JPH0929277A - Device for purifying quality of water of river - Google Patents

Device for purifying quality of water of river

Info

Publication number
JPH0929277A
JPH0929277A JP7202874A JP20287495A JPH0929277A JP H0929277 A JPH0929277 A JP H0929277A JP 7202874 A JP7202874 A JP 7202874A JP 20287495 A JP20287495 A JP 20287495A JP H0929277 A JPH0929277 A JP H0929277A
Authority
JP
Japan
Prior art keywords
water
septic tank
river
pool
weir
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.)
Pending
Application number
JP7202874A
Other languages
Japanese (ja)
Inventor
Yoshiki Taki
善樹 滝
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.)
B BAI B KK
Original Assignee
B BAI B KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by B BAI B KK filed Critical B BAI B KK
Priority to JP7202874A priority Critical patent/JPH0929277A/en
Publication of JPH0929277A publication Critical patent/JPH0929277A/en
Pending 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

Abstract

PROBLEM TO BE SOLVED: To provide a device in which quality of water can be surely purified, and faclities can be easily protected and maintained in the case of a flood and sludge can be handled by installing the device on a river bed. SOLUTION: A closed biofilm purifying tank 2 is installed in a pool provided on a river bed and a variable weir 3 is provided downstream of the pool 1 so that the water level of the pool 1 can be made higher than a usual water level of rivers, and a flow-in port 12 is provided downstream of the biofilm purifying tank 2 and a flow-out pipe of purified water is provided upstream of the tank 2, and a delivery port 15 of a water transfer pipe 14 connected to the flow-out pipe is provided downstream of the weir 3 so as to be opened to a position lower than the water level on upstream side of the weir 3.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は都市河川等の水を浄
化する浄化装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a purifying device for purifying water from an urban river or the like.

【0002】[0002]

【従来の技術】最近、都市河川の生活雑排水による汚濁
の進行は顕著であるため浄化の必要が進められつつあ
る。これに対応した従来の浄化施設は陸上に設置され、
いったん河川水を汲み上げて施設で浄化した後に河川に
放流する方式のものが一般的である。しかし、都市部で
は特に浄化施設を設置する敷地の確保が困難であるほ
か、浄化に要するエネルギーコストが大きく、また管理
も面倒であった。
2. Description of the Related Art Recently, since the progress of pollution due to domestic wastewater from urban rivers is remarkable, the need for purification is being promoted. The conventional purification facility corresponding to this is installed on land,
In general, the method of pumping up the river water, purifying it at the facility, and then discharging it into the river is common. However, in urban areas, it is particularly difficult to secure a site for installing a purification facility, the energy cost required for purification is large, and management is troublesome.

【0003】このため、河川床上に直接に浄化施設を設
置することも試みられた。
Therefore, it has been attempted to install a purification facility directly on the river floor.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、従来の
河川の直接の直接浄化方式は、各種の接触炉材がむき出
しであるため、土砂等による埋没、損傷があり、修復に
労力を要するという問題があるほか、河川床に大きなス
ペースが必要であり、流速をコントロ−ル出来ないため
も水質が不安定になる等の欠点があった。
However, in the conventional direct direct purification method for rivers, since various contact furnace materials are exposed, there is a problem that there is burial and damage due to earth and sand, etc., and labor is required for restoration. In addition, a large space is required on the river bed, and the flow velocity cannot be controlled, so that the water quality becomes unstable.

【0005】本発明は前記問題点を解消し、河床に設置
することにより確実な水質浄化、洪水時の施設の保護、
維持管理の容易性と汚泥処理ができる河川等の水質浄化
装置をその課題とする。
The present invention solves the above-mentioned problems and, by installing it on the riverbed, ensures water purification, protects facilities during floods,
The subject is a water purification device for rivers that is easy to maintain and manage sludge.

