JPH0494795A - Submersible sewage cleaning device - Google Patents

Submersible sewage cleaning device

Info

Publication number
JPH0494795A
JPH0494795A JP2208125A JP20812590A JPH0494795A JP H0494795 A JPH0494795 A JP H0494795A JP 2208125 A JP2208125 A JP 2208125A JP 20812590 A JP20812590 A JP 20812590A JP H0494795 A JPH0494795 A JP H0494795A
Authority
JP
Japan
Prior art keywords
chamber
water
sewage
oxidation chamber
screen
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.)
Granted
Application number
JP2208125A
Other languages
Japanese (ja)
Other versions
JP3061838B2 (en
Inventor
Takeshi Isshi
一志 毅
Fusao Takahashi
房雄 高橋
Katsuyuki Tanaka
克幸 田中
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.)
Ee & G kk
Original Assignee
Ee & G 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 Ee & G kk filed Critical Ee & G kk
Priority to JP2208125A priority Critical patent/JP3061838B2/en
Publication of JPH0494795A publication Critical patent/JPH0494795A/en
Application granted granted Critical
Publication of JP3061838B2 publication Critical patent/JP3061838B2/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

Abstract

PURPOSE:To obtain the small-scale submersible sewage cleaning device of simple structure by arranging a screen, sand settling chamber, flow straightening chamber, catalytic oxidation chamber packed with a filter medium and submersible suction pump in series practically along the water bottom. CONSTITUTION:The catalytic oxidation chamber 4 packed with a cylindrical filter medium 7 has buoyancy and is difficult to sink. However, since the chamber is sucked by a submersible pump 5 from the screen side, the pressure in the chamber is made negative, a part of the screen 1 of the device A is exposed, the device is successively sunk in water to the pump side and set along the water bottom WB as a whole. Sewage is passed through the sand settling chamber 2 to remove easy-to-settle SS. The sewage flow toward the oxidation chamber 4 is straightened by the hole 8a of the flow straightening chamber 3. The sewage is passed through the oxidation chamber 4, SS is collected, and the org. matter is oxidized and decomposed.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、湖沼等において、光合成が活発で水中の溶存
酸素濃度が比較的高い水域の浄化に好適な水中型汚水浄
化装置に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a submersible sewage purification device suitable for purifying waters such as lakes and marshes where photosynthesis is active and the dissolved oxygen concentration in the water is relatively high.

[従来の技術] 河川の浄化に関し、従来から種々の方法が提案されてい
る。その様な方法の一つとして、曝気による汚水浄化が
ある。これは、浄化すべき汚水中に空気を送り込んで、
該汚水と空気とを強制的に接触させるものである 従来の曝気による汚水浄化方法には、全面曝気法と、部
分曝気法とがあり、全面曝気法は、濾材の底部全面を曝
気して濾材全体に酸素を供給するものである。一方、部
分曝気法は、曝気槽の一部だけを曝気して旋回流を起こ
し、以て槽全体に酸素を供給するものである。
[Prior Art] Various methods have been proposed for river purification. One such method is wastewater purification by aeration. This pumps air into the wastewater to be purified,
Conventional sewage purification methods using aeration, which forcefully bring the sewage into contact with air, include a full-surface aeration method and a partial aeration method. It supplies oxygen throughout. On the other hand, in the partial aeration method, only a portion of the aeration tank is aerated to create a swirling flow, thereby supplying oxygen to the entire tank.

[発明が解決しようとする課題] しかし、湖沼、或いは流域面積が大きく且つ流速が比較
的遅い様な大河等の水面に存在する汚水に対しては、曝
気浄化の様な従来の方法による浄化は非常に非能率であ
った。すなわち、湖沼や大河等を全面曝気しようとすれ
ば、非常に大規模で且つ複雑な構造を必要とし、そのコ
ストが膨大なものとなってしまうので、全面曝気の実施
は事実上不可能である。一方、部分曝気する場合、湖沼
や大河等は大量の水を保有していることから、浄化すべ
き水量は非常に大量であり、それに対して濾材の充填量
が少ないため効果的ではない。
[Problem to be solved by the invention] However, it is difficult to purify sewage existing on the water surface of lakes, marshes, or large rivers with large basin areas and relatively slow flow rates using conventional methods such as aeration purification. It was extremely inefficient. In other words, if you try to aerate the whole area of lakes, marshes, large rivers, etc., you will need a very large and complex structure, and the cost will be enormous, so it is virtually impossible to implement full-scale aeration. . On the other hand, in the case of partial aeration, the amount of water to be purified is extremely large since lakes, marshes, large rivers, etc. hold a large amount of water, and the amount of filter material filled in the filter medium is small, so it is not effective.

