手段から放出または流出
された被処理水に存在する浮遊物質を沈降させる沈殿手
段とを備え、前記取水された被処理水に存在する汚染物
を前記濾過手段と沈殿手段とで分離除去して処理水を前
記処理水域に放出または流出するように構成した浄化装
置とを備え、該浄化装置で浄化された前記処理水域内の
水を浄水場へ取水するように構成したことを特徴とする
局所水域浄化システム及びその方法である。The present invention also provides a partitioning object or partitioning device for partitioning at least a part of a closed water area such as a lake or dam, which is a water source, in the depth direction so as to form at least a part of a treated water area, Intake means for taking in water in the closed water area or treated water area, and filtration means for contacting and purifying the treated water taken by the intake means with a filter material and discharging or flowing out, and discharging from the filtering means And a sedimentation means for settling floating substances existing in the treated water that has flowed out, wherein contaminants existing in the treated water that has been taken in are separated and removed by the filtration means and the sedimentation means to treat the treated water. A local water purification system, comprising: a purification device configured to be discharged or discharged into a water area, and configured to take water in the treated water area purified by the purification device to a water purification plant. It is a non-and a method thereof.
【0009】また本発明は、水源である湖沼、ダム湖な
どの閉鎖性水域の少なくとも一部を囲むように深さ方向
に仕切って処理水域の少なくとも一部を形成する仕切り
物体または仕切り装置と、前記閉鎖性水域または処理水
域の水を取水するための取水手段と該取水手段によって
取水された被処理水に存在する浮遊物質を沈降させる沈
殿手段と該沈殿手段で処理された被処理水を瀘材と接触
させて浄化して処理水を放出または流出する濾過手段と
を備え、前記取水された被処理水に存在する汚染物を前
記沈殿手段と濾過手段とで分離除去して処理水を前記処
理水域に放出または流出するように構成した浄化装置と
を備え、該浄化装置で浄化された前記処理水域内の水を
浄水場へ取水するように構成したことを特徴とする局所
水域浄化システム及びその方法である。また本発明は、
水源である湖沼、ダム湖などの閉鎖性水域から取水また
は流入される被処理水に存在する浮遊物質を沈降させる
沈殿手段と該沈殿手段で処理された被処理水を瀘材と接
触させて浄化して処理水を放出または流出する濾過手段
とを備え、前記被処理水に存在する汚染物を前記沈殿手
段と濾過手段とで分離除去して浄化された処理水を処理
水域に放出または流出するように構成した浄化装置を備
え、該浄化装置で浄化された処理水を浄水場へ取水する
ように構成したことを特徴とする局所水域浄化システム
及びその方法である。また本発明は、水源である湖沼、
ダム湖などの閉鎖性水域から取水または流入される被処
理水を瀘材と接触させて浄化して放出または流出する濾
過手段と該濾過手段で浄化された被処理水に存在する浮
遊物質を沈降させる沈殿手段とを備え、前記被処理水に
存在する汚染物を前記濾過手段と沈殿手段とで分離除去
して浄化された処理水を処理水域に放出または流出する
ように構成した浄化装置を備え、該浄化装置で浄化され
た処理水を浄水場へ取水するように構成したことを特徴
とする局所水域浄化システム及びその方法である。The present invention also provides a partitioning object or a partitioning device that partitions at least a part of a closed water body such as a lake or a dam lake, which is a water source, in the depth direction to form at least a part of a treated water body, Water intake means for taking in water in the closed water area or treated water area, settling means for settling floating substances present in the treated water taken by the water intake means, and treated water treated by the settling means And a filtering means for purifying the treated water by contacting with the material to release or discharge the treated water. The treated water is separated and removed by the sedimentation means and the filtering means existing in the water to be treated. A local water purification system comprising: a purifying device configured to be discharged or discharged into a treated water region, and configured to take water in the treated water region purified by the purifying device to a water purification plant. Beauty is that way. The present invention also provides
Precipitation means for sedimenting suspended solids present in the treated water that is taken in or flowing in from closed water areas such as lakes and dams that are water sources, and the treated water treated by the sedimentation means is contacted with a filter to purify And a discharge means for discharging or discharging the treated water, wherein contaminants existing in the water to be treated are separated and removed by the precipitation means and the filtering means, and purified treated water is discharged or discharged to the treated water area. A local water area purification system and a method thereof, comprising the purification device configured as described above, and configured to take the treated water purified by the purification device to a water purification plant. In addition, the present invention is a lake, which is a water source,
Filtering means that purifies treated water that is taken in or flowing in from a closed water area such as a dam lake by contacting with a filter and discharges or discharges it, and settles suspended substances existing in the treated water purified by the filtering means And a purifying device configured to discharge or outflow the treated water purified by separating and removing the contaminants existing in the water to be treated by the filtering means and the sedimenting means. A local water area purification system and a method thereof, wherein the treated water purified by the purification apparatus is configured to be taken into a water purification plant.
【0010】また本発明は、前記局所水域浄化システム
において、前記浄化装置の濾過手段として、流動床式の
濾過槽で構成したことを特徴とする。また本発明は、前
記局所水域浄化システムにおいて、前記浄化装置の濾過
手段として、水頭圧差により、濾材を充填した濾過槽の
底部に放出された被処理水に対して前記濾材と接触しな
がら上昇流が生じるように構成したことを特徴とする。
また本発明は、前記局所水域浄化システムにおいて、前
記浄化装置を前記閉鎖性水域内を浮漂するように構成し
たことを特徴とする。また本発明は、前記局所水域浄化
システムにおいて、前記浄化装置の濾過手段として、被
処理水を木炭等の濾材と接触しながら通過させると共に
爆気することによって被処理水中のアンモニア性窒素を
硝酸性窒素に変換するように構成したことを特徴とす
る。また本発明は、前記局所水域浄化システムにおい
て、前記浄化装置の沈殿手段として、被処理水について
底部に沿った流れから上昇流を発生させて、この流れに
よる遠心力によって浮遊物質を沈降させて除去するよう
に構成したことを特徴とする。また本発明は、前記局所
水域浄化システムにおいて、前記浄化装置の沈殿手段と
して、被処理水について底部に沿った流れから上昇流を
発生させて、この流れによる遠心力によって浮遊物質を
沈降させて堆積させることによって除去し、この堆積し
た汚泥を回収するように構成したことを特徴とする。Further, the present invention is characterized in that, in the local water area purification system, a fluidized bed type filtration tank is used as a filtration means of the purification apparatus. Further, in the present invention, in the local water purification system, as a filtering means of the purification device, due to a head pressure difference, an ascending flow of the water to be treated discharged to the bottom of the filter tank filled with the filter medium is brought into contact with the filter medium. It is characterized in that it is configured to occur.
Further, the present invention is characterized in that, in the local water purification system, the purification device is configured to float in the closed water. Further, the present invention, in the local water purification system, as the filtering means of the purification device, the treated water is allowed to pass while being in contact with a filter medium such as charcoal, and at the same time, decomposing ammoniacal nitrogen in the treated water into nitric acid. It is characterized in that it is configured to be converted into nitrogen. Further, in the present invention, in the local water purification system, as a sedimentation means of the purification device, an upward flow is generated from the flow along the bottom of the water to be treated, and the suspended matter is sedimented and removed by the centrifugal force of this flow. It is characterized in that it is configured to. Further, the present invention is, in the above-mentioned local water purification system, as a settling means of the above-mentioned purification apparatus, an ascending flow is generated from a flow along the bottom of the water to be treated, and a floating substance is settled and deposited by centrifugal force due to this flow. It is characterized in that it is configured to collect the sludge accumulated by removing the sludge.
【0011】また本発明は、水源である湖沼、ダム湖な
どの閉鎖性水域の少なくとも一部を囲むように深さ方向
に仕切って処理水域を形成する仕切り物体と、前記処理
水域内に設置され、前記処理水域から取水された水に存
在する汚染物を瀘材と接触させて分離除去する濾過槽を
有し、該濾過槽で処理された処理水を前記処理水域に放
出する浄化装置とを備え、該浄化装置で浄化された前記
処理水域内の水を浄水場へ取水するように構成したこと
を特徴とする局所水域浄化システム及びその方法であ
る。また本発明は、水源である湖沼、ダム湖などの閉鎖
性水域内に形成された流路に沿って被処理水を流してに
おいて、沿っての少なくとも一部を囲うように深さ方向
に仕切って処理水域の少なくとも一部を形成するととも
に汚染物除去機能を有する仕切り物体と、前記処理水域
の水の中に存在する藻類を除去する藻類除去装置と、該
藻類除去装置で藻類が除去された処理水を通すことによ
って浄化する浄化装置とを備え、該浄化装置で浄化され
た前記処理水域内の水を浄水場へ取水するように構成し
たことを特徴とする局所水域浄化システム及びその方法
である。The present invention is also provided with a partitioning object for partitioning at least a part of a closed water area such as a lake or dam, which is a water source, in the depth direction to form a treated water area, and a partition object installed in the treated water area. A purification device having a filter tank for separating and removing contaminants existing in water taken from the treated water area by contacting with a filter, and discharging the treated water treated in the filter tank to the treated water area. A local water area purification system and a method thereof, characterized by being configured to take in water in the treated water area purified by the purification apparatus to a water purification plant. In addition, the present invention is a method of flowing water to be treated along a flow path formed in a closed water area such as a lake or a dam, which is a water source, and partitioning it in the depth direction so as to surround at least a part of the water. A partition body that forms at least a part of the treated water area and has a contaminant removal function, an algae removal device that removes algae present in the water of the treated water area, and algae removed by the algae removal apparatus A local water purification system and method comprising a purifying device for purifying the treated water by passing the treated water into the water purification plant. is there.
【0012】また本発明は、前記局所水域浄化システム
において、前記浄化装置は、流路の所望の個所に布状ま
たは格子状または網状の瀘材を設置して形成したことを
特徴とする。また本発明は、水源である湖沼、ダム湖な
どの閉鎖性水域の少なくとも一部を囲うように深さ方向
に仕切ると共に汚染物除去機能を備えた仕切り装置と、
浄水場へ処理水域の水を汲み上げる処理水域内に設置さ
れた取水配管と、この取水配管と仕切り装置の間に存在
し、処理水域の水の藻類を除去する藻類除去装置と、こ
の藻類除去装置と取水配管の間に存在し、処理水域の水
を不織布で浄化する不織布浄化装置とを備えたことを特
徴とする局所水域浄化システム及びその方法である。ま
た本発明は、被処理水を流す流路を形成し、底部に被処
理水を流入させる通路を有する第1の通路形成手段(第
1のフェンス)と、該第1の通路形成手段の通路を通っ
て流入する底部に沿った被処理水の流れを上昇流に変え
てこの流れに基づく遠心力によって浮遊物質を沈降させ
て底部に汚泥として堆積させる第2の通路形成手段(第
2のフェンス)と、該第2の通路形成手段の上部に有す
る通路を通して流れる被処理水を更に底部に導いて底部
に通路を有する第3の通路形成手段(第3のフェンス)
と、該第3の通路形成手段の通路を通して流入される被
処理水を、木炭等の濾材層を通して曝気することによっ
て被処理水中のアンモニア性窒素を硝酸性窒素に変換す
るように構成した濾過手段とを前記流路に沿って設置し
て構成したことを特徴とする汚染物質除去装置である。Further, the present invention is characterized in that, in the system for purifying local water, the purifying device is formed by installing a cloth-like, lattice-like, or net-like filter material at a desired portion of a flow path. Further, the present invention is a partitioning device having a contaminant removing function as well as partitioning in the depth direction so as to surround at least a part of a closed water area such as a lake or a dam that is a water source,
A water intake pipe that pumps water from the treated water area to the water treatment plant, an algae removal device that exists between the water intake pipe and the partitioning device, and removes algae from the water in the treated water area, and this algae removal device And a non-woven fabric purifying device for purifying water in a treated water region with a non-woven fabric, which is provided between the water intake pipe and the water intake pipe. Further, the present invention provides a first passage forming means (first fence) having a passage through which the water to be treated flows, and a passage through which the water to be treated flows in, and a passage of the first passage forming means. Second passage forming means (second fence) for changing the flow of the water to be treated flowing through the bottom through the upward flow into an upward flow, and causing a centrifugal force based on the flow to settle suspended solids and deposit the sludge as sludge on the bottom. ), And third passage forming means (third fence) having the passage at the bottom by further guiding the water to be treated flowing through the passage provided at the upper part of the second passage forming means to the bottom.
And a filtering means configured to convert ammonia nitrogen in the water to be treated into nitrate nitrogen by aerating the water to be treated flowing through the passage of the third passage forming means through a filter medium layer such as charcoal. Is installed along the above-mentioned flow path, and is a contaminant removal device characterized by the above-mentioned.
【0013】また本発明は、水源である湖沼、ダム湖な
どの閉鎖性水域内において被処理水を流す流路を形成
し、底部に被処理水を流入させる通路を有する第1の通
路形成手段(第1のフェンス)と、該第1の通路形成手
段の通路を通って流入する底部に沿った被処理水の流れ
を上昇流に変えてこの流れに基づく遠心力によって浮遊
物質を沈降させて底部に汚泥として堆積させる第2の通
路形成手段(第2のフェンス)と、該第2の通路形成手
段の上部に有する通路を通して流れる被処理水を更に底
部に導いて底部に通路を有する第3の通路形成手段(第
3のフェンス)と、該第3の通路形成手段の通路を通し
て流入される被処理水を、木炭等の濾材層を通して曝気
することによって被処理水中のアンモニア性窒素を硝酸
性窒素に変換するように構成した濾過手段とを前記流路
に沿って設置して構成した汚染物質除去装置を備えたこ
とを特徴とする局所水域浄化システムである。Further, according to the present invention, there is provided a first passage forming means for forming a flow path for the water to be treated in a closed water area such as a lake or a dam lake, which is a water source, and having a passage for allowing the water to be treated to flow into the bottom portion. (First fence), and the flow of the water to be treated along the bottom flowing through the passage of the first passage forming means is changed to an upward flow, and the suspended matter is settled by the centrifugal force based on this flow. Second passage forming means (second fence) for depositing sludge on the bottom, and water to be treated flowing through the passage provided at the upper part of the second passage forming means further guided to the bottom so as to have a passage at the bottom. The passage forming means (third fence) and the water to be treated flowing through the passage of the third passage forming means are aerated through a filter medium layer of charcoal or the like, so that ammoniacal nitrogen in the water to be treated is converted into nitric acid. I'll convert it to nitrogen It is the local water purification system, characterized in that the filtering means arranged with a contaminant removal device constructed and placed along the flow path.
