Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP2961278B2 - Seawater purification structure - Google Patents
[go: Go Back, main page]

JP2961278B2 - Seawater purification structure - Google Patents

Seawater purification structure

Info

Publication number
JP2961278B2
JP2961278B2 JP2171925A JP17192590A JP2961278B2 JP 2961278 B2 JP2961278 B2 JP 2961278B2 JP 2171925 A JP2171925 A JP 2171925A JP 17192590 A JP17192590 A JP 17192590A JP 2961278 B2 JP2961278 B2 JP 2961278B2
Authority
JP
Japan
Prior art keywords
seawater
tidal flat
sea area
pond
water level
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
JP2171925A
Other languages
Japanese (ja)
Other versions
JPH0462212A (en
Inventor
千明 丹羽
清志 二階堂
忍 山口
潔 西原
和秀 古川
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.)
Shimizu Construction Co Ltd
Kumagai Gumi Co Ltd
Takenaka Doboku Co Ltd
Original Assignee
Shimizu Construction Co Ltd
Kumagai Gumi Co Ltd
Takenaka Doboku Co Ltd
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 Shimizu Construction Co Ltd, Kumagai Gumi Co Ltd, Takenaka Doboku Co Ltd filed Critical Shimizu Construction Co Ltd
Priority to JP2171925A priority Critical patent/JP2961278B2/en
Publication of JPH0462212A publication Critical patent/JPH0462212A/en
Application granted granted Critical
Publication of JP2961278B2 publication Critical patent/JP2961278B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Treatment Of Biological Wastes In General (AREA)

Description

【発明の詳細な説明】 [産業上の利用分野] この発明は、半閉鎖性海域の干潟に設けられ、前記半
閉鎖性海域の海水を効果的かつ低コストで浄化すること
ができる海水浄化構造物に関するものである。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention is provided in a tidal flat in a semi-enclosed sea area, and is capable of purifying the sea water in the semi-enclosed sea area effectively and at low cost. It is about things.

[従来の技術] 近年、特に大都市圏における干潟、海浜等を有する半
閉鎖性海域では社会的ニーズの高まりにより埋め立てが
急速に進み、これらの水辺には人工的に護岸や堤防が形
成されてきた。これに対し、最近では、上記の半閉鎖性
海域の自然を取り戻し生活に潤いを与えるために、これ
らの海域内の海水の水質を人が水に触れることができる
程度まで向上させ、自然環境を取り戻すことが望まれて
いる。
[Related Art] In recent years, especially in semi-enclosed sea areas having tidal flats, beaches, and the like in metropolitan areas, landfills have rapidly progressed due to increasing social needs, and seawalls and embankments have been artificially formed on these watersides. Was. On the other hand, recently, in order to restore the nature of the semi-enclosed sea area and to enrich life, the quality of seawater in these sea areas has been improved to the extent that people can touch the water, and the natural environment has been improved. It is hoped to regain.

例えば、干潟は粘土、シルト、砂等から構成されるも
のであるからある程度の透水性を有し、透水係数は10-5
cm/secの程度である。この干潟に海水の浄化効果がある
ことはよく知られており、その理由は、干潟の構成要素
である粘土、シルト、砂等の粒子間隙及び表面に棲息す
る微生物や底生生物が海水に含まれる有機物や汚濁物質
等を分解し海水を浄化するためと、粘土、シルト、砂等
の粒子には濾過効果があるので、これらの粒子が海水に
含まれる不溶性物質を除去し海水を浄化するためであ
る。勿論、海水溶解性の汚染物質は水質の組成により分
解速度がかなり異なるのではあるが、干潟では、交換海
水中の懸濁性物質(SS分)は殆ど除去され浄化されるの
で、懸濁性物質に起因するCODやT−C等も同時に除去
され浄化される。
For example, since tidal flats are composed of clay, silt, sand, etc., they have a certain degree of water permeability, and the water permeability coefficient is 10 -5.
cm / sec. It is well known that this tidal flat has the effect of purifying seawater because the seawater contains microorganisms and benthic organisms that live in the particle gaps and surfaces of clay, silt, sand, etc., which are the constituents of the tidal flat. To purify seawater by decomposing organic substances and pollutants, etc., and to purify seawater by removing particles of seawater, such as clay, silt, and sand, because these particles have a filtering effect. It is. Of course, the decomposition rate of seawater-soluble contaminants varies considerably depending on the composition of water quality. However, in tidal flats, suspended solids (SS content) in the exchanged seawater are almost completely removed and purified. COD, TC, and the like caused by the substance are also removed and purified at the same time.

