JPH0613115B2 - Dam turbid water purification device - Google Patents

Dam turbid water purification device

Info

Publication number
JPH0613115B2
JPH0613115B2 JP60150530A JP15053085A JPH0613115B2 JP H0613115 B2 JPH0613115 B2 JP H0613115B2 JP 60150530 A JP60150530 A JP 60150530A JP 15053085 A JP15053085 A JP 15053085A JP H0613115 B2 JPH0613115 B2 JP H0613115B2
Authority
JP
Japan
Prior art keywords
water
fence
dam
intake
lake
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP60150530A
Other languages
Japanese (ja)
Other versions
JPS6211591A (en
Inventor
幸雄 大井
倫 波多野
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
NIPPON SORITSUDO KK
OYO CHISHITSU KK
Original Assignee
NIPPON SORITSUDO KK
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 NIPPON SORITSUDO KK, OYO CHISHITSU KK filed Critical NIPPON SORITSUDO KK
Priority to JP60150530A priority Critical patent/JPH0613115B2/en
Publication of JPS6211591A publication Critical patent/JPS6211591A/en
Publication of JPH0613115B2 publication Critical patent/JPH0613115B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、洪水やダム湖底の洗掘、ダム湖岸の波食、富
栄養化現象等によって生じるダム湖内の濁りを浄化処理
する装置に関する。
TECHNICAL FIELD The present invention relates to a device for purifying turbidity in a dam lake caused by flooding, scouring of the bottom of a dam lake, wave erosion of a dam lake shore, eutrophication phenomenon, and the like. .

[従来の技術] 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もとの清流に復する。しかし一度
ダムが構築されると、粘土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、貯水がダ
ム湖から流出するまでの期間内に沈降せず、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。
[Prior Art] Since rivers in Japan are often short and rapid, turbidity due to floods, etc. will flow back to the original clear stream within a few days. However, once the dam is constructed, sedimentation of clay minerals and other fine particles of a few microns or less is extremely slow to settle, so the sediment does not settle within the period until the reservoir flows out of the dam lake, and the flow rate is It is inevitable that the turbidity of the river is prolonged because it is controlled and released.

また渇水期にダムの水位が降下するとバックウオータ部
の堆砂、堆泥が水面上に露出し、未固結の泥土が河川水
によってダム湖内に持ち込まれ濁水が発生する。更には
ダム湖に流入する畜産、工場、生活排水中に含まれる栄
養塩が湖内の生物活動を盛んにし、濁りや異臭を発生し
水質を悪化させる富栄養化現象も生じる。
When the water level of the dam drops during the dry season, sediment and mud in the backwater area are exposed on the water surface, and unconsolidated mud is brought into the dam lake by the river water and turbid water is generated. In addition, nutrients contained in livestock, factories, and domestic wastewater that flow into the dam lake activate biological activities in the lake, which causes turbidity and offensive odors, resulting in eutrophication that deteriorates water quality.

このような様々な原因によって生じるダム濁水は、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等に大きな経済
的影響を与える。
Dam turbid water caused by such various causes has a great economic impact on environments such as river landscapes and freshwater fisheries, as well as agriculture, domestic water, or industrial use that uses the water.

しかし全てのダムが濁水現象を起こす訳ではなく、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以上では洪水
による濁水の問題は生じないとされている。この指数α
はダム湖が成層(温度躍層)型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って成形されるもので、この時
期に洪水等により濁水が流入すると、その温度は一般に
湖面水よりも低くか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、濁水はこの位置に潜り込む形で
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難くなり濁質の沈降が妨げられる。
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, which depends on the topography, geology, natural environment such as vegetation, social environment such as development activities, and the nature of the surface of the catchment area, and also depends on the scale of the dam. Empirically, the annual index of the number of dam lake water exchanges α
If (= total annual inflow / total reservoir capacity) is 30 or more, it is said that the problem of turbid water due to flooding will not occur. This index α
Is also an index of whether the dam lake is stratified (thermocline) type. If α is small (especially 10 or less), it becomes a stratified dam lake. The thermocline is formed when the surface temperature of the lake rises and the density of the water decreases in the summer, and when turbid water flows in during this period, the temperature is generally lower than that of the surface water and The density of the turbid water is almost equal to that of the stratocline, and turbid water flows into the lake in such a form that it sunk into this position. When turbid water enters such a stable stratification, it becomes difficult to dilute and diffuse, and sedimentation of suspended matter is prevented.
If it is a dam that draws water from the position of this layer, turbid water will be prolonged 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き部分を避け、出来るだけ
湖内を攪拌しないように取水する方法である。
The selective water intake method is one of the measures against turbid water in dam lakes. This is a method of adjusting the water intake level to avoid high turbidity and to avoid water agitation in the lake as much as possible.