【0014】また本発明は、前記局所水域浄化システム
における前記汚染物質除去装置において、前記第2の通
路形成手段で底部に堆積した汚泥を回収する回収手段を
設置したことを特徴とする。また本発明は、水源である
湖沼、ダム湖などの閉鎖性水域の少なくとも一部を囲う
ように深さ方向に仕切って処理水域の少なくとも一部を
構成する仕切り装置と、浄水場へ前記処理水域の水を汲
み上げる前記処理水域に設置された取水配管と、前記処
理水域外の水域の水を取り込みこの取り込まれた水の中
に存在する汚染物を分離除去し、この分離除去した処理
水を前記処理水域に放出する浄化装置とを備えたことを
特徴とする局所水域浄化システムである。また本発明
は、水源である湖沼、ダム湖などの閉鎖性水域の少なく
とも一部を囲むように深さ方向に仕切る水域仕切り物体
において、複数の仕切り物体を鎖で簾状に接続し、該簾
状の仕切り物体の一部に前記処理水域外の水域の水が通
る開口を形成し、ブイで前記簾状の仕切り物体を水中に
保持するように構成したことを特徴とする水域仕切り物
体である。Further, the present invention is characterized in that, in the pollutant removing device in the local water purification system, a collecting means for collecting the sludge accumulated on the bottom portion by the second passage forming means is installed. Further, the present invention is a partitioning device that partitions at least a part of a closed water area such as a lake or a dam lake as a water source so as to surround at least a part of the closed water area to form at least a part of the treated water area, and the treated water area to the water treatment plant. The intake pipe installed in the treated water area for pumping up the water and the water in the water area outside the treated water area are taken in to separate and remove the contaminants present in the taken water, and the separated and removed treated water is A local water area purification system, comprising: a purifying device that discharges the treated water area. Further, the present invention is a water body partitioning body that partitions in the depth direction so as to surround at least a part of a closed water body such as a lake or a dam that is a water source, and connects a plurality of partitioning bodies with a chain in a blind shape, A water-area partitioning object, characterized in that an opening through which water in a water area outside the treated water area is formed is formed in a part of the water-shaped partitioning object, and the buoy is used to hold the blind-shaped partitioning object in water. .
【0015】また本発明は、閉鎖性水域の少なくとも一
部を深さ方向に仕切る一つ以上の仕切り装置と、浄水場
へ前記処理水域の水を汲み上げる前記処理水域に設置さ
れた取水配管と、前記閉鎖性水域の水を取り込みこの取
り込まれた水の中に存在する汚染物を分離除去し、この
汚染物を分離除去された処理水を前記仕切り装置と前記
取水配管の間に放出する浄化装置とを備えたことを特徴
とする局所水域浄化システムである。また本発明は、閉
鎖性水域の少なくとも一部を囲うように水底に散気管を
設けこの散気管から気泡を発生させ処理水域の少なくと
も一部を構成する仕切り手段と、浄水場へ前記処理水域
の水を汲み上げる前記処理水域に設置された取水配管
と、前記閉鎖性水域の水を取り込みこの取り込まれた水
の中に存在する汚染物を分離除去し、この汚染物を分離
除去された処理水を前記処理水域に放出する浄化装置と
を備えたことを特徴とする局所水域浄化システムであ
る。Further, the present invention comprises one or more partitioning devices for partitioning at least a part of the closed water area in the depth direction, and an intake pipe installed in the treated water area for pumping the water of the treated water area to a water treatment plant, A purification device that takes in water in the closed water area, separates and removes contaminants existing in the taken-in water, and releases treated water from which the contaminants have been separated and removed between the partition device and the intake pipe. It is a local water area purification system characterized by having and. Further, the present invention provides a diffusing pipe at the bottom of the water so as to surround at least a part of the closed water area, a partition means for generating bubbles from this diffusing tube and constituting at least a part of the treated water area, and a treatment means to the water treatment plant of The intake pipe installed in the treated water area for pumping water and the water in the closed water area are taken in to separate and remove the pollutants present in the taken water, and the treated water from which the pollutant is separated and removed is It is a local water area purification system provided with the purification device which discharges to the above-mentioned treated water area.
【0016】また本発明は、水源である湖沼、ダム湖な
どの閉鎖性水域において、被処理水中に存在する汚染物
を分離除去して浄化された処理水を仕切られた処理水域
に放出し、前記処理水域内の処理水を取水配管により浄
水場へ供給することを特徴とする局所水域浄化方法であ
る。また本発明は、浄化するための水を取水するポンプ
と、このポンプで取水した被処理水を浄化するための濾
材を充填した濾過槽と、該濾過槽で浄化された処理水を
放出する放出部と、この放出部の下流側に水中の浮遊物
質を沈降させて除去する沈殿槽を備えたことを特徴とす
る浄化装置である。また本発明は、前記局所水域浄化シ
ステム及びその方法において、前記処理水域の容積が一
日の取水量の2倍から3倍であり、前記浄化装置の一日
の処理能力が一日の取水量の1/2から1/3であるこ
とを特徴とする。Further, according to the present invention, in a closed water area such as a lake or a dam lake, which is a water source, the treated water purified by separating and removing contaminants existing in the water to be treated is discharged to the partitioned treated water area, A method for purifying a local water area, characterized in that the treated water in the treated water area is supplied to a water purification plant through a water pipe. The present invention also provides a pump for taking in water for purification, a filter tank filled with a filter medium for purifying the water to be treated taken in by this pump, and a discharge for releasing the treated water purified by the filter tank. And a settling tank for settling and removing suspended solids in water on the downstream side of the discharge section. Further, the present invention is the above-mentioned local water area purification system and method, wherein the volume of the treated water area is 2 to 3 times the daily water intake amount, and the daily treatment capacity of the purification device is the daily water intake amount. It is characterized in that it is 1/2 to 1/3.
【0017】[0017]
【作用】前記構成により、浄水場の水源である湖沼、ダ
ム湖などの閉鎖性水域において、流入する栄養塩濃度が
高くなり、藻類等が大量に発生する富栄養化現象が生じ
て、この大量発生した藻類等が死滅して底泥に堆積し、
底泥において微生物の作用で死滅した藻類の分解が起こ
って窒素成分がアンモニア性窒素の形で水中に溶出し、
それが直接浄水場へ供給されることを防止することがで
きる。そのため、上記閉鎖性水域における処理水域から
浄水場へ供給される水に含まれるアンモニア性窒素の濃
度が著しく低くなり、浄水場において投入される消毒用
の塩素の量が著しく低減されて、残留塩素と有機物とが
化合してできるトリハロメタン等の発癌性物質の発生を
殆どなくすことができる。また上記閉鎖性水域から、汚
染物による富栄養化現象を解決して、水質を大幅に改善
した多量の処理水を浄水場へ供給することができるの
で、浄水場における浄化処理量を大幅に低減することが
できる。[Advantage] With the above structure, in a closed water area such as a lake, a dam lake, etc., which is the water source of the water purification plant, the concentration of inflowing nutrients becomes high, and a eutrophication phenomenon occurs in which a large amount of algae and the like occur, and this large The generated algae die and accumulate in the bottom mud,
In the bottom mud, the decomposition of algae killed by the action of microorganisms occurs, and the nitrogen component is eluted in water in the form of ammonia nitrogen.
It can be prevented from being directly supplied to the water purification plant. Therefore, the concentration of ammonia nitrogen contained in the water supplied from the treated water area to the water purification plant in the above closed water area is significantly reduced, and the amount of chlorine for disinfection input in the water purification plant is significantly reduced, resulting in residual chlorine. The generation of carcinogenic substances such as trihalomethane, which are formed by the combination of the organic substances with organic substances, can be almost eliminated. Also, from the closed water area, it is possible to solve the eutrophication phenomenon due to pollutants and supply a large amount of treated water with significantly improved water quality to the water treatment plant, so the amount of purification treatment at the water treatment plant is greatly reduced. can do.
【0018】また前記構成により、浄水場の水源である
湖沼、ダム湖などの閉鎖性水域において、簡易な装置ま
たはシステムにより被処理水中の富栄養化物質や藻類等
の汚染物質を効率よく分離除去して浄化された処理水を
浄水場へ供給することができる。また前記構成により、
簡易な装置により被処理水中の富栄養化物質や藻類等の
汚染物質を効率よく分離除去して浄化する浄化装置及び
汚染物質除去装置を実現することができる。また前記構
成により、浄化装置等を閉鎖性水域内に浮漂または閉鎖
性水域内に形成した流路に沿って設置したことにより、
陸地に設置場所(設置スペース)を確保する必要がなく
なる。また前記構成により、浄化装置等において被処理
水の流れを水頭圧差または自然の流れによって生じるよ
うにしたので、被処理水を流すための動力が不要とな
り、簡素な構成にすることができ、設備費、運転費、保
守費を安価にすることができる。Further, with the above-mentioned constitution, in a closed water area such as a lake, a dam lake or the like which is the water source of the water purification plant, a simple device or system can efficiently separate and remove eutrophication substances and pollutants such as algae in the water to be treated. The purified treated water can be supplied to the water purification plant. Further, according to the above configuration,
It is possible to realize a purifying device and a pollutant removing device that efficiently separate and remove pollutants such as eutrophication substances and algae in the water to be treated with a simple device. Further, with the above configuration, by installing a purifying device or the like along the flow path formed in the closed water area or floating in the closed water area,
There is no need to secure an installation site (installation space) on land. Further, with the above-mentioned configuration, the flow of the water to be treated is caused by the head pressure difference or the natural flow in the purifying device and the like, so that the power for flowing the water to be treated is not required, and the structure can be simplified. Costs, operating costs, and maintenance costs can be reduced.
【0019】またポンプ等の電力を、ソ−ラ発電パネル
から得るようにしたので、電力を供給する必要がない。
また浄水場の水源である湖沼、ダム湖などの閉鎖性水域
を仕切り装置で仕切って処理水域を形成したので、処理
水域の水量を限定することができ、処理能力の小さな浄
化装置でも、十分富栄養化物質や藻類等の汚染物質を分
離除去して浄化された処理水を処理水域に放出または流
出して浄水場へ安定して供給することができる。また浄
水場の水源である湖沼、ダム湖などの閉鎖性水域を仕切
り装置で仕切って処理水域を形成したので、処理水域の
水が安定状態となり、処理水域内の汚染物の分布位置が
定まるため浄化装置の汚染物の取り込み効率を高くする
ことができる。Further, since the electric power of the pump or the like is obtained from the solar power generation panel, it is not necessary to supply the electric power.
In addition, because the treated water area is formed by partitioning closed water areas such as lakes and dams, which are the water sources of the water treatment plant, with a partitioning device, it is possible to limit the amount of water in the treated water area, and even a purification apparatus with a small treatment capacity is sufficiently rich. Treated water purified by separating and removing pollutants such as nutrients and algae can be discharged or discharged into the treated water area and stably supplied to the water purification plant. Also, because the treated water area was formed by partitioning closed water areas such as lakes and dams, which are the water sources of the water treatment plant, with partitioning devices, the water in the treated water area will be in a stable state and the distribution position of pollutants within the treated water area will be determined. The efficiency of uptake of contaminants in the purification device can be increased.
【0020】また十分富栄養化物質や藻類等の汚染物質
を分離除去して浄化された処理水をしばらくの間(約1
日〜2日程度)処理水域内に停留するようにすることに
よって、浄化装置にて処理しきれなかった汚染物を水中
の微生物に吸収させ、その微生物を約1日〜2日程度の
間のライフサイクルが終えて沈降して浄化することがで
きる。また汚染物質除去装置を、第1〜第3の通路形成
手段(第1〜第3のフェンス)と濾過手段とを流路に沿
って設置して構成したことにより、事前に処理水域の水
の汚染物を除去することができ、処理水域での浄化量を
大幅に低減することができる。Further, treated water purified by separating and removing sufficiently eutrophication substances and pollutants such as algae can be treated for a while (about 1
By staying in the treated water area, contaminants that could not be completely treated by the purification equipment will be absorbed by microorganisms in the water, and the microorganisms will be absorbed for about 1 to 2 days. It can be purified by sedimentation after the end of its life cycle. Further, since the pollutant removing device is configured by installing the first to third passage forming means (first to third fences) and the filtering means along the flow path, the water in the treated water area can be preliminarily obtained. Pollutants can be removed, and the amount of purification in the treated water area can be greatly reduced.
【0021】[0021]
【実施例】本発明の実施例について、図面を用いて説明
する。Embodiments of the present invention will be described with reference to the drawings.
【0022】本発明に係る局所水域浄化システムの一実
施例を図1乃至図9を用いて説明する。図1は、浄水場
(水処理場)への水源である湖沼、ダム湖等の閉鎖性水
域を上から見た図である。6は、浄水場(水処理場)1
への水源である湖沼、ダム湖等の閉鎖性水域を示す。こ
の湖沼、ダム湖等の閉鎖性水域6には、多量の水が蓄え
られることになる。1は浄水場(水処理場)を示す。2
は、浄水場1への取水口であり、浄水場1まで送水管5
でつながっている。3は防波堤を示す。4は陸地を示
す。そして、水源である湖沼、ダム湖等の閉鎖性水域6
(7、8)において、最近窒素や燐等の富栄養物質の流
入量が多くなり、藻類が大量発生し、汚染物質が多く存
在することになる。そこで、取水口2から多量の汚染物
質(富栄養物質(富栄養要素)や藻類等)が存在する水
が浄水場1へ供給されないように浄化させることが必要
となる。そのために、取水口6の周りの処理水域7を、
ブイ15を取り付けた仕切り装置14によって仕切って
この処理水域7内の水を浄化させる必要がある。そし
て、仕切り装置14によって仕切る処理水域7の容量
が、上記取水口2から浄水場1へ取水される1日の取水
量の約2〜3倍になるように仕切り装置14を設置すれ
ばよい。いずれにしても、閉鎖性水域6において仕切り
装置14によって処理水域7を仕切ることによって処理
水域7の外の水域8から多量の汚染物質を有する水が処
理水域7内に進入して処理水域7内の浄化された水と混
ざりあうことをできるだけ少なくして、処理水域7内の
水を浄化させた状態で保つことができる。One embodiment of the local water purification system according to the present invention will be described with reference to FIGS. 1 to 9. FIG. 1 is a view of a closed water area such as a lake, a dam lake or the like, which is a water source to the water purification plant (water treatment plant), seen from above. 6 is a water purification plant (water treatment plant) 1
Indicates a closed water area such as a lake, dam lake, etc. A large amount of water will be stored in the closed water area 6 such as the lake or dam. 1 shows a water purification plant (water treatment plant). Two
Is a water intake to the water treatment plant 1, and a water pipe 5 to the water treatment plant 1.
