JPS5815037B2 - Sewage purification equipment - Google Patents

Sewage purification equipment

Info

Publication number
JPS5815037B2
JPS5815037B2 JP55002820A JP282080A JPS5815037B2 JP S5815037 B2 JPS5815037 B2 JP S5815037B2 JP 55002820 A JP55002820 A JP 55002820A JP 282080 A JP282080 A JP 282080A JP S5815037 B2 JPS5815037 B2 JP S5815037B2
Authority
JP
Japan
Prior art keywords
liquid
aeration chamber
chamber
treatment tank
pipe
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
Application number
JP55002820A
Other languages
Japanese (ja)
Other versions
JPS56100697A (en
Inventor
伊藤亘
根岸直毅
田村孝章
藤田矩彦
尾沢留好
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.)
KAIHATSU KENKYUSHO IND RES
Original Assignee
KAIHATSU KENKYUSHO IND RES
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 KAIHATSU KENKYUSHO IND RES filed Critical KAIHATSU KENKYUSHO IND RES
Priority to JP55002820A priority Critical patent/JPS5815037B2/en
Publication of JPS56100697A publication Critical patent/JPS56100697A/en
Publication of JPS5815037B2 publication Critical patent/JPS5815037B2/en
Expired 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

  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Activated Sludge Processes (AREA)

Description

【発明の詳細な説明】 この発明は、活性汚泥法にもとづいて汚水を浄;化する
ための汚水浄化装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a sewage purification device for purifying sewage based on an activated sludge method.

活性汚泥法によって汚水を処理する場合、処理ずみの液
体から活性汚泥をどのようにして迅速に除去するかが重
要な問題となる。
When treating wastewater using the activated sludge method, an important issue is how to quickly remove activated sludge from the treated liquid.

最も一般的には、活性汚泥の除去は、曝気を終えた液体
を沈殿槽に移し、この液体に含まれている活性汚泥を沈
降させ、上澄液をオーバーフローさせることによって行
われている。
Most commonly, activated sludge is removed by transferring the aerated liquid to a settling tank, allowing the activated sludge contained in the liquid to settle, and allowing the supernatant to overflow.

しかしながら活性汚泥の沈降には長い時間を必要とする
ために処理効率が低い。
However, since activated sludge requires a long time to settle, the treatment efficiency is low.

また分離した活性汚泥を長時間にわたって酸素の供給か
ら遮断することは、活性汚泥の活性低下を招き、その一
部を曝気槽に返送して再び生物化学的酸化に関与させる
とき、活性が回復するのに時間がかかるという不都合の
原因となる。
In addition, cutting off the separated activated sludge from oxygen supply for a long period of time leads to a decrease in the activity of the activated sludge, and when a part of it is returned to the aeration tank and involved in biochemical oxidation again, the activity is restored. This causes the inconvenience of taking a long time.

この発明は、活性汚泥を急速に沈降させるとともに、こ
の活性汚泥の活性を低下させることなく生物化学的酸化
に関与させ得るような汚水浄化装置を提供することを目
的としている。
An object of the present invention is to provide a sewage purification device that allows activated sludge to rapidly settle and to participate in biochemical oxidation without reducing the activity of the activated sludge.

この発明の一実施例を図面にしたがって説明する。An embodiment of the invention will be described with reference to the drawings.

図中の符号1は、上面が開放された処理槽を示し、この
処理槽1内に曝気機構2が設けられている。
Reference numeral 1 in the figure indicates a processing tank with an open top surface, and an aeration mechanism 2 is provided within this processing tank 1.

曝気機構2は、同軸的に配置された3つの筒体3,4,
5を有し、その各々の内部に、1次曝気室6.セトラー
7および2次曝気室8が形成されている。
The aeration mechanism 2 includes three coaxially arranged cylinder bodies 3, 4,
5, each having a primary aeration chamber 6. A settler 7 and a secondary aeration chamber 8 are formed.

1次曝気室6は、その底部で処理槽1内に連通ずるとと
もに、筒体3の上端部に設けた孔3aを介してセトラー
1に連通している。
The primary aeration chamber 6 communicates with the inside of the processing tank 1 at its bottom, and also with the settler 1 through a hole 3a provided at the upper end of the cylindrical body 3.

また2次曝気室8は、その底部でセトラー7の底部に、
そして頂部で処理槽1の内部にそれぞれ連通している。
In addition, the secondary aeration chamber 8 has its bottom located at the bottom of the settler 7.
The top portions communicate with the inside of the processing tank 1, respectively.

1さらに1
次曝気室6および2次曝気室8の各々の底部には、それ
ぞれディフューザ9.10が配置されている。
1 further 1
A diffuser 9.10 is arranged at the bottom of each of the secondary aeration chamber 6 and the secondary aeration chamber 8, respectively.