その他、集水域の植生によってダム濁水の発生を防止す
る方法や、ダム湖全体に沈澱促進剤を混入する方法、あ
るいは上流に副ダムを造り洪水時の濁水をそれに一旦貯
留し、水量を調節して下流にトンネルで放流する方法、
堆砂を浚渫する方法等も考えられている。
In addition, methods to prevent the generation of dam turbid water by vegetation in the catchment area, methods of mixing sedimentation accelerators throughout the dam lake, or building a secondary dam upstream to temporarily store the turbid water during floods and adjust the water volume And then releasing it in a tunnel downstream,
Methods such as dredging sediment are also being considered.

[発明が解決しようとする問題点] 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いし、
要求される清浄化の程度が高く選択取水では対応しきれ
ない場合も多く、抜本的な解決法とはなり得ない。また
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
なってしまうため選択取水の効果はなくなってしまう。
[Problems to be solved by the invention] Although the selective water intake method is the most effective turbid water prevention measure at the present time, it may be difficult to change the equipment of an existing dam because the intake has to be mechanically moved up and down. Many,
In many cases, the required degree of cleaning is too high to be handled by selective water intake, and it cannot be a drastic solution. If the scale of flood increases, the entire upper part of the thermocline becomes muddy water, and the effect of selective water intake will be lost.

植生による防御や砂防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
国においては山地が急峻なため山地への対策で濁質を完
全に抑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
なく混合攪拌が不可能だから高価は少なく。上流に副ダ
ムを造る方法は大土木工事となり経済的に不利であるば
かりでなく副ダムが造れない地形では実施出来ない。
Although the protection by vegetation and the installation of erosion control facilities are effective to some extent, it is not possible in the case of landslides or collapses, and since the mountains are steep in Japan, it is not possible to completely suppress turbidity by taking measures against them. There are many difficult aspects. In addition, if the precipitation accelerator is mixed in the whole lake water, it is not only very expensive, but also expensive because the mixing and stirring is impossible. The method of constructing the secondary dam upstream is not only economically disadvantageous because it requires large civil engineering work, but also cannot be implemented in the terrain where the secondary dam cannot be constructed.

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, the conventional techniques have various problems to be solved, and at present, no measures other than the selective water intake method are taken.

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って濁水が生じた時に放流水
のみを効率よく浄化できる経済的な装置を提供すること
にある。
An object of the present invention is to solve the above-mentioned drawbacks of the prior art and to provide an economical apparatus capable of efficiently purifying only discharge water when turbid water is generated by a relatively simple facility.

[問題点を解決するための手段] 上記のような目的を達成することのできる本発明は、上
縁に浮きを、下部に錘を取り付けて、ダムの取水口また
は放水口を囲むように水面から水中に垂設した不透水性
のフェンスと、上縁に浮きを、下部に錘を取り付けて樋
状に保形し、該不透水性のフェンスの水面直下で切り欠
いた開口部を通るように延設した導水路と、該導水路の
先端寄りの底部に設置した気泡発生装置と、前記取水口
または放水口と前記不透水性フェンスとの間で、該取水
口または放水口を囲むように位置し、上縁に浮きを、下
部に錘を取り付けて水面から水中に垂設した透水性のフ
ェンスを有する構成である。
[Means for Solving the Problems] In the present invention that can achieve the above-mentioned object, a float is attached to the upper edge and a weight is attached to the lower portion so as to surround a water intake or a water outlet of a dam. Impermeable fence that hangs in water from above, and float on the upper edge, attach a weight to the lower part to keep the shape like a gutter, and pass through the notched opening just below the water surface of the impermeable fence. The water conduit extending to the bottom, an air bubble generator installed at the bottom of the water conduit near the tip, and the water intake or water discharge port and the impermeable fence so as to surround the water intake or water discharge port. It is a structure having a water-permeable fence which is located at the upper edge and has a float attached to the upper edge and a weight attached to the lower portion so as to hang vertically from the water surface into the water.

