JPH0435562B2 - - Google Patents

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Publication number
JPH0435562B2
JPH0435562B2 JP1167346A JP16734689A JPH0435562B2 JP H0435562 B2 JPH0435562 B2 JP H0435562B2 JP 1167346 A JP1167346 A JP 1167346A JP 16734689 A JP16734689 A JP 16734689A JP H0435562 B2 JPH0435562 B2 JP H0435562B2
Authority
JP
Japan
Prior art keywords
gravel
water
gravel layer
soil particles
river
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
JP1167346A
Other languages
Japanese (ja)
Other versions
JPH0333313A (en
Inventor
Setsuo Yamanoi
Hideaki Takahashi
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.)
Kawasaki Steel Metal Products and Engineering Inc
Original Assignee
Kawasaki Steel Metal Products and Engineering Inc
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 Kawasaki Steel Metal Products and Engineering Inc filed Critical Kawasaki Steel Metal Products and Engineering Inc
Priority to JP16734689A priority Critical patent/JPH0333313A/en
Publication of JPH0333313A publication Critical patent/JPH0333313A/en
Publication of JPH0435562B2 publication Critical patent/JPH0435562B2/ja
Granted legal-status Critical Current

Links

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は河水に含まれる土粒子のフイルター方
法に係り、詳しくは、微細で軽いシルトや粘土分
を含む流水を礫層内へ導き、その間に、土粒子な
どを分離するようにした流水のフイルター方法に
関するものである。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a method for filtering soil particles contained in river water. The invention also relates to a method of filtering running water to separate soil particles and the like.

〔従来の技術〕[Conventional technology]

河川の流水中に浮遊する土粒子を除去するため
に、古くから、上流側に沈砂池を設け、そこで予
め分離する方法がとられている。沈砂池では、粒
径が大きく重い砂や土粒子などが沈降して除去さ
れるが、微細で軽い土粒子、すなわち、例えば
100μm以下のシルトや粘土は、沈下しにくい傾向
にある。除去されなかつたシルトなどは、流水を
濁らせ、そのまま河川を下ることになる。一方、
降雨が異常に多くなる洪水期では、沈砂池に沈降
していた砂などの土粒子が、乱流化した流水のた
めに、再度、流水中に浮遊して流れ去ることも多
い。
In order to remove soil particles floating in flowing water of a river, a method has been used since ancient times to install a settling pond on the upstream side and separate the particles in advance. In the settling basin, large and heavy sand and soil particles are settled and removed, but fine and light soil particles, e.g.
Silt and clay with a diameter of 100 μm or less tend to be difficult to settle. Silt and other debris that is not removed will muddy the water and flow down the river. on the other hand,
During flood seasons when rainfall is abnormally high, sand and other soil particles that have settled in settling basins often become suspended in the flowing water and flow away due to the turbulent flow of water.

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

河川の濁つた水がそのまま海に流れ込むと、観
光地や海水浴場の水が汚染され、観光客の誘致に
支障をきたし、地元民に経済的なダメージを与え
る問題がある。また、海中に漂うシルトなどが
徐々に沈降すると、海底の礫層などで目詰まりが
生じる。それによつて、海草が枯死し、ひいて
は、アワビなどの海中生息物も死滅するいわゆる
磯枯れを引き起こす。もちろん、珊瑚礁があれ
ば、その生息環境も悪化し、自然破壊を招くこと
になる。
If murky water from rivers flows directly into the sea, the water at tourist spots and beaches will be contaminated, hindering the ability to attract tourists, and causing economic damage to local residents. In addition, as silt floating in the ocean gradually settles, it can clog the gravel layer on the ocean floor. This causes the seaweed to wither and, by extension, abalone and other underwater creatures to die, causing so-called rockfish blight. Of course, if coral reefs exist, their habitat will deteriorate, leading to the destruction of nature.

一方、従来から行われている河水に含まれる土
粒子をフイルターする方法として、砂防ダムがあ
る。砂防ダムは一般に堆砂と称されるが、土粒子
が小さい場合や混入土砂量が多い場合には、フイ
ルター効果が得られず、通常は、沈砂池と併用さ
れる。しかし、流水中の濁りの主成分をなすシル
トおよび粘土は、沈砂池を通過しても、その大部
分は沈降時間が非常に長く、除去できない問題が
ある。
On the other hand, erosion control dams are a conventional method of filtering soil particles contained in river water. Sabo dams are generally referred to as sediment control dams, but if the soil particles are small or the amount of soil mixed in is large, a filter effect cannot be obtained, so they are usually used in conjunction with a settling basin. However, there is a problem in that most of the silt and clay, which are the main components of turbidity in running water, cannot be removed even if they pass through a settling basin because most of them take a very long time to settle.

