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JP3200773B2 - Purification structure and method of using same - Google Patents
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JP3200773B2 - Purification structure and method of using same - Google Patents

Purification structure and method of using same

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Publication number
JP3200773B2
JP3200773B2 JP14302792A JP14302792A JP3200773B2 JP 3200773 B2 JP3200773 B2 JP 3200773B2 JP 14302792 A JP14302792 A JP 14302792A JP 14302792 A JP14302792 A JP 14302792A JP 3200773 B2 JP3200773 B2 JP 3200773B2
Authority
JP
Japan
Prior art keywords
purification structure
inflow chamber
inflow
water
closed
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
JP14302792A
Other languages
Japanese (ja)
Other versions
JPH0663576A (en
Inventor
千明 丹羽
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 Corp
Original Assignee
Shimizu Corp
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 Corp filed Critical Shimizu Corp
Priority to JP14302792A priority Critical patent/JP3200773B2/en
Publication of JPH0663576A publication Critical patent/JPH0663576A/en
Application granted granted Critical
Publication of JP3200773B2 publication Critical patent/JP3200773B2/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

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

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、海、河川、運河、湖沼
等の水を浄化する浄化構造物およびその使用方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a purification structure for purifying water such as seas, rivers, canals, lakes and marshes and a method of using the same.

【0002】[0002]

【従来の技術】従来、防災、流量制御等の目的で、石積
護岸、消波堤等の港湾構造物が設けられている。このよ
うな港湾構造物は、生物濾過、エアレーション作用等に
より、ある程度の水質浄化作用を有するものである。こ
の水質浄化作用は、構造物の表面に付着した微生物に依
存するところが大きい。しかしながら、前記従来の港湾
構造物は、要求される水質浄化能力を発揮できるほどの
微生物が付着する表面が存在しないので、海水浄化への
寄与は極めて限定されたものである。
2. Description of the Related Art Conventionally, port structures such as masonry embankments and breakwaters are provided for the purpose of disaster prevention, flow control, and the like. Such a harbor structure has a certain degree of water purification action by biological filtration, aeration and the like. This water purification action largely depends on microorganisms attached to the surface of the structure. However, the conventional port structure does not have a surface to which microorganisms adhere so as to exhibit the required water purification ability, and thus the contribution to seawater purification is extremely limited.

【0003】前記問題を解決するため本発明者らは、
海、河川、運河、湖沼等の水中に設けられる各種の構造
物において、壁間の領域に、生物膜を付着させる接触材
が充填されていると共に、上記壁、または壁間の上部を
封鎖する天端部に、開口部が設けられている水質浄化構
造物を提案した。(特願平1ー137298号)
[0003] In order to solve the above problem, the present inventors have:
In various structures provided in water, such as the sea, rivers, canals, and lakes, the area between the walls is filled with a contact material for attaching a biofilm, and the wall or the upper part between the walls is closed. A water purification structure with an opening at the top is proposed. (Japanese Patent Application No. 1-137298)

【0004】また、図7は、特願平2ー171925号
にて発明者らが提案した海水浄化構造物である。この海
水浄化構造物1は、半閉鎖性海域2の干潟3に設けら
れ、前記半閉鎖性海域2の海水を前記干潟3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1であって、前記干潟3に底面の位置が潮間帯の中等
水位以下となる池4を設け、前記干潟3にこの干潟3の
周辺海域5から前記池4の内部に海水を進入させるため
の透水性の導水路6を設け、当該導水路6の前記周辺海
域5側に天端の位置が潮間帯の中等水位以上の潜堤7を
設け、前記干潟3内にこの干潟3に海水を透過させるた
めに前記池4から前記周辺海域5に向って延びる複数の
配水路8を設けてなり、導水路6内には、砕石9…が充
填され、配水路8内には、礫10…が充填されたもので
ある。このような海水浄化構造物1によれば、導水路6
及び配水路8の透水性は干潟3と比較して非常に大きく
なり、導水路6及び配水路8の圧損は干潟3と比較して
著しく小さくなり、干潟3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3において海水交換量を
大きくとることができ、干潟3の浄化能力を著しく増加
させることができる。また、周辺海域5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。
FIG. 7 shows a seawater purification structure proposed by the present inventors in Japanese Patent Application No. 2-171925. The seawater purification structure 1 is provided in a tidal flat 3 in a semi-enclosed sea area 2, and the seawater purification structure 1 that purifies the water quality of the seawater by transmitting the seawater in the semi-enclosed sea area 2 through the tideland 3. A pond 4 whose bottom is located below the middle water level in the intertidal zone in the tidal flat 3, and a permeability for allowing seawater to enter the pond 4 from the sea area 5 around the tidal flat 3 to the tidal flat 3. A waterway 6 is provided, and a submerged bank 7 is provided on the side of the waterway 6 on the side of the surrounding sea area 5 at a top end at a middle water level or higher in the intertidal zone, and the seawater is transmitted through the tideland 3 into the tideland 3. For this purpose, a plurality of water distribution channels 8 extending from the pond 4 to the surrounding sea area 5 are provided, and crushed stones 9 are filled in the water channel 6 and gravel 10 is filled in the water distribution channel 8. It was done. According to such a seawater purification structure 1, the headrace 6
And the water permeability of the water distribution channel 8 becomes very large compared with the tidal flat 3, and the pressure loss of the water conveyance channel 6 and the water distribution channel 8 becomes extremely small as compared with the tidal flat 3, so that the entire tidal flat 3 can be an effective purification area. it can. Therefore, the amount of seawater exchange in the tidal flat 3 can be increased, and the purification capacity of the tidal flat 3 can be significantly increased. Further, by using the tidal force, which is the natural energy of the surrounding sea area 5, the water quality of the seawater can be purified efficiently and at low cost.