Connected. Reference numeral 3 indicates a breakwater. 4 indicates land. And closed water areas such as lakes and dams that are water sources 6
In (7, 8), the inflow of rich nutrients such as nitrogen and phosphorus has increased recently, a large amount of algae is generated, and many pollutants are present. Therefore, it is necessary to purify the water containing a large amount of pollutants (rich nutrients (rich nutrient elements), algae, etc.) from the intake port 2 so as not to be supplied to the water purification plant 1. For that purpose, the treated water area 7 around the intake 6 is
It is necessary to partition by the partition device 14 to which the buoy 15 is attached to purify the water in the treated water area 7. Then, the partitioning device 14 may be installed so that the volume of the treated water area 7 partitioned by the partitioning device 14 is about 2 to 3 times the daily intake amount of water taken from the water intake 2 to the water purification plant 1. In any case, by partitioning the treated water area 7 by the partitioning device 14 in the closed water area 6, the water containing a large amount of pollutants enters the treated water area 7 from the water area 8 outside the treated water area 7 and enters the treated water area 7. It is possible to keep the water in the treated water area 7 in a purified state by minimizing the mixing with the purified water in (1).
【0023】ところで、仕切り装置14によって外から
多くの上記汚染物質が処理水域7内に進入するのを防止
できる場合には、浄化装置11、12によって主に処理
水域7内の汚染物質を分離除去して浄化された処理水を
処理水域7内に放出すればよい。更に仕切り装置14の
外側近傍の水域に存在する汚染物質を分離除去して浄化
された処理水を処理水域7内に放出する浄化装置(図4
に11b、11cで示す。)を設置しても良い。このよ
うにすれば、処理水域7内に浄化された水をより多く作
って放出して保有することができる。なお、上記浄化装
置11、12の処理可能水量は1日の取水量の100%
から70%程度でよい。また、上記浄化装置11、12
は、図1においては、処理水域7内に浮漂させて設置す
る場合を示したが、処理水域7内で水底に固定して設置
しても良く、また配管は多少長くなるが処理水域7の外
側の水域8に浮漂若しくは水底に固定して設置してもよ
く、また配管は長くなるが陸地4に設置しても良い。浄
化装置11、12を水域7、8内に設置した場合、分離
除去した汚染物質を陸上まで回収できるようにすること
が必要となる。また浄化装置11、12を水域7、8内
に浮漂にして設置した場合、陸地に近付けてメンテナン
スすることができる。By the way, when the partitioning device 14 can prevent a large amount of the pollutants from entering the treated water area 7 from the outside, the purifying devices 11 and 12 mainly separate and remove the pollutants in the treated water area 7. Then, the purified treated water may be discharged into the treated water area 7. Further, a purification device for separating and removing pollutants existing in the water area near the outside of the partitioning device 14 and discharging purified water into the treated water area 7 (see FIG. 4).
11b and 11c. ) May be installed. By doing so, it is possible to make more purified water in the treated water area 7, release it, and retain it. The amount of water that can be treated by the purification devices 11 and 12 is 100% of the daily intake amount.
To about 70%. Further, the purification devices 11 and 12
In FIG. 1, the case where it is floated and installed in the treated water area 7 is shown, but it may be fixed to the bottom of the water in the treated water area 7, and the pipe becomes slightly longer, but It may be floated in the outer water area 8 or fixedly installed at the bottom of the water, and may be installed on the land 4 although the pipe is long. When the purifiers 11 and 12 are installed in the water bodies 7 and 8, it is necessary to enable the pollutants separated and removed to be recovered to the land. Further, when the purification devices 11 and 12 are installed in the water areas 7 and 8 in a floating state, they can be brought close to the land for maintenance.
【0024】上記汚染物質の一つである窒素、燐等など
の富栄養物質は、水底からの溶出成分であるため、水底
近傍で高濃度となり水面に近づくほどその濃度は低くな
る。そこで富栄養物質用浄化装置11により上記富栄養
物質(富栄養要素)を分離除去するためには、富栄養物
質用浄化装置11の取水口を水底近傍に設置することに
より高濃度の富栄養物質を直接扱うことができ、浄化効
率を高めることができる。また同様に、浮遊性の藻類等
は、水面近傍に高濃度の領域が形成される。そこでこれ
らの藻類を分離除去するための藻類用浄化装置(藻類除
去装置)12の取水口を水面近傍に設置することにより
藻類を高効率で除去することができる。即ち、浄化装置
12は濾材を用いて濾過して微生物との吸収等により藻
類等を分離除去する装置である。Since one of the above pollutants, such as nitrogen and phosphorus, is a leaching component from the bottom of the water, it has a high concentration near the bottom of the water and its concentration becomes lower as it approaches the water surface. Therefore, in order to separate and remove the above-mentioned eutrophication substances (eutrophication elements) by the eutrophication substance purification device 11, the intake port of the eutrophication substance purification device 11 is installed in the vicinity of the bottom of the water to provide a high concentration of eutrophication substances. Can be directly handled, and purification efficiency can be increased. Similarly, for floating algae, a high-concentration region is formed near the water surface. Therefore, the algae can be removed with high efficiency by installing the intake port of the algae purifying device (algae removing device) 12 for separating and removing these algae near the water surface. That is, the purifying device 12 is a device that separates and removes algae or the like by absorbing with microorganisms by filtering with a filter medium.
【0025】以上説明したように、汚染物質の多くを上
記浄化装置11、12で除去するが、上記浄化装置1
1、12の処理可能水量は1日の取水量の100%から
70%程度であり全ての汚染物質が除去される訳ではな
い。しかし、浄化装置11、12で除去されない汚染物
質は、しばらくの間(約2〜5日)処理水域7内に停留
することにより微生物により吸収され、その微生物が数
日間でライフサイクルを終えて沈降することになる。従
って汚染物質は、取水口2から浄水場1への取水される
可能性は低減される。何れにしても、上記浄化装置1
1、12によって富栄養物質や藻類等の汚染物質が分離
除去された浄化された処理水が処理水域7内に溜められ
て、給水管5を通して浄水場1へ供給されることにな
る。従って、常に浄水場1へ供給する処理水に含まれる
アンモニア性窒素成分を大幅に低減することができ、浄
水場1における水処理を大幅に低減することができる。
上記仕切り装置14は、樹脂性のシートあるいはネット
が用いられる。仕切り装置14は、水の出入りが殆ど生
じないように遮断する必要はなく、処理水域7の外の水
域8からの多量の汚染物質が処理水域7に進入して処理
水域7内の浄化された水と混じり合うことがある程度押
さえることができれば十分である。逆に仕切り装置14
に少しの水の出入りを許容することにより吹送流による
仕切り装置14への外力が緩和され、仕切り装置14の
流出を防止することができる。As described above, most of the pollutants are removed by the purification devices 11 and 12, but the purification device 1
The treatable water amounts of 1 and 12 are about 100% to 70% of the daily intake amount, and not all pollutants are removed. However, pollutants that are not removed by the purifiers 11 and 12 are absorbed by microorganisms by staying in the treated water area 7 for a while (about 2 to 5 days), and the microorganisms complete their life cycle within a few days and settle down. Will be done. Therefore, the pollutant is less likely to be taken from the water intake 2 to the water purification plant 1. In any case, the purification device 1
Purified treated water from which contaminants such as nutrients and algae have been separated and removed by 1 and 12 is stored in the treated water area 7 and supplied to the water purification plant 1 through the water supply pipe 5. Therefore, the ammonia nitrogen component contained in the treated water constantly supplied to the water purification plant 1 can be greatly reduced, and the water treatment in the water purification plant 1 can be greatly reduced.
As the partition device 14, a resin sheet or net is used. The partitioning device 14 does not need to be shut off so that water hardly enters and exits, and a large amount of pollutants from the water area 8 outside the treated water area 7 enter the treated water area 7 to be purified in the treated water area 7. It is enough to be able to prevent some mixing with water. Conversely, the partition device 14
By allowing a small amount of water to flow in and out, the external force to the partitioning device 14 due to the blowing flow is mitigated, and the outflow of the partitioning device 14 can be prevented.
【0026】次に上記浄化装置11について具体的に説
明する。即ち、図2は、上記浄化装置11の一実施例で
あるは流動床式浄化装置を示す外観斜視図、図3は図2
に示す流動床式浄化装置の縦断側面図である。上記浄化
装置11の一実施例である流動床式浄化装置11’は、
コ字状に連結された浮子46a〜46cが設けられ、閉
鎖性水域6(7、8)内に浮漂できるように構成されて
いる。なお、閉鎖性水域6(7、8)内の水底に固定す
る場合には、浮子46a〜46cの代わりに杭を設けて
支持すれば良い。流動床式浄化装置11’を陸地4上に
設置する場合には、上記浮子46a〜46cは不要とな
る。しかし、流動床式浄化装置11’を、浮子46a〜
46cで閉鎖性水域6(7、8)内に浮漂させることに
よって、閉鎖性水域6内で水上を容易に移動させて固定
することができ、汚染物質の発生状況に合わせて取水口
44を位置つけることができ、メンテナンスできるよう
に陸地に近付けることができる。また流動床式浄化装置
11’を、浮子46a〜46cで閉鎖性水域6(7、
8)内に浮漂させることによって、流動床式浄化装置1
1’を陸上に設置するより配管を短くすることができる
と共に、流動床式浄化装置11’を設置するスペースを
陸上に確保する必要がない。Next, the purifying device 11 will be specifically described. That is, FIG. 2 is an external perspective view showing a fluidized bed type purification apparatus which is one embodiment of the purification apparatus 11, and FIG.
It is a vertical side view of the fluidized bed type purification apparatus shown in FIG. The fluidized bed type purification apparatus 11 ′, which is an example of the purification apparatus 11, is
Floats 46a to 46c connected in a U-shape are provided so that they can float in the closed water area 6 (7, 8). In addition, when fixing to the water bottom in the closed water area 6 (7, 8), a pile may be provided and supported instead of the floats 46a to 46c. When the fluidized bed purification apparatus 11 'is installed on the land 4, the floats 46a to 46c are unnecessary. However, the fluidized bed type purifying apparatus 11 ′ is attached to the float 46 a.
By floating in the closed water area 6 (7, 8) at 46c, it can be easily moved and fixed on the water in the closed water area 6, and the intake port 44 can be positioned according to the generation status of pollutants. It can be turned on and brought close to the land for maintenance. In addition, the fluidized bed type purifying apparatus 11 ′ is provided with the floats 46a to 46c to close the closed water area 6 (7,
8) By floating in the inside, a fluidized bed type purification device 1
The pipe can be shorter than the case where 1'is installed on land, and it is not necessary to secure a space for installing the fluidized bed purification apparatus 11 'on land.
【0027】流動床式浄化装置11’は、主として、濾
材49を充填した流動床式の濾過槽42を有し、導水管
48によって導かれ、水頭差によってこの導水管48の
下端において分岐された複数の管56によって被処理水
が底から吹き出して瀘材49との間で流動することによ
って流動床を形成して瀘材49との間で接触して富栄養
物質等の汚染物質を分離除去しながら矢印で示す如く上
昇して浄化された処理水として放流管52から放出する
ものである。なお、図3においては、閉鎖性水域6内の
深さが浅い場合を考慮して、濾過槽42を複数段に形成
することによって濾過槽42の実質的な長さを長くした
ものである。上記濾材49としては、例えばゼオライト
等の鉱石とプラスチック濾材とで形成される。更に流動
床式浄化装置11’には、上記放流管52からの処理水
を一旦受けて処理水中に含まれる浮遊物質を沈殿除去す
るための沈殿槽51が設けられている。そしてこの沈殿
槽51で浮遊物質が沈殿除去された処理水が放流管53
から前記処理水域7内に放出(排出)される。更に流動
床式浄化装置11’には、水底近傍に多く存在する富栄
養物質(富栄養要素)等の汚染物質を含む被処理水を取
水口44から取水(流入)して上記導水管48の上端ま
で導く配管59と水中ポンプ45とが設けられている。
更にこの水中ポンプ45等に電力を供給する電源及び水
中ポンプ45等を制御する制御装置47が設けられてい
る。なお、この電源は、例えば、太陽光による発電であ
るソーラ発電パネル43と該ソーラ発電パネル43で発
生した電力を蓄える蓄電器とで構成されている。The fluidized bed type purifying apparatus 11 'mainly has a fluidized bed type filtration tank 42 filled with a filter medium 49, is guided by a water guiding pipe 48, and is branched at a lower end of the water guiding pipe 48 by a head difference. The water to be treated blows out from the bottom by a plurality of pipes 56 and flows with the filter material 49 to form a fluidized bed, which comes into contact with the filter material 49 to separate and remove contaminants such as eutrophic substances. However, as shown by the arrow, it rises and is discharged from the discharge pipe 52 as purified treated water. Note that, in FIG. 3, in consideration of the case where the depth in the closed water area 6 is shallow, the substantial length of the filtration tank 42 is lengthened by forming the filtration tank 42 in a plurality of stages. The filter medium 49 is formed of an ore such as zeolite and a plastic filter medium. Further, the fluidized bed purification apparatus 11 ′ is provided with a settling tank 51 for once receiving the treated water from the discharge pipe 52 and precipitating and removing the suspended matter contained in the treated water. Then, the treated water from which the suspended solids are removed by sedimentation in the sedimentation tank 51 is discharged into the discharge pipe 53.
Is discharged (discharged) into the treated water area 7. Further, in the fluidized bed type purification apparatus 11 ′, the treated water containing pollutants such as eutrophication substances (eutrophication elements) existing in the vicinity of the bottom of the water is taken (inflowed) from the water intake port 44, and the treated water of the water conduit 48 is introduced. A pipe 59 leading to the upper end and a submersible pump 45 are provided.
Further, a power supply for supplying electric power to the submersible pump 45 and the like and a control device 47 for controlling the submersible pump 45 and the like are provided. The power source is composed of, for example, a solar power generation panel 43, which is a power generation by sunlight, and a power storage device that stores the power generated by the solar power generation panel 43.
【0028】次に複数段に形成した流動床式の濾過槽4
2について、図3を用いて説明する。即ち、図3に詳述
するように、流動床式の濾過槽42a〜42cは、直列
関係に接続された例えば3段で構成され、この流動床式
の濾過槽42a〜42cはその下部が設置水域に水没す
るように浮子46a〜46cの間に並べて支持されてい
る。各流動床式の濾過槽42a〜42cの水位は、浮漂
する水域の水面よりも高い位置にあり、且つ、第1段目
の流動床式の濾過槽42aの上部は第2段目の流動床式
の濾過槽42b上部より高く、第2段目の流動床式の濾
過槽42bの上部は第3段目の流動床式の濾過槽42c
上部より高くなっている。従って、水中ポンプ45で汲
み上げた被処理水57は、導水管48aによって第1段
目の流動床式の濾過槽42aの下部に供給され、各々の
流動床式の濾過槽42a〜42cの高さの差に基づく水
頭差によって第1段目の流動床式の濾過槽42a、第2
段目の流動床式の濾過槽42b、第3段目の流動床式の
濾過槽42cの順番に流れる。Next, a fluidized bed type filtration tank 4 formed in a plurality of stages
No. 2 will be described with reference to FIG. That is, as will be described in detail with reference to FIG. 3, the fluidized bed type filtration tanks 42a to 42c are composed of, for example, three stages connected in series, and the fluidized bed type filtration tanks 42a to 42c are installed at their lower portions. The floats 46a to 46c are arranged and supported side by side so as to be submerged in the water. The water level of each of the fluidized bed type filtration tanks 42a to 42c is higher than the water surface of the floating water area, and the upper part of the first fluidized bed type filtration tank 42a is the second fluidized bed. Is higher than the upper part of the second type fluidized bed type filter tank 42b, and the upper part of the second stage fluidized bed type filtered tank 42b is the third stage fluidized bed type filtered tank 42c.
