JP3758099B2 - Water purification levee - Google Patents

Water purification levee Download PDF

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Publication number
JP3758099B2
JP3758099B2 JP22317596A JP22317596A JP3758099B2 JP 3758099 B2 JP3758099 B2 JP 3758099B2 JP 22317596 A JP22317596 A JP 22317596A JP 22317596 A JP22317596 A JP 22317596A JP 3758099 B2 JP3758099 B2 JP 3758099B2
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JP
Japan
Prior art keywords
water
permeable
levee
body material
water purification
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JP22317596A
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Japanese (ja)
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JPH1046542A (en
Inventor
博和 辻
衛 石垣
修二 宮岡
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Obayashi Corp
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Obayashi Corp
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Description

【0001】
【発明の属する技術分野】
本発明は、所望の浄化水域を取り囲むようにして構築される水質浄化堤に関する。
【0002】
【従来の技術】
ウオーターフロントにおいてアメニティに富んだ親水空間を確保するためには、水質を浄化して良好な水環境を形成することが不可欠である。
【0003】
このような水質浄化手段として、いわゆる水質浄化堤が注目されている。
【0004】
水質浄化堤1は、図4に示すように礫や砕石からなる堤体材2を海底3から台形状に積み上げ、これを所定の被覆石4で被覆したものであり、かかる水質浄化堤1を所定の水域を取り囲むようにして構築しておくと、外水域5の海水は、水質浄化堤1で浄化されて内水域6に流入する。
【0005】
すなわち、潮の干満や波の作用によって外水域の海水が内水域6に移動する際、該海水は、水質浄化堤1の堤体材2の間隙を通過するが、そのときに海水中に含まれるプランクトン等の汚濁成分は、堤体材2の表面に付着形成された微生物群からなる生物膜によって付着あるいは捕捉され、さらに礫間に棲息する貝類や甲殻類によって摂取され除去される。
【0006】
このように、水質浄化堤1は、自然生態系の水質浄化機能によって清浄な水質の内水域を創造できる海岸構造物であることがわかってきた。
【0007】
【発明が解決しようとする課題】
しかしながら、水質浄化が必要となるような水域では、水質の富栄養化が進行しており、海底付近では堆積ヘドロからの溶出負荷によって溶存酸素が消費され、貧酸素化している場合が多い。特に、水温が上昇し日射量が増える夏場では、その傾向が顕著となる。
【0008】
したがって、海底3付近の貧酸素水が水質浄化堤1を通過して内部水域6に流入すれば、内部水域6の溶存酸素濃度が低下し、底生生物の生存に悪影響を及ぼすとともに、水質浄化堤1を通過する際に堤体の海水浄化機能をも低下させるという問題を生じていた。
【0009】
かかる問題は、水質浄化堤1内に遮断構造を設置しておき、季節等に応じて該遮断構造を開閉するようにすれば解決することができるが、浄化堤の構築コストが高くなるという別の問題を生じる。
【0010】
本発明は、上述した事情を考慮してなされたもので、比較的低コストで外水域の貧酸素水の流入を防止可能な水質浄化堤を提供することを目的とする。
【0011】
【課題を解決するための手段】
上記目的を達成するため、本発明の水質浄化堤は請求項1に記載したように、所定の堤体材をほぼ台形状に積み上げた水質浄化堤において、前記堤体材のうち、水底から所定高さまでを難透水性の堤体材で構成して難透水層とし、前記高さから上方を透水性の堤体材で構成して透水層とするとともに、前記難透水層の隣接位置に難透水性の堤体材を水底から積み上げて流入阻止層としたものである。
【0014】
本発明に係る水質浄化堤においては、水底付近の水は、水底に構築された難透水層に阻まれて内水域にほとんど流入しないが、水面付近の水は、難透水層の上に構築された透水層を介して内水域に流入する。すなわち、内水域には溶存酸素濃度の低い貧酸素水はほとんど流入せず、溶存酸素濃度の高い水だけが、透水層の堤体材で浄化作用を受けてから内水域に流入する。
【0015】
ここで、前記難透水層の隣接位置に難透水性の堤体材を水底から積み上げて流入阻止層とした場合、貧酸素水の内水域への流入をほぼ完全に阻止することができる。
【0016】
