JPH0481002B2 - - Google Patents

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Publication number
JPH0481002B2
JPH0481002B2 JP27882584A JP27882584A JPH0481002B2 JP H0481002 B2 JPH0481002 B2 JP H0481002B2 JP 27882584 A JP27882584 A JP 27882584A JP 27882584 A JP27882584 A JP 27882584A JP H0481002 B2 JPH0481002 B2 JP H0481002B2
Authority
JP
Japan
Prior art keywords
water
lake
dam
sheet
turbid
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP27882584A
Other languages
Japanese (ja)
Other versions
JPS61155508A (en
Inventor
Yukio Ooi
Original Assignee
Oyo Chishitsu Kk
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Oyo Chishitsu Kk filed Critical Oyo Chishitsu Kk
Priority to JP27882584A priority Critical patent/JPS61155508A/en
Publication of JPS61155508A publication Critical patent/JPS61155508A/en
Publication of JPH0481002B2 publication Critical patent/JPH0481002B2/ja
Granted legal-status Critical Current

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Classifications

    • EFIXED CONSTRUCTIONS
    • E02HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
    • E02BHYDRAULIC ENGINEERING
    • E02B15/00Cleaning or keeping clear the surface of open water; Apparatus therefor

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  • Engineering & Computer Science (AREA)
  • General Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Civil Engineering (AREA)
  • Structural Engineering (AREA)
  • Cleaning Or Clearing Of The Surface Of Open Water (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、洪水等によりダム湖内に濁水現象が
生じても取水を効率よく浄化できる方法に関し、
更に詳しくは、水平方向に延びる開口部を備えた
シート状物をダム湖の取水口を取り囲むように垂
設し、前記開口部近傍に生じる湖水の急流を利用
して沈澱促進剤を局部的に拡散させ濁質の沈降に
より水質改善を図るようにしたダム濁水の浄化方
法に関するものである。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a method that can efficiently purify intake water even if a turbid water phenomenon occurs in a dam lake due to a flood or the like.
More specifically, a sheet-like material with an opening extending horizontally is placed vertically around the water intake of a dam lake, and the precipitation accelerator is applied locally using the rapid flow of lake water generated near the opening. This invention relates to a method for purifying turbid water from a dam, which improves water quality by dispersing and settling turbidity.

〔従来の技術〕[Conventional technology]

我国の河川は急流が多く短いため洪水等による
濁りは数日を待たずして流下し元の清流に復す
る。しかし一度ダムが構築されると、粘度鉱物等
数ミクロン以下の微粒子で構成される濁質は沈降
が極端に遅いため、濁水がダム湖に貯溜されてい
る期間内に沈降せず、また流量が制御されて放流
されるため河川の濁りが長期化することは避け難
い。ダム濁水は、河川景観や淡水漁業等の環境に
対して、またそれを取水して利用する農業、生活
用水あるいは工業用水等に大きな経済的影響を与
える。
Our country's rivers have many rapids and are short, so when they become cloudy due to floods, they drain away within a few days and return to their original clear waters. However, once a dam is constructed, the turbidity composed of fine particles of a few microns or less, such as clay minerals, settles extremely slowly, so the turbid water does not settle during the period that it is stored in the dam lake, and the flow rate decreases. Because the water is released in a controlled manner, it is unavoidable that the river will remain cloudy for a long period of time. Turbid water from dams has a major economic impact on the environment, including river landscapes and freshwater fisheries, as well as on the agricultural, domestic and industrial water sources that use the water.