本発明は上述の問題に鑑みなされたもので、そ
の目的は、河川をたどつて海に流入する河水か
ら、シルトや粘土などを、河川を流れる間に除去
したり、沈砂させることができるようにして、海
浜や海水の汚染、磯枯れなどの自然破壊を防止す
ることができるフイルター方法を提供することで
ある。
The present invention was made in view of the above-mentioned problems, and its purpose is to remove silt, clay, etc. from river water that follows the river and flow into the sea, and to make it possible to settle it. To provide a filter method that can prevent natural destruction such as pollution of beaches and seawater and drying up of rocky shores.

ちなみに、本発明は、例えば容器に礫や砂を充
填しておき、上方から入れられた濁水を浄化する
という伝統的な浄化技術をもとに、それを河川に
おける流水に適用することができるように発展さ
せたものである。それによつて、大量の土砂が混
入した流水をフイルターすることができ、その濁
り成分も除去し、洪水時においても、濁り成分の
再流出を抑制できるようにすることである。
Incidentally, the present invention is based on the traditional purification technology of filling a container with gravel or sand and purifying the turbid water poured in from above, so that it can be applied to flowing water in rivers. It was developed into Thereby, it is possible to filter running water mixed with a large amount of earth and sand, and also remove the turbid components, thereby suppressing the re-flow of the turbid components even during a flood.

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

本発明の河水に含まれる土粒子のフイルター方
法の特徴とするところは、第1図に示すように、
河川1内に通常の水位hより高い礫層3を構築
し、その礫層3の形状安定を図る堰を透過壁5に
より形成して、これを礫層3の下流側3bに設
け、流水2が礫層3内を流過する間に、流水2中
の土粒子を分離させ、礫層3内が目詰まりする
と、礫4と捕捉された土粒子18とを除去して、
新しい礫4に置き換えるようにしたことである。
The features of the method of filtering soil particles contained in river water according to the present invention are as shown in Fig. 1.
A gravel layer 3 higher than the normal water level h is constructed in the river 1, a weir is formed with a permeable wall 5 to stabilize the shape of the gravel layer 3, and this is installed on the downstream side 3b of the gravel layer 3, and the flowing water 2 While flowing through the gravel layer 3, the soil particles in the flowing water 2 are separated, and when the gravel layer 3 becomes clogged, the gravel 4 and the trapped soil particles 18 are removed.
This was done by replacing it with new gravel 4.

第2図に示すように、透過壁5Aを礫層3の上
流側3aにも設けるようにしてもよい。
As shown in FIG. 2, the permeable wall 5A may also be provided on the upstream side 3a of the gravel layer 3.

第3図および第4図に示すように、礫層3の上
流側3aに、河幅を広くした沈砂池11を設け、
その沈砂池11で粗い土粒子18aが除去された
流水2を、礫層3内へ流過させるようにしてもよ
い。
As shown in FIGS. 3 and 4, a settling pond 11 with a wider river width is provided on the upstream side 3a of the gravel layer 3,
The flowing water 2 from which the coarse soil particles 18a have been removed in the sand settling basin 11 may be allowed to flow into the gravel layer 3.

第5図に示すように、礫層3内に、端面12a
が透水材13でふたをされ、礫4の侵入を阻止し
た管体12を埋設することもできる。
As shown in FIG.
It is also possible to bury a pipe body 12 covered with a water-permeable material 13 to prevent gravel 4 from entering.

また、第6図に示すように、礫層3内へ流水2
を案内する導水管14もしくは溝を、上流側3a
に位置する透過壁5Aを貫通して設け、流れ方向
となつている通路によつて、流水2を礫層3内へ
積極的に誘導するようにしてもよい。
In addition, as shown in Fig. 6, water 2 flows into the gravel layer 3.
The water conduit 14 or groove that guides the upstream side 3a
The flowing water 2 may be actively guided into the gravel layer 3 by a passage provided through the permeable wall 5A located in the flow direction.

第7図に示すように、礫4をパツケージ化し
て、礫4の置き換えを容易にすることもできる。
As shown in FIG. 7, the gravel 4 can be packaged to facilitate replacement of the gravel 4.

以上のいずれの方法においても、礫4〔第1図
参照〕に代えて、第8図に示すように、透水材1
5を採用することもできる。
In any of the above methods, instead of the gravel 4 (see Figure 1), as shown in Figure 8, a water-permeable material 1 is used.
5 can also be adopted.