[発明が解決しようとする課題] ところで、一般の干潟における交換水量は、第3図に
示すように半閉鎖性海域1の干潮面(LWL)を起点とす
る干潟2内の日最低水頭線(L)と、満潮面(HWL)を
起点とする干潟2内の日最高水頭線(H)とで囲まれる
斜線部領域Sにより表される。干潟2の構成要素である
粘土、シルト、砂等の粒子径は砂浜の砂等の粒子径と比
べて小さいために海水が干潟2内に浸透し難くなり、し
たがって、日最高水頭線(H)が急勾配になり易く、干
潟2の実質交換水量が低下してしまうという欠点があっ
た。この場合、干潟2の透水量が極めて少ないので、1
日の浄化量はCODで0.3g/m2/g−SS/日 程度と言われて
おり、砂浜の4分の1程度の浄化量しかないこととな
る。これより、干潟2において海水交換量を大きくとる
ことが出来れば、干潟2の浄化能力は著しく増加するこ
とになる。
[Problems to be Solved by the Invention] By the way, as shown in FIG. 3, the amount of exchanged water in a general tidal flat is the daily minimum headline () in the tidal flat 2 starting from the low tide surface (LWL) of the semi-enclosed sea area 1. L) and a daily high water head line (H) in the tidal flat 2 starting from the high tide surface (HWL). Since the particle diameter of clay, silt, sand, etc., which is a constituent element of the tidal flat 2, is smaller than the particle diameter of sand, etc. on the sandy beach, it becomes difficult for seawater to penetrate into the tidal flat 2, and therefore, the daily maximum headline (H) However, there is a drawback that the slope tends to be steep and the actual exchange water amount of the tidal flat 2 is reduced. In this case, the permeability of the tidal flat 2 is extremely small.
The daily purification amount is said to be about 0.3 g / m 2 / g-SS / day in COD, which means that the purification amount is only about one-fourth of the sand beach. Thus, if the amount of seawater exchange in the tidal flat 2 can be increased, the purification capacity of the tidal flat 2 will be significantly increased.

この発明は、上記の事情に鑑みてなされたもので、半
閉鎖性海域の海水を浄化する際に、従来の干潟と比較し
て海水交換量を大きくとることができ、かつ浄化能力を
著しく増加させることができ、自然のエネルギーである
潮汐による潮位差を利用して効率的かつ低コストで海水
の水質の浄化を行うことができる海水浄化構造物を提供
することにある。
The present invention has been made in view of the above circumstances, and when purifying seawater in a semi-enclosed sea area, the amount of seawater exchange can be increased as compared with a conventional tidal flat, and the purification capacity is significantly increased. It is an object of the present invention to provide a seawater purification structure capable of efficiently and inexpensively purifying the quality of seawater by utilizing a tidal level difference caused by tide which is natural energy.

[課題を解決するための手段] 上記課題を解決するために、この発明は次の様な海水
浄化構造物を採用した。すなわち、半閉鎖性海域の干潟
に設けられ、前記半閉鎖性海域の海水を前記干潟内を透
過させることによりこの海水の水質を浄化する海水浄化
構造物であって、前記干潟の底面の位置が潮間帯の中等
水位以下となる池を設け、前記干潟にこの干潟の周辺海
域から前記池の内部に海水を進入させるための透水性の
導入路を設け、当該導水路の前記周辺海域側に天端の位
置が潮間帯の中等水位以上の潜堤を設け、前記干潟内に
この干潟に海水を透過させるために前記池から前記周辺
海域に向って延びる複数の配水路を設けてなることを特
徴としている。
[Means for Solving the Problems] In order to solve the above problems, the present invention employs the following seawater purification structure. That is, a seawater purification structure that is provided in a tidal flat in a semi-enclosed sea area and that purifies the quality of the seawater by transmitting the seawater in the semi-enclosed sea area through the tidal flat, wherein the position of the bottom of the tidal flat is A pond that is below the middle water level in the intertidal zone is provided, and a permeable introduction channel is provided in the tidal flat to allow seawater to enter the inside of the pond from the sea area around the tidal flat, and a ceiling is provided in the surrounding sea area side of the headrace channel. It is characterized by providing a submergence at an end position at a middle water level or higher in an intertidal zone, and providing a plurality of water distribution channels extending from the pond to the surrounding sea area in the tidal flat to allow seawater to pass through the tidal flat. And