しかしすべてのダムが濁水現象を起こすわけで
はなく、地形や地質、植生等の自然環境、開発行
為等の社会環境による集水域の地表の性状に左右
されるし、またダムの規模にもよる。経験的には
ダム湖水の年間交換回数指数α(=年間総流入
量/貯水池総容量)が30以上では濁水の問題が生
じないとされている。この指数αはダム湖が成層
型(温度躍層)であるか否かの指標でもあり、α
が小さいと(特に10以下では)成層型(温度躍
層)ダム湖となる。温度躍層は夏期に湖水面の温
度が上昇し水の密度が小さくなることにより成形
されるものであるが、この形成期に洪水等により
濁水が流入すると、洪水の温度は一般的に湖面水
より低く且つ濁質を含むので密度がほぼ躍層位置
の密度に等しくなり、濁水はこの位置にもぐり込
む形で湖内に流入する。このように安定した成層
に濁水が浸入すると稀釈拡散されにくくなり濁質
の沈降が妨げられる。もし、この躍層の位置から
取水しているダムであればこの層の水が排出され
尽くすまで濁水が長期化することになる。
However, not all dams cause turbid water phenomena, and it depends on the surface characteristics of the catchment area due to the natural environment such as topography, geology, vegetation, and social environment such as development activities, and also depends on the size of the dam. Experience has shown that when the annual exchange frequency index α (=annual total inflow/total reservoir capacity) of dam lake water is 30 or higher, problems with turbid water do not occur. This index α is also an indicator of whether the dam lake is a stratified type (thermocline), and α
If it is small (especially below 10), it becomes a stratified (thermocline) dam lake. The thermocline is formed during the summer when the temperature of the lake water surface rises and the density of the water decreases, but if turbid water flows in due to a flood during this formation period, the temperature of the flood generally becomes lower than that of the lake surface water. Because it is lower and contains turbidity, its density is almost equal to the density at the cline, and the turbid water flows into the lake by sinking into this position. When turbid water enters such a stable stratification, it becomes difficult to dilute and diffuse, and sedimentation of the turbidity is hindered. If a dam takes water from the location of this cline, the water will remain murky for a long time until the water in this layer is exhausted.

ダム湖の濁水対策の一つに選択取水法がある。
これは取水レベルを調節して、濁度の高い部分を
避けて、できるだけ湖内を撹拌しないように取水
する方法である。
One of the measures against turbid water in dam lakes is the selective water intake method.
This is a method of adjusting the water intake level, avoiding areas with high turbidity, and avoiding stirring the lake as much as possible.

その他、集水域の植生によつてダム濁水の発生
する方法や、ダム湖全体に沈澱促進剤を混入する
方法、更には上流に複ダムを作り洪水時の濁水を
それに一旦貯溜し、水量を調節して下流にトンネ
ルで放流するといつた方法等も考えられている。
Other methods include creating turbid water in a dam due to vegetation in the catchment area, mixing sedimentation accelerators into the entire dam lake, and creating multiple dams upstream to temporarily store turbid water during floods to adjust the water volume. Another method being considered is to release the water downstream through a tunnel.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

選択取水法は現時点において最も有効な濁水防
止対策であるが、取水口を機械的に昇降しなけれ
ばならないから既設ダムについては設備の変更が
困難な場合が多く、根本的な解決法とはなりえな
い。その上、洪水の規模が大きくなると温度躍層
の上方全体が濁水となつてしまうため、選択取水
の効果はない。温度躍層下で取水を行うと水温が
低くなり農作物に悪影響を与えてしまうからであ
る。植生による防御や防砂設備の設置等はある程
度有効ではあるが、地滑りや崩壊等がある場合に
は不可能だし、我国においては山地で濁質を完全
におさえることは困難な面が多い。また沈澱促進
剤を湖水全体に混入しようとしても非常に高価と
なるばかりでなく混合撹拌が不可能であり、実施
不能である。上流に複ダムを作る方法は大土木工
事となり、経済的に不利であるばかりでなく複ダ
ムが作れない地形の場合は実施できない。
The selective water intake method is currently the most effective measure to prevent turbid water, but since the intake port must be raised and lowered mechanically, it is often difficult to change the equipment of existing dams, and it is not a fundamental solution. No. Furthermore, if the scale of the flood increases, the entire area above the thermocline becomes turbid, so there is no effect on selective water intake. This is because if water is taken under the thermocline, the water temperature will drop and have a negative impact on crops. Although protection with vegetation and the installation of sand prevention equipment are effective to some extent, they are impossible in cases where there are landslides or collapses, and in Japan, it is often difficult to completely suppress turbidity in mountainous areas. Furthermore, even if it is attempted to mix the precipitation accelerator into the entire lake water, it is not only very expensive but also impossible to mix and stir, making it impractical. The method of constructing multiple dams upstream requires large-scale civil engineering work, which is not only economically disadvantageous, but also cannot be implemented in cases where the terrain does not allow the construction of multiple dams.

このように従来技術にはそれぞれ解決すべき
様々な問題があり、現時点では選択取水法以外の
対策は採られていない。
As described above, each of the conventional techniques has various problems to be solved, and at present no countermeasures other than the selective water intake method have been adopted.

本発明の目的は、上記のような従来技術の欠点
を解消し、比較的簡単な設備によつて濁水が発生
したときに効率的に放流水のみを浄化することが
でき、また選択取水機能をももたせうるような経
済的な方法を提供することにある。
The purpose of the present invention is to eliminate the drawbacks of the prior art as described above, to be able to efficiently purify only effluent water when turbid water occurs using relatively simple equipment, and to provide a selective water intake function. The aim is to provide an economical method that can be used.

