JPH0669553B2 - Sewage purification method and equipment - Google Patents

Sewage purification method and equipment

Info

Publication number
JPH0669553B2
JPH0669553B2 JP2403686A JP40368690A JPH0669553B2 JP H0669553 B2 JPH0669553 B2 JP H0669553B2 JP 2403686 A JP2403686 A JP 2403686A JP 40368690 A JP40368690 A JP 40368690A JP H0669553 B2 JPH0669553 B2 JP H0669553B2
Authority
JP
Japan
Prior art keywords
equipment
polluted water
aeration
purifying
water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP2403686A
Other languages
Japanese (ja)
Other versions
JPH04219197A (en
Inventor
福永和久
彰 伊藤
尾島啓介
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.)
Nippon Steel Corp
Original Assignee
Nippon Steel 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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP2403686A priority Critical patent/JPH0669553B2/en
Publication of JPH04219197A publication Critical patent/JPH04219197A/en
Publication of JPH0669553B2 publication Critical patent/JPH0669553B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime 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)
  • Activated Sludge Processes (AREA)
  • Aeration Devices For Treatment Of Activated Polluted Sludge (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、汚濁した内湾や閉鎖性
海域、湖沼等の大量の汚水を浄化する方法及び設備に関
するもので、更に詳細には石積堤防の内部あるいは、片
側に微生物を固定化できる接触担体を充填した接触酸化
部を設け、内部あるいは、外部曝気により、生物学的な
浄化機能を与えた透水性の浄化設備を有する堤防を、汚
濁した水域内あるいは汚濁水を引き込んだ通路内に設置
し、汚濁水を該設備に通過させることにより、汚濁水を
処理する方法及び浄化設備に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and equipment for purifying a large amount of contaminated water such as polluted inner bays, closed sea areas, lakes and marshes. More specifically, it fixes microorganisms inside or on one side of a stone embankment. A corridor with polluted water inside or a polluted water purification facility equipped with a catalytic oxidation unit filled with a liquefiable contact carrier and having a biological purification function by internal or external aeration. The present invention relates to a method for treating polluted water by installing the same inside and passing the polluted water through the facility, and a purification facility.

【0002】[0002]

【従来の技術】下水や工場排水中の有機物、無機物を生
物学的に浄化する方法として、従来より、活性汚泥法や
散水濾床法・回転円盤法等がよく知られている。これら
の方法は、微生物の生育に必要な環境条件を人為的に造
り、微生物の有機物分解能力を最大限に利用し、汚水を
浄化しようとする水処理技術である。
2. Description of the Related Art As a method for biologically purifying organic substances and inorganic substances in sewage and factory wastewater, the activated sludge method, sprinkling filter method, rotating disk method, etc. have been well known. These methods are water treatment technologies that artificially create the environmental conditions necessary for the growth of microorganisms, make the most of the ability of microorganisms to decompose organic substances, and purify sewage.

【0003】しかし、この様な水処理設備は、前処理工
程、汚泥処理工程も含み、広大な用地と建設費を必要と
する為汚濁した内湾や閉鎖性海域、湖沼等の大量の汚水
を処理する上で、非効率なシステムである。
However, such a water treatment facility includes a pretreatment process and a sludge treatment process, and requires a vast amount of land and construction cost, so that a large amount of wastewater such as polluted inner bays, closed sea areas, lakes and marshes is treated. It is an inefficient system to do.

【0004】そこで、離岸堤や護岸付近の付着生物によ
る自浄作用を積極的に活用する事を狙いとして、下記の
様な浄化システムが考案されている。
Therefore, the following purification system has been devised with the aim of positively utilizing the self-cleaning action by the attached organisms near the breakwaters and revetments.