【0005】[0005]

【考案が解決しようとする課題】このような礫等の接触
材が充填された浄化構造物は、主に、接触沈殿作用、吸
着作用および酸化分解作用により浄化がなされるもので
ある。有機物を酸化分解することにより増殖する生物膜
は、厚くなると内部に酸素が届かなくなり、礫等の接触
材から剥離する。しかし、稚貝は、極く小さいときに接
触材間に入り込み接触材表面に固着し成育して、空隙を
徐々に塞いでいくものである。これは、水路等の始端部
において、顕著に起こり、特に代表径が小さい接触材、
空隙率が少ない接触材において著しい。始端部の空隙が
小さくなると、全体としての流量が減少し、浄化能力が
低下する。ところで、生活排水や産業排水の浄化処理に
おいて、接触材が目詰まりした場合には、空気曝気装置
や逆洗装置等を運転して処理空間内を洗浄していた。し
かし、生活排水や産業排水の浄化処理施設と比較して格
段に大形化する海水浄化構造物に、生活排水等の処理施
設で用いていた空気曝気装置や逆洗装置を設けると、処
理空間の洗浄を行うたびに莫大なコストがかかるという
問題がある。本発明は前記事情に鑑みてなされたもの
で、接触材の目詰まりを防止する浄化構造物およびその
使用方法を提供することを目的とする。
The purification structure filled with such a contact material as gravel is mainly purified by a contact settling action, an adsorption action and an oxidative decomposition action. When a biofilm that grows by oxidative decomposition of organic matter becomes thicker, oxygen does not reach the inside of the biofilm and peels off from a contact material such as gravel. However, juveniles enter between the contacting materials when they are extremely small, adhere to the surface of the contacting material, grow, and gradually close the voids. This occurs remarkably at the starting end of a water channel or the like, and particularly, a contact material having a small representative diameter.
It is remarkable in the contact material having a small porosity. When the gap at the start end is reduced, the overall flow rate is reduced, and the purification capacity is reduced. By the way, in the purification treatment of domestic wastewater or industrial wastewater, when the contact material is clogged, the inside of the treatment space is washed by operating an air aeration device, a backwashing device and the like. However, if a seawater purification structure, which is much larger than a domestic wastewater or industrial wastewater treatment facility, is equipped with an air aeration device or backwashing device used in a domestic wastewater treatment facility, the treatment space will be reduced. There is a problem that enormous cost is required for every cleaning. The present invention has been made in view of the above circumstances, and an object of the present invention is to provide a purification structure for preventing clogging of a contact material and a method of using the same.

【0006】[0006]

【課題を解決するための手段】前記課題を解決するため
に本発明の請求項1記載の浄化構造物は、水域から水を
導入し前記処理空間へと水を導出する流入室を有し、前
記処理空間内の水の流通を阻害する好気性生物を捕獲す
る濾材が前記流入室内に設けられ、該流入室の導入部お
よび導出部が開閉機構を具備してなるものである。
According to a first aspect of the present invention, there is provided a purification structure having an inflow chamber for introducing water from a body of water and leading out water to the treatment space. A filter medium for capturing aerobic organisms that hinders the flow of water in the treatment space is provided in the inflow chamber, and an introduction portion and an exit portion of the inflow chamber include an opening / closing mechanism.