また、本発明に係る水質浄化堤においては、水底付近の水は、水底に構築された遮水層に阻まれて内水域への流入が遮断され、水面付近の水は、遮水層の上に構築された透水層を介して内水域に流入する。すなわち、内水域には溶存酸素濃度の低い貧酸素水は流入せず、溶存酸素濃度の高い水だけが、透水層の堤体材で浄化作用を受けてから内水域に流入する。
【0017】
【発明の実施の形態】
以下、本発明に係る水質浄化堤の実施の形態について、添付図面を参照して説明する。なお、従来技術と実質的に同一の部品等については同一の符号を付してその説明を省略する。
【0018】
(第1実施形態)
図1は、本実施形態に係る水質浄化堤11を示した断面図である。同図でわかるように、本実施形態の水質浄化堤11も従来の水質浄化堤1と同様、所定の堤体材をほぼ台形状に積み上げて構成してあるが、本実施形態では、海底から所定高さまでの範囲(同図矢印の範囲)を難透水性の堤体材12で構成して難透水層とするとともに、前記高さから上方を透水性の堤体材13で構成して透水層とし、それらを被覆石4で被覆してある。
【0019】
難透水性の堤体材12としては、粒径数cm程度の砕石や砂利を使用するのがよい。また、透水性の堤体材13としては、生物膜が付着するとともに貝等の生物が棲息できるもの、例えば粒径が20cm〜30cm程度の礫や砕石を使用するのがよい。
【0020】
なお、堤体材12で構成された難透水層の高さについては、外水域において海水の溶存酸素濃度が鉛直方向にどのように変化するかを調査し、かかる調査にしたがって適宜決定すればよいが、例えば同図に示すように干潮時の水位14よりも1m程度下がった付近に設定しておけば、干潮時であっても、外水域5の海水を透水層で浄化させた上で内水域6に流入させることができる。
【0021】
かかる水質浄化堤11を所定の海域を取り囲むようにして配置しておくと、外水域5の海水は、潮の干満や波が生じた際、透水層を構成する堤体材13の間隙を通って内水域6に移動し、それらの海水は、間隙を移動中に堤体材13の表面に付着した微生物群からなる生物膜によって汚濁成分が除去されて清浄な海水となる。
【0022】
一方、外水域5の海底付近3の水は、堤体材12で構成された難透水層に阻まれて内水域6にほとんど流入しない。すなわち、内水域6には溶存酸素濃度の低い貧酸素水はほとんど流入せず、溶存酸素濃度の高い水だけが、透水層を構成する堤体材13で浄化作用を受けてから内水域6に流入する。
【0023】
以上説明したように、本実施形態に係る水質浄化堤によれば、海底に難透水層を設置し、その上に透水層を構築するようにしたので、溶存酸素濃度の低い貧酸素水を内水域にほとんど流入させず、溶存酸素濃度の高い水だけを透水層の堤体材で浄化させてから内水域に流入させることが可能となる。
【0024】
そのため、水質の富栄養化が進行している水域においても、溶存酸素が消費された貧酸素水が内水域に流入して該水域の生態に悪影響を及ぼすおそれがなくなる。しかも、かかる水質浄化堤は、粒径の異なる二種類の堤体材を積み上げるだけなので、コンクリート板等で遮断構造を構築するよりもはるかに安価に構築することができる。
【0025】
本実施形態では、難透水性の堤体材として、粒径数cm程度の砕石や砂利を使用したが、これらに代えて、コンクリート廃材、土砂等の建設副産物を利用するようにしてもよい。また、透水性の堤体材として、粒径が20cm程度の礫や砕石を使用したが、これらに代えて、コンクリート廃材などを利用してもよい。
【0026】
(第2実施形態)
次に、第2実施形態について説明する。なお、従来技術若しくは上述の実施形態と実質的に同一の部品等については同一の符号を付してその説明を省略する。
【0027】
図2(a)は、本実施形態に係る水質浄化堤21を示した断面図である。同図でわかるように、本実施形態の水質浄化堤21も上述の水質浄化堤11と同様、海底から所定高さまでの範囲(同図矢印の範囲)を難透水性の堤体材12で構成して難透水層とするとともに、前記高さから上方を透水性の堤体材13で構成して透水層とし、それらを被覆石4で被覆してあるが、本実施形態ではさらに、堤体材12で構成された難透水層の外水域5側の隣接位置に、同じく難透水性の堤体材24を海底から積み上げてその上を砂22で覆った流入阻止層を構築してある。
【0028】
堤体材24は、堤体材12と同様、粒径数cm程度の砕石や砂利を使用するのがよい。なお、堤体材24で構成された流入阻止層の先端には、砕石等で構築された潜堤23を設置してあり、堤体材24および砂22の流出を防止するようになっている。
【0029】
本実施形態の水質浄化堤においても、第1実施形態と同様、堤体材12で構成された難透水層の作用によって内水域6には溶存酸素濃度の低い貧酸素水はほとんど流入せず、溶存酸素濃度の高い水だけが、透水層の堤体材13で浄化されて内水域6に流入するが、本実施形態ではさらに、難透水性の堤体材24で構成された流入阻止層を設置してあるので、貧酸素水の流入をほぼ完全に阻止することが可能となる。
【0030】
本実施形態では、難透水性の堤体材24を砂22で覆って流入阻止層としたが、堤体材24のみで充分な流入阻止効果を期待できるのであれば、覆砂を施す必要はない。
【0031】
また、本実施形態では、流入阻止層を外水域5側に構築したが、これに代えてあるいはこれに加えて内水域側に構築するようにしてもよい。
【0032】