【0005】このシステムは、図2に示すように天然石
あるいは、多孔質の人工石1を海中に積み上げ、透過性
の堤体をつくり、汚濁した海水がこの堤体を何度も透過
する際に、堤体に付着しているフジツボやカキ等の付着
生物により、海水中の有機物を生物に取り込ませ浄化し
ようとするものである。
In this system, natural stones or porous artificial stones 1 are piled up in the sea as shown in FIG. 2 to form a permeable dam body, and when polluted seawater permeates this dam body many times. By the attached organisms such as barnacles and oysters attached to the levee body, organic substances in seawater are taken up by the organisms to be purified.

【0006】[0006]

【発明が解決しようとする課題】本発明は、上述した透
過性堤体に、水処理設備として利用されている接触酸化
法の考えを導入した新しい浄化システムであり、これを
用いて更に効率良く汚濁した内湾・閉鎖性水域を浄化す
ることを課題とするものである。
DISCLOSURE OF THE INVENTION The present invention is a new purification system in which the idea of the catalytic oxidation method used as water treatment equipment is introduced into the above-mentioned permeable levee body. The problem is to purify the polluted inner bay and closed water area.

【0007】[0007]

【課題を解決するための手段】本発明は、上記の課題を
達成するためのものであって、有機物を分解する微生物
を高濃度に保持できる接触酸化設備を透過式堤防内に組
み込み、自然の食物連鎖を最大限に利用したものであ
る。
Means for Solving the Problems The present invention is to achieve the above-mentioned object, and a catalytic oxidation facility capable of maintaining a high concentration of a microorganism decomposing an organic substance is incorporated into a permeable levee to realize a natural It makes the most of the food chain.

【0008】すなわち、割栗石等で構築した石積堤防の
内部あるいは片側に微生物を固定化できる接触担体を充
填した接触酸化部を設け、内部あるいは、外部曝気によ
り、生物学的な浄化機能を与えた透水性の浄化設備を有
する堤防を汚濁した水域あるいは、汚濁水を引き込んだ
通路内に設置し、一端から汚濁水を該設備に通過させる
ことにより、汚濁水を処理するものである。
That is, a catalytic oxidization section filled with a contact carrier capable of immobilizing microorganisms was provided inside or on one side of a masonry embankment constructed with split stone, etc., and a biological purification function was provided by internal or external aeration. A levee having a water-permeable purification facility is installed in a polluted water area or a passage into which polluted water is drawn, and the polluted water is treated by passing the polluted water from one end to the facility.

【0009】すなわち、発明者らが提案する透過式浄化
方式の狙いは、従来より考案されている天然石あるいは
多孔質の人工石を海中に積み上げた透過式堤防内に特に
有機物除去に中心的な役割をもつ微生物を高濃度に保持
する為の接触酸化部を設けることであり、この高濃度微
生物の活動により浄化レベルの向上及び浄化効率の向上
を図ろうとするものである。
That is, the purpose of the permeation type purification method proposed by the inventors is to play a central role in removing organic matters, particularly in the permeation type embankment in which natural stones or porous artificial stones that have been conventionally devised are piled up in the sea. The purpose of this is to provide a catalytic oxidation part for keeping the microorganisms having the above-mentioned concentration at a high concentration, and to improve the purification level and the purification efficiency by the activity of the high concentration microorganisms.

【0010】[0010]

【実施例及び作用】以下本発明を、図1に示す実施例浄
化設備を有する堤体による実施例に基づいて詳細に説明
する。図中、1は石積堤防、2は接触担体、3は接触酸
化部、4は汚泥堆積部、5は水中攪拌散気装置、6は遊
歩道を示す。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described in detail below based on an embodiment with a dam body having the embodiment purification equipment shown in FIG. In the figure, 1 is a masonry embankment, 2 is a contact carrier, 3 is a contact oxidation part, 4 is a sludge accumulation part, 5 is an underwater agitation diffuser, and 6 is a boardwalk.