ディフューザ9は、1次曝気室6内の液体中に、パイプ
11を経て供給された空気を吹込むためのものであり、
そしてディフューザ10は、2次曝気室8内の液体中に
、パイプ12を経て送られた高濃度酸素ガス(ここでは
空気よりも高い濃度で酸素を含有するガスを指す)を吹
込むために設けられている。
The diffuser 9 is for blowing air supplied through the pipe 11 into the liquid in the primary aeration chamber 6,
The diffuser 10 is provided to blow high-concentration oxygen gas (here, gas containing oxygen at a higher concentration than air) sent through the pipe 12 into the liquid in the secondary aeration chamber 8. There is.

さらに処理槽1内には、その周壁の上端部との間に環状
の分離室13を形成するためのセパレータ14が設けら
れている。
Furthermore, a separator 14 is provided in the processing tank 1 to form an annular separation chamber 13 between the processing tank 1 and the upper end of the peripheral wall thereof.

この分離室13は、処理槽1内の液体を一時的に収容し
、この液体に含まれている活性汚泥を沈降分離するため
のもので、上澄液は処理槽1の上縁をオーバーフローし
たのち、受器15に入る。
This separation chamber 13 is for temporarily storing the liquid in the treatment tank 1 and separating the activated sludge contained in this liquid by sedimentation, and the supernatant liquid overflows the upper edge of the treatment tank 1. Afterwards, it enters receiver 15.

なおセパレーク14の上端は、筒体4の上端と接続され
、2次曝気室8の液面上に放出された高濃度酸素ガスを
捕集するための閉じた室を形成している。
The upper end of the separate lake 14 is connected to the upper end of the cylindrical body 4 to form a closed chamber for collecting high concentration oxygen gas released onto the liquid surface of the secondary aeration chamber 8.

さらに分離室13と2次曝気室8とを接続する汚泥パイ
プ16が設けられている。
Furthermore, a sludge pipe 16 connecting the separation chamber 13 and the secondary aeration chamber 8 is provided.

この汚泥パイプ16の一端は、分離室13内の適当な個
所、好ましくは分離室13内に形成された汚泥層の上端
部に開口する。
One end of the sludge pipe 16 opens at a suitable location within the separation chamber 13, preferably at the upper end of the sludge layer formed within the separation chamber 13.

処理すべき流入汚水は、パイプ17から1次曝気室6の
底部に導入され、処理水は、受器15からパイプ18を
経て取出される。
The inflowing wastewater to be treated is introduced into the bottom of the primary aeration chamber 6 through the pipe 17, and the treated water is taken out from the receiver 15 through the pipe 18.

また分離室13内で分離された活性汚泥は汚泥パイプ1
6を経て2次曝気室8内に戻される。
In addition, the activated sludge separated in the separation chamber 13 is transferred to the sludge pipe 1
6 and is returned to the secondary aeration chamber 8.

ディフューザ9から1次曝気室6内に存在する液体中に
吹込まれた空気は、この液体中に気泡となって分散し、
この液体中に存在するCO□を追い出す作用と、液体中
に酸素を供給する作用さ、液体に湧昇力を与える作用と
を行う。
The air blown into the liquid existing in the primary aeration chamber 6 from the diffuser 9 becomes bubbles and disperses in this liquid.
It has the functions of expelling CO□ present in the liquid, supplying oxygen to the liquid, and giving upwelling force to the liquid.

これによって液体は1次曝気室6内を上昇し、孔3aか
らセトラー7に移行する。
As a result, the liquid rises within the primary aeration chamber 6 and transfers to the settler 7 from the hole 3a.

液体中に存在する気泡は、液体が1次曝気室6内を上昇
し、ついでセトラー7内を下降する間に液体から分離し
、外部に放出される。
Air bubbles present in the liquid are separated from the liquid while the liquid rises in the primary aeration chamber 6 and then descends in the settler 7, and is discharged to the outside.

セトラー7の底部に達した液体は、これに隣接する2次
曝気室8に入り、その底部に設けられたディフューザ1
0から高濃度酸素ガスの吹込みを受ける。
The liquid that has reached the bottom of the settler 7 enters the secondary aeration chamber 8 adjacent thereto, and enters the diffuser 1 provided at the bottom.
Receives high concentration oxygen gas injection from 0.

この場合にも、液体中の気泡の湧昇力によって、2次曝
気室80)底部に連通ずるセトラー7から液体を吸込み
、同時にパイプ16を介して、分離室13内の活性汚泥
を吸込む作用が行われる。
In this case as well, the upwelling force of air bubbles in the liquid causes the liquid to be sucked in from the settler 7 communicating with the bottom of the secondary aeration chamber 80), and at the same time, the activated sludge in the separation chamber 13 is sucked in through the pipe 16. be exposed.