しかし、湖沼等において、光合成が活発で水中の溶存酸
素濃度が比較的高い水域であることは知られている。
However, it is known that lakes and marshes are bodies of water where photosynthesis is active and the concentration of dissolved oxygen in the water is relatively high.

本発明は、湖沼等の光合成が活発で水中の溶存酸素濃度
か比較的高い水域の汚水を浄化する小規模で構造簡単な
水中型汚水浄化装置を提供することを目的としている。
SUMMARY OF THE INVENTION An object of the present invention is to provide a small-scale, simple-structured submersible sewage purification device for purifying sewage in water areas such as lakes and marshes where photosynthesis is active and the concentration of dissolved oxygen in the water is relatively high.

[課題を解決するための手段] 本発明によれば、略水底に沿ってスクリーン、沈砂室、
整流室、濾材を充填した接触酸化室及び吸引型水中ポン
プを直列に配置している。
[Means for Solving the Problems] According to the present invention, a screen, a settling chamber,
A rectification chamber, a contact oxidation chamber filled with filter media, and a suction type submersible pump are arranged in series.

−1二記濾材は、公知技術による任意のものを使用する
ことができるカベ例えば商品名ヤクルトの容器の底部を
除去した多数の円筒状体を密に集合してアトランダムに
配置したもので構成するのが好ましい。
-1 The filter medium mentioned above is composed of a large number of cylindrical bodies, which are formed by removing the bottom of a container of the brand name Yakult, and are arranged in a dense manner at random. It is preferable to do so.

また、接触酸化室の断面積及び長さは、流出部の溶存酸
素濃度が1 mg / (1以上になるように決めるの
が好ましい。
Further, the cross-sectional area and length of the catalytic oxidation chamber are preferably determined so that the dissolved oxygen concentration at the outflow portion is 1 mg/(1 or more).

さらに、前記接触酸化室は塩化ビニール製の筒の前後縁
部に穿孔した仕切板を設けて画成しても良く、或いは大
径のパイプを多数束ねて形成しても良い。そして、穿孔
した仕切板に代えて、金網によって塩化ビニール筒を仕
切っても良い。
Furthermore, the catalytic oxidation chamber may be defined by providing partition plates with holes in the front and rear edges of a cylinder made of vinyl chloride, or may be formed by bundling a large number of large diameter pipes. In place of the perforated partition plate, the vinyl chloride tube may be partitioned by a wire mesh.

本発明の実施に際して、吸入11にその内部に濾材を充
填した濾過装置を設けるのが好ましい。この場合、該濾
過装置は切り離し可能な所謂アタッチメントタイプであ
るのが好ましい。
In carrying out the invention, it is preferable that the suction 11 is provided with a filtering device filled with a filtering medium. In this case, the filtration device is preferably of a so-called attachment type that can be separated.

これに加えて、接触酸化室内に汚泥引き抜き管を設ける
のが好ましい。ここで、該汚泥引き抜き管はスライド自
在である様に構成され、バキュームカー、吸引ポンプ、
その他の吸引手段に接続されているのが好ましい。
In addition to this, it is preferred to provide a sludge extraction pipe within the catalytic oxidation chamber. Here, the sludge extraction pipe is configured to be slidable, and is equipped with a vacuum car, a suction pump,
Preferably, it is connected to other suction means.

[作用] 上記のように構成された浄化装置において、接触酸化室
は空間であるため浮力が生じるが、水中ポンプで吸引す
るので内部圧力が負圧となり、装置はスクリーンが一部
水中に露出し、水中ポンプ側になだらかに順次水没して
全体として水底に沿った形となる。そして、スクリーン
から水中ポンプで吸引された汚水は、沈砂室に流入し、
沈殿性のSSが除去される。次いて、整流室で整流され
て接触酸化室に流入し、円筒状体の濾材でssが効果的
に捕捉されると共に、有機物の酸化分触が行われ浄化さ
れて水中ポンプから排出される。
[Function] In the purification device configured as described above, buoyancy occurs because the contact oxidation chamber is a space, but since suction is carried out by a submersible pump, the internal pressure becomes negative pressure, and the screen of the device is partially exposed in the water. , the submersible pump side is gradually submerged in water, and the overall shape follows the bottom of the water. Then, the wastewater sucked from the screen by the submersible pump flows into the settling chamber.
Precipitable SS is removed. Next, the flow is rectified in the rectification chamber and flows into the catalytic oxidation chamber, where the ss is effectively captured by the cylindrical filter medium, and organic matter is oxidized and purified before being discharged from the submersible pump.