【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、本発明に係る河川等の水質浄化装置は、河川床に設
けたプール内に密閉した生物膜浄化槽を設置し、プール
の下流側にはプール上の水位を河川等の通常時の水位よ
り高くできる可変堰を設け、流入口を浄化槽の下流側
に、浄化された水の流出口管を浄化槽の上流側に設け、
流出口に接続した送水管の吐出口を上記可変堰の下流側
でかつ可変堰の上流側の水位よりも低い位置に開口させ
たことを特徴とする。
In order to solve the above-mentioned problems, a water purification apparatus for a river or the like according to the present invention has a closed biofilm septic tank in a pool provided on a river bed, and is installed downstream of the pool. Is equipped with a variable weir that allows the water level above the pool to be higher than the normal water level of rivers, etc., with an inlet on the downstream side of the septic tank and an outlet pipe for purified water on the upstream side of the septic tank.
The discharge port of the water supply pipe connected to the outflow port is opened at a position lower than the water level on the downstream side of the variable weir and on the upstream side of the variable weir.

【0007】なお、前記堰の上流域・下流域の水位差と
前記送水管の径とにより一定水量が前記浄化槽施設を通
過して前記吐出口より放流するのが好ましい。
It is preferable that a constant amount of water is discharged from the discharge port after passing through the septic tank facility due to the difference in water level between the upstream and downstream regions of the weir and the diameter of the water supply pipe.

【0008】[0008]

【発明の実施の形態】図1、図2及び図3は水質浄化装
置を示すもので、この浄化装置は河川床に設けたプール
1とその内側に設置された生物膜浄化槽2と可変堰3と
から構成されている。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIGS. 1, 2 and 3 show a water purification device, which comprises a pool 1 installed on a river bed, a biofilm purification tank 2 and a variable weir 3 installed inside the pool 1. It consists of and.

【0009】プール1は河川床面を掘削して形成する。
プール1内には密閉した生物膜浄化槽2を設置するとと
もに、この浄化槽2と可変堰3との間には壁4を形成し
て沈砂部5を設ける。河川床はPC板6で被覆する。
The pool 1 is formed by excavating the river floor.
A closed biofilm septic tank 2 is installed in the pool 1, and a sand 4 is formed by forming a wall 4 between the septic tank 2 and the variable weir 3. The river bed is covered with a PC board 6.

【0010】可変堰3はエアを出し入れたりゲートを起
倒したりして必要時に河川の水を堰3止めるラバーダム
や転倒式ゲート等を利用すればよい。これにより、プー
ル1の下流側にはプール1上の水位を河川等の通常時の
水位より高くすることができる。降雨時等には可変堰3
を調整操作し、可変堰3の上流域と下流域の水位差を無
くする。
The variable weir 3 may be a rubber dam, a tumbling type gate or the like for stopping the weir 3 from the river when air is taken in and out or the gate is raised and lowered. As a result, the water level above the pool 1 on the downstream side of the pool 1 can be made higher than the normal water level of a river or the like. Variable weir 3 when it rains
Is adjusted to eliminate the water level difference between the upstream region and the downstream region of the variable weir 3.

【0011】生物膜浄化槽2は、密閉されたコンクリー
ト製の箱体7内にFRP製のカゴ8などの適宜の手段に
よって多数の接触濾材9を吊下げ状態で収容したもの
で、河川の汚染度合いに応じて1基又は複数基設置す
る。なお、箱体7は保守等のため開閉できるように構成
するのが好ましい。
The biofilm septic tank 2 contains a large number of contact filter media 9 suspended in a closed concrete box body 7 by an appropriate means such as a FRP basket 8 and the like. Depending on the situation, one or more units will be installed. The box 7 is preferably constructed so that it can be opened and closed for maintenance or the like.