[作用] この発明に係る海水浄化構造物は、自然のエネルギー
である潮汐による潮位差を有効に用いて、半閉鎖性海域
の海水を低コストで効率よく浄化する。すなわち、上記
海水浄化構造物において、周辺海域の海面が低水位(干
潮位)から高水位(満潮位)に上昇していく際には、上
記周辺海域の海面と上記海水浄化構造物の池の水面との
間に水位差が生じる。水位が高い上記周辺海域の海水
は、上記海水浄化構造物の潜堤を越えて導水路に進入し
池の中に貯留される。このようにして上記周辺海域が高
水位になった時に上記池の水位も同一水位まで周辺海域
より少し遅れて上昇することとなる。池内に貯留される
海水の水面は干潟内の海水の水頭より高いため、配水路
を経由して干潟の水位全域へ放出される。この際、海水
に含まれる有機物や汚濁物物質等は上記導水路や配水路
や干潟内を透過する間に微生物や低生生物により分解さ
れ効果的に浄化される。
[Operation] The seawater purification structure according to the present invention effectively and efficiently purifies seawater in a semi-enclosed sea area at low cost by effectively using a tidal level difference due to tide which is natural energy. That is, in the seawater purification structure, when the sea level of the surrounding sea area rises from a low water level (low tide level) to a high water level (high tide level), the sea surface of the surrounding sea area and the pond of the seawater purification structure are not used. There is a difference in water level with the water surface. The seawater in the surrounding sea area having a high water level enters the headrace channel over the submerged dike of the seawater purification structure and is stored in the pond. In this way, when the surrounding sea area becomes a high water level, the water level of the pond also rises to the same water level slightly later than the surrounding sea area. Since the water level of the seawater stored in the pond is higher than the head of the seawater in the tidal flat, it is discharged through the distribution channel to the entire water level of the tidal flat. At this time, the organic matter and pollutant substances contained in the seawater are decomposed by microorganisms and low-living organisms while passing through the above-mentioned headraces, waterways and tidal flats, and are effectively purified.

また、上記周辺海域の海面が高水位から低水位にかけ
て下降していく際には、上記周辺海域の海面と上記池の
水面との間に水位差が生じ、その水位差による位置エネ
ルギーにより、水位が高い上記池から複数の配水路及び
干潟内を透過し水位が低い上記周辺海域へ向かう海水の
流れが生じる。池内に貯留される海水は配水路を経由し
て干潟の水位全域へ放出され、これは池の水面が干潮位
に近ずくまで続く。この際、上記池に貯留された海水は
複数の配水路及び干潟内を透過する間に微生物や底生生
物により不溶物質や懸濁物質が取り除かれ浄化され上記
周辺海域に流出することとなる。
Further, when the sea surface of the surrounding sea area descends from a high water level to a low water level, a water level difference occurs between the sea surface of the surrounding sea area and the water surface of the pond. The seawater flows from the pond with high water to the surrounding sea area passing through a plurality of water distribution channels and tidal flats and having a low water level. The seawater stored in the pond is discharged to the entire tidal water level via the distribution channel, and this continues until the water level of the pond approaches the low tide level. At this time, the seawater stored in the pond passes through a plurality of water distribution channels and tidal flats, while microorganisms and benthic organisms remove insoluble and suspended substances, purify the water, and flow out to the surrounding sea area.

[実施例] 第1図及び第2図はこの発明の一実施例を示す図であ
る。図において、符号11はこの発明に係る海水浄化構造
物である。
Embodiment FIG. 1 and FIG. 2 are views showing an embodiment of the present invention. In the figure, reference numeral 11 denotes a seawater purification structure according to the present invention.

海水浄化構造物11は、半閉鎖性海域12の干潟13に設け
られたもので、半閉鎖性海域12の潮間帯に位置し、この
半閉鎖性海域12の海水の水質の浄化を目的とするもので
ある。ここで、半閉鎖性海域12は、潮汐による潮位差に
より海水の一部が外海の海水と絶えず交換されている湾
や入り江等である。また、干潟13は、満潮時においても
全体が冠水することがないように、半閉鎖性海域12の中
に天然に、もしくは粘土、シルト、砂等の造成材を用い
て人工的に造成されたものである。
The seawater purification structure 11 is provided in the tidal flat 13 of the semi-enclosed sea area 12, and is located in the intertidal zone of the semi-enclosed sea area 12, and aims at purifying the quality of seawater in the semi-enclosed sea area 12. Things. Here, the semi-enclosed sea area 12 is a bay or a bay where a part of seawater is constantly exchanged with seawater of the open sea due to a tidal level difference due to tide. Also, the tidal flat 13 is formed naturally in the semi-enclosed sea area 12 or artificially using a forming material such as clay, silt, sand, etc. so that the whole is not flooded even at high tide. Things.

海水浄化構造物11は、池21、導水路22、潜堤23、複数
の配水路24,24,…とから構成されている。
The seawater purification structure 11 is composed of a pond 21, a headrace 22, a submergence 23, and a plurality of water distribution paths 24, 24,.