It is higher than the top. Therefore, the treated water 57 drawn by the submersible pump 45 is supplied to the lower part of the fluidized bed type filtration tank 42a of the first stage by the water conduit 48a, and the height of each fluidized bed type filtration tank 42a to 42c is increased. The first head fluidized bed type filtration tank 42a, the second head
The fluidized bed type filtration tank 42b of the second stage and the fluidized bed type filtration tank 42c of the third stage flow in this order.
【0029】水中ポンプ45で第1段目の流動床式の濾
過槽42aに汲み上げられた被処理水57は、第1段目
の流動床式の濾過槽42aの上部から下部に至る導水管
48aを通って下部に到達し、導水管48aの下端にお
いて分岐された複数の管56aから第1段目の流動床式
の濾過槽42aの下部に放出される。第1段目の流動床
式の濾過槽42aの下部に放出された被処理水は、第1
段目の流動床式の濾過槽42a内で濾材49aとの間で
流動することによって流動床を形成して濾材49aと接
触しながら浄化され、導水管48aとの間の水頭圧によ
って矢印で示すように徐々に上昇し、第1段目の流動床
式の濾過槽42aの上部に形成された排出管50aを通
って第2段目の流動床式の濾過槽42bの導入管48b
の入口部分(上端部分)に供給される。この供給された
被処理水は、第2段目の流動床式の濾過槽42bの上部
から下部に至る導水管48bを通って下部に到達し、導
水管48bの下端において分岐された複数の管56bか
ら第2段目の流動床式の濾過槽42bの下部に放出され
る。第2段目の流動床式の濾過槽42bの下部に放出さ
れた被処理水は、第2段目の流動床式の濾過槽42b内
で濾材49bとの間で流動することによって流動床を形
成して濾材49bと接触しながら浄化され、導水管48
bとの間の水頭圧によって矢印で示すように徐々に上昇
し、第2段目の流動床式の濾過槽42bの上部に形成さ
れた排出管50bを通って第3段目の流動床式の濾過槽
42cの導入管48cの入口部分(上端部分)に供給さ
れる。同様にこの供給された被処理水は、第3段目の流
動床式の濾過槽42cの上部から下部に至る導水管48
cを通って下部に到達し、導水管48cの下端において
分岐された複数の管56cから第3段目の流動床式の濾
過槽42cの下部に放出される。第3段目の流動床式の
濾過槽42cの下部に放出された被処理水は、第3段目
の流動床式の濾過槽42c内で濾材49cとの間で流動
することによって流動床を形成して濾材49cと接触し
ながら浄化され、導水管48cとの間の水頭圧によって
矢印で示すように徐々に上昇し、第3段目の流動床式の
濾過槽42cの上部に形成された排出管50c、即ち放
流管52を通って沈殿槽51に放出される。沈殿槽51
においては、放流管52からの処理水を一旦受けて処理
水中に含まれる浮遊物質を沈殿除去して浄化された処理
水が放流管53から前記処理水域7内に放出(排出)さ
れる。The water to be treated 57, which has been pumped up to the first-stage fluidized bed type filtration tank 42a by the submersible pump 45, is a water conduit 48a extending from the upper part to the lower part of the first staged fluidized bed type filtration tank 42a. Through a plurality of pipes 56a branched at the lower end of the water conduit 48a to be discharged to the lower part of the first-stage fluidized bed type filtration tank 42a. The water to be treated discharged to the lower part of the first-stage fluidized bed type filtration tank 42a is
In the fluidized bed type filter tank 42a of the second stage, the fluidized bed is formed by flowing with the filter medium 49a to be purified while being in contact with the filter medium 49a, and indicated by an arrow by the head pressure between the water conduit 48a. As described above, and passes through the discharge pipe 50a formed in the upper part of the first-stage fluidized bed type filtration tank 42a, and the introduction pipe 48b of the second-staged fluidized bed type filtration tank 42b.
Is supplied to the inlet part (upper end part) of the. The supplied water to be treated reaches the lower part through the water guiding pipe 48b extending from the upper part to the lower part of the fluidized bed type filtration tank 42b of the second stage, and reaches the lower part, and a plurality of pipes branched at the lower end of the water guiding pipe 48b. It is discharged from 56b to the lower part of the second fluidized bed type filtration tank 42b. The water to be treated discharged to the lower part of the second-stage fluidized bed type filter tank 42b flows between the second stage fluidized bed type filter tank 42b and the filter medium 49b to form a fluidized bed. It is formed and purified while contacting with the filter medium 49b, and the water conduit 48
As shown by the arrow, the pressure gradually rises due to the head pressure between the fluid b and b, and passes through the discharge pipe 50b formed in the upper part of the fluidized bed type filtration tank 42b of the second stage to the fluidized bed type of the third stage. Is supplied to the inlet portion (upper end portion) of the introduction pipe 48c of the filtration tank 42c. Similarly, the supplied water to be treated is a water conduit 48 from the upper part to the lower part of the third-stage fluidized bed type filtration tank 42c.
It reaches the lower part through c and is discharged to the lower part of the third-stage fluidized bed type filtration tank 42c from a plurality of pipes 56c branched at the lower end of the water conduit 48c. The water to be treated discharged to the lower part of the fluidized bed type filtration tank 42c at the third stage flows between the water to be treated and the filter medium 49c in the fluidized bed type filtration tank 42c at the third stage to form a fluidized bed. It is formed and purified while being in contact with the filter medium 49c, gradually rising as indicated by the arrow due to the head pressure between the water conduit 48c, and formed on the upper part of the fluidized bed type filtration tank 42c of the third stage. It is discharged to the settling tank 51 through the discharge pipe 50c, that is, the discharge pipe 52. Settling tank 51
In the above, the treated water that has been once treated by receiving the treated water from the discharge pipe 52 and purified by removing the suspended matter contained in the treated water is discharged (discharged) from the discharge pipe 53 into the treated water area 7.
【0030】流動床式の濾過槽42に入っている濾材4
9は、例えばゼオライト等の鉱石とプラスチック濾材と
で形成されているため、富栄養物質等の汚染物質を付着
して水を浄化させるが、付着物質がある程度大きくなる
と付着物質は濾材49から剥離する。剥離した付着物質
は、処理水と一緒に放流管52から放流されるが、沈殿
槽51にて一旦分離され、沈殿槽51の底に沈殿物質5
8として沈殿する。そのため、濾材49に付着して剥離
した富栄養物質等の汚染物質は、処理水域7内に流入す
ることはない。なお、沈殿槽51内の沈殿物質58は、
定期的に船等を用いて陸地4まで運んで取り除くことが
できる。また上記浄化装置11(流動床式浄化装置1
1’)にエンジンを搭載して自動走行できるようにすれ
ば、沈殿槽51内の沈殿物質58を、定期的に陸地4ま
で直接運ぶか、または後述する仕切り装置14の上部に
形成された補助通路20まで運んで取り除くことができ
る。また沈殿槽51の底に溜った沈殿物質58を配管6
0を通してポンプ59により吸いあげて配管61により
陸地4まで直接搬送(輸送)するか、または後述する仕
切り装置14の上部に形成された補助通路20まで搬送
(輸送)することによって取り除くことができる。補助
通路20から陸地4までは、例えば、補助通路20の底
を一方から他方に向けて傾けて、水を流すことによって
補助通路20に運ばれた(搬送または輸送された)沈殿
物質58等を陸地へ運ぶことができる。Filter medium 4 contained in a fluidized bed type filter tank 42.
Since 9 is formed of ore such as zeolite and a plastic filter medium, contaminants such as eutrophic substances adhere to purify water, but when the adhered substance becomes large to some extent, the adhered substance is separated from the filter medium 49. . The adhered substance that has peeled off is discharged from the discharge pipe 52 together with the treated water, but is once separated in the settling tank 51, and the settling material 5
Precipitate as 8. Therefore, contaminants such as rich nutrients that have adhered to and peeled off the filter medium 49 do not flow into the treated water area 7. The settling material 58 in the settling tank 51 is
It can be regularly carried to the land 4 by ship or the like and removed. In addition, the purification device 11 (fluidized bed purification device 1
1 ') is equipped with an engine so that it can be automatically driven, the settling material 58 in the settling tank 51 is directly carried to the land 4 on a regular basis, or an auxiliary member formed on the upper part of the partitioning device 14 described later. It can be carried to the aisle 20 and removed. In addition, the settling material 58 collected at the bottom of the settling tank 51 is connected to the pipe 6
It can be removed by sucking through 0 through the pump 59 and directly conveying (transporting) it to the land 4 by the pipe 61, or by conveying (transporting) it to the auxiliary passage 20 formed in the upper part of the partitioning device 14 described later. From the auxiliary passage 20 to the land 4, for example, by tilting the bottom of the auxiliary passage 20 from one side to the other, and flowing the water, the precipitated substances 58 and the like carried (conveyed or transported) to the auxiliary passage 20 are discharged. Can be transported to land.
【0031】図3においては、流動床式の濾過槽42と
して、3段42a、42b、42cを直列に並べた場合
を示した。これは、流動床式の濾過槽の長さを確保しな
がら流動床式の濾過槽42の高さを低くして水中ポンプ
45の揚程を小さくするためであり、流動床式の濾過槽
42は、1段、または複数段(2段及び4段以上)であ
っても良い。また並べ方は、必ずしも直列に並べる必要
はない。次に本発明に係る図1に示す実施例と異なる実
施例について、図4を用いて説明する。即ち、図4には
浄化装置11を閉鎖性水域6(7、8)水域内に配置さ
せた図1と異なる実施例を示す。閉鎖性水域6は、図1
に示すのと同様に仕切り装置14によって処理水域7と
処理水域外の水域8とに分割されている。処理水域7内
には浄水場1へ供給するための取水口6が設置されてい
る。そして、浄化装置11として、処理水域7内の被処
理水を取水して、この被処理水の中に存在する汚染物質
である富栄養物質(富栄養要素)を分離除去して浄化し
て処理水域7内に放出する浄化装置11a(図1に示す
11と同様である。)と、処理水域7の外側の水域8の
被処理水を取水して、この被処理水の中に存在する汚染
物質である富栄養物質を分離除去して浄化して処理水域
7内に放出する複数の浄化装置11b、11cとで構成
する。即ち、浄化装置11aは、処理水域7内の被処理
水を浄化させるためのものである。一方、浄化装置11
b、11cは、より多くの浄化された処理水を処理水域
7内に溜めるために、処理水域7の外側の水域8の被処
理水を浄化させるためのものである。これら浄化装置1
1a、11b、11cは、前記したとおり、処理水域7
内または処理水域7の外側の水域8(仕切り装置14の
どちら側の水域7、8)に設置してもよく、浮漂させる
場合においても、同様でどちらの水域7、8に浮漂させ
てもよい。FIG. 3 shows a case where three stages 42a, 42b and 42c are arranged in series as the fluidized bed type filtration tank 42. This is because the height of the fluidized bed type filtration tank 42 is lowered and the head of the submersible pump 45 is reduced while ensuring the length of the fluidized bed type filtration tank. There may be one step or a plurality of steps (two steps and four steps or more). Moreover, it is not always necessary to arrange them in series. Next, an embodiment different from the embodiment shown in FIG. 1 according to the present invention will be described with reference to FIG. That is, FIG. 4 shows an embodiment different from FIG. 1 in which the purifying device 11 is arranged in the closed water area 6 (7, 8). Closed water area 6 is shown in Figure 1.
Similarly to the one shown in FIG. 3, the partition device 14 divides the treated water area 7 and the water area 8 outside the treated water area. An intake 6 for supplying water to the water purification plant 1 is installed in the treated water area 7. Then, as the purifying device 11, the treated water in the treated water area 7 is taken in, and the eutrophication substance (eutrophication element) which is a pollutant present in the treatment water is separated and removed to be treated. A purifying device 11a (similar to 11 shown in FIG. 1) that discharges into the water area 7 and the treated water in the water area 8 outside the treated water area 7 are taken in, and the pollution existing in this treated water is taken. It is composed of a plurality of purification devices 11b and 11c for separating and purifying the nutrient rich substance, which is a substance, and purifying the separated substance into the treated water area 7. That is, the purifying device 11a is for purifying the water to be treated in the treated water area 7. On the other hand, the purification device 11
b and 11c are for purifying the treated water in the water area 8 outside the treated water area 7 in order to store a larger amount of the purified water in the treated water area 7. These purification devices 1
1a, 11b and 11c are treated water areas 7 as described above.
It may be installed inside or outside the treated water area 7 (on either side of the partition device 14, the water area 7 or 8), and in the case of floating, it may be floated to either water area 7 or 8. .
【0032】何れにしても、浄化装置11a、11b、
11c、12によって、富栄養物質や藻類等の汚染物質
が分離除去された多量の浄化された処理水を処理水域7
内に溜めることが可能となった。なお、浄化装置11a
〜11c、12で除去されない汚染物質は、しばらくの
間(約2〜5日)処理水域7内に停留することにより微
生物により吸収され、その微生物が数日間でライフサイ
クルを終えて沈降することになる。従って汚染物質は、
取水口2から浄水場1への取水される可能性は低減され
る。その結果、常に窒素成分(アンモニア性窒素成分)
が含有が大幅に低減された浄化された処理水が給水管5
を通して浄水場1へ供給することができ、浄水場1にお
ける水処理を大幅に低減することができる。In any case, the purification devices 11a, 11b,
A large amount of purified treated water from which contaminants such as rich nutrients and algae have been separated and removed by 11c and 12 is treated water area 7
It has become possible to store it inside. In addition, the purification device 11a
Contaminants that are not removed by ~ 11c, 12 are absorbed by microorganisms by staying in the treated water area 7 for a while (about 2 to 5 days), and the microorganisms complete their life cycle within a few days and settle down. Become. So the pollutant is
The possibility of water being taken from the water intake 2 to the water purification plant 1 is reduced. As a result, the nitrogen component (ammonia nitrogen component) is always
Purified treated water whose content is greatly reduced is the water supply pipe 5
Can be supplied to the water purification plant 1 through the water treatment system, and the water treatment in the water purification plant 1 can be significantly reduced.