【0012】接触濾材9としては、例えば特願平6−1
92942号に示されるものと同様、レーヨン、コット
ン、ポリエチレン、ポリプロピレンなどの繊維よりなる
多孔質の不織布の表面に、ハロゲン化されたピリジニウ
ム基を分子内に有する不溶性ピリジニウム型樹脂をコー
ティング処理して断面星形の紐又は短冊状に形成したも
のを利用すればよい。
The contact filter medium 9 is, for example, Japanese Patent Application No. 6-1.
Similar to the one shown in No. 92942, the surface of a porous non-woven fabric made of fibers such as rayon, cotton, polyethylene, polypropylene, etc. is coated with an insoluble pyridinium type resin having a halogenated pyridinium group in the molecule to form a cross section. A star-shaped string or a strip-shaped one may be used.

【0013】各生物膜浄化槽2の底部には十分な大きさ
の汚泥貯留部10が形成されている。底部の前後の壁に
は汚泥を除去処理するための開閉部11が設けられてい
る。なお、開閉部11に代えて底部に一定間隔に引き抜
き管(図示せず)を設ける構成でもよい。
A sludge storage section 10 having a sufficient size is formed at the bottom of each biofilm purification tank 2. Opening / closing sections 11 for removing sludge are provided on the front and rear walls of the bottom. It should be noted that instead of the opening / closing portion 11, a configuration may be adopted in which pull-out pipes (not shown) are provided on the bottom portion at regular intervals.

【0014】次に、上記各生物膜浄化槽2の流入口12
は浄化槽の下流側に、浄化された水の流出口13は浄化
槽2の上流側に設けられている。そして、各流出口13
から連結接続された送水管14は地中に埋設され、その
吐出口15は上記可変堰3の下流側でかつ可変堰3の上
流側の水位よりも低い位置に開口している。
Next, the inflow port 12 of each biofilm septic tank 2 described above.
Is provided on the downstream side of the septic tank, and the purified water outlet 13 is provided on the upstream side of the septic tank 2. And each outlet 13
The water supply pipe 14 connected and connected to is buried in the ground, and its discharge port 15 is opened at a position lower than the water level on the downstream side of the variable weir 3 and on the upstream side of the variable weir 3.

【0015】ここで、前記構成の水質浄化装置の作動に
ついて説明すると、プール1上に溜った水の水位は可変
堰3によりその下流域の水位よりも高くなる。そのた
め、浄化槽内の水は送水管14から引き抜かれて下流域
に放流されるので、浄化槽2の流入口12から水が導入
される。これにより可変堰3の上流域の水は浄化槽の下
流側の流入口12から供給されてから浄化槽内を通過し
た後、上流側の流出口13から送水管14を通って吐出
口15に流れる。
The operation of the water purification apparatus having the above structure will now be described. The water level of the water accumulated on the pool 1 becomes higher than the water level in the downstream region by the variable weir 3. Therefore, the water in the septic tank is drawn out from the water supply pipe 14 and discharged to the downstream region, so that the water is introduced from the inflow port 12 of the septic tank 2. As a result, the water in the upstream region of the variable weir 3 is supplied from the inflow port 12 on the downstream side of the septic tank, passes through the septic tank, and then flows from the outflow port 13 on the upstream side to the discharge port 15 through the water supply pipe 14.

【0016】なお、河川水は可変堰3の上下流域の水位
差と送水管14の径により一定水量が浄化槽を通過する
ように設定される。
The river water is set so that a constant amount of water passes through the septic tank depending on the water level difference between the upstream and downstream regions of the variable weir 3 and the diameter of the water pipe 14.

【0017】ところで、河川水が流入口12から浄化槽
の内部に一定速度で連続的に通水されると、表面積の大
きい接触濾材9に大量の微生物が固定化され、バイオマ
スが形成される。そして、河川水に含まれる有機物等の
固型物は接触濾材9上に吸着、捕捉され、生物膜を形成
する細菌を始めとする微生物群(原生動物、微小後生動
物等)の栄養源として摂取される。したがって、生物膜
槽は流入側では主として好気的である。
By the way, when river water is continuously passed through the inflow port 12 into the septic tank at a constant rate, a large amount of microorganisms are immobilized on the contact filter medium 9 having a large surface area to form biomass. Then, solid matter such as organic matter contained in river water is adsorbed and captured on the contact filter medium 9 and ingested as a nutrient source for microorganism groups (protozoa, micro metazoa, etc.) including bacteria forming a biofilm. To be done. Therefore, the biofilm tank is predominantly aerobic on the inflow side.