池21は、半閉鎖性海域12から進入した海水を貯留する
ためのもので、干潟13の中央部に構築され、その底面の
位置が潮間帯の中等水位以下となるものである。池21の
底面の位置は、好適には干潮位以上であることが望まし
い。ここでは、この池21に貯留された海水の水位は半閉
鎖性海域12の水位とほぼ等しくなっている。この池21の
周囲の一端には導水路22が接続されている。
The pond 21 is for storing seawater that has entered from the semi-enclosed sea area 12, and is constructed in the central part of the tidal flat 13, and its bottom position is lower than the middle water level in the intertidal zone. The position of the bottom surface of the pond 21 is desirably at or above the low tide level. Here, the water level of the seawater stored in the pond 21 is substantially equal to the water level of the semi-enclosed sea area 12. A headrace 22 is connected to one end around the pond 21.

導水路22は、砕石31等を充填したもので、干潟13の周
辺海域25から池21内に海水を容易に透過させるためのも
のである。この導水路22は、全体が干潟13の中に埋設さ
れて水平方向に延在しており、その位置が潮間帯の中等
水位付近以上となるように造成されたものである。この
導水路22の一端部22aは池21に接続され、他端部22bには
潜堤23が取り付けられている。
The headrace 22 is filled with crushed stones 31 and the like, and is used to easily transmit seawater from the surrounding sea area 25 of the tidal flat 13 into the pond 21. The headrace channel 22 is entirely buried in the tidal flat 13 and extends in the horizontal direction. The headrace channel 22 is constructed so that its position is equal to or higher than the middle water level near the intertidal zone. One end 22a of the water conduit 22 is connected to the pond 21, and a submerged bank 23 is attached to the other end 22b.

潜堤23は、断面台形状、かつ、その天端が半閉鎖性海
域12の潮間帯の中等水位以上となるように形成され、海
底に固定されている。
The submerged levee 23 is formed to have a trapezoidal cross section and a top end that is equal to or higher than the middle water level in the intertidal zone of the semi-closed sea area 12, and is fixed to the sea floor.

配水路24は、礫32等を充填したもので、池21から周辺
海域25へ向って海水を容易に透過させるためのものであ
る。これらの配水路24,24,…は、池21から周辺海域25へ
向って放射状に配置されており、個々の配水路24は全体
が干潟13の中に埋設され、池21から周辺海域25に向って
やや下降するように樹状に延びており、その位置が潮間
帯の中等水位付近以下となるように造成されたものであ
る。
The water distribution channel 24 is filled with gravel 32 and the like, and is used to easily transmit seawater from the pond 21 to the surrounding sea area 25. These distribution channels 24, 24, ... are arranged radially from the pond 21 to the surrounding sea area 25, and the individual distribution channels 24 are entirely buried in the tidal flat 13 and extend from the pond 21 to the surrounding sea area 25. It extends like a tree so that it descends slightly, and is constructed so that its position is below the middle water level of the intertidal zone.

上記の様に構成された海水浄化構造物11の作用等につ
いて説明する。
The operation and the like of the seawater purification structure 11 configured as described above will be described.

周辺海域25の海面が低水位(干潮)LWLから高水位
(満潮)HWLにかけて上昇していく際には、周辺海域25
の海面と池21の水面との間に水位差が生じ、海水は水位
が高い周辺海域25から水位が低い池21に潜堤23の天端を
越えて進入し貯留される。この際、砕石31等の表面に付
着する微生物やこれらの間隙に棲息する底生生物により
海水が浄化される。このようにして周辺海域25が高水位
HWLになった時に、池21の水位もほぼ同一水位まで上昇
することとなる。この池21内に貯留される海水の水面は
干潟13内の海水の水頭より高いため、配水路24から干潟
13の水位全域へ放出される。この際、礫32等や干潟13を
構成する粘土、シルト、砂等の表面に付着する微生物や
これらの間隙に棲息する底生生物により海水が浄化され
る。
When the sea level in the surrounding sea area 25 rises from low water level (low tide) LWL to high water level (high tide) HWL, the surrounding sea area 25
A difference in water level occurs between the sea surface of the lake and the water surface of the pond 21, and the seawater enters the pond 21 having a low water level from the surrounding sea area 25 over the top of the submerged bank 23 and is stored. At this time, seawater is purified by microorganisms adhering to the surface of the crushed stones 31 and the like and benthic organisms living in the gaps therebetween. In this way, the surrounding sea area 25 has a high water level
When the water level becomes HWL, the water level of the pond 21 also rises to almost the same water level. Since the surface of the seawater stored in this pond 21 is higher than the head of the seawater in the tideland 13,
Released to all 13 water levels. At this time, the seawater is purified by microorganisms adhering to the surface of clay, silt, sand, or the like constituting the gravel 32 or the like, the tidal flat 13, and the benthic organisms living in these gaps.