〔問題点を解決するための手段〕[Means for solving problems]

上記のような目的を達成することのできる本発
明は、湖水の流れを規制する前記シート状物が水
平方向に延びる開口部を備え、ダム湖の取水口ま
たは放水口を囲むように取水または放水レベルよ
りも上方から温度躍層下まで垂設され、沈澱促進
剤が前記開口部に沿つて水平方向に配設されてい
る放散手段から湖水中に放散するように構成した
ことを特徴とするものであり、それによつて前記
開口部近傍で湖水の局所的急流を作り、湖水と沈
澱促進剤を混合撹拌させ、濁質粒子の会合を促進
して沈澱させ、放流水を浄化するようにしたダム
濁水の浄化方法である。
In the present invention, which can achieve the above objects, the sheet-like material regulating the flow of lake water is provided with an opening that extends in the horizontal direction, and the sheet-like material that regulates the flow of lake water is provided with an opening that extends in the horizontal direction, and the water intake or discharge is carried out so as to surround the water intake or water outlet of the dam lake. The device is characterized by being arranged vertically from above the level to below the thermocline, and configured so that the precipitation accelerator is dissipated into the lake water from a dissipation means disposed horizontally along the opening. The dam thereby creates a local rapid flow of lake water near the opening, mixes and stirs the lake water and the sedimentation accelerator, promotes the association of turbid particles and causes them to settle, thereby purifying the discharged water. This is a method of purifying turbid water.

ダムの取水口または放水口を囲む態様として
は、シート状物のみによつてそれらを取り囲んで
もよいし、ダム湖岸やダムそのものを利用し両岸
間にシート状物を張設して囲むようにしてもよ
い。
The water intake or water outlet of a dam may be surrounded by only a sheet-like material, or by using the dam lakeshore or the dam itself and surrounding it with a sheet-like material stretched between both banks. good.

ダム湖からの放流量は貯溜量によつて調節され
るが、これらの量の変動に対して本発明の効果を
更に一層増大させる方法としては、開口部の面積
を調節することである。それによつて該開口部を
通る湖水の流速、カルマン渦の強さを調節し、沈
澱促進剤の湖水中への混合を最も効率のよい状態
にすることができる。
The discharge amount from the dam lake is adjusted by the storage amount, and a method for further increasing the effect of the present invention in response to fluctuations in these amounts is to adjust the area of the opening. Thereby, the flow rate of the lake water passing through the opening and the strength of the Karman vortex can be adjusted to achieve the most efficient mixing of the precipitation accelerator into the lake water.

〔作用〕[Effect]

ダム湖の流速はその大きさにもよるが通常毎秒
数mm程度と非常に小さいが、前記シート状物によ
つてダム湖の流れが規制され開口部のみが水路と
なるため、該開口部近傍での湖水の流れは局所的
にかなり速くなり、沈澱促進剤の混合に有効なカ
ルマン渦が発生する。その開口部に沈澱促進剤の
放散手段が設けられると、前記開口部近傍で生じ
る湖水の局部的急流によつて沈澱促進剤は混合撹
拌されるから、濁質粒子の会合が促進され少量の
沈澱促進剤で効率よく浄化することが可能とな
る。
The flow rate of a dam lake is usually very low, about several millimeters per second, depending on its size, but the sheet-like material restricts the flow of the dam lake and only the opening becomes a waterway, so the flow rate near the opening The flow of lake water locally becomes considerably faster, creating Karman vortices that are effective for mixing precipitation accelerators. When a means for dispersing the sedimentation accelerator is provided at the opening, the sedimentation accelerator is mixed and agitated by local rapids of lake water generated near the opening, which promotes association of turbid particles and forms a small amount of sediment. It becomes possible to purify efficiently with an accelerator.

またダム湖は大きな表面積を有するから、沈澱
促進剤の放散手段を備えたシート状物の設置位置
を調整することによつて沈澱促進剤と接触し大き
な粒径に成長した濁質が沈降に要するに十分な滞
留時間を与えることができ、それによつて取水口
あるいは放水口から放流される湖水は濁質粒子を
含まないきれいなものとなる。
In addition, since dam lakes have a large surface area, by adjusting the installation position of the sheet-like material equipped with means for dispersing the sedimentation accelerator, the turbidity that comes into contact with the sedimentation accelerator and grows to a large particle size can be Sufficient residence time can be provided, so that the lake water discharged from the water intake or outlet will be clean and free of turbid particles.