【0018】水の流下に従い溶存酸素は消耗され、生物
膜槽は徐々に嫌気的に変化していく。バイオマスが大と
なると、溶存酸素も盛んに消耗されるため、嫌気的な微
生物環境が恒常的に保たれる。したがって、生物膜槽の
中央から流出側にかけては必然的に嫌気的微生物環境が
創出される。
Dissolved oxygen is consumed as water flows down, and the biofilm tank gradually changes anaerobically. When the biomass becomes large, the dissolved oxygen is also exhausted so that the anaerobic microbial environment is constantly maintained. Therefore, an anaerobic microbial environment is inevitably created from the center of the biofilm tank to the outflow side.

【0019】このように、流入側では主に硝化と酸化分
解を行なう微生物が、流出側では主に脱窒を行なう脱窒
菌が集積、固定されるから、生物膜槽の前半においては
有機物の好気的分解と硝化作用が、後半においては嫌気
的微生物環境の形成と脱窒作用が行われ、流入した河川
水は生物膜の生分解作用により浄化されて流出口13か
ら送水管14を通って吐出口15から可変堰3の下流側
に放流される。
As described above, microorganisms mainly nitrifying and oxidatively decomposing on the inflow side and denitrifying bacteria mainly denitrifying on the outflow side are accumulated and fixed. Air decomposition and nitrification are performed, and in the latter half, formation of an anaerobic microbial environment and denitrification are performed, and the inflowing river water is purified by biodegradation of biofilm, and flows from the outlet 13 through the water pipe 14. It is discharged from the discharge port 15 to the downstream side of the variable weir 3.

【0020】また、浄化槽2を通過した水の汚濁物質は
生物膜によって生分解され浄化されて送水されるが、そ
の一部は生物膜から剥離して汚泥となって汚泥貯留部1
0に沈殿する。沈殿した汚泥は、洪水時に底部の前後の
開閉部11を同時に連動して開放させることによりフラ
ッシュアウトし、回収した汚泥は乾燥後堆肥として畑地
に還元すればよい。引き抜き管が設けられている場合は
引き抜きによって槽外に排出する。
Further, the pollutants of the water passing through the septic tank 2 are biodegraded by the biofilm, purified and sent, but a part thereof is separated from the biofilm and becomes sludge to form a sludge storage section 1.
Precipitates to 0. The sludge that has settled may be flushed out by simultaneously opening and closing the opening / closing sections 11 at the bottom of the bottom during flooding, and the collected sludge may be dried and returned to the field as compost. If a drawing pipe is provided, discharge it outside the tank by drawing.

【0021】さらに、浄化槽の流入口12は下流側に設
けられているため、河川に含まれる泥、砂、ゴミ、SS
物質や固形物は沈砂部5に沈殿し、浄化槽への流入は規
制される。沈殿物は定期的に除去すればよい。
Furthermore, since the inflow port 12 of the septic tank is provided on the downstream side, mud, sand, dust, SS contained in the river
Substances and solids settle in the sand settling section 5 and their inflow into the septic tank is regulated. The precipitate may be removed regularly.

【0022】なお、大雨等洪水時には可変堰3の高さを
下げ調整して上下流の水位を等しくする。これにより可
変堰3の上流域と下流域との水位差がなくなるから、送
水管14による吸水力は失われ、浄化槽内の水流は自動
的に停止する。
In the case of heavy rain or the like, the height of the variable weir 3 is lowered and adjusted so that the water levels in the upstream and downstream are equal. As a result, the water level difference between the upstream region and the downstream region of the variable weir 3 disappears, so the water absorption capacity of the water supply pipe 14 is lost, and the water flow in the septic tank automatically stops.