【0011】この堤防の内でも特に接触酸化部は有機物
の分解・除去に重要な役割をもち、有機物を分解する微
生物を高濃度に付着・保持できる接触担体により構成さ
れている。接触担体としては、通常、下水や工場排水の
処理に使われているものが使われる。例えば、ハニカム
チューブや礫、網、プラスチック担体等を適宜に使用す
る。
Of these levees, the catalytic oxidation part plays an important role in decomposing / removing organic substances, and is constituted by a contact carrier capable of adhering / holding a high concentration of microorganisms decomposing organic substances. As the contact carrier, those used for treating sewage and industrial wastewater are usually used. For example, a honeycomb tube, gravel, a net, a plastic carrier, or the like is appropriately used.

【0012】発明者らは、これらの担体の中でも、特に
ひも状担体が優れている事を発見した。
The inventors have found that, among these carriers, the string-shaped carrier is particularly excellent.

【0013】一般に接触担体には、微生物を高濃度に保
持できる様、比表面積が大きい事が好ましい。又、本発
明方法は、生物生産性の高い海水中あるいは水中に堤体
を築造する為、逆流装置等の機械品、配管類を設けない
事が好ましい。例えばエアーを供給する散気管及びディ
フューザーを海中に設置した場合、生物生産の高い時期
にフジツボ等が付着し、散気管、ディフューザーの閉そ
くや詰まり等の問題を起こす。従って、使用する担体も
空隙率が大きく、接触酸化部の逆洗が不要なものが好ま
しい。特に好ましいひも状担体は、繊細で強靭な放射状
の輪状体を多数有するひも状の接触材で浄化槽や排水処
理設備に実績が多いものである。この担体は、比表面積
が大きく、しかも空隙率が高いという特徴をもってい
る。
In general, it is preferable that the contact carrier has a large specific surface area so that microorganisms can be maintained at a high concentration. Further, since the method of the present invention constructs a dam body in seawater or water having high biological productivity, it is preferable not to provide a mechanical article such as a backflow device and pipes. For example, when an air diffuser for supplying air and a diffuser are installed in the sea, barnacles or the like adhere to the air diffuser and the diffuser during periods of high biological production, causing problems such as clogging and clogging of the air diffuser and diffuser. Therefore, it is preferable that the carrier used also has a large porosity and does not require backwashing of the catalytic oxidation part. A particularly preferable string-shaped carrier is a string-shaped contact material having a large number of delicate and tough radial ring-shaped carriers, and has a large track record in septic tanks and wastewater treatment facilities. This carrier is characterized by a large specific surface area and a high porosity.

【0014】発明者らは、礫やプラスチック担体、そし
てひも状担体等を用いた比較実験を行い、ひも状担体の
優位性を確認している。
The inventors have conducted comparative experiments using gravel, a plastic carrier, a string-shaped carrier and the like, and confirmed the superiority of the string-shaped carrier.

【0015】この比較実験において、ひも状担体には、
他の担体にはあまり見られない原生動物、後生動物が数
多く見られ、生物相が多岐に渡っている事が確認でき
た。生物相が多岐に渡る程、処理水質が良く発生汚泥量
も少なくなる事は従来より知られている。又、図1の設
備で実施した結果表1に示す如く実験期間中のCOD除
去率、SS除去率は、ひも状担体が最も高かった。
In this comparative experiment, the string-shaped carrier was
Many protozoa and metazoans, which are rarely seen in other carriers, were found, and it was confirmed that the biota were diverse. It is conventionally known that the more diverse the biota, the better the quality of treated water and the smaller the amount of generated sludge. Further, as shown in Table 1 as a result of carrying out with the equipment of FIG. 1, the COD removal rate and the SS removal rate during the experiment period were highest in the cord-shaped carrier.