【0033】次に本発明に係る仕切り装置14の一実施
例について図5及び図6を用いて説明する。即ち、仕切
り装置14は、合成樹脂等のシートで形成された多数の
仕切り物質体(構造物質)14a〜14gを鎖17a、
17bによって繋げて簾状に配置して湖底まで届くよう
に構成し、ブイ15によって水中に保持されるものであ
る。各仕切り物質体(構造物質)14a〜14gの下部
には、重り16がそれぞれ取り付けられていて、各仕切
り物質体14a〜14gが流されないようにしている。
従って、重り16は、各仕切り物質体14a〜14gに
取り付ける必要はないことは明らかである。また各仕切
り物質体14a〜14gを必ずしも簾状に配置する必要
はない。一方、鎖17a、17bを縮めることにより、
各仕切り物質体14a〜14gを引上げて回収すること
を可能にすることができる。また、各仕切り物質体(構
造物質)14a〜14gの内、少なくとも1枚には仕切
りの外部の水を取り込むための制限された複数の開口
(複数の穴)18a、18b、18cがあけられてい
る。何れにしても、仕切り装置14は、湖沼、ダム湖等
の閉鎖性水域6において、取水口2の周りの防波堤3で
は部分を囲って処理水域7を作り上げるものである。一
方、湖沼、ダム湖等の閉鎖性水域6には、木材等が流れ
込むことになる。従って、流木等に耐えうるように、内
側に杭を打つなどして補強することが必要となる。また
仕切り装置14として、内側に杭を打つなどして補強し
て比較的細かな網状、または格子状または布状で形成し
ても良い。何れにしても、多量の汚染物質を含む水が処
理水域7内に入り込まないようにする必要がある。Next, one embodiment of the partitioning device 14 according to the present invention will be described with reference to FIGS. That is, the partitioning device 14 connects a large number of partitioning material bodies (structural materials) 14a to 14g formed of a sheet of synthetic resin or the like to the chain 17a,
17b are connected to each other and arranged in the shape of a blind so that they reach the bottom of the lake, and are retained in water by the buoy 15. Weights 16 are attached to the lower portions of the respective partition substance bodies (structural substances) 14a to 14g so that the respective partition substance bodies 14a to 14g are prevented from flowing.
Therefore, it is clear that the weight 16 does not need to be attached to each partition substance body 14a to 14g. Further, it is not always necessary to arrange the partition substance bodies 14a to 14g in a blind shape. On the other hand, by contracting the chains 17a and 17b,
It is possible to pull up and collect each partition material body 14a to 14g. In addition, at least one of the partition substance bodies (structural substances) 14a to 14g has a plurality of restricted openings (a plurality of holes) 18a, 18b, 18c for taking in water outside the partition. There is. In any case, the partitioning device 14 forms a treated water area 7 by surrounding a part of the breakwater 3 around the intake 2 in the closed water area 6 such as a lake or a dam lake. On the other hand, timber and the like will flow into the closed water area 6 such as lakes and dams. Therefore, it is necessary to stake a pile inside to reinforce it so as to withstand driftwood and the like. Further, the partitioning device 14 may be formed in a relatively fine mesh shape, a lattice shape, or a cloth shape by reinforcing it by hitting a pile inside. In any case, it is necessary to prevent water containing a large amount of contaminants from entering the treated water area 7.
【0034】次に、本発明に係る仕切り装置14に補助
通路20を形成した場合の一実施例を図6を用いて説明
する。即ち、補助通路形成用仕切り装置18と補助通路
形成用ブイ19とにより形成された補助通路20を、ブ
イ15に取り付けられた仕切り装置14の上部に備え付
けたものである。この補助通路20は、浄化装置11に
て回収された汚染物質(沈殿槽51の底に沈殿した沈殿
物質58)を配管等を用いて集積して、陸地近くの1ヶ
所に集めるための通路である。次に本発明に係る仕切り
装置14の他の実施例を図7および図8を用いて説明す
る。即ち、図7に示す仕切り装置14xおよび14y
は、図1及び図4に示す仕切り装置14とは異なり、途
中で開放しており、処理水域7と処理水域7の外側の水
域8とを完全に分割していない。そのため、この開放し
ている部分から多量に汚染物質が含まれる水が流入する
ことになる。従って、浄化装置11、12の台数を、多
量に汚染物質が含まれる水が上記開放している部分から
流入することを考慮して決めれば、開放しない場合に比
べて取水口2から浄水場1へ供給される水質は大幅に悪
くはならない。一方、上記浄化装置11(流動床式浄化
装置11’)、12にエンジンを搭載して自動走行でき
るようにすれば、上記開放している部分を通して上記浄
化装置11(流動床式浄化装置11’)、12を航行し
て汚染物質(沈殿槽51の底に沈殿した沈殿物質58)
を回収することができると共に上記浄化装置11(流動
床式浄化装置11’)、12のメンテナンスも容易にす
ることができる。また船を用いて行う場合にも、上記開
放している部分を通して航行させることができる。Next, an embodiment in which the auxiliary passage 20 is formed in the partition device 14 according to the present invention will be described with reference to FIG. That is, the auxiliary passage 20 formed by the auxiliary passage forming partition device 18 and the auxiliary passage forming buoy 19 is provided above the partition device 14 attached to the buoy 15. The auxiliary passage 20 is a passage for accumulating pollutants (precipitated substance 58 settled on the bottom of the settling tank 51) collected by the purification device 11 using a pipe or the like and collecting the polluted substances at one place near the land. is there. Next, another embodiment of the partitioning device 14 according to the present invention will be described with reference to FIGS. 7 and 8. That is, the partitioning devices 14x and 14y shown in FIG.
1 is different from the partitioning device 14 shown in FIGS. 1 and 4, it is opened midway and does not completely divide the treated water area 7 and the water area 8 outside the treated water area 7. Therefore, a large amount of water containing pollutants will flow in from this open portion. Therefore, if the number of purification devices 11 and 12 is determined in consideration of the fact that water containing a large amount of pollutants flows in from the open portion, the water purification plant 1 from the water intake 2 can be compared with the case where the water is not opened. The quality of the water supplied to is not significantly deteriorated. On the other hand, if the purifying devices 11 (fluidized bed type purifying device 11 ′) and 12 are equipped with an engine so as to be able to run automatically, the purifying device 11 (fluidized bed type purifying device 11 ′) can be passed through the open portion. ), 12 and pollutants (precipitate 58 that settled to the bottom of settling tank 51)
In addition to being able to collect the above, it is possible to facilitate maintenance of the purification devices 11 (fluidized bed type purification device 11 ′) and 12. Also, when using a ship, it is possible to navigate through the open portion.
【0035】この実施例の場合も、図1及び図4に示す
実施例と同様に、富栄養物質や藻類等の汚染物質が分離
除去された多量の浄化された処理水を処理水域7内に溜
めることが可能となった。なお、浄化装置11、12で
除去されない汚染物質は、しばらくの間(約2〜5日)
処理水域7内に停留することにより微生物により吸収さ
れ、その微生物が数日間でライフサイクルを終えて沈降
することになる。従って汚染物質は、取水口2から浄水
場1への取水される可能性は低減される。その結果、常
に窒素成分(アンモニア性窒素成分)が含有が大幅に低
減された浄化された処理水が給水管5を通して浄水場1
へ供給することができ、浄水場1における水処理を大幅
に低減することができる。次に仕切り装置14によって
仕切る程度に応じた水質浄化の進行度について図8を用
いて説明する。即ち、図8は、仕切り装置14によって
仕切る程度に応じた水質浄化の進行度に示すグラフであ
る。図8に示すグラフの縦軸は、水質の汚染度で、燐濃
度、窒素濃度、COD等がその指標となる。図8に示す
グラフの横軸は、浄化に要する日数を示している。Also in the case of this embodiment, as in the embodiment shown in FIGS. 1 and 4, a large amount of purified treated water from which contaminants such as rich nutrients and algae are separated and removed is introduced into the treated water area 7. It became possible to store. It should be noted that pollutants that are not removed by the purification devices 11 and 12 are for a while (about 2 to 5 days).
By staying in the treated water area 7, it will be absorbed by microorganisms, and the microorganisms will complete their life cycle within a few days and settle. Therefore, the pollutant is less likely to be taken from the water intake 2 to the water purification plant 1. As a result, the purified treated water in which the content of nitrogen component (ammonia nitrogen component) is greatly reduced is constantly passed through the water supply pipe 5 to the water treatment plant 1.
The water treatment in the water purification plant 1 can be significantly reduced. Next, the progress of water purification according to the degree of partitioning by the partitioning device 14 will be described with reference to FIG. That is, FIG. 8 is a graph showing the progress of water purification according to the degree of partitioning by the partitioning device 14. The vertical axis of the graph shown in FIG. 8 is the degree of water pollution, and phosphorus concentration, nitrogen concentration, COD, etc. are used as indices. The horizontal axis of the graph shown in FIG. 8 indicates the number of days required for purification.
【0036】は、仕切り装置14なしの場合の浄化の
進行の様子を示し、最初汚染度Aであった水質が改善さ
れて、汚染度がDになった時点でそれ以上の浄化は達成
されなくなる。これは自然の混合作用と浄化装置での浄
化能力とが釣合い、仕切りなしの場合にはこれ以上浄化
は望めないものである。または、仕切り装置14で完
全に仕切った(開放なし)場合の浄化の達成度を示し、
仕切りなしの場合の汚染度の到達点Dよりはかなり低い
B点にまで浄化が進むことがわかる。または、仕切り
装置14x、14yで示すように一部分を開放した場合
であり、完全にしきった場合における浄化の最終到達点
(汚染度の最終到達点)Bよりは高いC点になってい
る。しかしながら、仕切りのない場合に比べてかなり浄
化は進み、仕切ることによる効果は、十分に達成されて
いる。従って、例えば、浄化装置11、12の台数等を
増やして能力を向上させることによって、仕切り装置1
4x、14yで示すように一部分を開放したの場合で
あっても、汚染度の到達点CをBに近付けることは可能
となる。Indicates the progress of purification without the partitioning device 14, and when the pollution degree A is improved and the pollution degree becomes D, further purification is not achieved. . This is because the natural mixing action and the purifying ability of the purifying device are in balance, and further purification cannot be expected without the partition. Alternatively, it indicates the degree of achievement of purification when completely partitioned by the partition device 14 (without opening),
It can be seen that the purification proceeds to point B, which is considerably lower than the reaching point D of the contamination degree in the case of no partition. Alternatively, as shown by the partitioning devices 14x and 14y, when a part is opened, the point C is higher than the final reaching point (final reaching point of the degree of pollution) B of the purification when it is completely completed. However, purification is considerably advanced as compared with the case without a partition, and the effect of partitioning is sufficiently achieved. Therefore, for example, by increasing the number of the purifying devices 11 and 12 to improve the capacity, the partitioning device 1
Even when a part is opened as shown by 4x and 14y, it is possible to bring the reaching point C of the degree of contamination close to B.
【0037】次に本発明に係る仕切り装置14として、
エアカーテン14tで構成した実施例について図9を用
いて説明する。即ち、本実施例(エアカーテン方式の仕
切り装置14t)では、図9に示すように、散気管21
を仕切り装置14を形成すべき水底に配設し、この散気
管21に空気を供給して散気管21から上昇する気泡2
2を発生させるようにして、この気泡22の上昇するの
に伴う鉛直方向の水流20により、空気中のエアカーテ
ンと同様な仕切りを形成するものである。図9におい
て、散気管21から生じる上昇する気泡によって形成さ
れるエアカーテン方式の仕切り装置14tの右側が処理
水域7である。取水口44から取り込まれた被処理水
は、浄化装置11’にて浄化されて放流管53より処理
水域7内に放出される。本実施例によれば、図5に示す
ような合成樹脂等のシートで形成された多数の仕切り物
質体(構造物質)14a〜14gで形成された仕切り装
置14を設ける必要が無いので、船の航行に支障を及ぼ
すことが無い。また、台風による多数の仕切り物質体
(構造物質)14a〜14gで形成された仕切り装置1
4の流失を心配する必要がない。しかし、流木等が流入
して閉鎖性水域6(7、8)内にある浄化装置11、1
2と衝突して浄化装置11、12を破壊する可能性があ
るので、エアカーテン方式の仕切り装置14tの場合に
は、その外側にフェンス等を設けて、流木等が流入しな
いようにする必要がある。Next, as the partitioning device 14 according to the present invention,
An embodiment constituted by the air curtain 14t will be described with reference to FIG. That is, in the present embodiment (air curtain type partitioning device 14t), as shown in FIG.
Is installed on the bottom of the water where the partitioning device 14 is to be formed, and air is supplied to the air diffusing pipe 21 to raise bubbles 2 from the air diffusing pipe 21.
2 is generated, and a partition similar to an air curtain in the air is formed by the vertical water flow 20 as the bubbles 22 rise. In FIG. 9, the treated water area 7 is on the right side of the partitioning device 14t of the air curtain system formed by the rising bubbles generated from the air diffuser 21. The water to be treated taken in through the water intake port 44 is purified by the purifying device 11 ′ and discharged into the treated water area 7 through the discharge pipe 53. According to the present embodiment, it is not necessary to provide the partitioning device 14 formed of a large number of partitioning material bodies (structural materials) 14a to 14g formed of a sheet of synthetic resin or the like as shown in FIG. It does not hinder navigation. Further, the partitioning device 1 formed of a large number of partitioning material bodies (structural materials) 14a to 14g by a typhoon
There is no need to worry about the loss of 4. However, the purifiers 11 and 1 in the closed water area 6 (7, 8) due to the inflow of driftwood etc.
Since there is a possibility of colliding with the cleaning device 11 and 12 and destroying the purifying devices 11 and 12, in the case of the air curtain type partitioning device 14t, it is necessary to provide a fence or the like on the outside thereof to prevent driftwood or the like from entering. is there.