ここで「不透水性のフェンス」とは、水の流れを阻止し
て水流がほぼ導水路のみに集中するように制御するもの
をいい、また「透水性のフェンス」とは、構造的に多数
の開口や隙間等が存在して水がある程度自由に通過しう
るようなものをいう。
Here, the "impermeable fence" refers to one that blocks the flow of water and controls the flow so that the water flow is concentrated almost exclusively in the headrace, and "permeable fence" is structurally numerous. There are openings and gaps in which water can pass through to some extent.

また導水路には薬剤注入手段を配置して各種凝集剤等を
混入できるようにするのが望ましい。
Further, it is desirable to arrange a drug injection means in the water conduit so that various coagulants and the like can be mixed.

2種類のフェンスは取水口等の回りをそれらのみで完全
に取り囲む必要はない。ダム湖の両岸を利用して、前記
取水口等の上流側にそれらフェンスを張り渡す構成も可
能である。本発明において「取水口等を取り囲む」と
は、湖岸やダム等と協働して取り囲む態様をも含んでい
る。
It is not necessary for the two types of fences to completely surround them around the intake and the like. It is also possible to use both sides of the dam lake to stretch the fences upstream of the intake and the like. In the present invention, "surrounding the intake, etc." also includes a mode in which it surrounds in cooperation with a lake shore, a dam, etc.

[作用] 通常ダム湖の流速は毎秒数mm程度と非常に小さいが、前
記不透水性フェンスによってダム湖の流れが規制され導
水路のみに集中するため、該導水路中での流れは局所的
にかなり速くなりカルマン渦が発生し、充分に攪拌され
る。
[Operation] Normally, the flow velocity in a dam lake is very small, about several mm per second, but since the flow of the dam lake is restricted by the impermeable fence and concentrates only in the headrace, the flow in the headrace is local. It becomes considerably faster and a Karman vortex is generated, and it is sufficiently stirred.

気泡発生装置から生じる微細気泡は濁質に付着し、それ
によって濁質は浮上分離する。また同時に凝集剤を添加
すれば、前記攪拌効果によって濁質粒子同士の会合が一
層促進され少量の薬剤で効率よく浄化することが可能と
なる。
The fine bubbles generated from the bubble generating device adhere to the suspended matter, whereby the suspended matter floats and separates. If a coagulant is added at the same time, the agitation effect further promotes the association of the suspended particles with each other, and it becomes possible to efficiently purify with a small amount of the drug.

本発明では湖水全体を浄化の対象とするのではなく、導
水路を通過する濁水のみを処理の対象とするものである
から、処理量が少なく薬剤を使用する場合でも経済的に
非常に有利である。
In the present invention, the entire lake water is not targeted for purification, but only the turbid water that passes through the headrace is targeted for processing. Therefore, it is economically very advantageous even when a small amount of chemical is used and a chemical is used. is there.