【0007】前記課題を解決するために本発明の請求項
2記載の浄化構造物は、請求項1記載の浄化構造物の流
入室が複数設けられたものである。
According to a second aspect of the present invention, there is provided a purification structure having a plurality of inflow chambers for the purification structure according to the first aspect.

【0008】前記課題を解決するために本発明の請求項
3記載の浄化構造物の使用方法は、閉鎖した流入室内
に、還元剤を添加し、これにより閉鎖された流入室内を
嫌気状態とする方法である。
According to a third aspect of the present invention, there is provided a method of using a purifying structure, wherein a reducing agent is added to a closed inflow chamber, thereby making the closed inflow chamber anaerobic. Is the way.

【0009】前記課題を解決するために本発明の請求項
4記載の浄化構造物の使用方法は、閉鎖した流入室内
に、酸化剤を添加し、酸化剤の酸化作用によって流入室
内の生物を死滅させる方法である。
According to a fourth aspect of the present invention, there is provided a method for using a purification structure according to the present invention, wherein an oxidizing agent is added to a closed inflow chamber, and an organism in the inflow chamber is killed by an oxidizing action of the oxidizing agent. It is a way to make it.

【0010】前記課題を解決するために本発明の請求項
5記載の浄化構造物の使用方法は、請求項2記載の複数
の流入室の少なくとも一つを閉鎖状態として前記好気性
生物を死滅させる一方、他の流入室を流通状態として浄
化作用を継続させ、これら複数の各流入室を、選択的に
閉鎖状態、流通状態とする方法である。
According to a fifth aspect of the present invention, there is provided a method of using a purification structure according to the present invention, wherein at least one of the plurality of inflow chambers is closed to kill the aerobic organism. On the other hand, this is a method in which the purifying action is continued by setting the other inflow chambers to the flowing state, and these plural inflow chambers are selectively brought into the closed state and the flowing state.

【0011】[0011]

【作用】本発明の請求項1記載の浄化構造物によれば、
水域から水を導入し処理空間へ水を導出する流入室内
に、貝類等の生物を捕獲する濾材が設けられているの
で、浄化構造物内に流入した貝類等が前記濾材に付着
し、処理空間内に貝類等が流入するのを防止する。ま
た、濾材が粒径の大きい懸濁物質を濾材の上流側および
内部に留め、処理空間内に流入するのを防止する。
According to the purifying structure of the first aspect of the present invention,
In the inflow chamber for introducing water from the body of water and drawing out water to the treatment space, a filter medium for capturing living organisms such as shellfish is provided, so that the shellfish and the like flowing into the purification structure adhere to the filter medium, and the treatment space. Prevents shellfish, etc. from flowing into the interior. Further, the filter medium keeps the suspended substance having a large particle diameter on the upstream side and inside of the filter medium to prevent the suspended substance from flowing into the processing space.

【0012】本発明の請求項3記載の浄化構造物の使用
方法によれば、閉鎖された流入室内に還元剤を添加する
ので、溶存酸素が減少し流入室内が嫌気状態となり、流
入室の内部の貝類等が死滅する。
According to the method of using the purification structure according to the third aspect of the present invention, since the reducing agent is added to the closed inflow chamber, the dissolved oxygen decreases, the inflow chamber becomes anaerobic, and the inside of the inflow chamber is reduced. Shellfish etc. die.

【0013】本発明の請求項4記載の浄化構造物の使用
方法によれば、閉鎖された流入室内に酸化剤を添加する
ので、酸化作用によりこの流入室内の好気性生物が死滅
する。
According to the method of using the purification structure according to the fourth aspect of the present invention, since the oxidizing agent is added to the closed inflow chamber, the aerobic organisms in the inflow chamber are killed by the oxidizing action.

【0014】本発明の請求項5記載の浄化構造物の使用
方法によれば、複数の流入室の少なくとも一つを閉鎖状
態とするので、閉鎖された流入室内の水の溶存酸素が、
この流入室内の好気性生物により消費され、この流入室
内の水の溶存酸素濃度が低下する。また、栄養分が補給
されないので、この流入室の内部の貝類等が死滅する。
According to the method of using the purification structure according to the fifth aspect of the present invention, since at least one of the plurality of inflow chambers is closed, the dissolved oxygen in the water in the closed inflow chamber is:
It is consumed by aerobic organisms in the inflow chamber, and the dissolved oxygen concentration of water in the inflow chamber decreases. Further, since nutrients are not supplied, shells and the like inside the inflow chamber die.