【0038】次に本発明に係る浄化装置を含めた局所水
域浄化システムの他の実施例を図10乃至図12を用い
て説明する。図10は、本発明に係る浄化装置を含めた
局所水域浄化システムの他の実施例を浄水場1への取水
口2の上から見て示した図である。即ち局所水域浄化シ
ステムは、閉鎖性水域6内において、矢印の方向からネ
ット23、第1のフェンス24、第2のフェンス25、
第3のフェンス26及び第4のフェンス27からなる汚
染物質除去装置41と、藻類除去装置28と、浄化装置
29とを被処理水を流す流路35に沿って配設して構成
する。浄化装置29を通過して浄化された部分に浄水場
1への取水口2が設けられている。そして、閉鎖性水域
6内において、ネット23から取水口2まで流路35の
両側は側壁36で仕切られている。この側壁36は、防
波堤3で兼ねても良い。従って、ネット23の外側の水
域8の被処理水が、汚染物質除去装置41を構成するネ
ット23、第1のフェンス24、第2のフェンス25、
第3のフェンス26及び第4のフェンス27を通過する
ことによって被処理水に存在する汚染物質が分離除去さ
れて処理水域7’内に流入する。処理水域7’内に流入
した処理水は、藻類除去装置28及び浄化装置29によ
り最終段での浄化が行われ、取水口6へ流れる。なお、
処理水域7’においては、予め浚渫や被覆を施して底泥
からのアンモニア性窒素の溶出を抑える手立を施してあ
る。Next, another embodiment of the local water area purification system including the purification apparatus according to the present invention will be described with reference to FIGS. 10 to 12. FIG. 10 is a view showing another embodiment of the local water area purification system including the purification device according to the present invention as viewed from above the water intake 2 to the water purification plant 1. That is, the local water purification system includes the net 23, the first fence 24, the second fence 25, in the closed water area 6 in the direction of the arrow.
The pollutant removal device 41 including the third fence 26 and the fourth fence 27, the algae removal device 28, and the purification device 29 are arranged along the flow path 35 through which the water to be treated flows. A water intake 2 to the water purification plant 1 is provided in a portion purified by passing through the purification device 29. Then, in the closed water area 6, both sides of the flow path 35 from the net 23 to the water intake 2 are partitioned by side walls 36. The side wall 36 may also serve as the breakwater 3. Therefore, the water to be treated in the water area 8 outside the net 23 includes the net 23, the first fence 24, the second fence 25, which constitute the pollutant removal device 41.
By passing through the third fence 26 and the fourth fence 27, contaminants existing in the water to be treated are separated and removed and flow into the treated water area 7 ′. The treated water that has flowed into the treated water area 7 ′ is purified at the final stage by the algae removing device 28 and the purifying device 29, and flows to the water intake 6. In addition,
In the treated water area 7 ', dredging or coating is applied in advance to prevent elution of ammonia nitrogen from the bottom mud.
【0039】図11は、汚染物質除去装置41における
深さ方向の関係(流路35に沿った断面)を示したもの
である。ネット23の外側の水域8の被処理水は、図1
1の右側からネット23、第1のフェンス24、第2の
フェンス25、第3のフェンス26及び第4のフェンス
27を通過して処理水域7’に流入する。なお、37
は、ネット23、第1のフェンス24、第2のフェンス
25、第3のフェンス26及び第4のフェンス27の上
端を支持するブイである。またネット23、第1のフェ
ンス24、第2のフェンス25、第3のフェンス26及
び第4のフェンス27の下端は、水底に動かないように
固定するものとする。ネット23は、風波による抵抗を
緩和し流木等から内側のフェンス24〜27を保護する
目的で設置されている。FIG. 11 shows the relationship in the depth direction (cross section taken along the flow path 35) in the contaminant removing device 41. The treated water in the water area 8 outside the net 23 is shown in FIG.
From the right side of No. 1, it passes through the net 23, the first fence 24, the second fence 25, the third fence 26, and the fourth fence 27 and flows into the treated water area 7 ′. 37
Is a buoy that supports the upper ends of the net 23, the first fence 24, the second fence 25, the third fence 26, and the fourth fence 27. The lower ends of the net 23, the first fence 24, the second fence 25, the third fence 26, and the fourth fence 27 are fixed to the bottom of the water so as not to move. The net 23 is installed for the purpose of relaxing resistance due to wind waves and protecting the inside fences 24 to 27 from driftwood and the like.
【0040】第1のフエンス24は、第2のフェンス2
5との間で被処理水に対して上昇させる流れ(上向きの
流れ)40を作るためのもので、水底から約1〜3m程
度が被処理水の流入通路(網状、多数の大きな開口を配
設した状態、格子状、大きな通路等)39となり、その
上面から水面までは被処理水をより多く遮蔽するように
なっている。なお、第1のフェンス24において、流入
通路39の上面から水面まで被処理水を完全に遮断する
必要はなく、より多く遮断すれば良い。更に第2のフェ
ンス25は第1のフェンス24とは逆に、湖底から約1
〜3m程度の部分をより多く遮蔽し、被処理水に対して
上昇させる流れ(上向きの流れ)40を作ってこの流れ
40の遠心力によって被処理水に含まれる浮遊物質成分
を分離して第2のフェンス25の遮断面41や水底に向
けて沈殿させて底部に汚泥30として堆積させるもので
ある。即ち、第1のフェンス24の流入通路39を通過
した被処理水は、第2のフェンス25の遮蔽面41に当
り、流れ39の方向が上向きとなる。この時、被処理水
の中の浮遊物質成分は遠心力により被処理水から分離さ
れる。分離された浮遊物質成分は第2のフェンス25の
底部に汚泥30となって堆積される。この堆積された汚
泥30は、汚泥引き抜きポンプ33によって配管38を
介して例えば陸地4へ運ばれて回収される。次に上昇し
た水(上向きの流れの水)は、第2のフェンス25の上
側の通路42を通過し、第3のフェンス26の上側の遮
蔽部分43で進行が妨げられ、第2のフェンス25と第
3のフェンス26との間に形成される隙間を下降するこ
とになる。第3のフェンス26は第1のフェンス24と
同様に水底から約1〜3m程度が水の流入通路となり、
その上面から水面まで遮蔽部分43で水を遮蔽するよう
になっている。なお、通路35における平均水深さを約
2〜8m程度とする。The first fence 24 is the second fence 2
5 is to create a flow (upward flow) 40 that rises with respect to the water to be treated. About 1 to 3 m from the bottom of the water is an inflow passage for the water to be treated (mesh-shaped, with many large openings). (The installed state, a grid shape, a large passage, etc.) 39, and more water to be treated is shielded from the upper surface to the water surface. In the first fence 24, it is not necessary to completely block the water to be treated from the upper surface of the inflow passage 39 to the water surface, and more water may be blocked. Further, the second fence 25 is opposite to the first fence 24 from the bottom of the lake about 1
A part (about 3 m) is shielded more, and a flow (upward flow) 40 that raises the water to be treated is created, and the centrifugal force of this flow 40 separates suspended matter components contained in the water to be treated. The sludge 30 is deposited toward the blocking surface 41 and the water bottom of the fence 25 of No. 2 and deposited as sludge 30 on the bottom. That is, the water to be treated that has passed through the inflow passage 39 of the first fence 24 hits the shielding surface 41 of the second fence 25, and the direction of the flow 39 is upward. At this time, suspended matter components in the water to be treated are separated from the water to be treated by centrifugal force. The separated suspended matter component is accumulated as sludge 30 on the bottom of the second fence 25. The accumulated sludge 30 is carried by the sludge extraction pump 33 to the land 4 via the pipe 38 and collected. The next rising water (upward flow water) passes through the upper passage 42 of the second fence 25, is blocked from traveling by the upper shielding portion 43 of the third fence 26, and is blocked by the second fence 25. Therefore, the gap formed between the second fence 26 and the third fence 26 is lowered. Like the first fence 24, the third fence 26 has a water inflow passage of about 1 to 3 m from the bottom of the water,
The water is shielded by the shielding portion 43 from the upper surface to the water surface. The average water depth in the passage 35 is about 2 to 8 m.
【0041】第3のフェンス26の下方の通路を通過し
た水は、第3のフェンス26と第4のフェンス27との
隙間を上昇する流れとなる。第4のフェンス27は、第
2のフェンス25と水底から約1〜4m程度の部分の水
を遮蔽して、上昇流を生じさせる。この上昇流を生じた
水は、水底付近に置かれたネット31に包まれて置かれ
た木炭等の濾材層32を通過し、空気が供給されている
散気管34により曝気される。この曝気層で水中のアン
モニア性窒素の多くは、硝酸性窒素に変換される。この
ように水中のアンモニア性窒素の多くが硝酸性窒素に変
換された処理水が第4のフェンス27の上側の流入通路
44を通過して処理水域7’へと流入される。以上説明
したように汚染物質除去装置41は、通路35において
ネット23から入る被処理水に対して図11に示す如く
矢印で示す流れを生じさせて被処理水中の浮遊物質成分
を流れの遠心力により被処理水から分離除去して汚泥3
0として堆積させ、その後被処理水に対して木炭等の濾
材層32を通過させて散気管34により曝気することに
よって水中のアンモニア性窒素の多くを硝酸性窒素に変
換して処理水域7’へと流入させるものである。即ち、
ネット23から入る被処理水は、汚染物質除去装置41
によって浮遊物質成分が分離除去され、アンモニア性窒
素の多くが硝酸性窒素に変換処理されて処理水域7’へ
と流れ込むことになる。The water that has passed through the passage below the third fence 26 becomes a flow that rises through the gap between the third fence 26 and the fourth fence 27. The fourth fence 27 shields the second fence 25 and water in a portion of about 1 to 4 m from the bottom of the water to generate an upward flow. The water that has generated this upward flow passes through a filter medium layer 32 such as charcoal that is wrapped around a net 31 placed near the bottom of the water, and is aerated by a diffuser pipe 34 to which air is supplied. Much of the ammoniacal nitrogen in the water is converted to nitrate nitrogen in this aeration layer. In this way, the treated water in which most of the ammonia nitrogen in the water is converted to nitrate nitrogen passes through the inflow passage 44 on the upper side of the fourth fence 27 and flows into the treated water area 7 '. As described above, the pollutant removal device 41 causes the flow of the suspended substance component in the water to be treated to generate a flow indicated by an arrow as shown in FIG. Sludge is separated and removed from the water to be treated by
0 is deposited, and then the treated water is passed through the filter medium layer 32 such as charcoal and aerated by the diffuser pipe 34, whereby most of the ammonia nitrogen in the water is converted into nitrate nitrogen to the treated water area 7 ′. And let it flow in. That is,
The water to be treated entering from the net 23 is a pollutant removal device 41.
As a result, the suspended matter components are separated and removed, and most of the ammoniacal nitrogen is converted into nitrate nitrogen and flows into the treated water area 7 '.
【0042】次にこの処理水域7’の水は、藻類除去装
置(藻類濾過装置)28を通過することによって藻類が
除去されることになる。更に図12に示す浄化装置29
を通過することによって浄化され、浄水場1への取水口
2へ達し、この取水口2から浄水場1へ供給されること
になる。何れにしても、処理水域7’から取水口2まで
の間において約1〜2日程度滞留することになり、除去
されない汚染物質は微生物によって吸収され、その微生
物が約1〜2日程度の間でライフサイクルが終えて沈降
して浄化される。次に上記浄化装置29について図12
を用いて説明する。即ち、浄化装置29は、複数段の布
部分(例えば不織布部分)35と案内板36とから構成
されている。図中の右側から流入した処理水域7’から
の水はその一部が布部分(例えば不織布部分)35を通
過することにより濾過される。布部分35を通過しなか
った水は案内板36により次の布部分35に導かれ、徐
々に浄化されていく。即ち、処理水域7’からの水は、
複数段の布部分35を通過することによって徐々に浄化
されている。なお、この布部分35は、繊維を布状にし
たものでなくても良い。即ち、この布部分35は、通過
することによって浄化されるものであれば良く、例えば
緻密な網状または緻密な格子状なもので形成したもので
あっても良い。Next, the algae are removed from the water in the treated water area 7'by passing through the algae removing device (algae filtering device) 28. Further, the purification device 29 shown in FIG.
It is purified by passing through, reaches the water intake 2 to the water purification plant 1, and is supplied to the water purification plant 1 from this water intake 2. In any case, between the treated water area 7'and the intake port 2, it will stay for about 1 to 2 days, and the contaminants that are not removed will be absorbed by the microorganisms, and the microorganisms will remain for about 1 to 2 days. At the end of the life cycle, it settles and is purified. Next, regarding the purifying device 29, FIG.
This will be described with reference to FIG. That is, the purifying device 29 includes a plurality of stages of cloth portions (for example, non-woven fabric portions) 35 and a guide plate 36. The water from the treated water area 7 ′ that has flowed in from the right side of the drawing is partially filtered through a cloth portion (for example, a non-woven cloth portion) 35. The water that has not passed through the cloth portion 35 is guided to the next cloth portion 35 by the guide plate 36 and gradually purified. That is, the water from the treated water area 7'is
It is gradually purified by passing through a plurality of stages of cloth portions 35. The cloth portion 35 does not have to be a cloth-shaped fiber. That is, the cloth portion 35 may be any material as long as it is purified by passing the cloth portion 35, and may be formed, for example, in a dense mesh shape or a dense lattice shape.
【0043】本実施例で想定されている浄水場1におけ
る取水量は、一日当り約16万トン程度であるため、図
10に示す如く、通路35の大きさを、約1〜2日分の
取水量を確保できる程度に設定すれば良い。これにより
安定して浄水場1へ水を供給することができる。また浄
化装置29として、図3に示す構成の流動床式浄化装置
を用いても良い。Since the water intake in the water purification plant 1 assumed in this embodiment is about 160,000 tons per day, as shown in FIG. 10, the size of the passage 35 is about 1 to 2 days. It should be set so that the amount of water intake can be secured. Thereby, water can be stably supplied to the water purification plant 1. As the purifying device 29, a fluidized bed type purifying device having the configuration shown in FIG. 3 may be used.
【0044】[0044]
【発明の効果】本発明によれば、湖沼、池、ダム湖等の
閉鎖性水域(水源)において、富栄養化現象によって生
じるアンモニア性窒素の濃度を大幅に減少させて水質改
善を施した処理水を浄水場へ供給することができ、その
結果浄水場において多量の消毒用の塩素を投入すること
がなくなると共に、残留塩素量も大幅に低減することが
可能となり、この残留塩素と有機物とが化合してできる
トリハロメタン等の発癌性物質が生じるのを殆どなくす
ことができる効果を奏する。また本発明によれば、湖
沼、池、ダム湖等の閉鎖性水域(水源)から、溶解した
富栄養化物質及び浮遊物質の濃度を大幅に低減して水質
改善をはかった処理水を浄水場へ供給することを可能に
して、浄水場における処理を大幅に低減して良質の水を
浄水場から提供することができる効果を奏する。また本
発明によれば、湖沼、池、ダム湖等の閉鎖性水域の少な
くとも一部を囲うようにある深さ方向に仕切って処理水
域の少なくとも一部を構成する仕切り装置を設けること
により、処理水域の水の水量を限定することができ、ま
た処理水域の水が安定状態となるため浄化装置の汚染物
質の取り込み効率を高くすることができる効果を奏す
る。INDUSTRIAL APPLICABILITY According to the present invention, in a closed water area (water source) such as a lake, a pond or a dam lake, the concentration of ammonia nitrogen generated by the eutrophication phenomenon is greatly reduced to improve the water quality. Water can be supplied to the water treatment plant, and as a result, a large amount of chlorine for disinfection is not input to the water treatment plant, and the amount of residual chlorine can be significantly reduced. It is possible to almost eliminate the generation of carcinogenic substances such as trihalomethane formed by the combination. Further, according to the present invention, treated water from a closed water area (water source) such as lakes, ponds, dam lakes, etc., in which the concentration of dissolved eutrophication substances and suspended substances is significantly reduced to improve water quality is treated. It is possible to supply water to the water purification plant, and it is possible to significantly reduce the treatment at the water purification plant and provide high quality water from the water purification plant. Further, according to the present invention, by providing a partitioning device for partitioning at least a part of the closed water area of a lake, a pond, a dam lake, etc. so as to surround at least a part of the closed water area to form at least a part of the treated water area, Since the amount of water in the water area can be limited and the water in the treated water area is in a stable state, there is an effect that the efficiency of uptake of pollutants by the purification device can be increased.