不透水性フェンスの囲みの中に設けた網状等の透水性フ
ェンスは、浮上分離した濁質の集積領域を区画する機能
を果たすとともに凝集大粒化した濁質等が取水口等へ流
出するのを防止する機能を果たすほか、透水性フェンス
近傍はスラリーブランケットと呼ばれる濁質濃厚部とな
り水中の微細濁質を吸蔵付着する機能をも果たす。従っ
て透水性フェンスの作用によって、取水口等を取り囲む
フェンス面積を小さくすることができ、各フェンスにか
かる水圧等に対する強度の制約を著しく減少させること
が可能となる。
The mesh-like water-permeable fence provided in the enclosure of the impermeable fence functions to partition the accumulation area of suspended suspended suspended matter, and prevents aggregated suspended suspended matter from flowing out to the intake port. In addition to the function of preventing it, the vicinity of the water-permeable fence also functions as a turbidity concentrated part called a slurry blanket that absorbs and adheres fine suspended matter in water. Therefore, due to the action of the water-permeable fence, it is possible to reduce the area of the fence surrounding the water intake and the like, and it is possible to significantly reduce the restriction of the strength against the water pressure applied to each fence.

[実施例] 第1図は本発明に係るダム濁水浄化装置の一実施例を示
す配置図であり、第2図はその断面図である。ダム湖1
0は河川からの流水をダム12によって堰き止め一旦貯
留するものであり、貯留した水は取水口14から放流さ
れる。
[Embodiment] FIG. 1 is a layout view showing an embodiment of a dam turbid water purification device according to the present invention, and FIG. 2 is a sectional view thereof. Dam lake 1
No. 0 means that the water flowing from the river is dammed by the dam 12 and stored once, and the stored water is discharged from the intake 14.

本発明ではダム湖10の取水口14を囲むように不透水
性のフェンス16が設けられ、該フェンス16と前記取
水口14との間に網状等のフェンス18が設けられる。
不透水性のフェンス16としては、例えば合成樹脂製の
フィルム、不織布、緻密な織布等が用いられる。これら
のフェンス16,18は、上縁に浮き20が、下縁に錘
22が取り付けられ、それらによって水面から温度躍層
Tの下方まで垂設される。不透水性のフェンス16には
複数の開口部24が形成され、該開口部24に樋状の導
水路30が接続される。この不透水性のフェンス16は
湖水の流れを規制し、ほぼ該導水路30のみに集中させ
る機能を果たす。本発明に係る装置はこれらフェンスお
よび導水路30の他、前記導水路30を通る湖水の流れ
に微細気泡を付与する気泡発生装置36を備えている。
In the present invention, a water-impermeable fence 16 is provided so as to surround the intake 14 of the dam lake 10, and a net-like fence 18 is provided between the fence 16 and the intake 14.
As the water-impermeable fence 16, for example, a synthetic resin film, non-woven fabric, dense woven fabric, or the like is used. The fences 16 and 18 have a float 20 attached to the upper edge and a weight 22 attached to the lower edge, and are suspended from the water surface to below the thermocline T by these. A plurality of openings 24 are formed in the water-impermeable fence 16, and a gutter-shaped water conduit 30 is connected to the openings 24. The impermeable fence 16 has a function of restricting the flow of lake water and concentrating it only on the water conduit 30. The apparatus according to the present invention includes, in addition to the fence and the water conduit 30, a bubble generating device 36 for imparting fine bubbles to the flow of lake water passing through the water conduit 30.

不透水性フェンスおよびその開口部に連結される導水路
の詳細を第3図に示す。開口部24はフェンス16の上
端の一部を矩形状に切り欠いたものであり、該開口部2
4から上流側に樋状の導水路30が延設される。この樋
状の導水路30も不透水性シートによって形成され、上
方に浮き20が、下方に錘22が取り付けられて所定の
形を保つように構成される。この導水路30は第1図に
示すように不透水性フェンス16の適宜個所に複数個設
けてよい。
The details of the water-impervious fence and the water conduit connected to the opening are shown in FIG. The opening 24 is formed by cutting out a part of the upper end of the fence 16 in a rectangular shape.
A trough-shaped water conduit 30 is extended from 4 to the upstream side. The trough-shaped water conduit 30 is also formed of a water-impermeable sheet, and the float 20 is attached to the upper portion and the weight 22 is attached to the lower portion to maintain a predetermined shape. As shown in FIG. 1, a plurality of water conduits 30 may be provided at appropriate places on the impermeable fence 16.