〔発明の効果〕〔Effect of the invention〕

本発明によれば、河川中に、構築された礫層が
透過壁で形成された堰で、安定な断面形状に保持
される。流水が濁つていても礫層を流過する間
に、流水に含まれる土粒子などが礫層で捕捉され
るので、流水を能率よく大量に浄化して流下させ
ることができる。河川の水が浄化されると、海に
流れ込んだとき、海浜や海水はきれいになり、汚
染物や土粒子などの海底への沈降は回避される。
したがつて、磯枯れや自然破壊が阻止され、自然
環境が保全される。
According to the present invention, a gravel layer constructed in a river is maintained in a stable cross-sectional shape by a weir formed of a permeable wall. Even if the flowing water is turbid, the soil particles contained in the flowing water are captured by the gravel layer while it flows through the gravel layer, so that a large amount of flowing water can be efficiently purified and allowed to flow down. When river water is purified, when it flows into the ocean, beaches and seawater are cleaner, and pollutants and soil particles are prevented from settling on the ocean floor.
Therefore, drying up of the seashore and destruction of nature will be prevented, and the natural environment will be preserved.

一方、土粒子の捕捉で礫層内が目詰まりしたと
き、礫と捕捉された土粒子を除去して新しい礫に
置き換えることができ、礫層による浄化機能を再
生し、永続的な浄化作用が維持される。
On the other hand, when the gravel layer becomes clogged due to trapped soil particles, the gravel and trapped soil particles can be removed and replaced with new gravel, regenerating the purification function of the gravel layer and creating a permanent purification effect. maintained.

礫層の上流側に透過壁が設けられていれば、礫
層は一層安定な形状や姿勢を維持し、その浄化効
果が向上する。
If a permeable wall is provided on the upstream side of the gravel layer, the gravel layer will maintain a more stable shape and posture, and its purification effect will be improved.

礫層の上流側に河幅を広くした沈砂池を設ける
と、沈砂池で流水に含まれる粗い土粒子などが沈
降して予め除去され、主として、シルトや粘土分
などの微細なものだけを、礫層で分離することが
できる。その場合、それらの細かい粒子が能率よ
く除去されるので、礫層から流出する水は、より
一層浄化された清流となる。
If a settling basin with a wider river width is installed upstream of the gravel layer, coarse soil particles contained in the flowing water will settle in the settling basin and be removed in advance, mainly only fine particles such as silt and clay will be removed. It can be separated by a gravel layer. In that case, since those fine particles are efficiently removed, the water flowing out from the gravel layer becomes a clear stream that is even more purified.

礫層中に、礫の侵入を妨げるように端面が透水
材でふたをされた管体を埋設しておけば、礫間で
形成される間隙が増大され、礫層での捕捉機能が
高められる。流水を礫層内に積極的に誘導するよ
うに、上流側の透過壁を貫通して、流れ方向に配
置された導水管や溝を設ける場合にも、礫層の捕
捉効果が増大する。
By burying a tube whose end face is capped with a water-permeable material to prevent gravel from entering into the gravel layer, the gaps formed between the gravels will be increased and the trapping function of the gravel layer will be enhanced. . The trapping effect of the gravel layer is also increased when a water conduit or groove is provided that penetrates the permeable wall on the upstream side and is arranged in the flow direction so as to actively guide the flowing water into the gravel layer.

礫をパツケージ化しておけば、捕捉量が多くな
つた後の置き換えが極めて容易となる利点があ
る。
If the gravel is packaged, it has the advantage of being extremely easy to replace after the amount of trapped gravel increases.

以上の礫に代えて透水材を採用すると、礫層に
よる場合と同様に、土粒子などの除去効果を発揮
させることができる。
If a permeable material is used instead of the gravel described above, it is possible to exhibit the effect of removing soil particles, etc., as in the case of using a gravel layer.

〔実施例〕〔Example〕

以下に、本発明の河水に含まれる土粒子のフイ
ルター方法を、フイルター構層体を含む図面を参
照しながら、詳細に説明する。
Hereinafter, the method of filtering soil particles contained in river water according to the present invention will be explained in detail with reference to the drawings including the filter structure.

第1図に示すように、河川1内の河床1aに
は、流水2の通常水位hより高い礫層3が構築さ
れている。この礫層3は、複数のフイルター材で
ある礫4からなつている。ちなみに、礫4は、採
取された石材を機械加工で砕いた例えば粒径20cm
程度もしくはそれより小さいクラツシヤーランな
どである。礫層3の下流側3bには、コンクリー
ト壁または枠ダムなどの透過壁5が形成され、そ
れによつて、礫層3の断面の形状安定を図るよう
に堰を構成している。本例にあつては、透過壁
は、次に述べる枠ダムとしている。
As shown in FIG. 1, a gravel layer 3 higher than the normal water level h of the flowing water 2 is built on the riverbed 1a of the river 1. This gravel layer 3 is made up of a plurality of gravels 4 which are filter materials. By the way, gravel 4 is made by crushing collected stones by mechanical processing, for example, with a particle size of 20 cm.
degree or smaller than that. A permeable wall 5 such as a concrete wall or a frame dam is formed on the downstream side 3b of the gravel layer 3, thereby forming a weir so as to stabilize the shape of the cross section of the gravel layer 3. In this example, the transparent wall is a frame dam described below.