【0023】上述のように、上記構成の水質浄化装置に
よれば次のような効果が得られる。 (1) 浄化施設本体である生物膜生物膜浄化槽2は河床よ
り下にあるため、河川床上のスペースを必要としないと
ともに、生物膜浄化槽2が洪水時等においても治水上の
支障にはならない。 (2) 生物膜浄化槽2の流入口12は下流側に設けられて
いるため、河川に含まれる泥、砂、ゴミ、SS物質や固
形物は沈砂部5に沈殿し、生物膜浄化槽2へ流入は規制
される。従って生物膜槽の閉塞を少なくすることができ
る。 (3) 生物膜法による水質浄化は汚泥負荷によって接触ス
ピードと距離(滞留時間)を設定することによって一定
の水質浄化を行うものであり、処理水量に合わせた施設
容積を設定できる。通常の流速は0.5cm/s以下程
度に設計するのが好ましい。 (4) 可変堰3の上下流域の水位差により生物膜浄化槽2
内に河川水を通過させ、生物膜によって水質を浄化する
方式であるから、原則としてポンプ等の電気エネルギー
を消費しない。 (5) 生物膜浄化槽2は密閉されているから、人目に触れ
ることがなく、臭気や害虫等の発生の心配もない。 (6) 可変堰3の高さ調整により生物膜浄化槽2内の水流
を自動的にストップすることができるから、洪水時等に
生物膜浄化槽2内に土砂等が流入することがなく、生物
膜浄化槽2の損傷を防ぐことができる。 (7) 汚泥は生物膜浄化槽2の内部に貯留するので処理が
楽である。 (8) 維持管理が非常に楽で、その費用も非常に低くて済
む。
As described above, the following effects can be obtained by the water purification device having the above structure. (1) The biofilm biofilm septic tank 2, which is the main body of the septic facility, is below the riverbed, so it does not require space on the riverbed, and the biofilm septic tank 2 does not hinder flood control even in the event of a flood. (2) Since the inflow port 12 of the biofilm septic tank 2 is provided on the downstream side, mud, sand, dust, SS substances and solids contained in the river settle in the sand settling section 5 and flow into the biofilm septic tank 2. Is regulated. Therefore, clogging of the biofilm tank can be reduced. (3) The water purification by the biofilm method purifies water to a certain extent by setting the contact speed and distance (residence time) depending on the sludge load, and the facility volume can be set according to the amount of treated water. The normal flow rate is preferably designed to be about 0.5 cm / s or less. (4) Due to the water level difference between the upstream and downstream of the variable weir 3, the biofilm septic tank 2
In principle, it does not consume electric energy such as pumps because it is a system that allows river water to pass through and clean the water quality with a biofilm. (5) Since the biofilm septic tank 2 is hermetically closed, it is not exposed to the eyes and there is no concern about the generation of odors or harmful insects. (6) The water flow in the biofilm septic tank 2 can be automatically stopped by adjusting the height of the variable weir 3, so that sediment and the like will not flow into the biofilm septic tank 2 in the event of a flood, etc. It is possible to prevent the septic tank 2 from being damaged. (7) Sludge is stored inside the biofilm septic tank 2 so that it is easy to process. (8) Maintenance is very easy and its cost is very low.

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

【図1】本発明に係る河川等の水質浄化装置の全体図FIG. 1 is an overall view of a water purification device for rivers according to the present invention.

【図2】上記浄化装置の縦断面図FIG. 2 is a vertical sectional view of the purification device.

【図3】上記浄化装置の平面図FIG. 3 is a plan view of the purification device.