さらに吸入11に濾材を充填した濾過装置を設ければ、
沈砂効果が向上し且つ異物が装置内に侵入することが防
止される。その結果、装置の維持、管理が容易になる。
Furthermore, if a filtration device filled with a filter material is provided in the suction 11,
The sand settling effect is improved and foreign matter is prevented from entering the device. As a result, maintenance and management of the device becomes easier.

また、接触酸化室内に汚泥引き抜き管を設ければ、汚泥
、すなわち生物酸化が不可能な物質(例えは泥、固形物
)の過剰蓄積によって生じる水流抵抗の増大、好気性部
分の減少、有効容積の減少等が、効果的に防雨される。
In addition, if a sludge withdrawal pipe is installed in the contact oxidation chamber, the increase in water flow resistance caused by excessive accumulation of sludge, that is, substances that cannot be biologically oxidized (e.g. mud, solids), the reduction of the aerobic part, and the effective volume rain is effectively prevented.

[実施例] 以下図面を参照して本発明の詳細な説明する。[Example] The present invention will be described in detail below with reference to the drawings.

第1図及び第2図において、全体を7〕号Aで示す浄化
装置は、湖沼等の光合成が活発で水中の溶存酸素濃度が
比較的高い水域の水面WLと水底W13の間に、略水底
WBに沿って設けられている。
In FIGS. 1 and 2, the purification device designated as No. 7A as a whole is located between the water surface WL and the water bottom W13 of a water body such as a lake where photosynthesis is active and the dissolved oxygen concentration in the water is relatively high. It is provided along the WB.

この装置Aには、スクリーン1、沈砂室2、整流室3及
び接触酸化室4及び吸引型の水中ポンプ5か直列に配置
されている。前記スクリーン1は、後記するように一部
が水面状に露出されており、汚水のゴミ等を除去すると
共に、空気を吸引するようになっている。
In this apparatus A, a screen 1, a settling chamber 2, a rectification chamber 3, a contact oxidation chamber 4, and a suction type submersible pump 5 are arranged in series. As will be described later, a portion of the screen 1 is exposed to the water surface, and is designed to remove dirt and the like from sewage and to suck in air.

前記沈砂室2は、スクリーン1から流入した汚水中の沈
殿性固形物(S S)を沈殿させて除去するようになっ
ている。
The settling chamber 2 is designed to settle and remove settleable solids (SS) in the wastewater that has flowed in from the screen 1.

前記整流室3は、沈砂室2と仕切板3aにより上方間]
コ部3bまで仕切られ、その開口部3bから流入した汚
水を、後記する前部仕切板8の穴8aを通過させて整流
するようになっている。
The rectifying chamber 3 is separated from the sand settling chamber 2 by a partition plate 3a above]
It is partitioned up to the corner portion 3b, and the wastewater flowing in from the opening 3b is rectified by passing through a hole 8a of a front partition plate 8, which will be described later.

前記接触酸化室4は、塩化ビニール筒6に濾材7を充填
し、前後部をそれぞれ濾材7がはみ出ない程度の大きい
穴8as9aを形成した前部仕切板8、後部仕切板9で
画成されている。その濾材7は、公知技術による任意の
ものであるが、例えば商品名ヤクルトの容器の底部を除
去した多数の」筒状体を密に集合してアトランダムに配
置したもので構成するのが好ましい。これにより汚水中
の浮遊物質(S S)を効果的に捕捉すると共に、好気
性生物nψを保持し、有機物の酸化分解を行うようにな
っている。
The contact oxidation chamber 4 is formed by filling a vinyl chloride tube 6 with a filter medium 7, and defining a front partition plate 8 and a rear partition plate 9, each having a hole 8as9a large enough to prevent the filter medium 7 from protruding at the front and rear thereof. There is. The filtering medium 7 may be any known technology, but is preferably composed of a large number of cylindrical bodies, the bottoms of which are removed from containers of the brand name Yakult, which are densely assembled and arranged at random, for example. . This effectively captures suspended solids (SS) in wastewater, retains aerobic organisms nψ, and oxidizes and decomposes organic matter.