〔実施例〕〔Example〕

以下、図面に基づき本発明について更に詳しく
説明する。第1図は本発明を適用したダム濁水の
浄化方法を示すダム湖の説明図、第2図はその断
面図である。ダム湖10は河川12からの流水を
ダム14によつて塞き止め一旦貯溜するものであ
り、貯溜した水は取水口16から下流に放流され
る。
Hereinafter, the present invention will be explained in more detail based on the drawings. FIG. 1 is an explanatory diagram of a dam lake showing a method for purifying turbid water from a dam to which the present invention is applied, and FIG. 2 is a sectional view thereof. The dam lake 10 blocks water flowing from the river 12 with a dam 14 and temporarily stores it, and the stored water is discharged downstream from the water intake 16.

さて本発明においては第1図および第2図に示
すように、ダム湖10の取水口16の上流側で湖
水の流れを規制するように濁水防止フエンス18
が設けられる。この濁水防止フエンス18は、本
実施例では水平方向に延びる開口部を備えたシー
ト状物を両湖岸間にかけて取水レベルの上方から
温度躍層Tの下方まで垂設され、前記開口部近傍
に沈澱促進剤の放散手段が設けられる。
Now, in the present invention, as shown in FIGS. 1 and 2, a turbid water prevention fence 18 is installed on the upstream side of the water intake 16 of the dam lake 10 to regulate the flow of lake water.
is provided. In this embodiment, the turbid water prevention fence 18 is a sheet-like material with an opening extending horizontally, which is vertically installed between both lake shores from above the water intake level to below the thermocline layer T, to prevent sedimentation near the opening. Promoting agent dissipation means are provided.

本発明で用いられる濁水防止フエンスの一例を
第3図に示す。この例は、上部に浮き20が取り
付けられ、下端に重り22を有するシート状物2
4が一方の湖岸から他方の湖岸に至るように延設
される構成である。このシート24は、水平方向
に延びる開口部26が複数個形成されたものであ
り、各開口部26に沿つて薬液注入パイプ28が
水平方向に設けられる。該薬液注入パイプ28は
多数のノズル30を備え、上端で送液パイプ33
に連結される。各薬液注入パイプ28はそれぞれ
支持ワイヤー32によつて所定の位置に設置され
るとともに、開口部26の上下両端にもそれぞれ
ワイヤー34あるいはシートと同じ材質の補強材
が渡設されて、過度に開かないようになつてい
る。送液パイプ33から送られてくる液状の沈澱
促進剤は、各薬液注入パイプ28を通りノズル3
0から湖水中に加圧放散されることになる。
An example of the muddy water prevention fence used in the present invention is shown in FIG. In this example, a sheet-like material 2 has a float 20 attached to its upper part and a weight 22 at its lower end.
4 extends from one lakeshore to the other lakeshore. This sheet 24 has a plurality of openings 26 extending in the horizontal direction, and a chemical liquid injection pipe 28 is provided horizontally along each opening 26. The chemical liquid injection pipe 28 is equipped with a large number of nozzles 30, and has a liquid sending pipe 33 at its upper end.
connected to. Each chemical injection pipe 28 is installed at a predetermined position by a support wire 32, and reinforcing materials made of the same material as the wire 34 or the sheet are provided at both upper and lower ends of the opening 26 to prevent it from opening excessively. It seems like there is no such thing. The liquid precipitation accelerator sent from the liquid sending pipe 33 passes through each chemical injection pipe 28 to the nozzle 3.
It will be pressurized and released into the lake water from zero.