【符号の説明】[Explanation of symbols]

1 プール 2 生物膜浄化槽 3 可変堰 12 流入口 13 流出口 14 送水管 15 吐出口 1 pool 2 biofilm septic tank 3 variable weir 12 inflow port 13 outflow port 14 water pipe 15 discharge port

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 河川床に設けたプール内に密閉した生物
膜浄化槽を設置し、プールの下流側にはプール上の水位
を河川等の通常時の水位より高くできる可変堰を設け、
水の流入口を浄化槽の下流側に、浄化された水の流出口
を浄化槽の上流側に設け、流出口に接続した送水管の吐
出口を上記可変堰の下流側でかつ可変堰の上流側の水位
よりも低い位置に開口させたことを特徴とする河川等の
水質浄化装置。
1. A sealed biofilm septic tank is installed in a pool provided on a river bed, and a variable weir is provided on the downstream side of the pool so that the water level above the pool can be higher than the normal water level of a river or the like.
The water inlet is provided on the downstream side of the septic tank, the purified water outlet is provided on the upstream side of the septic tank, and the outlet of the water pipe connected to the outlet is on the downstream side of the variable weir and on the upstream side of the variable weir. A water purification device for rivers, which is opened at a position lower than the water level of.
【請求項2】 前記堰の上流域・下流域の水位差と前記
送水管の径とにより一定水量が前記浄化槽施設を通過し
て前記吐出口より放流されるようにした請求項1記載の
河川等の水質浄化装置。
2. The river according to claim 1, wherein a constant amount of water passes through the septic tank facility and is discharged from the discharge port depending on the difference in water level between the upstream and downstream regions of the weir and the diameter of the water pipe. Water purification equipment such as.
JP7202874A 1995-07-17 1995-07-17 Device for purifying quality of water of river Pending JPH0929277A (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR19990075893A (en) * 1998-03-26 1999-10-15 박화랑 Use of riverbed storage facilities and river resources. Management facility
JP2007144343A (en) * 2005-11-29 2007-06-14 Mitsuru Takasaki Water treatment method and apparatus for river
KR100883886B1 (en) * 2007-04-16 2009-02-17 민승기 Reinforced purifying dike of stream water
CN106745742A (en) * 2016-12-27 2017-05-31 中冶华天南京工程技术有限公司 River water body ammonia nitrogen cleaning system
CN111042072A (en) * 2020-01-03 2020-04-21 商丘市水利建筑勘测设计院 Ecological water purification weir system
CN113480100A (en) * 2021-07-22 2021-10-08 中建环能科技股份有限公司 River water body treatment equipment
CN113880243A (en) * 2021-10-12 2022-01-04 无锡市政设计研究院有限公司 Integrated facility for repairing low-flow-rate hardened urban river water environment

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR19990075893A (en) * 1998-03-26 1999-10-15 박화랑 Use of riverbed storage facilities and river resources. Management facility
JP2007144343A (en) * 2005-11-29 2007-06-14 Mitsuru Takasaki Water treatment method and apparatus for river
KR100883886B1 (en) * 2007-04-16 2009-02-17 민승기 Reinforced purifying dike of stream water
CN106745742A (en) * 2016-12-27 2017-05-31 中冶华天南京工程技术有限公司 River water body ammonia nitrogen cleaning system
CN111042072A (en) * 2020-01-03 2020-04-21 商丘市水利建筑勘测设计院 Ecological water purification weir system
CN111042072B (en) * 2020-01-03 2021-03-19 商丘市水利建筑勘测设计院 Ecological water purification weir system
CN113480100A (en) * 2021-07-22 2021-10-08 中建环能科技股份有限公司 River water body treatment equipment
CN113880243A (en) * 2021-10-12 2022-01-04 无锡市政设计研究院有限公司 Integrated facility for repairing low-flow-rate hardened urban river water environment
CN113880243B (en) * 2021-10-12 2023-08-11 华昕设计集团有限公司 Integrated facility for repairing low-flow-rate hardened urban river water environment

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