その枠ダムは、第9図に示すように、例えば形
鋼などで製作された横部材6a、縦部材6bおよ
び前後接続部材6cで構成され、それらが、工場
などで予め部分組み立てされた後、現場に搬入さ
れる。そして、それらの鉄材6が、順次ボルト締
結や溶接〔図示せず〕などによつて枠組体7に組
み上げられる。一方、河床1aや河岸から採取さ
れた現採土砂に、混合比が5〜10%となる量のソ
イルセメントを混入した安価な中詰土砂8が準備
される。透水性のある袋9に中詰土砂8を詰めて
養生させ、内部が固化した土砂袋10を、枠組体
7の内部へ投入する。このようにして形成された
枠ダム5は、流水2を流過させる透水性を備え
る。すなわち、通常、枠組体7の内部に砕石が投
入された透水性のある枠ダムと同じ機能を備えた
堰とされ、この堰5と礫層3とにより、第1図に
示すフイルター構層体16が形成される。なお、
堰をコンクリート壁〔図示せず〕として、その一
部に透水性を有する構造としたものでもよい。
As shown in FIG. 9, the frame dam is composed of a horizontal member 6a, a vertical member 6b, and an anteroposterior connecting member 6c made of, for example, section steel.After these are partially assembled in advance at a factory or the like, Delivered to the site. Then, these iron materials 6 are sequentially assembled into a framework 7 by bolting, welding (not shown), or the like. On the other hand, inexpensive filling soil 8 is prepared by mixing soil cement in an amount of 5 to 10% with the currently excavated sand collected from the riverbed 1a or river bank. A water-permeable bag 9 is filled with packed earth and sand 8 and cured, and the earth and sand bag 10 whose inside is solidified is put into the framework body 7. The frame dam 5 formed in this manner has water permeability that allows the flowing water 2 to flow through. In other words, it is normally a weir with the same function as a permeable frame dam in which crushed stone is placed inside the framework body 7, and the weir 5 and the gravel layer 3 form the filter structure shown in FIG. 16 is formed. In addition,
The weir may be a concrete wall (not shown), with a portion of the wall having water permeability.

第1図に示す河川1の上流側の流水2は濁つて
おり、間隙を有するように礫4が積み上げられて
形成された礫層3内を流過する間に、浮遊する土
粒子分(シルト)などの微細な汚濁原因物が沈降
して分離され、間隙を通過した流水2は浄化され
る。そして、一年近く経過して、礫層3内が目詰
まりすると、礫4と捕捉された土粒子18などと
が除去され、その都度、新しい礫4に置き換えら
れる。したがつて、フイルター構層体16におけ
る浄化機能が保持され、河水が流入する海岸や海
浜の環境破壊が防止されるようになつている。
Flowing water 2 on the upstream side of the river 1 shown in Fig. 1 is turbid, and floating soil particles (silt) flow through the gravel layer 3 formed by piling up gravel 4 with gaps. ), etc., are settled and separated, and the flowing water 2 that has passed through the gap is purified. When the inside of the gravel layer 3 becomes clogged after nearly a year, the gravel 4 and the trapped soil particles 18 are removed and replaced with new gravel 4 each time. Therefore, the purification function of the filter structure 16 is maintained, and environmental destruction of the coast and seashore into which river water flows is prevented.

ちなみに、礫層の前後における流水を採取し、
コールターカウンター法により分析された現地実
証試験の結果を、第10図ないし第12図に示
す。これらのデータから判るように、濁水中に含
まれる土粒子のうち、粒径が1μm〜20μmの土粒
子の70%以上がフイルターされていることが判
る。そして、このフイルター構層体16が用いら
れていると、洪水時に、礫層の間隙で分離し滞留
した土粒子18などの再流出が抑制されること
が、長岡・大垣氏の研究「礫で構成された河床に
おける生物学的自浄作用」からも十分に推測する
ことができる。すなわち、その報告によれば、礫
層中の浸透流は、礫径の大小にかかわらず、表面
から第三層目付近で流速が零に近づく、と述べら
れていることからも、上記のデータの正当性が裏
付けられる。したがつて、径が20cm程度の礫が用
いられた礫層によつても、粒径が1μmといつた小
さな土粒子をフイルターできる沈降時間が確保さ
れること、第三層以深では、洪水による増水があ
つても、滞留した土粒子などが再流出しないこと
になる。
By the way, we collected running water before and after the gravel layer,
The results of the field demonstration tests analyzed using the Coulter counter method are shown in Figures 10 to 12. As can be seen from these data, more than 70% of the soil particles contained in the turbid water, with a particle size of 1 μm to 20 μm, are filtered. When this filter structure 16 is used, the re-outflow of soil particles 18 that have separated and accumulated in the gaps between the gravel layers during floods is suppressed, according to a study by Mr. Nagaoka and Ogaki. This can be fully inferred from the biological self-cleaning effect of the structured river bed. In other words, the report states that the velocity of seepage flow in a gravel layer approaches zero near the third layer from the surface, regardless of the size of the gravel diameter. The validity of this is confirmed. Therefore, even if a gravel layer is made of gravel with a diameter of about 20 cm, it is necessary to ensure that the settling time is sufficient to filter out small soil particles with a particle size of 1 μm. Even if the water rises, the accumulated soil particles will not flow out again.