【0016】[0016]

【表1】 [Table 1]

【0017】又、発生汚泥量も少なく、閉そく等の心配
は、全くなかった。担体から剥離した汚泥は、低部に若
干堆積するが、容易に除去することができる。このひも
状担体を用いると、汚泥がたまらない為、逆洗システム
は不要であるが、担体から剥離し底部に若干堆積する汚
泥を処理する為にはこの接触酸化部の下部に、汚泥を浚
渫除去できる空間を設けることが好ましい。その際汚泥
を浚渫除去する方法として、沈澱池等の汚泥の浚渫・除
去に実積のある汚泥浚渫ロボットを用いる事もできる。
この接触酸化部は、割栗石等で構築した石積堤防の内部
あるいは片側に設置する。又、この接触酸化部は、汚水
に流入側あるいは流出側のどちらにも設置することがで
きる。もちろん石積堤防にも接触担体程多くはないが、
微生物が付着し、更に太陽光のもと動・植物プランクト
ンや貝類、海藻類が付着し、その上に、多毛類・甲殻類
も生息し、幅広い食物連鎖を形成しており、有機物の分
解・除去を行っている。又、この食物連鎖は、接触酸化
部で見られる様な細菌−原生動物−後生動物よりもかな
り大きな食物連鎖であり、汚泥の発生量はかなり少な
い。
Also, the amount of sludge generated was small, and there was no concern about clogging. The sludge separated from the carrier is slightly deposited on the lower part, but can be easily removed. If this string-shaped carrier is used, the backwashing system is not necessary because the sludge does not collect, but in order to treat the sludge that is separated from the carrier and slightly accumulates on the bottom, the sludge is dredged under the contact oxidation part. It is preferable to provide a space that can be used. At that time, as a method for dredging and removing sludge, a sludge dredging robot having a real volume for dredging and removing sludge such as a sedimentation pond can be used.
This contact oxidation part is installed inside or on one side of the masonry embankment constructed with split stone. Further, this catalytic oxidation unit can be installed on either the inflow side or the outflow side of the wastewater. Of course, there are not as many contact carriers as masonry embankments,
Microorganisms adhere to it, and under the sunlight, animals and phytoplankton, shellfish, and seaweed adhere, and on top of that, polychaetes and crustaceans also inhabit, forming a wide food chain. It is being removed. Also, this food chain is a much larger food chain than bacteria-protozoa-metazoa as seen in the catalytic oxidation part, and the amount of sludge generated is considerably small.

【0018】又、石積堤防は、SSの補足性が大きいと
いう特徴も有しており、流入側に設けた場合は、接触酸
化部に流入してくる粗浮遊物を除去する前処理として、
又、流出側に設置する場合は、接触酸化部の接触担体よ
り剥離する浮遊汚泥を補促する機能をもつ。
Further, the masonry embankment is also characterized in that it has a high complementarity with SS. When it is installed on the inflow side, it is used as a pretreatment for removing the coarse suspended matter flowing into the catalytic oxidation part.
Further, when it is installed on the outflow side, it has a function of accelerating the floating sludge separated from the contact carrier of the contact oxidation part.

【0019】これら堤体内に生息する生物に必要な酸素
量は、水中に溶け込んでいる溶存酸素量、あるいは堤体
全面で起こる砕波等により供給できる。しかし、堤体内
を汚濁水が通過する際、生物の呼吸に酸素が多く使われ
接触酸化部で酸素が不足する。その為に、接触酸化部を
強制曝気し、酸素を供給する必要がある。
The amount of oxygen required for the organisms living in these levee bodies can be supplied by the amount of dissolved oxygen dissolved in water, or by breaking waves occurring on the entire levee body. However, when polluted water passes through the bank, much oxygen is used for the respiration of living organisms, and oxygen is insufficient at the contact oxidation part. Therefore, it is necessary to forcibly aerate the catalytic oxidation part and supply oxygen.

【0020】強制曝気の手段としては、内部曝気あるい
は、堤体外で曝気する外部曝気があるが、維持管理の面
からは外部曝気の方が好ましい。
As means for forced aeration, there are internal aeration and external aeration outside the levee body, but external aeration is preferable from the viewpoint of maintenance.