【0015】[0015]

【実施例】以下、本発明の海水浄化構造物およびその使
用方法について、実施例によって詳しく説明する。図1
ないし図3は本発明の浄化構造物の一実施例を示す図で
あり、これらの図において符号11は浄化構造物であ
る。この浄化構造物11は、海域内に設置された水路型
のもので、浄化処理室12と、第一流入室13と、第一
流入室13に囲まれた連通路14と、連通路14と連通
した第二流入室15とからなるものである。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the seawater purification structure of the present invention and the method of using the same will be described in detail with reference to examples. FIG.
FIG. 3 to FIG. 3 are views showing one embodiment of the purification structure of the present invention. In these drawings, reference numeral 11 denotes a purification structure. The purification structure 11 is a water channel type installed in the sea area, and communicates with the purification treatment chamber 12, the first inflow chamber 13, the communication path 14 surrounded by the first inflow chamber 13, and the communication path 14. And a second inflow chamber 15.

【0016】浄化処理室12はその内部が処理空間12
aであり、この処理空間12aは、表面に生物膜が付着
した接触材16…が充填されたものである。この処理空
間では、主に生物膜による有機物の酸化分解により、海
水の浄化がなされるものである。接触材16…には、例
えば礫や砕石が用いられる。この浄化処理室12には、
流入側の端部に多孔板等の整流板17が取り付けられて
いる。
The purification processing chamber 12 has a processing space 12 inside.
a, and the processing space 12a is filled with contact materials 16 with a biofilm attached to the surface. In this processing space, seawater is purified mainly by oxidative decomposition of organic substances by a biofilm. For the contact members 16, for example, gravel or crushed stone is used. In this purification processing chamber 12,
A rectifying plate 17 such as a perforated plate is attached to the end on the inflow side.

【0017】整流板17の上流側には、第一流入室13
が設けられている。この第一流入室13は、整流板17
と対向する位置すなわち下流側端部に、開閉機構18a
を有した導出部18が備えられ、水域Aとの隔壁13a
に開閉機構19aを有した導入部19が備えられている
ものである。この第一流入室13は、その内部に圧損が
ほとんど生じないように濾材20…が配置されている。
The first inflow chamber 13 is provided upstream of the current plate 17.
Is provided. The first inflow chamber 13 is provided with a current plate 17
The opening / closing mechanism 18a
Is provided, and a partition 13a with the water area A is provided.
And an introduction section 19 having an opening / closing mechanism 19a. The first inflow chamber 13 is provided with the filter media 20 so as to cause almost no pressure loss therein.

【0018】濾材20は、図3に示すようにプラクチッ
ク製紐状体が絡み合った状態に形成された板体等であ
る。この濾材20は、その空隙率が90%以上となるよ
うに成形されたものである。
As shown in FIG. 3, the filter medium 20 is a plate or the like formed in a state in which a string of plastics is intertwined. The filter medium 20 is formed so that the porosity is 90% or more.

【0019】連通路14は、第一流入室13の中央部の
下に形成されたもので、導出部18とほぼ同じ位置に開
閉機構21aを有した導出部21を備えたものである。
この連通路14は、上流側の第二流入室15と連通して
おり、第二流入室15からの水を浄化処理室12へと送
るものである。
The communication passage 14 is formed below the center of the first inflow chamber 13 and has a lead-out portion 21 having an opening / closing mechanism 21a at substantially the same position as the lead-out portion 18.
The communication passage 14 communicates with the second inflow chamber 15 on the upstream side, and sends water from the second inflow chamber 15 to the purification processing chamber 12.

【0020】第二流入室15は、水域Aとの隔壁15a
に開閉機構22aを有した導入部22を備えたもので、
流入室15の内部には、第一流入室13と同様に接触材
20…が配置されている。
The second inflow chamber 15 has a partition wall 15a with the water area A.
And an introduction portion 22 having an opening / closing mechanism 22a.
Contact members 20 are arranged inside the inflow chamber 15 similarly to the first inflow chamber 13.