第2図の例においては、礫層3の下流側3bに
設けられた透過壁5に加えて、礫層3の上流側3
aにも透水性の堰5Aが設置され、二つの透過壁
5,5Aと礫層3とによりフイルター構層体16
が形成されている。本例では、礫層3はやや高層
化されると共に、二つの透過壁5,5Aで礫層3
の形状が保持され、能率よく土粒子18などが除
去され、濁流の浄化が促進される。
In the example of FIG. 2, in addition to the permeable wall 5 provided on the downstream side 3b of the gravel layer 3, the upstream side 3b of the gravel layer 3
A permeable weir 5A is also installed in a, and the filter structure 16 is formed by the two permeable walls 5, 5A and the gravel layer 3.
is formed. In this example, the gravel layer 3 is made a little taller, and the two transparent walls 5 and 5A make the gravel layer 3
shape is maintained, soil particles 18, etc. are efficiently removed, and purification of the turbid stream is promoted.

第3図および第4図の例では、礫層3の上流側
3aすなわち透過壁5Aの上流には、河川1より
河幅が広げられ、さらに、河底11aが深くされ
た沈砂池11が形成されている。その上流から沈
砂池11に流入する濁流は、広い河幅の沈砂池1
1で流速が極めて弱められ、大きい粒径の土粒子
18a、例えば100μm以上のものが除去され、礫
層3においては、効果的な浄化が図られる。すな
わち、礫層3の上流側3aに設置された透過壁5
Aから礫層3に入つた濁流は、礫層3内を流過す
る間に、粒径の小さい例えば100μm以下のシルト
や粘土分18が分離され、清流となつて下流側3
bの透過壁5から流出する。大きい粒径の土粒子
18aなどは沈砂池11で予め分離されるので、
礫層3内の目詰まりが緩和され、礫層3を長持ち
させることができる利点がある。
In the examples shown in FIGS. 3 and 4, a settling pond 11 is formed on the upstream side 3a of the gravel layer 3, that is, upstream of the permeable wall 5A, which is wider than the river 1 and has a deeper river bed 11a. has been done. The turbid flow flowing into the settling basin 11 from the upstream is the wide settling basin 1.
1, the flow rate is extremely weakened, large soil particles 18a, for example, those larger than 100 μm are removed, and the gravel layer 3 is effectively purified. That is, the permeable wall 5 installed on the upstream side 3a of the gravel layer 3
The turbid stream that entered the gravel layer 3 from A separates silt and clay with small particle sizes, e.g., 100 μm or less, while flowing through the gravel layer 3, becoming a clear stream and flowing into the downstream side 3.
It flows out from the permeable wall 5 of b. Since large-sized soil particles 18a and the like are separated in advance in the settling basin 11,
This has the advantage that clogging in the gravel layer 3 is alleviated and the gravel layer 3 can last longer.

ところで、礫間の間隙は、礫層全体積の40%程
度が限界であると言われている。そこで、第5図
に示すように、礫層3の間隙を拡げるために、礫
層3の底部の河床1aに、耐蝕性を有する例えば
50cm程度の長さの塩化ビニール管などを複数〔図
示は四個〕採用し、その管体12を埋没させてお
くとよい。管体12の端面12aは透水マツトで
ある透水材13でふたをされており、管体12内
への礫4の侵入が阻止されるようになつている。
このように、管体12が埋設されたフイルター構
層体16は、土粒子18などを滞留させる間隙が
広く、ひいては、礫層3の単位体積当たりの土粒
子の捕捉容量が増大され、フイルター構層体16
の浄化機能が高められる。
By the way, it is said that the gap between gravels is limited to about 40% of the total area of the gravel layer. Therefore, as shown in FIG. 5, in order to widen the gap in the gravel layer 3, a corrosion-resistant material such as
It is preferable to use a plurality of vinyl chloride pipes (four shown) each having a length of about 50 cm, and bury the pipe body 12 therein. The end surface 12a of the tube body 12 is covered with a water-permeable material 13, which is a water-permeable mat, to prevent gravel 4 from entering the tube body 12.
In this way, the filter structure 16 in which the pipe body 12 is buried has a wide gap for retaining the soil particles 18, etc., and as a result, the capacity for capturing soil particles per unit volume of the gravel layer 3 is increased, and the filter structure Layer 16
Purification function is enhanced.