前記水中ポンプ5は、電線10により図示しない陸上の
電源に接続され、浄化された水を吸引し、吐出するよう
になっている。
The submersible pump 5 is connected to a land power source (not shown) via an electric wire 10, and is configured to suck purified water and discharge it.

次に作用について説明する。Next, the effect will be explained.

接触酸化室4は、円筒状の濾材7が充填されているので
浮力が生じ、水没しにくい。しかし、水中ポンプ5てス
クリーン1側からを吸引するので、内部か負圧になり、
装置Aはスクリーン1の一部が露出し、水中ポンプ5側
に順次なだらかに水没して全体として水底WBに沿って
セットされる。
Since the contact oxidation chamber 4 is filled with a cylindrical filter medium 7, buoyancy is generated and it is difficult to be submerged in water. However, since the submersible pump 5 sucks from the screen 1 side, there is negative pressure inside.
The device A is set as a whole along the water bottom WB with a part of the screen 1 exposed and gradually submerged in water on the side of the submersible pump 5.

また、接触酸化室4は、内部が負圧てあっても、充填さ
れた円筒状の濾+A7により形が保持され、破損が防止
される。
Further, even if the inside of the catalytic oxidation chamber 4 is under negative pressure, the shape is maintained by the filled cylindrical filter +A7 and damage is prevented.

沈砂室2は、例えば直径DJが50cm、長さLlが1
mに形成されており、内部流速を例えば6゜7X10’
m/Sにして2.5分て汚水を通過させ、沈殿性のSS
を除去する。
For example, the sand settling chamber 2 has a diameter DJ of 50 cm and a length Ll of 1.
m, and the internal flow velocity is, for example, 6°7×10'
m/S for 2.5 minutes, and then pass through the wastewater to form a sedimentary SS.
remove.

整流室3は、例えば開lj部3bの高さCが10Cln
 N長さL 2が50cmに形成され、穴8aにより酸
化室4への汚水流を整流する。
In the rectifying chamber 3, for example, the height C of the open lj part 3b is 10Cln.
N length L2 is formed to be 50 cm, and the hole 8a rectifies the wastewater flow to the oxidation chamber 4.

接触酸化室4は、例えば断面積D2が0,264rIf
1長さL3が1−0mに形成され、汚水を流速0.5c
m/S以下で滞留時間33分で通過させる間に、SSを
捕捉すると共に、有機物の酸化分解を行って汚水を浄化
する。ただし、出L1部すなわち後部仕切板9から流出
する水の溶存酸素濃度がi mg / 12以下の場合
は、img/A以」二になるように、長さL3を短縮す
る。
The catalytic oxidation chamber 4 has a cross-sectional area D2 of 0,264rIf, for example.
1 Length L3 is formed to 1-0m, and the flow rate of wastewater is 0.5c.
While passing through the wastewater at a temperature of m/S or less and a residence time of 33 minutes, SS is captured and organic matter is oxidized and decomposed to purify the wastewater. However, if the dissolved oxygen concentration of the water flowing out from the outlet L1 section, that is, the rear partition plate 9, is less than i mg/12, the length L3 is shortened so that it becomes less than img/A.

スクリーン1側から汚水を圧送するのに比べ、浄化され
た水を吸引する方法では装置内に流入するSSか少な(
なり、SSの蓄積による閉塞が発生し難い。
Compared to pumping wastewater from the screen 1 side, the method of suctioning purified water reduces the amount of SS flowing into the device (
Therefore, blockage due to SS accumulation is less likely to occur.

第3図は本発明の第2実施例の要部を示している。この
実施例の場合、沈砂室2に濾過装置2゜が設けられてい
る。この濾過装置2oはその内部に濾材、例えば接触酸
化室4に充填されているものと同一の濾材7、が充填さ
れている。この濾材7により、比較的荒い粒子が接触酸
化室4内へ侵入する以前に除去されるのである。
FIG. 3 shows the main part of a second embodiment of the present invention. In this embodiment, the settling chamber 2 is provided with a filtering device 2°. This filtering device 2o is filled with a filtering medium, for example, the same filtering medium 7 as that filled in the contact oxidation chamber 4. This filter medium 7 removes relatively coarse particles before they enter the catalytic oxidation chamber 4.