【0045】また本発明によれば、浄化装置として流動
床式の濾過槽で構成したことにより、富栄養化物質等の
汚染物を効率良く分離除去することが可能となり、その
結果溶解した富栄養化物質及び浮遊物質の濃度を大幅に
低減して水質改善をはかった処理水を浄水場へ供給する
ことを可能にする効果を奏する。また本発明によれば、
浄化装置として流動床式の濾過槽で構成し、水頭差によ
って水を濾過槽内を流すようにしたことにより、取水す
るためのポンプを備えるだけの簡単な動力源で、富栄養
化物質等の汚染物を効率良く分離除去することができる
効果を奏する。また本発明によれば、陸地に浄化装置を
設置するスペースを確保することなく、浄化装置を閉鎖
性水域内に浮漂または固定して設置することを可能にし
て、閉鎖性水域(水源)から、溶解した富栄養化物質及
び浮遊物質の濃度を大幅に低減して水質改善をはかった
処理水を浄水場へ供給することができる効果を奏する。
また本発明によれば、閉鎖性水域内に設けられた流路に
沿って簡単な構成の汚染物質除去装置を配設するだけ
で、事前に処理水域の水の汚染物質を除去することがで
き、処理水域での浄化量を大幅に低減させることができ
る効果を奏する。Further, according to the present invention, since the purification device is constituted by a fluidized bed type filter tank, contaminants such as eutrophication substances can be efficiently separated and removed, and as a result, dissolved eutrophic substances can be removed. The effect that it is possible to supply the treated water to the water purification plant by significantly reducing the concentration of the chemical substance and the suspended substance and improving the water quality. According to the invention,
It is composed of a fluidized bed type filter tank as a purifying device, and water is made to flow through the filter tank due to the head difference, so it is a simple power source with only a pump for taking in water, The effect that the contaminants can be efficiently separated and removed is exhibited. Further, according to the present invention, without securing a space to install the purification device on land, it is possible to float or fix the purification device in the closed water area, and from the closed water area (water source), There is an effect that the concentration of dissolved eutrophication substances and suspended substances can be significantly reduced and the treated water with improved water quality can be supplied to the water purification plant.
Further, according to the present invention, it is possible to remove the pollutants of the water in the treated water area in advance only by disposing the pollutant removing device having a simple structure along the flow path provided in the closed water area. The effect of being able to greatly reduce the amount of purification in the treated water area is achieved.
【図1】本発明に係る局所水域浄化システムの一実施例
を閉鎖性水域における取水口を中心にして示した説明図
である。FIG. 1 is an explanatory view showing an embodiment of a local water area purification system according to the present invention, focusing on a water intake in a closed water area.
【図2】本発明に係る浄化装置の一実施例を示した流動
床式浄化装置の斜視図である。FIG. 2 is a perspective view of a fluidized bed purification apparatus showing an embodiment of the purification apparatus according to the present invention.
【図3】図2に示す流動床式浄化装置の配置関係を示し
た断面図である。FIG. 3 is a cross-sectional view showing a positional relationship of the fluidized bed purification apparatus shown in FIG.
【図4】本発明に係る局所水域浄化システムの他の一実
施例を閉鎖性水域における取水口を中心にして示した説
明図である。FIG. 4 is an explanatory view showing another embodiment of the local water area purification system according to the present invention, focusing on the intake in the closed water area.
【図5】本発明に係る仕切り装置の一実施例を示した部
分詳細図である。FIG. 5 is a partial detailed view showing an embodiment of the partitioning device according to the present invention.
【図6】図5に示す仕切り装置の上端に補助通路を付け
た場合の実施例を示した断面図である。6 is a cross-sectional view showing an embodiment in which an auxiliary passage is provided at the upper end of the partition device shown in FIG.
【図7】本発明に係る局所水域浄化システムの更に他の
一実施例を閉鎖性水域における取水口を中心にして示し
た説明図である。FIG. 7 is an explanatory view showing still another embodiment of the local water area purification system according to the present invention, focusing on the intake in the closed water area.
【図8】本発明に係る仕切り装置で仕切る程度に応じて
水質の汚染度と浄化に要する日数との関係を示した浄化
の進行度グラフである。FIG. 8 is a purification progress graph showing the relationship between the degree of pollution of water quality and the number of days required for purification according to the degree of partitioning by the partitioning device according to the present invention.
【図9】本発明に係る仕切り装置においてエアカーテン
方式(気泡方式)の実施例を示した図である。FIG. 9 is a view showing an embodiment of an air curtain system (air bubble system) in the partition device according to the present invention.
【図10】本発明に係る局所水域浄化システムの更に他
の一実施例を閉鎖性水域における取水口を中心にして示
した説明図である。FIG. 10 is an explanatory view showing still another embodiment of the local water area purification system according to the present invention, focusing on the intake in the closed water area.
【図11】図10に示す汚染物除去装置の一実施例を通
路に沿って示した断面図である。11 is a cross-sectional view showing an embodiment of the contaminant removing device shown in FIG. 10 along a passage.
【図12】図10に示す浄化装置の一実施例を示した詳
細図である。FIG. 12 is a detailed view showing an embodiment of the purification device shown in FIG.
1…浄水場、2…取水口、5…送水管、6…閉鎖性水
域、7、7’…処理水域 8…処理水域の外側の水域、11、11a、11b…浄
化装置 12…藻類除去装置(浄化装置) 14、14t、14x、14y、…仕切り装置、15…
ブイ 11’…流動床式浄化装置、14a〜14g…仕切り物
質体(構造物質) 16a〜16g…重り、18a〜18c…開口、20…
補助通路 21…散気管、22…気泡、23…ネット、24…第1
のフェンス 25…第2のフェンス、26…第3のフェンス、27…
第4のフェンス 28…藻類除去装置、29…浄化装置(布浄化装置)、
30…汚泥 31…ネット、32…木炭等の濾材層、33…汚泥引き
抜きポンプ 34…散気管、35…布部分、36…案内板 42、42a〜42c…流動床式の濾過槽、44…取水
口、45…水中ポンプ 48a〜48c…導水管、50a〜50c…排出管、5
1…沈殿槽 52、53…放流管、49、49a〜49c…濾材DESCRIPTION OF SYMBOLS 1 ... Water purification plant, 2 ... Intake port, 5 ... Water supply pipe, 6 ... Closed water area, 7, 7 '... Treated water area 8 ... Water area outside treated water area, 11, 11a, 11b ... Purification device 12 ... Algae removal device (Purification device) 14, 14t, 14x, 14y, ... Partitioning device, 15 ...
Buoy 11 '... Fluidized bed type purification device, 14a-14g ... Partition material body (structural material) 16a-16g ... Weight, 18a-18c ... Opening, 20 ...
Auxiliary passage 21 ... Air diffuser, 22 ... Bubbles, 23 ... Net, 24 ... First
Fence 25 ... Second Fence, 26 ... Third Fence, 27 ...
Fourth fence 28 ... Algae removing device, 29 ... Purifying device (cloth purifying device),
30 ... Sludge 31 ... Net, 32 ... Filter material layer such as charcoal, 33 ... Sludge drawing pump 34 ... Diffuser pipe, 35 ... Cloth portion, 36 ... Guide plate 42, 42a to 42c ... Fluidized bed type filtration tank, 44 ... Water intake Mouth, 45 ... Submersible pump 48a-48c ... Water conduit, 50a-50c ... Discharge pipe, 5
1 ... Settling tank 52, 53 ... Discharge pipe, 49, 49a to 49c ... Filter medium
───────────────────────────────────────────────────── フロントページの続き (72)発明者 依田 裕明 茨城県土浦市神立町603番地株式会社日立 製作所土浦工場内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Hiroaki Yoda 603 Kintatemachi, Tsuchiura City, Ibaraki Prefecture Hitachi Ltd. Tsuchiura Plant
Claims (31)
深さ方向に仕切って処理水域を形成する仕切り物体と、
前記閉鎖性水域または処理水域の水を取水してこの水に
存在する汚染物を分離除去し、この分離除去された処理
水を前記処理水域に放出する浄化装置とを備え、該浄化
装置で浄化された前記処理水域内の水を浄水場へ取水す
るように構成したことを特徴とする局所水域浄化システ
ム。1. A partitioning body that partitions in a depth direction so as to surround at least a part of a closed water body to form a treated water body,
A purification device for taking in water from the closed water area or the treated water area to separate and remove pollutants present in the water, and discharging the separated and removed treated water to the treated water area; A local water area purification system, which is configured to take in the treated water in the treated water area to a water purification plant.
から3倍であり、前記浄化装置の一日の処理可能水量が
前記一日の取水量の100%から70%であることを特
徴とする請求項1記載の局所水域浄化システム。2. The volume of the treated water area is 2 to 3 times the daily intake amount, and the daily treatable water amount of the purification device is 100% to 70% of the daily intake amount. The local water area purification system according to claim 1, wherein
物として富栄養物質または藻類を含むことを特徴とする
請求項1記載の局所水域浄化システム。3. The local water purification system according to claim 1, wherein the purification device contains a nutrient or an alga as a contaminant to be separated and removed.
理水域内に設置したことを特徴とする請求項1記載の局
所水域浄化システム。4. The local water purification system according to claim 1, wherein the purification device is installed in the closed water area or the treated water area.
理水域の水を取水するためのポンプと、このポンプの働
きによって取水された水を瀘材と接触させて浄化して処
理水を放出する濾過槽と、該濾過槽から放出された処理
水に存在する浮遊物質を沈降させる沈殿槽とを備えたこ
とを特徴とする請求項1記載の局所水域浄化システム。5. The purifier includes a pump for taking in water in the closed water area or the treated water area, and the water taken in by the operation of the pump is brought into contact with a filter to purify and release the treated water. The local water area purification system according to claim 1, further comprising: a filtration tank that performs the above treatment, and a settling tank that settles suspended substances existing in the treated water discharged from the filtration tank.
電源を備えたことを特徴とする請求項1記載の局所水域
浄化システム。6. The local water area purification system according to claim 1, wherein the purification apparatus is provided with a power source for driving the pump.
処理した汚染物を流す補助通路を形成したことを特徴と
する請求項1記載の局所水域浄化システム。7. The system for purifying local water bodies according to claim 1, wherein an auxiliary passage through which a contaminant treated by the purifying device flows is formed above the partition object.
させたことを特徴とする請求項1記載の局所水域浄化シ
ステム。8. The local water purification system according to claim 1, wherein the purification device is floated in the closed water area.
深さ方向に仕切って処理水域の少なくとも一部を形成す
る仕切り物体と、前記閉鎖性水域または処理水域の水を
取水するための取水手段と該取水手段によって取水され
た被処理水を瀘材と接触させて浄化して放出または流出
する濾過手段と該濾過手段から放出または流出された被
処理水に存在する浮遊物質を沈降させる沈殿手段とを備
え、前記取水された被処理水に存在する汚染物を前記濾
過手段と沈殿手段とで分離除去して処理水を前記処理水
域に放出または流出するように構成した浄化装置とを備
え、該浄化装置で浄化された前記処理水域内の水を浄水
場へ取水するように構成したことを特徴とする局所水域
浄化システム。9. A partitioning body which partitions at least a part of a closed water area in the depth direction so as to form at least a part of a treated water area, and water intake for taking in water of the closed water area or the treated water area. Means and a filtering means for contacting the water to be treated taken in by the water collecting means with a filter to purify and discharging or flowing out, and a settling to settle suspended substances existing in the treated water discharged or discharged from the filtering means And a purification device configured to discharge or outflow the treated water into the treated water area by separating and removing contaminants existing in the taken-in treated water by the filtering means and the precipitation means. A local water area purification system characterized in that the water in the treated water area purified by the purification apparatus is taken into a water purification plant.
に深さ方向に仕切って処理水域の少なくとも一部を形成
する仕切り物体と、前記閉鎖性水域または処理水域の水
を取水するための取水手段と該取水手段によって取水さ
れた被処理水に存在する浮遊物質を沈降させる沈殿手段
と該沈殿手段で処理された被処理水を瀘材と接触させて
浄化して処理水を放出または流出する濾過手段とを備
え、前記取水された被処理水に存在する汚染物を前記沈
殿手段と濾過手段とで分離除去して処理水を前記処理水
域に放出または流出するように構成した浄化装置とを備
え、該浄化装置で浄化された前記処理水域内の水を浄水
場へ取水するように構成したことを特徴とする局所水域
浄化システム。10. A partitioning body that partitions at least a part of a closed water body in the depth direction so as to form at least a part of a treated water area, and water intake for taking in water of the closed water area or the treated water area. Means and settling means for settling suspended solids present in the water to be treated taken by the water intake means and the treated water treated by the settling means are brought into contact with the filter to purify and release or discharge the treated water And a purifying device configured to discharge and outflow the treated water to the treated water area by separating and removing contaminants existing in the treated water that has been taken in by the sedimentation means and the filtering means. A local water area purification system, characterized in that the water in the treated water area, which is purified by the purification apparatus, is taken into a water purification plant.
式の濾過槽で構成したことを特徴とする請求項9または
10記載の局所水域浄化システム。11. The local water area purification system according to claim 9, wherein the purification means comprises a fluidized bed type filtration tank as the filtration means.
差により、濾材を充填した濾過槽の底部に放出された被
処理水に対して前記濾材と接触しながら上昇流が生じる
ように構成したことを特徴とする請求項9または10記
載の局所水域浄化システム。12. The filtering means of the purifying device is configured to generate an ascending flow of the water to be treated discharged to the bottom of a filter tank filled with a filter medium while being in contact with the filter medium due to a head pressure difference. The local water area purification system according to claim 9 or 10.