第6図の例は、礫層3の上流側3aに位置する
透過壁5Aを貫通し、河床1aに設置されて流れ
方向に沿つた複数〔図示は一本〕の導水管14を
設けたものである。この場合には、上流より流れ
込む流水2が礫層3内へ積極的に誘導される。そ
の結果、ほぼ全量の流水2が、フイルター構層体
16を構成する礫層3内で速やかに浄化される。
なお、導水管14に代えて、上流側3aの透過壁
5Aを貫通し、その透過壁5Aから礫層3に至る
河床1aに溝〔図示せず〕を掘削して、通路を形
成したものでもよい。
The example shown in FIG. 6 has a plurality of water pipes 14 (one shown) penetrating the permeable wall 5A located on the upstream side 3a of the gravel layer 3, installed in the river bed 1a, and running along the flow direction. It is. In this case, the running water 2 flowing from upstream is actively guided into the gravel layer 3. As a result, almost all of the flowing water 2 is quickly purified within the gravel layer 3 that constitutes the filter structure 16.
Note that instead of the water conduit 14, a channel may be formed by excavating a groove [not shown] in the riverbed 1a that penetrates the permeable wall 5A on the upstream side 3a and extends from the permeable wall 5A to the gravel layer 3. good.

第7図は、礫層3を構成する一群の礫4を、外
包する不錆鋼の線材で形成された籠体17などで
拘束し、パツケージ化したものを投入した例であ
る。日時経過に伴つて生じる礫層3内の目詰まり
が進行したとき、パツケージ化された一群の礫4
は、クレーン車などで吊り上げたり、吊り降ろし
たりすることが容易であり、一群の礫4を迅速に
置き換えることができる利点がある。なお、籠体
17を用いることなく、一群の礫4を袋〔図示せ
ず〕に詰めてパツケージ化してもよい。袋に砂を
詰めた土嚢としておいてもよいが、その場合、表
面に近い部分に、粒径の大きい礫を配置したり、
透水性のマツトを介装させ、洪水時の流失を防止
することができるようにしておけばよい。
FIG. 7 shows an example in which a group of gravels 4 constituting the gravel layer 3 are restrained by a cage body 17 made of rust-free steel wire, etc., and the gravels 4 are put into a package. When the clogging in the gravel layer 3 that occurs with the passage of time progresses, a group of gravel 4 that is packaged
This has the advantage that it is easy to lift up and lower down using a crane vehicle or the like, and that a group of gravel 4 can be quickly replaced. Note that, without using the cage 17, a group of gravels 4 may be packed into a bag (not shown) to form a package. It is also possible to use a bag filled with sand as a sandbag, but in that case, place large-sized gravel near the surface, or
Water-permeable pine may be interposed to prevent water from being washed away during floods.

以上は礫4〔第1図参照〕を採用した例である
が、第8図に示すように、それに代えて、土粒子
を収容する図示しない間隙を備えると共に透水性
を有する透水マツトなどの透水材15を組み立
て、河床1aに配置しておいても、同様の効果を
発揮させることができる。なお、透水マツトは、
例えば繊維状のものを押し固めるなどして、水を
通過させるが、細かい粒子を間隙で捕捉させるこ
とができるようなものであればよい。
The above is an example in which gravel 4 (see Fig. 1) is used, but as shown in Fig. 8, a water-permeable material such as water-permeable pine, which has gaps (not shown) to accommodate soil particles and has water permeability, can be used instead. The same effect can be achieved even if the materials 15 are assembled and placed on the river bed 1a. In addition, water-permeable pine is
For example, it may be made of a fibrous material that is compacted to allow water to pass through, but any material that allows fine particles to be trapped in the gaps may be used.

ちなみに、礫層3の上流側3aや下流側3bに
堰5,5Aを設け、礫層3の上流に沈砂池11を
形成し、礫層3中に管体12を埋設し、さらに
は、導水管14などを形成すれば、浄化作用は一
段と向上する。
Incidentally, weirs 5 and 5A are provided on the upstream side 3a and downstream side 3b of the gravel layer 3, a settling basin 11 is formed upstream of the gravel layer 3, a pipe body 12 is buried in the gravel layer 3, and If a water pipe 14 or the like is formed, the purification effect will be further improved.

以上の説明から判るように、河川に築かれた礫
層を透過壁で安定に保持させれば、流水が濁つて
いても礫層を流過する間に、浮遊する土粒子など
を礫層で捕捉することができ、大量の流水を能率
よく浄化させることができる。河川が浄化される
と、海に流れ込んだときの汚濁も少なく、海底へ
の沈降も回避される。したがつて、磯枯れや自然
破壊が防止され、自然環境の保全が実現できる。
As can be seen from the above explanation, if the gravel layer built in a river is stably held by a permeable wall, floating soil particles will be removed from the gravel layer while flowing water flows through the gravel layer even if the water is turbid. It is possible to efficiently purify large amounts of running water. When rivers are purified, there is less pollution when they flow into the ocean, and sedimentation to the ocean floor is also avoided. Therefore, drying up of the seashore and destruction of nature can be prevented, and conservation of the natural environment can be achieved.