ここて、濾過装置20は所謂アタッチメントとして構成
されており、沈砂室2から自在に切り離したり取り付け
たりすることか出来るのである。
Here, the filtration device 20 is configured as a so-called attachment, and can be detached from or attached to the sand settling chamber 2 at will.

この濾過装置20の取り付けに際しては、沈砂室2内に
形成された突起22を濾過装置20の凹部24に嵌合さ
せれば良い。そして、この様な取り付は及び切り離し自
在にすることにより、保守、点検の労力が非常に軽減さ
れるのである。
When installing this filter device 20, it is sufficient to fit the protrusion 22 formed in the sand settling chamber 2 into the recess 24 of the filter device 20. By making it possible to attach and detach the device in this way, the effort required for maintenance and inspection can be greatly reduced.

第4図は本発明の第3実施例の要部を示している。水中
ポンプ5により接触酸化室4へ水を吸引すると、濾材に
微生物が付着して生物作用によって浄化が進行する。し
かし、接触酸化室4には第4図中点線で示す様に汚泥り
が蓄積されてしまう。
FIG. 4 shows the main part of a third embodiment of the present invention. When water is sucked into the contact oxidation chamber 4 by the submersible pump 5, microorganisms adhere to the filter medium and purification proceeds by biological action. However, sludge accumulates in the catalytic oxidation chamber 4 as shown by the dotted line in FIG.

これに対して、本発明の第3実施例によればりき抜き管
30が設けられているので、汚泥りは接触酸化室4の内
部に蓄積することなく、該引き抜き管30を介して排出
されるのである。すなわち、この引き抜き管30には多
数の開口32・・・が形成されており、目、っ引き抜き
管30の端部は図示しない吸引手段に接続されている。
On the other hand, according to the third embodiment of the present invention, since the draw-out pipe 30 is provided, the sludge is discharged through the draw-out pipe 30 without accumulating inside the contact oxidation chamber 4. It is. That is, a large number of openings 32... are formed in this pull-out tube 30, and the ends of the pull-out tube 30 are connected to a suction means (not shown).

そのため、接触酸化室4の内部に侵入した汚泥りは開口
32・・より引き抜き管30内に吸引され、月っ該管3
0を介して接触酸化室4外部へ吸引されて排出されるの
である。なお、汚泥りを逆流する必要かある場合は、吸
引手段を取り去り、流体(水又は空気)吸込手段を取付
ければよい。
Therefore, the sludge that has entered the contact oxidation chamber 4 is sucked into the extraction pipe 30 through the opening 32, and
0 and is sucked out of the catalytic oxidation chamber 4 and discharged. If it is necessary to backflow the sludge, the suction means may be removed and a fluid (water or air) suction means may be installed.

第5図は第3図の実施例において濾過装置20を沈砂室
2から着脱自在に構成した例である。すなわち、沈砂室
2および濾過装置20にはそれぞれ流体出入口A1、A
2を設け、ホースHで相互に連結しである。このように
すると両者の着脱が容易となる。
FIG. 5 shows an example in which the filtration device 20 is configured to be detachable from the sand settling chamber 2 in the embodiment shown in FIG. That is, the settling chamber 2 and the filtration device 20 have fluid inlets and outlets A1 and A1, respectively.
2 are provided and interconnected by a hose H. This makes it easy to attach and detach both.

[発明の効果] 本発明は、以上説明したように構成されているので、小
規模で簡単な構造で湖沼等の光合成が活発で水中の溶存
酸素濃度が比較的高い水域の汚水を浄化することができ
る。
[Effects of the Invention] Since the present invention is configured as described above, it is possible to purify wastewater in water bodies such as lakes and marshes where photosynthesis is active and the concentration of dissolved oxygen in the water is relatively high with a small-scale and simple structure. I can do it.

また、溶存酸素濃度が低い場合は、公知の散気装置を組
合せ、汚水を浄化することができる。
Furthermore, when the dissolved oxygen concentration is low, a known aeration device can be combined to purify the wastewater.