【0021】例えば、堤体上部から堤体外下部に曝気装
置を吊し、容易に上部に吊り上げれる構造にすれば、維
持管理面で問題が少ない。
For example, if an aerator is hung from the upper part of the dam body to the outer lower part of the dam body so that it can be easily lifted to the upper part, there are few problems in terms of maintenance.

【0022】又、本発明の浄化設備を有する堤体を数基
・直列して設置し、数段の連続処理を行うことも可能で
ある。その際、後段に設置する堤体へ流入する汚水は、
縦方向にもあまり、汚濁濃度の勾配や温度勾配がない事
が望ましい。従って、外部曝気の装置は、通常のディフ
ューザータイプでなく、強制攪拌も同時に行える水中攪
拌散気装置の方が好ましい。
It is also possible to install several levee bodies having the purification equipment of the present invention in series and carry out continuous treatment of several stages. At that time, the sewage flowing into the bank installed in the latter stage is
It is desirable that there is not much gradient of concentration of pollutants or temperature gradient in the vertical direction. Therefore, the device for external aeration is not a normal diffuser type, but a submersible agitating and diffusing device capable of simultaneously performing forced agitation is preferable.

【0023】通常、夏場の海は、海面があたためられ、
温度躍層ができ植物プランクトンの発生により、汚濁濃
度についても躍層ができる。従って、堤体へ流入する汚
水を縦方向に汚濁濃度が不均一となり汚水の処理上好ま
しくない。そこで、外部曝気の際、同時に水中攪乱がで
きれば汚水を縦方向に均一な濃度にすること可能であり
安定した処理が期待できる。
Usually, in the summer sea, the sea surface is warmed,
A thermocline is formed, and the generation of phytoplankton also causes a thermocline in the pollutant concentration. Therefore, the pollutant concentration of the wastewater flowing into the bank is not uniform in the vertical direction, which is not preferable in treating the wastewater. Therefore, when external aeration can be performed at the same time as underwater agitation, the sewage can be made to have a uniform concentration in the vertical direction, and stable treatment can be expected.

【0024】本発明の浄化設備を有する堤体を汚濁した
水域内に設置した場合、堤体内及び堤体間の水、あるい
は堤体処理水が遅滞・滞留しない様、うまく流れを造り
だすことが必要である。その際、自然の潮位差や潮流・
沿岸流・離岸流を利用することもできる。
When a dam body having the purification equipment of the present invention is installed in a polluted water area, it is possible to create a good flow so that the water in and between the dam bodies or the dam body treated water is not delayed or accumulated. is necessary. At that time, the difference in tidal level and the tidal current
You can also use coastal currents and offshore currents.

【0025】あるいは、堤体の出側の水をポンプ等で引
き抜くことで、堤体内に水の流れを起こすことも有効な
手段である。
Alternatively, it is also an effective means to cause the flow of water in the levee body by drawing out the water on the outlet side of the levee body with a pump or the like.

【0026】又、該ポンプを使用した場合は、間欠運転
する事も可能である。すなわち、比較的水域の水が清澄
化する冬場や雨天時の雨水の流入により、流れが自然に
形成される場合は、ポンプを停止しても良い。該設備の
動力源としては、唯一曝気装置があり、動力費の要因と
なっている。この動力費についても、曝気量を制御する
ことにより消減する事が十分可能である。
When the pump is used, it is possible to operate intermittently. That is, the pump may be stopped when the flow naturally forms due to the inflow of rainwater in the winter or when it is raining when the water in the water area is relatively clarified. The only power source of the equipment is the aeration device, which is a factor of power cost. This power cost can be sufficiently reduced by controlling the aeration amount.