一方、土粒子の捕捉で礫層内が目詰まりして
も、礫と捕捉された土粒子を除去して新しい礫に
置き換えれば、礫層の浄化機能を再生し、永続的
な浄化が図られる。礫層の上流側にも透過壁を設
ければ、礫層の一層安定な形状や機能が維持され
る。
On the other hand, even if the gravel layer becomes clogged due to trapped soil particles, removing the gravel and the trapped soil particles and replacing it with new gravel will restore the purification function of the gravel layer and achieve permanent purification. . If a permeable wall is also provided on the upstream side of the gravel layer, the more stable shape and function of the gravel layer can be maintained.

礫層の上流側に沈砂池があると、粗い土粒子な
どが予め除去され、主として微細なものだけを礫
層で分離すればよくなり、細かい粒子の除去能率
も向上する。礫層中に管体を埋設しておけば、礫
の間隙が大きくなり、捕捉機能が高められる。流
水を礫層内に積極的に誘導するように、上流側の
透過壁を貫く導水管や溝を設けておけば、捕捉効
果は増大する。
If there is a settling basin upstream of the gravel layer, coarse soil particles are removed in advance, and only fine particles need be separated by the gravel layer, which improves the efficiency of removing fine particles. By burying the tube in the gravel layer, the gaps between the gravel will become larger and the trapping function will be enhanced. If a water conduit or groove is provided that penetrates the permeable wall on the upstream side so as to actively guide running water into the gravel layer, the trapping effect will be increased.

礫をパツケージ化しておけば、その交換が極め
て容易となる。上記の礫に代えて、透水マツトな
どを使用しても、同様の機能を発揮させることが
できる。
If the gravel is packaged, it will be extremely easy to replace it. The same function can be achieved by using water-permeable pine instead of the gravel described above.

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

第1図は本発明の河水に含まれる土粒子のフイ
ルター方法が適用されるフイルター構層体が設置
された河川の縦断面図、第2図は礫層の上流側お
よび下流側に透過壁が設けられた場合の縦断面
図、第3図は礫層の上流に沈砂池が設けられた場
合の縦断面図、第4図は第3図の−線矢視
図、第5図は礫層中に管体が埋設されたフイルタ
ー構層体の概略図、第6図は導水管が設置された
フイルター構層体の概略図、第7図は一群の礫が
パツケージ化されたフイルター構層体の概略図、
第8図は礫に代わる透水材が用いられたフイルタ
ー構層体の概略図、第9図は透過壁として採用さ
れる枠ダムの一例における部分外観図、第10図
ないし第12図は、礫層の前後から採取された流
水に含まれる土粒子量を比較した現地実証試験デ
ータのグラフである。 1……河川、2……流水、3……礫層、3a…
…上流側、3b……下流側、4……礫、5,5A
……透過壁(堰、コンクリート壁、枠ダム)、1
1……沈砂池、12……管体(塩化ビニール管)、
12a……端面、13……透水材(透水マツト)、
14……導水管、15……透水材(透水マツト)、
18……土粒子、h……通常の水位。
Figure 1 is a vertical cross-sectional view of a river in which a filter structure is installed, to which the method of filtering soil particles contained in river water of the present invention is applied, and Figure 2 shows a permeable wall installed on the upstream and downstream sides of the gravel layer. Fig. 3 is a longitudinal cross-sectional view when a settling basin is provided upstream of the gravel layer, Fig. 4 is a view taken along the - line in Fig. 3, and Fig. 5 is a longitudinal cross-sectional view of the gravel layer. A schematic diagram of a filter structure with a pipe buried inside it, Figure 6 is a schematic diagram of a filter structure with a water conduit pipe installed, and Figure 7 is a filter structure in which a group of gravel is packaged. Schematic diagram of
Figure 8 is a schematic diagram of a filter structure using a permeable material instead of gravel, Figure 9 is a partial external view of an example of a frame dam used as a permeable wall, and Figures 10 to 12 are gravel This is a graph of field verification test data comparing the amount of soil particles contained in running water collected from before and after the layer. 1...river, 2...running water, 3...gravel layer, 3a...
...upstream side, 3b...downstream side, 4...gravel, 5,5A
...Transparent wall (weir, concrete wall, frame dam), 1
1...Sand basin, 12...Pipe body (vinyl chloride pipe),
12a... End face, 13... Water-permeable material (water-permeable pine),
14...Water pipe, 15...Water permeable material (water permeable pine),
18...Soil particles, h...Normal water level.