図2(b)は、かかる流入阻止層を内水域側に構築した変形例を示したものである。すなわち、同図に係る水質浄化堤31も水質浄化堤11と同様、海底3から所定高さまでの範囲(同図矢印の範囲)を難透水性の堤体材12で構成して難透水層とするとともに、前記高さから上方を透水性の堤体材13で構成して透水層とし、それらを被覆石4で被覆してあるが、本実施形態ではさらに、堤体材12で構成された難透水層の内水域6側の隣接位置に、同じく難透水性の堤体材25を海底から積み上げた流入阻止層を構築してある。
【0033】
堤体材25も、堤体材12や堤体材24と同様、粒径数cm程度の砕石や砂利を使用するのがよい。
【0034】
本変形例に係る水質浄化堤31においても、上述の実施形態と同様、堤体材12で構成された難透水層および同じく堤体材25で構成された流入阻止層の作用によって内水域6への貧酸素水の流入をほぼ完全に阻止しつつ、溶存酸素濃度の高い水だけを、透水層の堤体材13で浄化させてから内水域6に流入させることが可能となる。
【0035】
(第3実施形態)
次に、第3実施形態について説明する。なお、従来技術若しくは上述の実施形態と実質的に同一の部品等については同一の符号を付してその説明を省略する。
【0036】
図3は、本実施形態に係る水質浄化堤41を示した断面図である。同図でわかるように、本実施形態の水質浄化堤41は、海底3に遮水層としてのコンクリート函体42を設置し、該コンクリート函体42の上に透水性の堤体材13をほぼ台形状に積み上げて透水層とし、それらを被覆石4で被覆してある。
【0037】
コンクリート函体42の高さ(同図矢印)についても、外水域において海水の溶存酸素濃度が鉛直方向にどのように変化するかを調査し、かかる調査にしたがって適宜決定すればよいが、例えば同図に示すように干潮時の水位14よりも1m程度下がった付近に設定しておけば、干潮時であっても、外水域5の海水を透水層で浄化させた上で内水域6に流入させることができる。
【0038】
かかる水質浄化堤41についても、溶存酸素濃度の高い海面付近の水は、堤体材13の水質浄化作用を受けて外水域5から内水域6に流入する一方、溶存酸素濃度の低い海底付近の水は、コンクリート函体42にほぼ完全に遮断されて内水域6に流入しない。
【0039】
したがって、水質の富栄養化が進行している水域であっても、溶存酸素が消費された貧酸素水が内水域に流入して該水域の生態に悪影響を及ぼすおそれはほとんどなくなる。
【0040】
【発明の効果】
以上述べたように、本発明の水質浄化堤は請求項1に記載したように、比較的低コストで外水域の貧酸素水の流入を防止することができるほか、難透水性の堤体材で構成された流入阻止層を設置したので、貧酸素水の流入をほぼ完全に阻止することが可能となる。
【0042】
【図面の簡単な説明】
【図1】第1実施形態に係る水質浄化堤の断面図。
【図2】別の実施形態に係る水質浄化堤の断面図であり、(a)は第2実施形態に係る図、(b)はその変形例に係る図。
【図3】第3実施形態に係る水質浄化堤の断面図。
【図4】従来技術に係る水質浄化堤の断面図。
【符号の説明】
11、21、31、41 水質浄化堤
12、24、25 難透水性の堤体材
13 透水性の堤体材
42 コンクリート函体(遮水層)
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a water purification bank constructed so as to surround a desired purification water area.
[0002]
[Prior art]
In order to secure a hydrophilic space rich in amenities at the waterfront, it is essential to purify the water quality and form a good water environment.
[0003]
As such a water purification means, a so-called water purification bank is drawing attention.
[0004]
As shown in FIG. 4, the water purification dam 1 is a structure in which levee body materials 2 made of gravel and crushed stone are stacked in a trapezoidal shape from the sea bottom 3 and covered with a predetermined covering stone 4. If it is constructed so as to surround a predetermined water area, the seawater in the outer water area 5 is purified by the water purification dam 1 and flows into the inner water area 6.
[0005]