濁水現象は、ダム湖の年間交換回数指数αが小
さい成層型(温度躍層)のダムで顕著に起こる。
温度躍層(第2図符号Tで示される範囲)は夏期
に湖水面の温度が上昇し水の密度が小さくなるこ
ととダム湖内の流速が小さいことによつて生じ
る。冬期は表層が冷やされるので密度が高くなり
降下し底部の水が上昇して大循環が起こる。濁水
の主要発生原因である洪水の発生期および渇水に
よるバツクウオータ部洗掘は夏から秋であり躍層
Tの発生期である。湖内に浸入する洪水塊は、小
規模洪水ではその水温と濁質の混入程度で決まる
比重によつて湖内同一密度の深度に浸入するし、
それより大きな規模になると躍層Tより上方全体
が混合撹拌される。湖内の水の流れは前述の密度
流の他に風の影響を受ける表層の流れ、取水によ
つて生じる取水口レベルの流れがある。このうち
取水によつて生じる流れが最も大きいが、その流
速は前記のように極めて小さく(毎秒数mm程度)、
その流れの速度分布は取水口レベルを頂点とする
ガウス分布曲線(第2図符号参照)と考えられ
る。
Turbid water phenomena occur significantly in stratified (thermocline) dams where the annual exchange frequency index α of the dam lake is small.
The thermocline (the area indicated by the symbol T in Figure 2) is created by the temperature of the lake water surface rising during the summer, the density of the water becoming smaller, and the flow velocity within the dam lake being lower. During the winter, the surface layer cools, becoming denser and sinking, causing water at the bottom to rise and create a general circulation. Floods, which are the main causes of turbid water, and backwater scouring due to drought occur from summer to autumn, and this is the period when cline T occurs. In the case of small-scale floods, the floodwaters that infiltrate into the lake will infiltrate to the same depth within the lake, depending on the specific gravity determined by the water temperature and the degree of turbidity.
When the scale is larger than that, the entire area above the cline T is mixed and stirred. In addition to the above-mentioned density flow, water flow within the lake includes surface flow influenced by wind and flow at the intake level caused by water intake. Of these, the flow generated by water intake is the largest, but as mentioned above, the flow velocity is extremely small (about a few mm per second).
The velocity distribution of the flow is considered to be a Gaussian distribution curve (see the reference numerals in Figure 2) with the peak at the water intake level.

ところで、前記のように本発明によつて取水口
の上流側に濁水防止フエンス18が設けられる
と、第4図からも明らかなようにシート24によ
つて湖水の流れが阻害され、すべて前記開口部2
6を流過しようとするから(矢印A参照)、その
部分での流速が局部的に増大する。前記の例では
シート24は湖水の表層から温度躍層Tの下方ま
で懸垂されている。取水は湖底の冷水塊を取り入
れないように表層から躍層Tに至るまでの範囲内
に設定されるのが一般的で、取水レベルの流れは
このシート24で十分阻害できる。シート24を
躍層Tより下まで垂設すれば、その下方を流れよ
うとする水は密度の大きい冷水塊によつて受け止
められ流れが阻害されるため、結局湖水の流れは
開口部26のみを通つて取水口16に至るからで
ある。但し躍層T以下まで設けるべきシートの長
さは、躍層の上下の水温差および流れを阻害する
ことによつて生じる圧力(この圧力は流量と開口
部26の面積によつて決まる)から計算により求
めることができる。これはそのダム湖固有の長さ
であり、ダム湖毎に最も厳しい条件のもとに求め
る必要がある。勿論、経済的に許容されれば湖底
まで達するシートを設けてもかまわない。シート
24の上端は取水レベルの上方に位置させておけ
ばよいが、湖水表面に位置させる方が好ましい。
By the way, when the muddy water prevention fence 18 is provided on the upstream side of the water intake according to the present invention as described above, the flow of lake water is obstructed by the sheet 24, as is clear from FIG. Part 2
6 (see arrow A), the flow velocity locally increases in that part. In the above example, the sheet 24 is suspended from the surface layer of the lake water to below the thermocline layer T. Generally, the water intake is set within the range from the surface layer to the cline T so as not to take in the cold water mass at the bottom of the lake, and the flow at the water intake level can be sufficiently inhibited by the sheet 24. If the sheet 24 is installed vertically below the cline T, the water that attempts to flow below will be intercepted by the dense cold water mass and the flow will be obstructed, so the flow of lake water will only flow through the opening 26. This is because the water passes through the water intake port 16 and reaches the water intake port 16. However, the length of the sheet that should be provided below the cline T is calculated from the difference in water temperature above and below the cline and the pressure generated by obstructing the flow (this pressure is determined by the flow rate and the area of the opening 26). It can be found by This length is unique to each dam lake, and must be determined under the most severe conditions for each dam lake. Of course, if it is economically acceptable, a sheet that reaches the bottom of the lake may be provided. The upper end of the sheet 24 may be located above the water intake level, but it is preferably located at the surface of the lake water.