本実施例では薬剤注入用のパイプ32を有し浮き20に
沿って配置され、その先端のノズル34は水路30の上
流側端部近傍で開口する。気泡発生装置36は導水路3
0の底部に取り付けられる。導水路30の内部には邪魔
板38を取り付けるのが望ましい。薬液は各薬液注入パ
イプ32を通りノズル34から導水路30内の湖水中に
放散される。気泡発生装置36にはパイプ40を通って
空気混入水が供給され流れに対して微細気泡を発生させ
る。
In this embodiment, a pipe 32 for injecting a drug is provided and is arranged along the float 20, and the nozzle 34 at the tip thereof opens near the upstream end of the water channel 30. The bubble generating device 36 is the headrace 3
It is attached to the bottom of 0. It is desirable to install a baffle 38 inside the water conduit 30. The chemical liquid is diffused into the lake water in the water conduit 30 from the nozzle 34 through each chemical liquid injection pipe 32. Aerated water is supplied to the bubble generator 36 through a pipe 40 to generate fine bubbles in the flow.

次に本発明装置の動作について第4図および第5図によ
り説明する。取水口14の回りにフェンス16が水面か
ら温度躍層Tの下方まで垂設されており、取水口14は
湖底の冷水塊を取り入れないように水面から躍層Tまで
の範囲内で設定されるのが一般的だから、取水レベルの
流れはこのフェンス16で充分規制される。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って受け止められ、流れが阻害され
るからである。従って全て前記導水路34を流過しよう
とするから(矢印A参照)、その部分での流速は局部的
に増加する。
Next, the operation of the device of the present invention will be described with reference to FIGS. A fence 16 is hung around the water intake 14 from the surface of the water to below the thermocline T, and the water intake 14 is set within the range from the water surface to the thermocline T so as not to take in cold water mass at the lake bottom. Since it is general, the flow at the intake level is sufficiently regulated by this fence 16. This is because, if the water is hung vertically below the stratocline T, the water flowing therebelow is caught by the cold water mass having a high density and the flow is obstructed. Therefore, since all of them try to flow through the water conduit 34 (see arrow A), the flow velocity at that portion locally increases.

導水路30は流入する湖水と注入する薬液との混合攪拌
並びに微細気泡の付着を促進する機能を果たす。ノズル
34からは無機系あるいは有機系の凝集剤を供給する。
それによって湖水と微細気泡、凝集剤とが混合攪拌さ
れ、濁質が凝集し気泡が付着するため浮上することにな
る。浮上分離した濁質42は不透水性フェンス16と網
状フェンス18との間の領域に集まる。また網状のフェ
ンス18は濁質が取水口14に至らないようにする機能
を果たす。またこの網状のフェンス18近傍は、硅藻や
濁質が付着して濁質濃厚部(スラリーブランケット)を
形成し、一種の濾材のような作用を果たし流過する水の
浄化を促進する。
The water conduit 30 has a function of promoting mixing and stirring of the inflowing lake water and the chemical solution to be injected and adhesion of fine bubbles. An inorganic or organic flocculant is supplied from the nozzle 34.
As a result, the lake water, the fine air bubbles, and the coagulant are mixed and stirred, and the suspended matter aggregates and the air bubbles adhere to the surface to float. The suspended suspended matter 42 collects in the area between the impermeable fence 16 and the mesh fence 18. In addition, the mesh fence 18 serves to prevent suspended matter from reaching the water intake port 14. In the vicinity of the mesh fence 18, diatoms and suspended matter adhere to form a suspended matter concentrated portion (slurry blanket), which acts as a kind of filter medium and promotes purification of flowing water.