That is, when the seawater in the outer water area moves to the inner water area 6 due to the tides and the action of waves, the seawater passes through the gap between the dam body materials 2 of the water purification dam 1 and is included in the seawater at that time. Contaminated components such as plankton are attached or captured by a biofilm composed of a microorganism group attached to the surface of the levee body material 2, and are further ingested and removed by shellfish and crustaceans living between gravel.
[0006]
Thus, it has been found that the water purification bank 1 is a coastal structure that can create an inner water area with a clean water quality by the water purification function of the natural ecosystem.
[0007]
[Problems to be solved by the invention]
However, in water areas where water purification is required, eutrophication of the water quality is progressing, and dissolved oxygen is consumed by the elution load from sediment sludge in the vicinity of the sea bottom, and is often hypoxic. This tendency is particularly noticeable in summer when the water temperature rises and the amount of solar radiation increases.
[0008]
Therefore, if the oxygen-poor water near the seabed 3 passes through the water purification levee 1 and flows into the internal water area 6, the dissolved oxygen concentration in the internal water area 6 decreases, adversely affecting the survival of benthic organisms, and water purification. When passing through the bank 1, there was a problem that the seawater purification function of the bank was also reduced.
[0009]
Such a problem can be solved by installing a breaker structure in the water purification dam 1 and opening and closing the breaker structure according to the season, etc. Cause problems.
[0010]
The present invention has been made in consideration of the above-described circumstances, and an object of the present invention is to provide a water purification levee that can prevent the inflow of poor oxygen water in an outside water area at a relatively low cost.
[0011]
[Means for Solving the Problems]
In order to achieve the above object, a water purification levee according to the present invention is a water purification levee obtained by stacking a predetermined levee body material in a substantially trapezoidal shape, as defined in claim 1. The permeable wall material is composed of a hardly permeable body material up to the height, and the permeable dam body material is formed upward from the height to form a permeable layer. A water-permeable wall material is stacked from the bottom to form an inflow blocking layer.