また、周辺海域25の海面が高水位HWLから低水位LWLに
かけて下降していく際には、周辺海域25の水面と池21の
水面との間に水位差が生じ、その水位差による位置エネ
ルギーにより水位が高い池21から水位が低い周辺海域25
へ向かう水の流れが生じる。したがって、池21に貯留さ
れた海水は、配水路24を経由して干潟13の内部へ浸透し
周辺海域25へ流出することとなる。このようにして周辺
海域25が低水位LWLになった時に池21の水位も同一水位
まで下降することとなり、配水路24内に空隙が生じ、微
生物や底生生物の浄化作用に必要な酸素の供給が行なわ
れることとなる。この際、礫32等や干潟13を構成する粘
土、シルト、砂等の表面に付着する微生物やこれらの間
隙に棲息する底生生物により海水が浄化される。
Also, when the sea surface of the surrounding sea area 25 descends from the high water level HWL to the low water level LWL, a water level difference occurs between the water surface of the surrounding sea area 25 and the water surface of the pond 21, and the potential energy due to the water level difference causes Pond 21 with high water level to surrounding sea area 25 with low water level
There is a flow of water towards Therefore, the seawater stored in the pond 21 permeates into the tidal flat 13 via the water distribution channel 24 and flows out to the surrounding sea area 25. In this way, when the surrounding sea area 25 becomes the low water level LWL, the water level of the pond 21 also falls to the same water level, a void is created in the water distribution channel 24, and oxygen necessary for the purification action of microorganisms and benthic organisms is reduced. Supply will take place. At this time, the seawater is purified by microorganisms adhering to the surface of the gravel 32 and the like, clay, silt, sand, etc. composing the tidal flat 13 and benthic organisms living in these gaps.

以上詳細に説明したように、この海水浄化構造物11に
おいては、干潟13に底面の位置が潮間帯の中等水位以下
となる池21を設け、この干潟13の内部に干潟13の周辺海
域25から池21の内部に海水を進入させるための透水性の
導水路22を設け、導水路22の周辺海域25側に天端の位置
が潮間帯の中等水位以上の潜堤23を設け、干潟13の内部
にこの干潟13に海水を透過させるために他21から周辺海
域25に向って樹状に延びる複数の配水路24を設けたの
で、下記の優れた効果を奏することができる。
As described in detail above, in the seawater purification structure 11, the tidal flat 13 is provided with the pond 21 whose bottom position is equal to or lower than the middle water level of the intertidal zone, and inside the tidal flat 13 from the sea area 25 around the tidal flat 13. A permeable headrace 22 is provided inside the pond 21 to allow seawater to penetrate, and a submergence 23 is provided on the side of the seawater 25 near the headrace 22 with a top end at a middle water level or higher in the intertidal zone. Since a plurality of water distribution channels 24 extending in a tree shape from the other 21 to the surrounding sea area 25 are provided inside in order to allow seawater to permeate through the tidal flat 13, the following excellent effects can be obtained.

(イ) 導入路22及び配水路24の透水性は干潟13と比較
して1000〜10000倍程度大きくなり、導水路22及び配水
路24の圧損は干潟13と比較して著しく小さくなり、干潟
13全域を好気性の有効浄化領域とすることができる。し
たがって、干潟13において海水交換量を大きくとること
ができ、干潟13の浄化能力を著しく増加させることがで
きる。
(B) The permeability of the introduction channel 22 and the distribution channel 24 is about 1000 to 10,000 times greater than that of the tidal flat 13, and the pressure loss of the headrace channel 22 and the distribution channel 24 is significantly smaller than that of the tidal flat 13.
The entire 13 area can be an aerobic effective purification area. Therefore, the amount of seawater exchange in the tidal flat 13 can be increased, and the purification ability of the tidal flat 13 can be significantly increased.

(ロ) 周辺海域25の自然エネルギーである潮汐力を利
用することにより効率的かつ低コストで海水の水質の浄
化を行うことができる。
(B) By using the tidal force, which is the natural energy of the surrounding sea area 25, it is possible to purify seawater efficiently and at low cost.

(ハ) 砕石31等や礫32等や干潟13を構成する粘土、シ
ルト、砂等の表面には微生物が膜状に付着しており、こ
れらの間隙には底生生物が棲息しているので、海水に含
まれる有機物や汚濁物質等がこれらの間を透過する間に
微生物により分解され効果的に浄化され、高度な海水の
浄化が可能となる。また、底生生物の作用により懸濁物
質や増殖した微生物が補食され、目詰りが軽減される。
(C) Microorganisms adhere to the surface of clay, silt, sand, etc. composing crushed stones 31, gravel 32, etc. and tidal flat 13 in a film-like manner, and these gaps are inhabited by benthic organisms. In addition, organic substances and pollutants contained in seawater are decomposed by microorganisms while passing between them, and are effectively purified, thereby enabling high-grade purification of seawater. In addition, suspended substances and grown microorganisms are eaten by the action of benthic organisms, and clogging is reduced.