前記開口部26に設けられている薬液注入パイ
プ28のノズル30から液状の沈澱促進剤が放散
されると(第4図矢印B参照)、前記開口部26
の近傍に発生する局所的な急流、カルマン渦によ
つて沈澱促進剤が混合撹拌されるので濁水中の濁
質粒子の会合が促進され効果的に沈澱浄化できる
のである。
When the liquid precipitation accelerator is released from the nozzle 30 of the chemical injection pipe 28 provided in the opening 26 (see arrow B in FIG. 4), the opening 26
The precipitation accelerator is mixed and stirred by the Karman vortex, a local rapid current generated near the turbid water, which promotes the association of turbid particles in the turbid water, making it possible to effectively settle and purify the turbid water.

またこの濁水防止フエンスは、選択取水と同一
の効果を生じさせることができる。第5図におい
て取水口16が選択取水機能の無い固定構造であ
るとする。今、濁水防止フエンス18が仮想線で
示す位置にセツトされ、開口部26が深度Lbに
位置しているとすると、この深度Lbを頂点とす
るようなガウス分布曲線Vbで示される流れが生
じている。
Moreover, this turbid water prevention fence can produce the same effect as selective water intake. In FIG. 5, it is assumed that the water intake port 16 has a fixed structure without a selective water intake function. Now, if the turbid water prevention fence 18 is set at the position shown by the imaginary line and the opening 26 is located at the depth Lb, a flow shown by a Gaussian distribution curve Vb with the apex at this depth Lb will occur. There is.

小規模洪水が生じて密度流がこの深度に浸入し
てきたとすると、濁水防止フエンス18を巻き上
げて実線で示す位置に設定し、開口部26を深度
Laに位置させる。すると湖水の流れは、この深
度Laを頂点とするようなガウス分布曲線Vaとな
り濁水の流過を防止できることになる。このよう
に、水平方向に開口部を有する濁水防止フエンス
を用いることによつて、選択取水と全く同一の効
果をもたせることができ、既設ダムへの選択取水
装置としての効果も大きい。
If a small-scale flood occurs and the density current intrudes into this depth, the turbid water prevention fence 18 is rolled up and set at the position shown by the solid line, and the opening 26 is set at the depth.
Place it in La. Then, the flow of lake water becomes a Gaussian distribution curve Va with the peak at this depth La, and it is possible to prevent the flow of turbid water. In this way, by using a turbid water prevention fence having openings in the horizontal direction, it is possible to have exactly the same effect as selective water intake, and it is also highly effective as a selective water intake device for existing dams.

ところで、このような濁水防止フエンスにかか
る圧力は、静水圧、流動圧、波浪圧の3種に分類
して考えることができるが、このうち強風時に発
生する波浪圧が最も大きくフエンスの強度によつ
ては破壊する虞れもある。それに対処するために
は、浮き20の中心部にユニバーサルジヨイント
により連結された軸芯を通し、それを湖岸からの
動力または浮き部に取り付けた動力等により回転
してシートを巻き上げれるようにするのが望まし
い。このような巻き上げ装置を付加することによ
つて上記の開口部の深度位置の調節も可能とな
る。その場合は、浮き20をジヨイント毎に分離
すると同時に薬液注入パイプ28への送液パイプ
33の水平部分はボールジヨイント等を使用する
必要があり、垂直部分には巻き込み可能な可撓性
チユーブを用いる。
By the way, the pressure exerted on such a muddy water prevention fence can be classified into three types: hydrostatic pressure, flow pressure, and wave pressure. Of these, the wave pressure generated during strong winds is the largest and depends on the strength of the fence. There is also a risk of destruction. In order to deal with this, a shaft core connected by a universal joint is passed through the center of the float 20, and it is rotated by power from the lake shore or power attached to the float, so that the sheet can be hoisted up. is desirable. By adding such a winding device, it is also possible to adjust the depth position of the opening. In that case, it is necessary to separate the float 20 into joints, and at the same time use a ball joint or the like for the horizontal part of the liquid sending pipe 33 to the chemical injection pipe 28, and use a flexible tube that can be rolled up in the vertical part. use

第6図は本発明で用いられる汚濁防止フエンス
の他の例を示すものである。なお、図面を判り易
くするため沈澱促進剤の放散手段は描かれていな
いが、実際には第3図のように取り付けられてい
る。この実施例では開口部26を有する2枚のシ
ート24,44が近接して配置され、それらの一
方もしくは両方を鉛直方向に相対的に移動するこ
とによつて湖水の流れの状況に応じて開口部26
の面積を自由に調節できる。
FIG. 6 shows another example of the pollution prevention fence used in the present invention. Although the means for dispersing the precipitation accelerator is not shown in order to make the drawing easier to understand, it is actually installed as shown in FIG. In this embodiment, two sheets 24, 44 each having an opening 26 are arranged close to each other, and by moving one or both of them relative to each other in the vertical direction, the opening can be adjusted according to the flow of lake water. Part 26
The area can be adjusted freely.