[0014]
In the water purification levee according to the present invention, the water near the bottom of the water is blocked by the impermeable layer built on the bottom of the water and hardly flows into the inner water area, but the water near the water surface is constructed on the impermeable layer. It flows into the inner water area through the permeable layer. That is, the poor oxygen water with a low dissolved oxygen concentration hardly flows into the inner water area, and only the water with a high dissolved oxygen concentration flows into the inner water area after being purified by the levee material of the permeable layer.
[0015]
Here, when the poorly permeable embankment material is piled up from the bottom of the water at the position adjacent to the hardly permeable layer to form an inflow blocking layer, the inflow of the poor oxygen water into the inner water area can be almost completely blocked.
[0016]
Further, in the water purification levee according to the present invention, the water near the bottom of the water is blocked by the impermeable layer built at the bottom of the water and blocked from flowing into the inner water area, and the water near the water surface is above the impermeable layer. It flows into the inner waters through the permeable layer constructed in That is, the poor oxygen water with a low dissolved oxygen concentration does not flow into the inner water area, and only the water with a high dissolved oxygen concentration flows into the inner water area after being purified by the levee material of the permeable layer.
[0017]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, embodiments of a water purification bank according to the present invention will be described with reference to the accompanying drawings. Note that components that are substantially the same as those of the prior art are assigned the same reference numerals, and descriptions thereof are omitted.
[0018]
(First embodiment)
FIG. 1 is a cross-sectional view illustrating a water purification bank 11 according to the present embodiment. As can be seen from the figure, the water purification dam 11 of the present embodiment is configured by stacking predetermined levee body materials in a substantially trapezoidal shape, similar to the conventional water purification dam 1, but in this embodiment, The range up to a predetermined height (the range indicated by the arrow in the figure) is composed of a non-permeable levee body material 12 to form a non-permeable layer, and the upper portion from the height is configured with a permeable levee body material 13 to transmit water. Layers are formed and coated with a covering stone 4.
[0019]
As the poorly permeable bank body material 12, it is preferable to use crushed stone or gravel having a particle size of several centimeters. Moreover, as the water-permeable bank body material 13, it is good to use the thing with which a biological film adheres and organisms, such as a shellfish, can inhabit, for example, gravel and crushed stones with a particle size of about 20 cm to 30 cm.
[0020]
In addition, about the height of the poorly permeable layer comprised with the bank body material 12, what is necessary is just to determine how the dissolved oxygen concentration of seawater changes to an orthogonal | vertical direction in an external water area, and to determine suitably according to this investigation. However, for example, as shown in the figure, if it is set around 1 m below the water level 14 at low tide, the seawater in the outer water area 5 is purified by the permeable layer even at low tide. It can flow into the water area 6.
[0021]
If the water purification dam 11 is arranged so as to surround a predetermined sea area, the seawater in the outer water area 5 passes through the gap between the dam body members 13 constituting the permeable layer when tides and waves occur. Then, the seawater moves to the inner water area 6, and the contaminated components are removed by the biofilm composed of a microorganism group attached to the surface of the levee body material 13 while moving through the gap, so that the seawater becomes clean seawater.
[0022]
On the other hand, the water in the vicinity of the sea bottom 3 in the outer water area 5 is blocked by the hardly permeable layer formed of the dam body material 12 and hardly flows into the inner water area 6. That is, the poor oxygen water having a low dissolved oxygen concentration hardly flows into the inner water region 6, and only the water having a higher dissolved oxygen concentration is purified by the levee body material 13 constituting the permeable layer and then enters the inner water region 6. Inflow.
[0023]
As described above, according to the water purification levee according to the present embodiment, the poorly permeable layer is installed on the seabed, and the permeable layer is constructed thereon. Almost no water is allowed to flow into the water area, and only water having a high dissolved oxygen concentration can be purified by the levee material of the permeable layer and then flowed into the inner water area.
[0024]
Therefore, even in a water area where the eutrophication of water quality is progressing, there is no possibility that the anoxic water in which dissolved oxygen is consumed flows into the inner water area and adversely affects the ecology of the water area. Moreover, such a water purification levee can be constructed at a much lower cost than constructing a barrier structure with a concrete plate or the like because it only stacks two kinds of levee body materials having different particle sizes.