(ニ) 潜堤23を設けたことにより、導水路22が干潮位
付近までの流路断面を有していても、池21内の海水が導
水路22から周辺海域25へ逆流することがなく、浄化に寄
与する導水路22が増加する。
(D) By providing the submerged levee 23, the seawater in the pond 21 does not flow backward from the headrace channel 22 to the surrounding sea area 25 even if the headrace channel 22 has a cross section near the low tide level. Thus, the number of water conduits 22 that contribute to purification increases.

(ホ) 干潟13の中に水と親しめる安全な水域を確保す
ることができ、周囲の景観を高め、好適なレクリェーシ
ョンを施設とすることができる。
(E) It is possible to secure a safe water area close to water in the tidal flat 13, enhance the surrounding scenery, and make suitable recreation facilities.

なお、上記の実施例においては、海水浄化構造物11を
干潟13に設けた構成としたが、この構成は、半閉鎖性海
域12の海水を浄化することができる構成であればよく、
例えば、海水浄化構造物11を海浜等に設けた構造とした
場合でも、上記と同様に海浜の浄化効率を著しく増加さ
せることが可能になる。
In the above-described embodiment, the seawater purification structure 11 is provided in the tidal flat 13, but this configuration may be any configuration that can purify the seawater in the semi-enclosed sea area 12,
For example, even when the seawater purification structure 11 is provided on a beach or the like, the purification efficiency of the beach can be significantly increased in the same manner as described above.

[発明の効果] 以上詳細に説明した様に、この発明によれば、半閉鎖
性海域の干潟に設けられ、前記半閉鎖性海域の海水を前
記干潟内を透過させることによりこの海水の水質を浄化
する海水浄化構造物であって、前記干潟に底面の位置が
潮間帯の中等水位以下となる池を設け、前記干潟にこの
干潟の周辺海域から前記池の内部に海水を進入させるた
めの透水性の導入路を設け、当該導水路の前記周辺海域
側に天端の位置が潮間帯の中等水位以上の潜堤を設け、
前記干潟にこの干潟に海水を透過させるために前記池か
ら前記周辺海域に向って延びる複数の配水路を設けたの
で、下記の優れた効果を奏することができる。
[Effects of the Invention] As described above in detail, according to the present invention, the quality of this seawater is provided in a tidal flat in a semi-enclosed sea area, and the seawater in the semi-enclosed sea area is transmitted through the tidal flat. A seawater purification structure for purifying, wherein a pond whose bottom is located at a middle water level or lower in an intertidal zone is provided in the tidal flat, and a permeable portion for allowing seawater to enter the pond from the sea area around the tidal flat into the tidal flat. Provision of a water introduction channel, a submerged levee at the top of the headwater on the side of the surrounding sea area of the headrace above the middle water level of the intertidal zone,
Since the tidal flat is provided with a plurality of water distribution channels extending from the pond to the surrounding sea area in order to allow seawater to pass through the tidal flat, the following excellent effects can be obtained.

(イ) 導水路及び配水路の透水性は干潟と比較して非
常に大きくなり、導水路及び配水路の圧損は干潟と比較
して著しく小さくなり、干潟全域を有効浄化領域とする
ことができる。したがって、干潟において海水交換量を
大きくすることができ、干潟の浄化能力を著しく増加さ
せることができる。
(A) The permeability of the headrace and the distribution channel is much larger than that of the tidal flat, the pressure loss of the headrace and the distribution channel is significantly smaller than that of the tidal flat, and the entire tidal flat can be an effective purification area. . Therefore, the amount of seawater exchange in the tidal flat can be increased, and the purification capacity of the tidal flat can be significantly increased.

(ロ) 周辺海域の自然エネルギーである潮汐力を利用
することにより効率的かつ低コストで海水の水質の浄化
を行うことができる。
(B) It is possible to purify seawater efficiently and at low cost by using the tidal force, which is natural energy in the surrounding sea area.