これは放流水量に合わせて沈澱促進剤の最適な
混合状況を得るために工夫されたものであり、先
に述べた巻き上げ装置により行われる。
This was devised to obtain the optimum mixing condition of the precipitation accelerator in accordance with the amount of discharged water, and is carried out by the above-mentioned hoisting device.

上記実施例ではシート状物を両岸間に張設し湖
岸とダムとを利用してダム取水口または放水口を
取り囲んでいるが、本発明にはシート状物のみに
よつて取り囲む実施態様も含まれる。特に後者の
ような構成とすると、ダム湖の水位が変化しても
シート状物の上縁はそれに追従して上下し、シー
ト状物を適切な位置で保持するのが容易となる点
で有利である。
In the above embodiment, a sheet-like material is stretched between both banks and the dam water intake or water outlet is surrounded using the lake shore and the dam, but the present invention also includes an embodiment in which the dam water intake or water outlet is surrounded by only the sheet-like material. included. In particular, the latter configuration is advantageous in that even if the water level of the dam lake changes, the upper edge of the sheet will move up and down to follow it, making it easier to hold the sheet at an appropriate position. It is.

〔発明の効果〕〔Effect of the invention〕

本発明によれば、ダム湖の流れをシート状物に
よつて規制し開口部近傍に局所的に急流、カルマ
ン渦を形成して、該開口部から沈澱促進剤を拡散
するように構成しているので、沈澱促進剤と濁水
との混合撹拌効果が極めて高くなり、そのため濁
質粒子の会合が促進され速やかに湖底に沈澱させ
ることが可能となり、放流水を少量の沈澱促進剤
によつて経済的に浄化することが可能となる。
According to the present invention, the flow of the dam lake is regulated by the sheet-like material to locally form a rapid current or Karman vortex near the opening, and the sedimentation accelerator is diffused from the opening. As a result, the effect of mixing and agitating the sedimentation accelerator and turbid water is extremely high, which promotes the association of turbid particles and allows them to quickly settle on the lake bottom. It becomes possible to purify it.

また本発明によれば、沈澱促進剤の放散手段付
きの濁水防止フエンスを垂設するだけだから、設
備的には他の方法に比して極めて簡単であり、既
設のダム湖にも対応できるし、また使用する沈澱
促進剤の量もダム湖全体に分散する場合に比べて
はるかに少なくてよく、下流に汚水が流下すると
きのみ、その濁水を放流量だけ処理することが可
能となり、極めて経済的である。
In addition, according to the present invention, since a turbid water prevention fence with means for dispersing sedimentation accelerator is simply installed vertically, the equipment is extremely simple compared to other methods, and it can be applied to existing dam lakes. In addition, the amount of sedimentation accelerator used is much smaller than when it is dispersed throughout the dam lake, making it possible to treat only the amount of turbid water discharged when the sewage flows downstream, making it extremely economical. It is true.

更にシート状物を巻き上げたり巻き下ろしたり
して水平開口部の位置を調節すれば選択取水の効
果が生じるから、たとえ選択取水機構を備えてい
ないダム湖であつても小規模洪水時の濁水防止を
より一層確実に行えるという効果がある。その
他、水道取水されているような場合、濁質粒子が
ダム湖内に沈降することになるので、取水後に処
理する場合に必要な汚泥処理施設が不要となる利
点もある。
Furthermore, by adjusting the position of the horizontal opening by rolling up or unrolling the sheet material, selective water intake can be achieved, so even in dam lakes that do not have a selective water intake mechanism, it is possible to prevent turbid water during small-scale floods. This has the effect of making it even more reliable. Another advantage is that when tap water is being taken in, turbid particles will settle in the dam lake, eliminating the need for a sludge treatment facility that would be required to treat the water after it is taken.