処理水に存在する浮遊物質を沈降させる沈殿手段と該沈
殿手段で処理された被処理水を瀘材と接触させて浄化し
て処理水を放出または流出する濾過手段とを備え、前記
被処理水に存在する汚染物を前記沈殿手段と濾過手段と
で分離除去して浄化された処理水を処理水域に放出また
は流出するように構成した浄化装置を備え、該浄化装置
で浄化された処理水を浄水場へ取水するように構成した
ことを特徴とする局所水域浄化システム。13. Treated water obtained by contacting and purifying the settling means for settling floating substances present in the treated water which is taken in or flowed in from the closed water area and the treated water treated by the settling means with a filter. And a filtering means for discharging or flowing out the pollutants existing in the water to be treated are separated and removed by the precipitation means and the filtering means, and the purified treated water is discharged or discharged to the treated water area. A local water area purification system comprising a purifying device, wherein the treated water purified by the purifying device is configured to be taken into a water purification plant.
処理水を瀘材と接触させて浄化して放出または流出する
濾過手段と該濾過手段で浄化された被処理水に存在する
浮遊物質を沈降させる沈殿手段とを備え、前記被処理水
に存在する汚染物を前記濾過手段と沈殿手段とで分離除
去して浄化された処理水を処理水域に放出または流出す
るように構成した浄化装置を備え、該浄化装置で浄化さ
れた処理水を浄水場へ取水するように構成したことを特
徴とする局所水域浄化システム。14. Filtering means for purifying and discharging or flowing out treated water which is taken in or flowed in from a closed water area by contacting with a filter, and suspended matter existing in the treated water purified by the filtering means. A purifying apparatus comprising a sedimentation means for sedimentation, and configured to discharge or outflow the treated water purified by separating and removing contaminants existing in the water to be treated by the filtering means and the sedimentation means. A local water area purification system, characterized in that the treated water purified by the purification device is taken into a water purification plant.
式の濾過槽で構成したことを特徴とする請求項13また
は14記載の局所水域浄化システム。15. The system for purifying local water bodies according to claim 13 or 14, wherein a fluidized bed type filtration tank is used as the filtration means of the purification device.
差により、濾材を充填した濾過槽の底部に放出された被
処理水に対して前記濾材と接触しながら上昇流が生じる
ように構成したことを特徴とする請求項13または14
記載の局所水域浄化システム。16. The filtering means of the purifying device is configured to generate an upward flow of the water to be treated discharged to the bottom of a filter tank filled with a filter medium while being in contact with the filter medium due to a head pressure difference. 15. The method according to claim 13 or 14,
The described local water purification system.
水を木炭等の濾材と接触しながら通過させると共に爆気
することによって被処理水中のアンモニア性窒素を硝酸
性窒素に変換するように構成したことを特徴とする請求
項13または14記載の局所水域浄化システム。17. A filter means of the purification device, wherein the water to be treated is passed through while contacting with a filter material such as charcoal and is detonated to convert ammonia nitrogen in the water to be treated into nitrate nitrogen. The local water area purification system according to claim 13 or 14, characterized in that.
水について底部に沿った流れから上昇流を発生させて、
この流れによる遠心力によって浮遊物質を沈降させて除
去するように構成したことを特徴とする請求項13また
は14記載の局所水域浄化システム。18. As the settling means of the purification device, an upward flow is generated from the flow along the bottom of the water to be treated,
The local water purification system according to claim 13 or 14, characterized in that the suspended matter is settled and removed by the centrifugal force of this flow.
水について底部に沿った流れから上昇流を発生させて、
この流れによる遠心力によって浮遊物質を沈降させて堆
積させることによって除去し、この堆積した汚泥を回収
するように構成したことを特徴とする請求項13または
14記載の局所水域浄化システム。19. As a settling means of the purification device, an ascending flow is generated from the flow along the bottom of the water to be treated,
15. The system for purifying local water bodies according to claim 13 or 14, characterized in that suspended matter is settled and accumulated by the centrifugal force of this flow to be removed, and the accumulated sludge is collected.
に深さ方向に仕切って処理水域を形成する仕切り物体
と、前記処理水域内に設置され、前記処理水域から取水
された水に存在する汚染物を瀘材と接触させて分離除去
する濾過槽を有し、該濾過槽で処理された処理水を前記
処理水域に放出する浄化装置とを備え、該浄化装置で浄
化された前記処理水域内の水を浄水場へ取水するように
構成したことを特徴とする局所水域浄化システム。20. A partitioning body that forms a treated water area by partitioning in the depth direction so as to surround at least a part of a closed water area, and is present in water that is installed in the treated water area and taken from the treated water area. A treated water area having a filtration tank for separating and removing contaminants by contacting with a filter material and discharging treated water treated in the filtration tank to the treated water area; and the treated water area purified by the purifying apparatus. A local water area purification system characterized in that the water inside is taken in to a water purification plant.
被処理水を流してにおいて、沿っての少なくとも一部を
囲うように深さ方向に仕切って処理水域の少なくとも一
部を形成するとともに汚染物除去機能を有する仕切り物
体と、前記処理水域の水の中に存在する藻類を除去する
藻類除去装置と、該藻類除去装置で藻類が除去された処
理水を通すことによって浄化する浄化装置とを備え、該
浄化装置で浄化された前記処理水域内の水を浄水場へ取
水するように構成したことを特徴とする局所水域浄化シ
ステム。21. When the water to be treated flows along a flow path formed in a closed water region, at least a part of the treated water region is formed by partitioning in the depth direction so as to surround at least a part of the water. And a partitioning object having a contaminant removal function, an algae removing device for removing algae present in the water of the treated water area, and a purification for purifying by passing the treated water from which algae have been removed by the algae removing device And a device for collecting water in the treated water purified by the purification device to a water purification plant.
状または格子状または網状の瀘材を設置して形成したこ
とを特徴とする請求項21記載の局所水域浄化システ
ム。22. The system for purifying local water bodies according to claim 21, wherein the purification device is formed by installing a cloth-shaped, lattice-shaped, or net-shaped filter material at a desired portion of the flow path.
処理水を流入させる通路を有する第1の通路形成手段
と、該第1の通路形成手段の通路を通って流入する底部
に沿った被処理水の流れを上昇流に変えてこの流れに基
づく遠心力によって浮遊物質を沈降させて底部に汚泥と
して堆積させる第2の通路形成手段と、該第2の通路形
成手段の上部に有する通路を通して流れる被処理水を更
に底部に導いて底部に通路を有する第3の通路形成手段
と、該第3の通路形成手段の通路を通して流入される被
処理水を、木炭等の濾材層を通して曝気することによっ
て被処理水中のアンモニア性窒素を硝酸性窒素に変換す
るように構成した濾過手段とを前記流路に沿って設置し
て構成したことを特徴とする汚染物質除去装置。23. First passage forming means having a passage through which water to be treated flows and having a passage into which the water to be treated flows, and a bottom portion flowing in through a passage of the first passage forming means. Second passage forming means for changing the flow of the treated water along the upward flow to an upward flow and causing the suspended matter to settle by the centrifugal force based on this flow and accumulating as sludge on the bottom, and an upper part of the second passage forming means The third passage forming means having a passage at the bottom by further guiding the treated water flowing through the passage provided in the first passage to the bottom portion, and the treated water flowing in through the passage of the third passage forming means into a filter medium layer such as charcoal. A pollutant removing device comprising: a filtering unit configured to convert ammoniacal nitrogen in the water to be treated into nitrate nitrogen by aerating through the channel and the filtering unit.
路を形成し、底部に被処理水を流入させる通路を有する
第1の通路形成手段と、該第1の通路形成手段の通路を
通って流入する底部に沿った被処理水の流れを上昇流に
変えてこの流れに基づく遠心力によって浮遊物質を沈降
させて底部に汚泥として堆積させる第2の通路形成手段
と、該第2の通路形成手段の上部に有する通路を通して
流れる被処理水を更に底部に導いて底部に通路を有する
第3の通路形成手段と、該第3の通路形成手段の通路を
通して流入される被処理水を、木炭等の濾材層を通して
曝気することによって被処理水中のアンモニア性窒素を
硝酸性窒素に変換するように構成した濾過手段とを前記
流路に沿って設置して構成した汚染物質除去装置を備え
たことをとく特徴とする局所水域浄化システム。24. A first passage forming means having a passage for flowing the water to be treated in the closed water region and having a passage for allowing the water to be treated to flow into the bottom portion, and a passage of the first passage forming means. Second passage forming means for converting a flow of the water to be treated flowing through the bottom through to an upward flow and causing a centrifugal force based on the flow to settle suspended solids and deposit the sludge on the bottom as sludge; Third passage forming means having a passage at the bottom by further guiding the untreated water flowing through the passage provided on the upper portion of the passage forming means to the bottom portion, and the treated water flowing through the passage of the third passage forming means, A pollutant removal device constituted by installing a filtering means configured to convert ammoniacal nitrogen in the water to be treated into nitrate nitrogen by aeration through a filter medium layer such as charcoal and the channel is provided. Special features Local water purification system to be.
2の通路形成手段で底部に堆積した汚泥を回収する回収
手段を設置したことを特徴とする請求項24記載の局所
水域浄化システム。25. The local water area purification system according to claim 24, wherein the pollutant removing device is provided with a collecting means for collecting the sludge accumulated at the bottom portion by the second passage forming means.
に深さ方向に仕切って処理水域の少なくとも一部を構成
する仕切り装置と、浄水場へ前記処理水域の水を汲み上
げる前記処理水域に設置された取水配管と、前記処理水
域外の水域の水を取り込みこの取り込まれた水の中に存
在する汚染物を分離除去し、この分離除去した処理水を
前記処理水域に放出する浄化装置とを備えたことを特徴
とする局所水域浄化システム。26. A partitioning device for partitioning at least a part of a closed water area in the depth direction so as to constitute at least a part of the treated water area, and a partition device installed in the treated water area for pumping the water of the treated water area to a water treatment plant. And a purification device that takes in water in the water area outside the treated water area, separates and removes the contaminants present in the taken water, and discharges the separated and removed treated water into the treated water area. A local water area purification system characterized by being equipped.
に深さ方向に仕切る水域仕切り物体において、複数の仕
切り物体を鎖で簾状に接続し、該簾状の仕切り物体の一
部に前記処理水域外の水域の水が通る開口を形成し、ブ
イで前記簾状の仕切り物体を水中に保持するように構成
したことを特徴とする水域仕切り物体。27. A body partitioning body for partitioning in a depth direction so as to surround at least a part of a closed body of water, wherein a plurality of partition bodies are connected in a chain shape by a chain, and the partition body in the shape of a blind is partly connected to the partition body. A water area partition object, characterized in that an opening through which water in the water area outside the treated water area passes is formed, and the buoy holds the partition object in water.
に仕切る一つ以上の仕切り装置と、浄水場へ前記処理水
域の水を汲み上げる前記処理水域に設置された取水配管
と、前記閉鎖性水域の水を取り込みこの取り込まれた水
の中に存在する汚染物を分離除去し、この汚染物を分離
除去された処理水を前記仕切り装置と前記取水配管の間
に放出する浄化装置とを備えたことを特徴とする局所水
域浄化システム。28. One or more partitioning devices for partitioning at least a part of the closed water area in the depth direction, an intake pipe installed in the treated water area for pumping water of the treated water area to a water treatment plant, and the closed property. A purifying device for taking in water from the water area, separating and removing pollutants existing in the taken water, and discharging the treated water from which the pollutant has been separated and removed between the partition device and the intake pipe A local water purification system that is characterized by
に水底に散気管を設けこの散気管から気泡を発生させ処
理水域の少なくとも一部を構成する仕切り手段と、浄水
場へ前記処理水域の水を汲み上げる前記処理水域に設置
された取水配管と、前記閉鎖性水域の水を取り込みこの
取り込まれた水の中に存在する汚染物を分離除去し、こ
の汚染物を分離除去された処理水を前記処理水域に放出
する浄化装置とを備えたことを特徴とする局所水域浄化
システム。29. A partition means for providing a diffusing pipe at the bottom of the water so as to surround at least a part of the closed water area, and forming a bubble from the diffusing tube to constitute at least a part of the treated water area; The intake pipe installed in the treated water area for pumping water and the water in the closed water area are taken in to separate and remove the pollutants present in the taken water, and the treated water from which the pollutant is separated and removed is A local water area purification system, comprising: a purifying device that discharges the treated water area.
する汚染物を分離除去して浄化された処理水を仕切られ
た処理水域に放出し、前記処理水域内の処理水を取水配
管により浄水場へ供給することを特徴とする局所水域浄
化方法。30. In a closed water area, the treated water purified by separating and removing the contaminants present in the water to be treated is discharged to the partitioned treated water area, and the treated water in the treated water area is purified by a water pipe. A method for purifying a local water area, characterized by supplying the water to the site.
このポンプで取水した被処理水を浄化するための濾材を
充填した濾過槽と、該濾過槽で浄化された処理水を放出
する放出部と、この放出部の下流側に水中の浮遊物質を
沈降させて除去する沈殿槽を備えたことを特徴とする浄
化装置。31. A pump for taking in water for purification,
A filtration tank filled with a filter medium for purifying the water to be treated taken by this pump, a discharge section for discharging the treated water purified by the filtration tank, and a suspended substance in the water settling on the downstream side of this discharge section. A purifying device comprising a settling tank for removing by removing.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7200840A JPH0947749A (en) | 1995-08-07 | 1995-08-07 | Local water purification system and method, and purification device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7200840A JPH0947749A (en) | 1995-08-07 | 1995-08-07 | Local water purification system and method, and purification device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0947749A true JPH0947749A (en) | 1997-02-18 |
Family
ID=16431087
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP7200840A Pending JPH0947749A (en) | 1995-08-07 | 1995-08-07 | Local water purification system and method, and purification device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0947749A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2006226052A (en) * | 2005-02-21 | 2006-08-31 | Chugoku Electric Power Co Inc:The | Water intake device |
| CN106219622A (en) * | 2016-08-18 | 2016-12-14 | 桂林市春晓环保科技有限公司 | A kind of novel sewage treatment agent and preparation method thereof |
| CN112755635A (en) * | 2020-12-21 | 2021-05-07 | 福建省春天生态科技股份有限公司 | Ecological purification method for water in rural pond |
-
1995
- 1995-08-07 JP JP7200840A patent/JPH0947749A/en active Pending
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2006226052A (en) * | 2005-02-21 | 2006-08-31 | Chugoku Electric Power Co Inc:The | Water intake device |
| CN106219622A (en) * | 2016-08-18 | 2016-12-14 | 桂林市春晓环保科技有限公司 | A kind of novel sewage treatment agent and preparation method thereof |
| CN112755635A (en) * | 2020-12-21 | 2021-05-07 | 福建省春天生态科技股份有限公司 | Ecological purification method for water in rural pond |
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