上記実施例のように導水路に邪魔板等を取り付ければ、
湖水の攪拌距離が長くなり、浮上分離の効果を充分高め
ることが出来ると共に両フェンスの間隔を短くでき装置
を小型化できる点で有利である。上記実施例では透水性
フェンスとして網状フェンスを用いているが、そに代え
て多数の穴が穿設されたフェンスや簾状あるいは暖簾状
のフェンス等を用いてもよい。勿論フェンスは湖底に至
るまで設けてもよい。またダム湖の両湖岸間にこのよう
なフェンスを張設することによって取水口等の一部を取
り囲むような構成としてもよい。両フェンスはそれぞれ
多重構造とすることも可能である。流れの量を制御する
ためには開口部の大きさを可変出来るような機構を付与
したり、あるいは導水路を開閉自在の構造としてもよ
い。
If a baffle plate etc. is attached to the water conduit as in the above embodiment,
This is advantageous in that the stirring distance of the lake water becomes long, the effect of floating separation can be sufficiently enhanced, the interval between both fences can be shortened, and the device can be downsized. Although a mesh fence is used as the water-permeable fence in the above-mentioned embodiments, a fence having a large number of holes, a fence-shaped fence, or a fence-shaped fence may be used instead. Of course, a fence may be provided up to the bottom of the lake. Further, by constructing such a fence between the two shores of the dam lake, a part such as the intake may be surrounded. Both fences can also have multiple structures. In order to control the amount of flow, a mechanism that can change the size of the opening may be provided, or the water conduit may be opened and closed.

なお上記実施例では導水路を不透水性のフェンスよりも
上流側に設けている。そのようにすると不透水性フェン
スで囲む面積を少なくできる利点がある。しかし、導水
路を不透水性フェンスの下流側に設けてもよい。そうす
れば導水路を所定の形状に保っておくのが容易となる利
点が生じる。勿論、不透水性のフェンスの上流側および
下流側に設置することも自由である。
In the above embodiment, the water conduit is provided upstream of the water impermeable fence. This has the advantage that the area enclosed by the impermeable fence can be reduced. However, the water conduit may be provided on the downstream side of the impermeable fence. Then, there is an advantage that it is easy to keep the headrace in a predetermined shape. Of course, it is also free to install it on the upstream side and the downstream side of the impermeable fence.

ところでこのようなフェンスにかかる圧力は、静水圧、
流動圧、波浪圧の3種類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い。そ
れに対処するためには、湖岸からの動力または浮きに取
り付けた動力等によりフェンスを巻き上げれるような構
造とするのが望ましい。
By the way, the pressure applied to such a fence is the hydrostatic pressure,
It can be considered by classifying into three types of fluid pressure and wave pressure, but the wave pressure generated during strong wind is the largest. In order to deal with this, it is desirable to have a structure in which the fence can be rolled up by the power from the lake shore or the power attached to the float.

[発明の効果] 本発明によればダム湖の流れをフェンスによって規制し
導水路によって局部的に急流を形成して微細気泡を付着
させるように構成しているので、濁水の攪拌が効率良く
行われ微細気泡の付着により濁質浮上が促進されるとい
う優れた効果を奏する。浮上した濁質は透水性フェンス
と不透水性フェンスとの狭い区域に集積するため、その
除去は極めて容易となる。
EFFECTS OF THE INVENTION According to the present invention, the flow of the dam lake is regulated by the fence and the rapid flow is locally formed by the water conduit to adhere the fine bubbles, so that the muddy water can be efficiently stirred. The excellent effect that floating of suspended matter is promoted by the adhesion of fine bubbles is exhibited. Since the suspended turbidity accumulates in a narrow area between the water-permeable fence and the water-impermeable fence, the removal thereof is extremely easy.

また本発明では取水口等を取り囲む構造であるから、取
水量だけを対象に処理し攪拌して分離することになり、
ダム湖全体の水量を処理対象とするのと異なり薬剤を使
用する場合でも、その使用量を大幅に節約できるし、殆
ど静止状態にあるダム湖内に全く動力を用いることなく
攪拌流をつくることができ、しかも濁水状態が悪化した
ときのみ運転操作すればよいから運転コストも安くなり
極めて経済的である。
Further, in the present invention, since it is a structure that surrounds the water intake, etc., it will be treated only for the amount of water intake and stirred to separate,
Even when a chemical is used unlike the case where the water volume of the entire dam lake is treated, the amount of the chemical used can be greatly saved, and a stirring flow can be created in the dam lake that is almost stationary without using any power. In addition, since the operation can be performed only when the muddy water state deteriorates, the operating cost is low and it is extremely economical.