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

第1図は本発明に係るダム湖の浄化方法を示す
平面図、第2図はその断面図、第3図は本発明方
法で用いるに好適な濁水防止フエンスの一例を示
す説明図、第4図はその動作説明図、第5図は濁
水防止フエンスの選択取水機能を示す説明図、第
6図は濁水防止フエンスの他の例を示す説明図で
ある。 10…ダム湖、12…河川、14…ダム、16
…取水口、18…濁水防止フエンス、20…浮
き、22…重り、24,44…シート、28…薬
液注入パイプ、30…ノズル。
FIG. 1 is a plan view showing the dam lake purification method according to the present invention, FIG. 2 is a sectional view thereof, FIG. 3 is an explanatory diagram showing an example of a muddy water prevention fence suitable for use in the method of the present invention, and FIG. FIG. 5 is an explanatory diagram showing the selective water intake function of the muddy water prevention fence. FIG. 6 is an explanatory diagram showing another example of the muddy water prevention fence. 10...dam lake, 12...river, 14...dam, 16
... Water intake, 18 ... Muddy water prevention fence, 20 ... Float, 22 ... Weight, 24, 44 ... Sheet, 28 ... Chemical injection pipe, 30 ... Nozzle.

Claims (1)

【特許請求の範囲】 1 水の流過部が形成されるようにシート状物を
水中に垂設し、該シート状物の近傍から沈澱促進
剤を放散して濁質粒子を沈澱させる濁水浄化方法
において、湖水の流れを規制する前記シート状物
は水平方向に延びる開口部を備え、ダム湖の取水
口または放水口を囲むように取水または放水レベ
ルよりも上方から温度躍層下まで垂設され、沈澱
促進剤は前記開口部に沿つて水平方向に配設され
ている放散手段から湖水中に放散されるようにし
たことを特徴とするダム濁水の浄化方法。 2 開口部を備えたシート状物が2枚近接して設
けられ、両者間の相対的な面方向移動によつて開
口面積を調節自在とした特許請求の範囲第1項記
載の方法。 3 シート状物はダム湖の取水口または放水口の
上流側でダム湖の両岸間に張設され、湖岸および
ダムとともに取水口または放水口を取り囲む特許
請求の範囲第1項または第2項記載の方法。 4 シート状物はそれ単独でダム湖の取水口また
は放水口を取り囲むように浮設される特許請求の
範囲第1項または第2項記載の方法。
[Claims] 1. Turbid water purification in which a sheet-like material is suspended in water to form a water flow area, and a sedimentation accelerator is dispersed from the vicinity of the sheet-like material to precipitate turbid particles. In the method, the sheet-like material regulating the flow of lake water has an opening extending in the horizontal direction, and is vertically installed from above the water intake or water discharge level to below the thermocline so as to surround the water intake or water outlet of the dam lake. A method for purifying turbid water in a dam, characterized in that the sedimentation accelerator is dispersed into lake water from a dispersion means disposed horizontally along the opening. 2. The method according to claim 1, wherein two sheet-like materials each having an opening are provided adjacent to each other, and the opening area can be adjusted by relative surface movement between the two. 3. The sheet-like material is stretched between both banks of the dam lake on the upstream side of the water intake or water outlet of the dam lake, and surrounds the water intake or water outlet together with the lakeshore and the dam as claimed in claim 1 or 2. Method described. 4. The method according to claim 1 or 2, wherein the sheet-like material is floated by itself so as to surround the water intake or water outlet of the dam lake.
JP27882584A 1984-12-26 1984-12-26 Cleaning method of turbid water in dam Granted JPS61155508A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27882584A JPS61155508A (en) 1984-12-26 1984-12-26 Cleaning method of turbid water in dam

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP27882584A JPS61155508A (en) 1984-12-26 1984-12-26 Cleaning method of turbid water in dam

Publications (2)

Publication Number Publication Date
JPS61155508A JPS61155508A (en) 1986-07-15
JPH0481002B2 true JPH0481002B2 (en) 1992-12-22

Family

ID=17602676

Family Applications (1)

Application Number Title Priority Date Filing Date
JP27882584A Granted JPS61155508A (en) 1984-12-26 1984-12-26 Cleaning method of turbid water in dam

Country Status (1)

Country Link
JP (1) JPS61155508A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4589613B2 (en) * 2003-10-14 2010-12-01 興治 菅野 Dam inflow polluted water control equipment and dam inflow polluted water control method
JP4861203B2 (en) * 2007-01-18 2012-01-25 株式会社四電技術コンサルタント Method for evaluating the location of a fence for muddy water countermeasures and method for installing a fence for muddy water countermeasures using the evaluation method
JP4774112B2 (en) * 2009-05-14 2011-09-14 株式会社シビルテック Pollution prevention method and pollution prevention device
JP5400810B2 (en) * 2011-01-14 2014-01-29 海和テック株式会社 Fence for preventing muddy water inflow

Also Published As

Publication number Publication date
JPS61155508A (en) 1986-07-15

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