(ハ) 砕石等や礫等や干潟を構成する粘土、シルト、
砂等の表面には微生物が膜状に付着しており、これらの
間隙には底生生物が棲息しているので、海水に含まれる
有機物や汚濁物質等がこれらの間を透過する間に微生物
により捕捉・分解され、効果的に浄化され、高度な海水
の浄化が可能となる。また、底生生物の作用により懸濁
物質や増殖した微生物が補食され、目詰りが軽減され
る。
(C) Crushed stones, gravel, etc., clay, silt,
Microorganisms adhere to the surface of sand etc. in the form of a film.Between these gaps, benthic organisms inhabit.Because organic matter and pollutants contained in seawater permeate between them, The water is trapped and decomposed, is effectively purified, and enables high-grade seawater purification. In addition, suspended substances and grown microorganisms are eaten by the action of benthic organisms, and clogging is reduced.

(ニ) 潜堤を設けたことにより、導水路が干潮位付近
までの流路断面を有していても、池内の海水が導水路か
ら周辺海域へ逆流することがなく、浄化に寄与する導水
路が増加する。
(D) By providing a submerged dike, seawater in the pond does not flow backward from the headrace channel to the surrounding sea area even if the headrace channel has a cross section near the low tide level. Waterways increase.

(ホ) 干潟の中に水と親しめる安全な水域を確保する
ことができ、周囲の景観を高め、好適なレクリェーショ
ン施設とすることができる。
(E) It is possible to secure a safe water area close to water in the tidal flat, enhance the surrounding scenery, and make it a suitable recreation facility.

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

第1図及び第2図はこの発明の一実施例を示す図であっ
て、第1図は海水浄化構造物の概略平面図、第2図は第
1図のII−II線に沿う横断面図、第3図は一般の干潟の
干満による海水交換を説明するための説明図である。 11……海水浄化構造物、 12……半閉鎖性海域、 13……干潟、 21……池、22……導水路、 23……潜堤、24……配水路、 25……周辺海域、 31……砕石、32……礫。
1 and 2 are views showing an embodiment of the present invention. FIG. 1 is a schematic plan view of a seawater purification structure, and FIG. 2 is a cross-sectional view taken along line II-II of FIG. FIG. 3 is an explanatory view for explaining seawater exchange due to ebb and flow of a general tidal flat. 11 ... Seawater purification structure, 12 ... Semi-enclosed sea area, 13 ... Tidal flat, 21 ... Pond, 22 ... Headway, 23 ... Submergence, 24 ... Distribution channel, 25 ... Surrounding sea area, 31 ... crushed stone, 32 ... gravels.

───────────────────────────────────────────────────── フロントページの続き (73)特許権者 999999999 三洋水路測量株式会社 東京都中央区日本橋堀留町1丁目3番17 号 (73)特許権者 999999999 株式会社竹中土木 東京都中央区銀座8丁目21番1号 (73)特許権者 999999999 株式会社本間組 新潟県新潟市西湊町通三ノ町3300番地3 (73)特許権者 999999999 三井不動産建設株式会社 東京都千代田区霞が関3丁目2番5号 (73)特許権者 999999999 りんかい建設株式会社 東京都港区芝2―3―8 (72)発明者 丹羽 千明 東京都中央区京橋2丁目16番1号 清水 建設株式会社内 (72)発明者 二階堂 清志 千葉県鎌ケ谷市丸山2丁目6番9号 (72)発明者 山口 忍 東京都品川区東大井1丁目11番25号 五 洋建設株式会社内 (72)発明者 西原 潔 東京都中央区銀座8丁目21番1号 株式 会社竹中土木内 (72)発明者 古川 和秀 東京都港区芝2―3―8 りんかい建設 株式会社内 (58)調査した分野(Int.Cl.6,DB名) C02F 3/00 E02B 3/00 C02F 3/06 ──────────────────────────────────────────────────続 き Continuing on the front page (73) Patent holder 999999999 Sanyo Hydrographic Surveying Co., Ltd. 1-3-17, Nihonbashi-Horidome-cho, Chuo-ku, Tokyo (73) Patent holder 999999999 Takenaka Civil Engineering Co., Ltd. 8-chome, Ginza, Chuo-ku, Tokyo 21-1 (73) Patent holder 999999999 Honma Gumi Co., Ltd. 3300-3, Minomachi, Nishiminato-machi, Niigata, Niigata Prefecture (73) Patent holder 999999999 Mitsui Fudosan Construction Co., Ltd. 3-5-2 Kasumigaseki, Chiyoda-ku, Tokyo (73) Patent holder 999999999 Rinkai Construction Co., Ltd. 2-3-8 Shiba, Minato-ku, Tokyo (72) Inventor Chiaki Niwa 2-16-1 Kyobashi, Chuo-ku, Tokyo Shimizu Corporation (72) Inventor Kiyoshi Nikaido 2-6-9 Maruyama, Kamagaya-shi, Chiba (72) Inventor Shinobu Yamaguchi 1-11-25 Higashioi, Shinagawa-ku, Tokyo Inside Goyo Construction Co., Ltd. (72) Akiya Nishihara Kiyoshi 8-21-1, Ginza, Chuo-ku, Tokyo (72) Inventor Kazuhide Furukawa 2-3-8 Shiba, Minato-ku, Tokyo Rinkai Construction Co., Ltd. (58) Field surveyed ( Int.Cl. 6 , DB name) C02F 3/00 E02B 3/00 C02F 3/06