【0021】この濾材20…の配置は、図2に示すよう
に両壁面13a,13aに濾材20a,20aの一辺を
固定し下流方向に徐々間隔が狭くなるように配し、その
下流側に濾材20a,20aとやや間隔を置き、流れと
垂直方向に壁13a,13aと間隔を設けて濾材20b
を配する。そして、このような配置を流れ方向に連続さ
せる。圧損が生じないような配置は、流入室の大きさ等
に応じて例えば図4に示すように、前記図2に示した配
置を横方向に連続させたものとしてもよい。流入室1
3,15内の流速は、濾材20a,20a間の徐々に狭
まる流路の接触速度が50cm/sec以下で、かつ濾
材20の内部を通過する流速が10cm/sec以下と
するのが、稚貝が濾材20…に付着、補足されるのに、
好適である。
As shown in FIG. 2, the filter media 20 are arranged such that one side of the filter media 20a, 20a is fixed to both wall surfaces 13a, 13a, and the interval therebetween is gradually reduced in the downstream direction. 20a, 20a, a filter medium 20b is provided at a distance from the walls 13a, 13a in a direction perpendicular to the flow.
Distribute. Then, such an arrangement is continued in the flow direction. For example, as shown in FIG. 4, the arrangement shown in FIG. 4 may be such that the arrangement shown in FIG. Inflow chamber 1
The flow velocity in the filter media 3 and 15 is such that the contact velocity of the gradually narrowing flow path between the filter media 20a and 20a is 50 cm / sec or less and the flow velocity passing through the inside of the filter media 20 is 10 cm / sec or less. Is attached to and supplemented by the filter media 20 ...
It is suitable.

【0022】濾材は、上述の例に限られず、例えば図5
に示すようなプラクチック製紐状体が絡み合った状態の
棒状の成形体30で、その内部に長さ方向の孔30a…
が形成されたものなど、微生物が付着する表面積が大き
いものが適宜使用される。また、図6に示すようにその
周囲が金網40aで構成された長方形板体40で、移動
用フック40b,40bが取り付けられ、その内部にか
き殻等からなる粒状物質、ないしは前記プラスチック製
紐状体が絡み合った成型体ないしは他の成型体が充填さ
れたものでもよい。特にかき殻は、廃棄物を有効に利用
したものである。
The filter medium is not limited to the above-described example.
Is a rod-shaped molded body 30 in which a plastic lacing body is intertwined, and has a longitudinal hole 30a therein.
A material having a large surface area to which the microorganisms adhere, such as a product having a surface, is appropriately used. Further, as shown in FIG. 6, a rectangular plate 40 having a wire mesh 40a around the periphery thereof, to which moving hooks 40b, 40b are attached, and a granular material made of a squid or the like, or the plastic string It may be a molded body in which the bodies are entangled or filled with another molded body. In particular, oysters make effective use of waste.

【0023】次に、上記の構成からなる浄化構造物11
の使用方法および作用について説明する。まず、開放さ
れていた第一流入室13の導入部19および導出部18
を閉め、第二流入室15の導入部22および連通路14
の導出部21を開く。干満エネルギー等により、水域A
から導入部22を通って第二流入室15へと海水が流入
し、第二流入室15内を流下する。流入した海水は、濾
材20…により粒径の大きい懸濁物質が取り除かれ、砂
等が沈降する。また、濾材20…には、極く小さい稚貝
等が取り付き、固着成育する。この時、閉鎖された第一
流入室13内は、流入室13内の好気性微生物等によっ
て溶存酸素が消費され、10分から5時間でほぼ溶存酸
素がなくなる。溶存酸素がなくなると、濾材20…に付
着していた稚貝等は1日から3日で死滅する。
Next, the purification structure 11 having the above configuration
The method of use and the operation of the device will be described. First, the inlet 19 and outlet 18 of the first inflow chamber 13 that have been opened.
Is closed, the introduction portion 22 of the second inflow chamber 15 and the communication passage 14 are closed.
Is opened. Water area A due to tidal energy
The seawater flows into the second inflow chamber 15 through the introduction part 22 and flows down in the second inflow chamber 15. From the inflowing seawater, suspended substances having a large particle diameter are removed by the filter medium 20 and sand and the like settle. In addition, extremely small juvenile shellfish and the like attach to the filter media 20 and grow firmly. At this time, dissolved oxygen is consumed in the closed first inflow chamber 13 by aerobic microorganisms and the like in the inflow chamber 13, and almost no dissolved oxygen is consumed in 10 minutes to 5 hours. When the dissolved oxygen is exhausted, the larvae attached to the filter media 20 die in one to three days.