【0027】例えば、接触酸化部出側あるいは、堤体出
側のORP(酸化還元電位)や、DO(溶存酸素濃度)
を計測し、この値を管理することにより曝気量をコント
ロールすることも可能である。又、本堤体の上部は、遊
歩道等に活用することができ、水域内に設置すれば、自
然公園等内の設備として美しい景観を生み出せるもので
ある。
For example, ORP (oxidation-reduction potential) or DO (dissolved oxygen concentration) on the side of the catalytic oxidation part or on the side of the bank body
It is also possible to control the aeration amount by measuring and controlling this value. In addition, the upper part of the main bank can be used as a promenade, etc. If it is installed in a water area, it can create a beautiful landscape as a facility in a natural park.

【0028】[0028]

【発明の効果】本発明の効果として、下記の優れた効果
があげられる。
The effects of the present invention include the following excellent effects.

【0029】まず第1に浄化レベルの向上及び浄化効率
の向上である。従来知られている透過式堤防は、特に有
機物除去に中心的な役割をもつ微生物の高濃度化につい
ては、考慮されておらず、高等生物まで含めた大きな食
物連鎖の形成に重点が置かれていた。しかし、本発明の
透過式浄化設備を有する堤防は、内部に微生物を高濃度
に保持できる接触酸化部を設けている為、有機物除去に
微生物がうまく機能し、浄化レベルが向上する。又、浄
化効率の向上にも有効である。
First, the purification level and the purification efficiency are improved. Conventionally known permeable levees do not take into account the high concentration of microorganisms that play a central role in removing organic matter, and focus on the formation of a large food chain including higher organisms. It was However, since the levee having the permeation type purification facility of the present invention is provided with the contact oxidation part capable of retaining the microorganisms at a high concentration inside, the microorganisms function well in removing organic substances and the purification level is improved. It is also effective in improving the purification efficiency.

【0030】第2に透過式浄化設備を有する堤防内に滞
留する汚泥の嫌気化を防ぐことができる。従来知られて
いる透過式堤防は、天然石あるいは多孔質の人工石を海
中に積み上げたものであるが内部に発生する汚泥の嫌気
化の防止は、特に考慮されていない。しかし、本発明の
透過式浄化設備を有する堤防の内部は空隙率の大きい接
触酸化部である為、内部に発生する汚泥は嫌気化しな
い。
Secondly, it is possible to prevent anaerobicization of sludge accumulated in the embankment having a permeation type purification facility. Conventionally known permeable levees are natural stones or porous artificial stones piled up in the sea, but the prevention of anaerobic sludge generated inside is not particularly considered. However, since the inside of the embankment having the permeation type purification equipment of the present invention is the catalytic oxidation part having a large porosity, the sludge generated therein is not anaerobicized.

【0031】第3に上部を遊歩道等にも活用でき、自然
公園等、美しい景観として十分利用することができる。
又、透過式浄化設備を有する堤防内に形成できる大きな
食物連鎖により、汚泥の発生も極めて少ない。
Thirdly, the upper part can be utilized as a promenade, etc., and can be fully utilized as a beautiful landscape such as a natural park.
Also, due to the large food chain that can be formed inside the levees with the permeation type purification equipment, the generation of sludge is extremely low.

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

【図1】本発明の実施例である内部に接触酸化部をもつ
透過式浄化設備を有する堤防の断面図である。
FIG. 1 is a cross-sectional view of an embankment having a permeation type purification facility having a catalytic oxidation unit inside, which is an embodiment of the present invention.

【図2】従来から考案されている透過式堤防の断面図で
ある。
FIG. 2 is a cross-sectional view of a transparent levee conventionally devised.