[0025]
In the present embodiment, crushed stones and gravel having a particle diameter of several centimeters are used as the hardly permeable embankment material. However, instead of these, construction by-products such as concrete waste and earth and sand may be used. Moreover, although the gravel and the crushed stone with a particle size of about 20 cm were used as a water-permeable embankment material, it may replace with these and a concrete waste material etc. may be utilized.
[0026]
(Second Embodiment)
Next, a second embodiment will be described. Note that components that are substantially the same as those of the conventional technology or the above-described embodiment are denoted by the same reference numerals, and description thereof is omitted.
[0027]
Fig.2 (a) is sectional drawing which showed the water quality purification bank 21 based on this embodiment. As can be seen in the figure, the water purification dam 21 of the present embodiment is also composed of a non-permeable levee body material 12 in the range from the sea bottom to a predetermined height (range of the arrow in the figure), like the water purification dam 11 described above. In this embodiment, the permeable body is made of a hardly permeable layer, and the permeable wall member 13 is formed from the above-mentioned height to form a permeable body material 13 and is covered with the covering stone 4. An inflow blocking layer is constructed in which a hardly permeable bank body material 24 is piled up from the seabed and covered with sand 22 at a position adjacent to the outer water region 5 side of the hardly permeable layer made of the material 12.
[0028]
The dam body material 24 is preferably made of crushed stone or gravel having a particle diameter of about several centimeters, like the dam body material 12. A dike 23 constructed of crushed stone or the like is installed at the tip of the inflow blocking layer composed of the dam body material 24 so as to prevent the levee body material 24 and the sand 22 from flowing out. .
[0029]
In the water purification levee of the present embodiment, as in the first embodiment, the poor oxygen water having a low dissolved oxygen concentration does not flow into the inner water region 6 due to the action of the poorly permeable layer composed of the dam body material 12, Only water with a high dissolved oxygen concentration is purified by the permeable body material 13 of the permeable layer and flows into the inner water region 6. In the present embodiment, an inflow blocking layer composed of the hardly permeable dam body material 24 is further provided. Since it is installed, it becomes possible to almost completely prevent the inflow of the oxygen-poor water.
[0030]
In the present embodiment, the non-permeable levee body material 24 is covered with sand 22 to form an inflow prevention layer. However, if a sufficient inflow prevention effect can be expected only by the dam body material 24, it is necessary to cover the sand. Absent.
[0031]
Moreover, in this embodiment, although the inflow prevention layer was constructed | assembled in the outer water area 5 side, you may make it construct in the inner water area side instead of this or in addition to this.
[0032]
FIG. 2 (b) shows a modification in which such an inflow blocking layer is constructed on the inner water area side. That is, similarly to the water purification dam 11, the water purification dam 31 according to the figure is composed of a non-permeable levee body material 12 in the range from the sea bottom 3 to a predetermined height (the range of the arrow in the figure). In addition, the permeable body material 13 is formed upward from the height to form a water permeable layer, and these are covered with the covering stone 4, but in the present embodiment, the levee body material 12 is further formed. An inflow blocking layer in which the hardly permeable bank body material 25 is piled up from the sea bottom is constructed at an adjacent position on the inner water area 6 side of the hardly permeable layer.
[0033]
The dam body material 25 is also preferably made of crushed stone or gravel having a particle size of about several centimeters, like the dam body material 12 and the dam body material 24.
[0034]
Also in the water purification dam 31 according to this modification, as in the above-described embodiment, the inner water area 6 is brought about by the action of the poorly permeable layer constituted by the levee body material 12 and the inflow blocking layer also constituted by the dam body material 25. It is possible to allow only the water having a high dissolved oxygen concentration to be purified by the levee body material 13 of the permeable layer and then flow into the inner water area 6 while almost completely preventing the inflow of the poor oxygen water.