【0024】所定期間後、第一流入室13の導入部19
および導出部18を開け、第二流入室15の導入部22
および連通路14の導出部21を閉めて、第一流入室1
3へ海水を流入させる。第一流入室13と第二流入室1
5との作用は、上述の作用と同様のものとなる。このよ
うにして流入室の一方を閉鎖し、他方を流通させて使用
し、所定期間毎に切り換える。この切り換えは、冬期に
おいては、10日から1箇月、春から秋期においては1
週間から10日間毎が適当である。
After a predetermined period, the introduction section 19 of the first inflow chamber 13
And the outlet section 18 is opened, and the introduction section 22 of the second inflow chamber 15 is opened.
And the outlet 21 of the communication passage 14 is closed, and the first inflow chamber 1 is closed.
3 Inlet seawater. First inflow chamber 13 and second inflow chamber 1
The action with 5 is similar to the action described above. In this way, one of the inflow chambers is closed, and the other is used while flowing, and is switched at predetermined intervals. This switch is from 10 days to 1 month in winter and 1 switch from spring to autumn.
Every week to every 10 days is appropriate.

【0025】閉鎖された流入室13,15内の溶存酸素
量の低下速度は、濾材20…の配置や生物膜の付着量に
より異なる。この速度を速くするには、水域Aを汚染し
ない還元剤、例えば亜硫酸ナトリウムを、流入室内の水
1m3当り90g程度添加することが効果的である。
The rate of decrease in the amount of dissolved oxygen in the closed inflow chambers 13 and 15 differs depending on the arrangement of the filter media 20 and the amount of the attached biofilm. To increase the speed, it is effective to add a reducing agent that does not contaminate the water area A, for example, sodium sulfite in an amount of about 90 g per 1 m 3 of water in the inflow chamber.

【0026】あるいは、閉鎖された流入室13,15内
に、次亜塩素酸ナトリウム等の殺傷性がありかつ水域A
を汚染しない塩素剤等の酸化剤を、有効塩素濃度5mg
/l〜10mg/l添加し、貝類および生物膜の微生物を
同時に死滅させる。
Alternatively, in the closed inflow chambers 13 and 15, there is a water killing area such as sodium hypochlorite and water A
Oxidizing agents such as chlorine agents that do not pollute the effective chlorine concentration 5mg
/ l to 10 mg / l to kill both shellfish and biofilm microorganisms at the same time.

【0027】以上のような本実施例の浄化構造物11に
よれば、処理空間12a内に稚貝等が流入しないので接
触材間の空隙が稚貝等の固着成育により塞がれることが
ない。また、濾材20…の濾過作用により粒径の大きい
有機物および無機物が前記処理空間に流入することが少
なく、また砂等の沈降性のものが、流入室内で沈降する
ので処理室内に沈殿することが少ない。そのため、接触
材間の空隙が塞がれることがなく、透水性が低下せず、
高い処理能力を維持する浄化構造物となる。また、長期
間使用し、濾材20…が目詰まりした場合には、この濾
材20…を取り外して洗浄することができる。
According to the purification structure 11 of the present embodiment as described above, juveniles and the like do not flow into the processing space 12a, so that the gap between the contact materials is not blocked by the growth of the immobilized juveniles. . Further, the organic substance and the inorganic substance having a large particle diameter rarely flow into the processing space due to the filtering action of the filter media 20. In addition, sedimentable substances such as sand settle down in the inflow chamber, so that they may precipitate in the processing chamber. Few. Therefore, the gap between the contact materials is not closed, the water permeability does not decrease,
It becomes a purification structure that maintains a high processing capacity. Further, when the filter media 20 are clogged after being used for a long time, the filter media 20 can be removed and washed.

【0028】なお、上記実施例は水路型の浄化構造物で
あるが、本発明は水路型に限定されるものではない。例
えば、微生物の付着面積を大きくするために接触材を使
用したケーソン型仕切堤、防波堤および消波構造物等に
適用可能である。また、本発明の浄化構造物は、海域の
浄化に限定されるものではなく、河川、運河、湖沼等の
水域を浄化するものである。
Although the above-described embodiment is a channel-type purification structure, the present invention is not limited to the channel type. For example, the present invention is applicable to caisson-type partition walls, breakwaters, wave-dissipating structures, and the like that use a contact material in order to increase the adhesion area of microorganisms. Further, the purification structure of the present invention is not limited to purification of sea areas, but purifies water bodies such as rivers, canals, lakes and marshes.