更に本発明は比較的簡単な構成であるから、設置や保守
が容易であり既設ダムへも容易に適用できる等の優れた
効果を有する。
Further, since the present invention has a relatively simple structure, it has an excellent effect that it can be easily installed and maintained and can be easily applied to an existing dam.

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

第1図は本発明に係るダム濁水浄化装置の一実施例を示
す配置図、第2図はその断面図、第3図は不透水性フェ
ンスとそれに連結された水路の一例を示す説明図、第4
図および第5図は本発明に係る装置の動作説明図であ
る。 10……ダム湖、12……ダム、14……取水口、16
……不透水性フェンス、18……網状フェンス、24…
…開口部、30……導水路、36……気泡発生装置。
FIG. 1 is a layout drawing showing an embodiment of a dam turbid water purification apparatus according to the present invention, FIG. 2 is a sectional view thereof, and FIG. 3 is an explanatory view showing an example of an impermeable fence and a water channel connected to it. Fourth
FIG. 5 and FIG. 5 are operation explanatory views of the device according to the present invention. 10 ... Dam lake, 12 ... Dam, 14 ... Intake port, 16
…… Impermeable fence, 18 …… net fence, 24…
… Opening part, 30 …… water conduit, 36 …… bubble generator.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】上縁に浮きを、下部に錘を取り付けて、ダ
ムの取水口または放水口を囲むように水面から水中に垂
設した不透水性のフェンスと、上縁に浮きを、下部に錘
を取り付けて樋状に保形し、該不透水性のフェンスの水
面直下で切り欠いた開口部を通るように延設した導水路
と、該導水路の上流側の底部に設置した気泡発生装置
と、前記取水口または放水口と前記不透水性フェンスと
の間で、該取水口または放水口を囲むように位置し、上
縁に浮きを、下部に錘を取り付けて水面から水中に垂設
した透水性のフェンスを有することを特徴とするダム濁
水の浄化装置。
1. An impermeable fence vertically suspended from the water surface so as to surround a dam intake or discharge port with a float attached to the upper edge and a weight attached to the lower portion, and a float attached to the lower edge. A weight is attached to the gutter to maintain the shape like a gutter, and a water conduit extending so as to pass through an opening cut out just below the water surface of the impermeable fence, and bubbles installed on the upstream side bottom of the water conduit. It is located between the generator and the water intake or water discharge port and the impermeable fence so as to surround the water intake or water discharge port. A device for purifying dam turbid water, which has a vertically permeable fence.
JP60150530A 1985-07-09 1985-07-09 Dam turbid water purification device Expired - Fee Related JPH0613115B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60150530A JPH0613115B2 (en) 1985-07-09 1985-07-09 Dam turbid water purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60150530A JPH0613115B2 (en) 1985-07-09 1985-07-09 Dam turbid water purification device

Publications (2)

Publication Number Publication Date
JPS6211591A JPS6211591A (en) 1987-01-20
JPH0613115B2 true JPH0613115B2 (en) 1994-02-23

Family

ID=15498886

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60150530A Expired - Fee Related JPH0613115B2 (en) 1985-07-09 1985-07-09 Dam turbid water purification device

Country Status (1)

Country Link
JP (1) JPH0613115B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0694030B2 (en) * 1989-12-06 1994-11-24 五洋建設株式会社 Aoko processing and recovery device
JP2012117241A (en) * 2010-11-30 2012-06-21 Nippon Solid Co Ltd Processing method of polluted water
JP6035135B2 (en) * 2012-12-13 2016-11-30 前田建設工業株式会社 Turbid water treatment method

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0698246B2 (en) * 1985-06-11 1994-12-07 応用地質株式会社 Dam turbid water purification device

Also Published As

Publication number Publication date
JPS6211591A (en) 1987-01-20

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