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】半閉鎖性海域の干潟に設けられ、前記半閉
鎖性海域の海水を前記干潟内を透過させることによりこ
の海水の水質を浄化する海水浄化構造物であって、前記
干潟に底面の位置が潮間帯の中等水位以下となる池を設
け、前記干潟にこの干潟の周辺海域から前記池の内部に
海水を進入させるための透水性の導水路を設け、当該導
水路の前記周辺海域側に天端の位置が潮間帯の中等水位
以上の潜堤を設け、前記干潟内にこの干潟に海水を透過
させるために前記池から前記周辺海域に向って延びる複
数の配水路を設けてなることを特徴とする海水浄水構造
物。
1. A seawater purification structure provided on a tidal flat in a semi-enclosed sea area and for purifying the quality of the seawater by permeating the seawater in the semi-enclosed sea area through the tidal flat. Is provided with a pond where the position of the intertidal zone is equal to or lower than the middle water level, a permeable headrace for allowing seawater to enter the inside of the pond from the sea area around the tidal flat to the tidal flat, and the surrounding sea area of the headrace. A submerged levee whose top end is located at a middle water level or higher in the intertidal zone is provided on the side, and a plurality of water distribution channels extending from the pond to the surrounding sea area are provided in the tidal flat to allow seawater to pass through the tidal flat. A seawater purification structure characterized by the following.
JP2171925A 1990-06-29 1990-06-29 Seawater purification structure Expired - Fee Related JP2961278B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2171925A JP2961278B2 (en) 1990-06-29 1990-06-29 Seawater purification structure

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2171925A JP2961278B2 (en) 1990-06-29 1990-06-29 Seawater purification structure

Publications (2)

Publication Number Publication Date
JPH0462212A JPH0462212A (en) 1992-02-27
JP2961278B2 true JP2961278B2 (en) 1999-10-12

Family

ID=15932391

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2171925A Expired - Fee Related JP2961278B2 (en) 1990-06-29 1990-06-29 Seawater purification structure

Country Status (1)

Country Link
JP (1) JP2961278B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5223051B2 (en) * 2005-01-26 2013-06-26 うつろ株式会社 Advanced purification method using closed water area by “Utsuro”
JP6866777B2 (en) * 2017-06-08 2021-04-28 株式会社大林組 Clam fishing ground

Also Published As

Publication number Publication date
JPH0462212A (en) 1992-02-27

Similar Documents

Publication Publication Date Title
KR101360271B1 (en) Sustainable structured biotop system using wetland, pond and settling pond structure adopting multi-cells and multi-lanes
KR101268382B1 (en) Hybrid constructed wetland for protecting the costal and natural wetlands
CN106145371A (en) A kind of ecological floating island device
JP2000186351A (en) Penetration-type water intake method
CN109437477A (en) A kind of river channel ecology environmental reconstruction system
JP2961278B2 (en) Seawater purification structure
US20080006567A1 (en) Advanced Purification System Utilizing Closed Water Area by Hollow Water Area (Utsuro)
KR101642355B1 (en) Filtered Water Intake System and Construction Method thereof
CN113698028A (en) River crab culture water circulation method
JPWO2002099202A1 (en) Hydropower generation method
JPS58173208A (en) Breakwater for clarifying water
JPH05345187A (en) Environmental cleaning material
KR20080015136A (en) Ecological Purification Artificial Wetland
JP3111200B2 (en) Seawater purification intake structure
JPH1136275A (en) Floating body type artificial island
JPH0713766Y2 (en) Seawater purification structure
JPH05131196A (en) Environmental purification structure
KR100513704B1 (en) Artificial mat cultivating plant
JP2001003344A (en) Underwater multi-purpose structure
JP3087227B2 (en) Seawater purification structure
KR100746245B1 (en) Ecological Water Purification Media and Handmade Basin System
JP4746362B2 (en) Water purification facility using wave energy
JP2005058957A (en) Floating water purification system
KR20120111320A (en) Vegetative block using bio mass with the organic matter absorption layer and vegetative retaining wall
JP3007939B2 (en) Artificial beach

Legal Events

Date Code Title Description
S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313117

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080806

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080806

Year of fee payment: 9

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313117

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080806

Year of fee payment: 9

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

LAPS Cancellation because of no payment of annual fees