【0029】[0029]

【発明の効果】本発明の請求項1記載の浄化構造物によ
れば、水域から水を導入し処理空間へ水を導出する流入
室内に、貝類等の生物を捕獲する濾材が設けられている
ので、浄化構造物内に流入した貝類等の生物が前記濾材
に付着し、処理空間内に貝類等の生物が流入するのを防
止する。また、濾材が粒径の大きい懸濁物質を濾材の上
流側および内部に留め、処理空間内に流入するのを防止
する。また、流入室内には砂等の沈降性のものが沈殿す
る。このため、接触材間の空隙が塞がれることがなく、
処理空間が目詰まりしないものである。そのため、長期
にわたって高い処理能力を有する。
According to the purifying structure of the first aspect of the present invention, a filter medium for capturing organisms such as shellfish is provided in an inflow chamber for introducing water from a water area and extracting water to a treatment space. Therefore, organisms such as shellfish that have flowed into the purification structure adhere to the filter medium, and prevent organisms such as shellfish from flowing into the processing space. Further, the filter medium keeps the suspended substance having a large particle diameter on the upstream side and inside of the filter medium to prevent the suspended substance from flowing into the processing space. In addition, sedimentable substances such as sand settle in the inflow chamber. For this reason, the gap between the contact materials is not closed,
The processing space is not clogged. Therefore, it has a high processing capability over a long period.

【0030】本発明の請求項3記載の浄化構造物の使用
方法によれば、閉鎖された流入室内に還元剤を添加する
ので、流入室内の水の溶存酸素が減少し嫌気状態とな
り、流入室内の貝類等が死滅する。そのため、処理空間
内に充填された接触材に貝等が固着し成育することがな
く、処理空間が目詰まりしない。
According to the method of using the purification structure according to the third aspect of the present invention, since the reducing agent is added to the closed inflow chamber, the dissolved oxygen in the water in the inflow chamber is reduced to be in an anaerobic state, so that the inflow chamber becomes anaerobic. Shellfish etc. die. Therefore, shellfish and the like do not adhere to and grow on the contact material filled in the processing space, and the processing space is not clogged.

【0031】本発明の請求項4記載の浄化構造物の使用
方法によれば、閉鎖された流入室内に酸化剤を添加する
ので、酸化作用によりこの流入室内の生物が死滅する。
そのため、下流側の処理空間内に生きている貝類等が流
入することがない。そのため、処理空間内の接触材に貝
等が固着し成育することがなく、処理空間が目詰まりし
ない。
According to the method of using the purification structure according to the fourth aspect of the present invention, since the oxidizing agent is added to the closed inflow chamber, organisms in the inflow chamber are killed by the oxidizing action.
Therefore, live shellfish and the like do not flow into the downstream processing space. Therefore, shellfish and the like do not adhere to the contact material in the processing space and grow, and the processing space is not clogged.

【0032】本発明の請求項5記載の浄化構造物の使用
方法によれば、複数の流入室の少なくとも一つを閉鎖状
態とする一方、他の流入室を流通状態として浄化作用を
継続させるので、閉鎖状態の流入室内の水の溶存酸素が
低下し、この流入室の内部の貝類が死滅する。そのた
め、処理空間内に充填された接触材に貝等が固着し成育
することがなく、処理空間が目詰まりしない。また、逆
洗のように浄化処理を一時停止することなく、継続的に
浄化処理を行い、浄化処理と同時に貝類等を死滅させる
ことができる。また、複数の各流入室を、選択的に閉鎖
状態、流通状態とするので、適切な期間毎に切り換える
ことができる。
According to the method of using the purification structure according to the fifth aspect of the present invention, at least one of the plurality of inflow chambers is closed, while the other inflow chambers are in the flow state to continue the purification action. Then, the dissolved oxygen in the water in the closed inflow chamber decreases, and the shells inside the inflow chamber die. Therefore, shellfish and the like do not adhere to and grow on the contact material filled in the processing space, and the processing space is not clogged. In addition, the purifying process can be continuously performed without temporarily stopping the purifying process as in the case of the backwashing, and shellfish and the like can be killed simultaneously with the purifying process. In addition, since each of the plurality of inflow chambers is selectively brought into the closed state and the circulation state, it can be switched at appropriate intervals.

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

【図1】本発明の浄化構造物の一実施例を示す平面図で
ある。
FIG. 1 is a plan view showing one embodiment of a purification structure of the present invention.

【図2】図1に示した浄化構造物の流入室内を示す平面
図である。
FIG. 2 is a plan view showing an inflow chamber of the purification structure shown in FIG.

【図3】図2に示した濾材の斜視図である。FIG. 3 is a perspective view of the filter medium shown in FIG. 2;

【図4】流入室内の他の実施例を示す平面図である。FIG. 4 is a plan view showing another embodiment of the inflow chamber.

【図5】濾材の他の実施例を示す斜視図である。FIG. 5 is a perspective view showing another embodiment of the filter medium.