【符号の説明】[Explanation of symbols]

1…石積堤防 2…接触担体 3…接触酸化部 4…汚泥堆積部 5…水中攪拌散気装置 6…遊歩道 1 ... Stone embankment 2 ... Contact carrier 3 ... Contact oxidation part 4 ... Sludge accumulation part 5 ... Underwater agitation diffuser 6 ... Promenade

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 割栗石等で構築した石積堤防の内部ある
いは片側に、微生物を固定化できる接触担体を充填した
接触酸化部を設け、更に内部あるいは外部に曝気装置を
設けたことを特徴とする生物学的な浄化機能を有する透
水性の汚水の浄化設備。
1. A catalytic oxidization unit filled with a contact carrier capable of immobilizing microorganisms is provided inside or on one side of a masonry embankment constructed of split stone, etc., and further an aeration device is provided inside or outside. A facility for purifying permeable sewage that has a biological purification function.
【請求項2】 請求項1の設備を汚濁した水域内あるい
は、汚濁水を引き込んだ通路内に設置し、一端あるい
は、両端から汚濁水を該設備に通過させることにより、
汚濁水を処理することを特徴とする汚水の浄化方法。
2. The equipment according to claim 1 is installed in a polluted water area or in a passage into which polluted water is drawn, and the polluted water is passed through the equipment from one end or both ends,
A method for purifying polluted water, which comprises treating polluted water.
【請求項3】 接触担体として、ひも状担体を用いた事
を特徴とする請求項1記載の汚水の浄化設備。
3. The wastewater purification facility according to claim 1, wherein a string-shaped carrier is used as the contact carrier.
【請求項4】 接触酸化部の低部に汚泥を浚渫除去でき
る空間を設けた事を特徴とする、請求項1記載の汚水の
浄化設備。
4. The wastewater purification facility according to claim 1, wherein a space where the sludge can be dredged and removed is provided at a lower portion of the catalytic oxidation unit.
【請求項5】 堤防上部に、遊歩道等の人間が活動でき
る空間を設ける事を特徴とする請求項1記載の汚水の浄
化設備。
5. The facility for purifying sewage according to claim 1, wherein a space for human activity such as a boardwalk is provided above the embankment.
【請求項6】 外部曝気の手段として、水中攪拌散気装
置を用いる事を特徴とする請求項1記載の汚水の浄化設
備。
6. The sewage purification facility according to claim 1, wherein an underwater agitating and diffusing device is used as a means for external aeration.
【請求項7】 請求項1の設備を汚濁した水域内に設置
した場合に、該設備の出側の水をポンプ等で間欠あるい
は、連続的に引き抜くことで、該設備内に水の流れを起
こす事を特徴とする請求項2記載の汚水の浄化方法。
7. When the equipment according to claim 1 is installed in a polluted water area, the water on the outlet side of the equipment is intermittently or continuously drawn out by a pump or the like, so that the water flow into the equipment. The method for purifying sewage according to claim 2, characterized in that it is caused.
【請求項8】 請求項1の設備の出側あるいは、接触曝
気部の出側のORPあるいはDOを検知し、曝気量を制
御することを特徴とする請求項2記載の汚水の浄化方
法。
8. The method for purifying sewage according to claim 2, wherein the amount of aeration is controlled by detecting ORP or DO on the outlet side of the equipment of claim 1 or on the outlet side of the contact aeration unit.
JP2403686A 1990-12-19 1990-12-19 Sewage purification method and equipment Expired - Lifetime JPH0669553B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2403686A JPH0669553B2 (en) 1990-12-19 1990-12-19 Sewage purification method and equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2403686A JPH0669553B2 (en) 1990-12-19 1990-12-19 Sewage purification method and equipment

Publications (2)

Publication Number Publication Date
JPH04219197A JPH04219197A (en) 1992-08-10
JPH0669553B2 true JPH0669553B2 (en) 1994-09-07

Family

ID=18513411

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2403686A Expired - Lifetime JPH0669553B2 (en) 1990-12-19 1990-12-19 Sewage purification method and equipment

Country Status (1)

Country Link
JP (1) JPH0669553B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110698012A (en) * 2019-10-18 2020-01-17 华南农业大学 Method for quickly reducing bottom mud of black and odorous river

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110698012A (en) * 2019-10-18 2020-01-17 华南农业大学 Method for quickly reducing bottom mud of black and odorous river

Also Published As

Publication number Publication date
JPH04219197A (en) 1992-08-10

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