Claims (1)

【特許請求の範囲】 1 河川内に通常の水位より高い礫層を構築し、
その礫層の形状安定を図る堰を透過壁により形成
して、上記礫層の下流側に設け、 流水が上記礫層内を流過する間に、流水中の土
粒子を分離させ、 礫層内が目詰まりすると、礫と捕捉された土粒
子とを除去して、新しい礫に置き換えることを特
徴とする河水に含まれる土粒子のフイルター方
法。 2 請求項1において、透過壁を前記礫層の上流
側にも設けることを特徴とする河水に含まれる土
粒子のフイルター方法。 3 請求項1または請求項2において、前記礫層
の上流側に、河幅を広くした沈砂池を設け、その
沈砂池で粗い土粒子が除去された流水を、前記礫
層内へ流過させるようにしたことを特徴とする河
水に含まれる土粒子のフイルター方法。 4 前記礫層内に、端面が透水材でふたをされ、
礫の侵入を阻止した管体を埋設しておくことを特
徴とする請求項1ないし請求項3のいずれかに記
載の河水に含まれる土粒子のフイルター方法。 5 前記礫層内へ流水を案内する導水管もしくは
溝を、前記上流側に位置する透過壁を貫通して設
け、流れ方向となつている通路によつて、流水を
礫層内へ積極的に誘導するようにしたことを特徴
とする請求項2に記載の河水に含まれる土粒子の
フイルター方法。 6 前記礫をパツケージ化して、礫の置き換えを
容易としたことを特徴とする請求項1ないし請求
項5のいずれかに記載の河水に含まれる土粒子の
フイルター方法。 7 前記礫に代えて、透水材としたことを特徴と
する請求項1ないし請求項6のいずれかに記載の
河水に含まれる土粒子のフイルター方法。
[Claims] 1. Constructing a gravel layer higher than the normal water level in a river,
A weir is formed with a permeable wall to stabilize the shape of the gravel layer, and is installed on the downstream side of the gravel layer, and while the flowing water is flowing through the gravel layer, soil particles in the flowing water are separated, and the gravel layer is A method for filtering soil particles contained in river water, which removes gravel and trapped soil particles and replaces them with new gravel when the inside becomes clogged. 2. The method for filtering soil particles contained in river water according to claim 1, characterized in that a permeable wall is also provided on the upstream side of the gravel layer. 3. In claim 1 or claim 2, a settling basin with a wider river width is provided upstream of the gravel layer, and running water from which coarse soil particles have been removed in the settling basin is allowed to flow into the gravel layer. A method for filtering soil particles contained in river water, characterized by: 4 In the gravel layer, the end surface is covered with a water-permeable material,
4. A method for filtering soil particles contained in river water according to any one of claims 1 to 3, characterized in that a pipe body that prevents the intrusion of gravel is buried. 5. A water conduit pipe or groove for guiding flowing water into the gravel layer is provided through the permeable wall located on the upstream side, and the passage in the flow direction actively directs the flowing water into the gravel layer. 3. The method for filtering soil particles contained in river water according to claim 2, characterized in that the soil particles are guided. 6. The method for filtering soil particles contained in river water according to any one of claims 1 to 5, characterized in that the gravel is packaged to facilitate replacement of the gravel. 7. The method for filtering soil particles contained in river water according to any one of claims 1 to 6, characterized in that a water-permeable material is used in place of the gravel.
JP16734689A 1989-06-28 1989-06-28 Filtering method of soil particle included in river water Granted JPH0333313A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16734689A JPH0333313A (en) 1989-06-28 1989-06-28 Filtering method of soil particle included in river water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16734689A JPH0333313A (en) 1989-06-28 1989-06-28 Filtering method of soil particle included in river water

Publications (2)

Publication Number Publication Date
JPH0333313A JPH0333313A (en) 1991-02-13
JPH0435562B2 true JPH0435562B2 (en) 1992-06-11

Family

ID=15848026

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16734689A Granted JPH0333313A (en) 1989-06-28 1989-06-28 Filtering method of soil particle included in river water

Country Status (1)

Country Link
JP (1) JPH0333313A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007146492A (en) * 2005-11-28 2007-06-14 Akio Nakaya Bank, and method of manufacturing bank
CN103696403B (en) * 2014-01-01 2015-10-21 中国科学院-水利部成都山地灾害与环境研究所 A kind of ladder-pool structural type debris flow drainage groove and application thereof

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5940961A (en) * 1982-09-01 1984-03-06 Niles Parts Co Ltd Mounting construction of column switch for vehicle
JPH01107884A (en) * 1987-10-22 1989-04-25 Nippon Cement Co Ltd Method for cleaning rivers

Also Published As

Publication number Publication date
JPH0333313A (en) 1991-02-13

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