【図6】濾材の他の実施例を示す斜視図である。FIG. 6 is a perspective view showing another embodiment of the filter medium.

【図7】従来の浄化構造物の一例を示す断面図である。FIG. 7 is a cross-sectional view showing an example of a conventional purification structure.

【符号の説明】[Explanation of symbols]

11 浄化構造物 12 浄化処理室 12a 処理空間 13 第一流入室 15 第二流入室 16 接触材 18 導出部 18a 開閉機構 19 導入部 19a 開閉機構 20 濾材 21 導出部 21a 開閉機構 22 導入部 22a 開閉機構 A 水域 DESCRIPTION OF SYMBOLS 11 Purification structure 12 Purification processing chamber 12a Processing space 13 First inflow chamber 15 Second inflow chamber 16 Contact material 18 Outlet 18a Opening / closing mechanism 19 Introducing section 19a Opening / closing mechanism 20 Filter medium 21 Outgoing section 21a Opening / closing mechanism 22 Introducing section 22a Opening / closing mechanism A Body of water

Claims (5)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 海、河川、運河、湖沼等の水域を浄化す
るものであり、生物膜が付着した接触材が充填された処
理空間を有する浄化構造物であって、 前記水域から水を導入し前記処理空間へと水を導出する
流入室を有し、この流入室内に前記処理空間内の水の流
通を阻害する好気性生物を捕獲する濾材が設けられ、該
流入室の導入部および導出部が開閉機構を具備してなる
ことを特徴とする浄化構造物。
1. A purification structure for purifying a water area such as a sea, a river, a canal, a lake, or a marsh, having a treatment space filled with a contact material to which a biofilm is attached, and introducing water from the water area. And a filter medium for capturing aerobic organisms that hinders the flow of water in the processing space is provided in the inflow chamber, and an inlet and an outlet for the inflow chamber are provided. A purification structure, characterized in that the part comprises an opening / closing mechanism.
【請求項2】 請求項1記載の浄化構造物において、 前記流入室が複数設けられていることを特徴とする浄化
構造物。
2. The purification structure according to claim 1, wherein a plurality of the inflow chambers are provided.
【請求項3】 請求項1記載の浄化構造物の使用方法で
あって、 閉鎖した流入室内に還元剤を添加し、これにより閉鎖さ
れた流入室内を嫌気状態とすることを特徴とする浄化構
造物の使用方法。
3. The method for using a purification structure according to claim 1, wherein a reducing agent is added to the closed inflow chamber, thereby bringing the closed inflow chamber into an anaerobic state. How to use things.
【請求項4】 請求項1記載の浄化構造物の使用方法で
あって、 閉鎖した流入室内に酸化剤を添加し、酸化作用により生
物を死滅させることを特徴とする浄化構造物の使用方
法。
4. The method for using a purification structure according to claim 1, wherein an oxidizing agent is added to the closed inflow chamber, and an organism is killed by an oxidizing action.
【請求項5】 請求項2記載の浄化構造物の使用方法で
あって、 前記複数の流入室の少なくとも一つを閉鎖状態として前
記好気性生物を死滅させる一方、他の流入室を流通状態
として浄化作用を継続させ、これら複数の各流入室を、
選択的に閉鎖状態、流通状態とすることを特徴とする浄
化構造物の使用方法。
5. The method of using the purification structure according to claim 2, wherein at least one of the plurality of inflow chambers is closed to kill the aerobic organisms, and the other inflow chambers are in circulation. The purifying action is continued, and each of the plurality of inflow chambers is
A method for using a purification structure, wherein the purification structure is selectively closed or distributed.
JP14302792A 1992-06-03 1992-06-03 Purification structure and method of using same Expired - Fee Related JP3200773B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14302792A JP3200773B2 (en) 1992-06-03 1992-06-03 Purification structure and method of using same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14302792A JP3200773B2 (en) 1992-06-03 1992-06-03 Purification structure and method of using same

Publications (2)

Publication Number Publication Date
JPH0663576A JPH0663576A (en) 1994-03-08
JP3200773B2 true JP3200773B2 (en) 2001-08-20

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ID=15329209

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14302792A Expired - Fee Related JP3200773B2 (en) 1992-06-03 1992-06-03 Purification structure and method of using same

Country Status (1)

Country Link
JP (1) JP3200773B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100443419C (en) * 2006-08-28 2008-12-17 王宝贞 On-site comprehensive purification method of polluted water body

Also Published As

Publication number Publication date
JPH0663576A (en) 1994-03-08

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