さらに、吸引型の水中ポンプにより、ポンプの負荷を小
さくできて経済的であり、接触酸化室の負荷を小さくし
て破損を防止し、更に、装置を水面と水底との間に略水
底に沿うように容易にセットすることかできる。
Furthermore, the suction type submersible pump reduces the load on the pump, which is economical, reduces the load on the contact oxidation chamber and prevents damage, and furthermore, allows the device to be installed between the water surface and the bottom, almost along the bottom of the water. It can be set up easily.

本発明において、吸入[1に濾十Aを充填した濾過装置
を設けれは、沈砂効果が向上し且つ異物が装置内に侵入
することが防11ユされ、装置の維持、管理か容易にな
る。
In the present invention, by providing a filtration device filled with filtration material in the suction [1], the settling effect is improved, foreign matter is prevented from entering the device, and the maintenance and management of the device is facilitated. .

また、接触酸化室内に汚泥引き抜き管を設ければ、水流
抵抗の増大、好気性部分の減少、有効容積の減少等、汚
泥の過剰蓄積によって生じる不都合が防11−されるの
である。
Further, by providing a sludge drawing pipe in the contact oxidation chamber, disadvantages caused by excessive accumulation of sludge, such as increased water flow resistance, decreased aerobic area, and decreased effective volume, can be prevented.

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

第1図は本発明の一実施例を示す垂直断面図、第2図は
フローシート図、第3図は本発明の第二実施例の要部を
示す部分拡大図、第4図は本発明の第三実施例の要部を
示す部分拡大図、第5図は第3図の変型例を示す部分拡
大図である。 Δ・・・浄化装置  1・・・スクリーン2・・・沈砂
室  3・・・整流室  4・・・接触酸化室 ・濾材 ] 第3図 手 続 補 正 書 7゜ 補正の内容 (]) 明細書第10頁第4行の 「逆流」 を 「逆洗」 と補正しまず。 1゜ 用件の表示 特願平2 2081、25号 2゜ 発明の名称 水中型汚水浄化装置 3゜ 補正をする者 名 称 株式会社 エーアンドジ 代表者 毅 4゜
Fig. 1 is a vertical sectional view showing one embodiment of the present invention, Fig. 2 is a flow sheet diagram, Fig. 3 is a partially enlarged view showing main parts of a second embodiment of the invention, and Fig. 4 is a diagram of the present invention. FIG. 5 is a partially enlarged view showing a modification of FIG. 3. FIG. Δ... Purification device 1... Screen 2... Sedimentation chamber 3... Rectification chamber 4... Contact oxidation chamber/filter material] Figure 3 Procedural amendment 7゜Contents of amendment (]) Specification No. First, correct "backflow" in line 4 of page 10 to "backwashing." 1゜Indication of requirements Patent application No. 2081, No. 25 2゜Name of the invention Submersible sewage purification device 3゜Name of person making the amendment Representative Tsuyoshi A&D Co., Ltd. 4゜

Claims (1)

【特許請求の範囲】[Claims] 略水底に沿ってスクリーン、沈砂室、整流室、濾材を充
填した接触酸化室及び吸引型水中ポンプを直列に配置し
たことを特徴とする水中型汚水浄化装置。
A submersible sewage purification device characterized in that a screen, a settling chamber, a rectification chamber, a contact oxidation chamber filled with a filter medium, and a suction type submersible pump are arranged in series substantially along the bottom of the water.
JP2208125A 1990-08-08 1990-08-08 Submersible sewage purification equipment Expired - Fee Related JP3061838B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2208125A JP3061838B2 (en) 1990-08-08 1990-08-08 Submersible sewage purification equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2208125A JP3061838B2 (en) 1990-08-08 1990-08-08 Submersible sewage purification equipment

Publications (2)

Publication Number Publication Date
JPH0494795A true JPH0494795A (en) 1992-03-26
JP3061838B2 JP3061838B2 (en) 2000-07-10

Family

ID=16551054

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2208125A Expired - Fee Related JP3061838B2 (en) 1990-08-08 1990-08-08 Submersible sewage purification equipment

Country Status (1)

Country Link
JP (1) JP3061838B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110372156A (en) * 2019-08-23 2019-10-25 重庆建工第三建设有限责任公司 A kind of water ecology selfreparing construction method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110372156A (en) * 2019-08-23 2019-10-25 重庆建工第三建设有限责任公司 A kind of water ecology selfreparing construction method
CN110372156B (en) * 2019-08-23 2022-06-10 重庆建工第三建设有限责任公司 Water body ecological self-repairing construction method

Also Published As

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