[0035]
(Third embodiment)
Next, a third embodiment will be described. Note that components that are substantially the same as those of the conventional technology or the above-described embodiment are denoted by the same reference numerals, and description thereof is omitted.
[0036]
FIG. 3 is a cross-sectional view showing the water purification bank 41 according to the present embodiment. As can be seen from the figure, the water purification dam 41 of the present embodiment has a concrete box 42 as a water shielding layer installed on the seabed 3, and the water-permeable dam member 13 is substantially placed on the concrete box 42. The trapezoidal shape is used to form a water permeable layer, which is covered with a covering stone 4.
[0037]
The height of the concrete box 42 (arrow in the figure) may be determined as appropriate by investigating how the dissolved oxygen concentration of seawater changes in the vertical direction in the outside water area. As shown in the figure, if it is set near 1m lower than the water level 14 at low tide, it will flow into the inner water area 6 after purifying the seawater in the outer water area 5 with a permeable layer even at low tide. Can be made.
[0038]
Also in the water purification levee 41, water near the sea surface with a high dissolved oxygen concentration receives the water purification action of the dam body material 13 and flows from the outer water area 5 into the inner water area 6, while the water near the sea bottom with a low dissolved oxygen concentration. The water is almost completely blocked by the concrete box 42 and does not flow into the inner water area 6.
[0039]
Therefore, even in a water area where eutrophication of the water quality is progressing, there is almost no possibility that the anoxic water in which dissolved oxygen is consumed flows into the inner water area and adversely affects the ecology of the water area.
[0040]
【The invention's effect】
As described above, the water purification levee according to the present invention can prevent the inflow of poor oxygen water in the outside water area at a relatively low cost as described in claim 1, and has a hardly permeable levee body material. Since the inflow prevention layer constituted by is installed, the inflow of the poor oxygen water can be almost completely prevented.
[0042]
[Brief description of the drawings]
FIG. 1 is a sectional view of a water purification bank according to a first embodiment.
FIG. 2 is a cross-sectional view of a water purification bank according to another embodiment, (a) is a diagram according to the second embodiment, and (b) is a diagram according to a modification thereof.
FIG. 3 is a sectional view of a water purification bank according to a third embodiment.
FIG. 4 is a cross-sectional view of a water purification bank according to the prior art.
[Explanation of symbols]
11, 21, 31, 41 Water purification levee 12, 24, 25 Water-permeable embankment material 13 Water-permeable embankment material 42 Concrete box (water-impervious layer)

Claims (1)

所定の堤体材をほぼ台形状に積み上げた水質浄化堤において、
前記堤体材のうち、水底から所定高さまでを難透水性の堤体材で構成して難透水層とし、前記高さから上方を透水性の堤体材で構成して透水層とするとともに、前記難透水層の隣接位置に難透水性の堤体材を水底から積み上げて流入阻止層としたことを特徴とする水質浄化堤。
In the water purification levee where a given levee body material is stacked in a trapezoidal shape,
Among the levee body materials, the water from the bottom to a predetermined height is made of a non-permeable levee body material to form a hardly permeable layer, and the upper part from the height is made of a permeable levee body material to make a permeable layer. A water purification levee characterized in that a non-permeable levee body material is stacked from the bottom of the water at a position adjacent to the non-permeable layer to form an inflow blocking layer.
JP22317596A 1996-08-05 1996-08-05 Water purification levee Expired - Lifetime JP3758099B2 (en)

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JP22317596A JP3758099B2 (en) 1996-08-05 1996-08-05 Water purification levee

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JP3758099B2 true JP3758099B2 (en) 2006-03-22

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JP2008144525A (en) * 2006-12-12 2008-06-26 Ohbayashi Corp Seawater infiltration intake system and seawater infiltration intake method
JP5609251B2 (en) * 2010-05-12 2014-10-22 株式会社大林組 Water purification structure
EP3088610B1 (en) * 2015-04-29 2018-11-14 Dredging International N.V. Scour protection for an underwater bottom alongside a quay wall, and method for providing the same

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