すなわち処理槽1内の液体は、1次曝気室6.セトラー
7および2次槽気槽8を通って処理槽1内に戻る経路で
循環する。
That is, the liquid in the treatment tank 1 is transferred to the primary aeration chamber 6. It circulates through the settler 7 and the secondary tank air tank 8 and returns to the processing tank 1.

そしてこの循環する液体中に、1次曝気室6の底部で流
入汚水が合流し、この流入汚水の流量に見合った量の液
体が分離室13から取出され、このとき分離室13内で
沈降した汚泥粒子によるフィルタ作用を受ける。
Then, inflowing sewage joins this circulating liquid at the bottom of the primary aeration chamber 6, and an amount of liquid corresponding to the flow rate of this inflowing sewage is taken out from the separation chamber 13, and at this time, it settles in the separation chamber 13. Filtered by sludge particles.

また分離室13内で沈降した活性汚泥は、長時間にわた
って滞留することなく、汚泥パイプ16を経て2次曝気
室8内に戻されるので、その活性が低下することはない
Furthermore, the activated sludge that has settled in the separation chamber 13 is returned to the secondary aeration chamber 8 via the sludge pipe 16 without being retained for a long period of time, so its activity does not decrease.

なお汚泥パイプ16の一端を2次曝気室8と連通させる
代りに、処理槽1の底部にパイプ19のように開口させ
、この部分を通って1次曝気室6に向かう液体の流れに
よって活性汚泥の吸込みを行うようにしてもよい。
Note that instead of communicating one end of the sludge pipe 16 with the secondary aeration chamber 8, an opening is made at the bottom of the treatment tank 1 like a pipe 19, and the activated sludge is Alternatively, the suction may be performed.

) また第2図に示すように、パイプ11から1次曝気
室6内のディフューザ9に高濃度酸素ガスを、そしてパ
イプ12から2次曝気室8内のディフューザ10に空気
をそれぞれ供給した場合にも同様の効果が期待できる。
) Also, as shown in FIG. 2, when high concentration oxygen gas is supplied from the pipe 11 to the diffuser 9 in the primary aeration chamber 6, and air is supplied from the pipe 12 to the diffuser 10 in the secondary aeration chamber 8. A similar effect can be expected.

この場合には、2次曝気室8の上方は開放され、代りに
1次曝気室6およびセトラー7の上方が外部から遮断さ
れる。
In this case, the upper part of the secondary aeration chamber 8 is opened, and the upper part of the primary aeration chamber 6 and the settler 7 is closed from the outside.

さらに第3図は、曝気機構2を処理槽1の外部に設けた
場合を示している。
Further, FIG. 3 shows a case where the aeration mechanism 2 is provided outside the processing tank 1.

この場合には、処理槽1内には、その内部の液体を取出
すための取出管21が設けられ、この取出管21の一端
は、流入汚水を導入するためのパイプ17とともに、曝
気機構2の筒体3の底部に接続される。
In this case, a take-out pipe 21 for taking out the liquid inside the treatment tank 1 is provided, and one end of this take-out pipe 21 is connected to the aeration mechanism 2 along with a pipe 17 for introducing the inflowing wastewater. It is connected to the bottom of the cylinder body 3.

また曝気機構2の筒体5の内部は、返送管22を介して
処理槽1の底部に連結される。
Further, the inside of the cylindrical body 5 of the aeration mechanism 2 is connected to the bottom of the processing tank 1 via a return pipe 22.

さらに汚泥パイプ16の一端は、処理槽1の外部に引き
出され、2次曝気室8に接続される。
Furthermore, one end of the sludge pipe 16 is drawn out of the treatment tank 1 and connected to the secondary aeration chamber 8 .

したがって処理槽1内の液体は、取出管21、曝気機構
2および返送管22を通って循環し、この間に酸素の供
給とCO2の除去を受ける。
Therefore, the liquid in the treatment tank 1 circulates through the take-off pipe 21, the aeration mechanism 2 and the return pipe 22, during which it is supplied with oxygen and removed with CO2.

そして処理された液体は、第1図、第2図に示した場合
と同様に、分離室13内で活性汚泥から分離されたのち
取出され、沈降した活性汚泥は汚泥パイプ16から2次
曝気室8に引き抜かれる。
The treated liquid is separated from the activated sludge in the separation chamber 13 and then taken out, as in the case shown in FIGS. 1 and 2, and the settled activated sludge is transferred from the sludge pipe 16 to the secondary aeration chamber. Pulled out at 8.

なお筒体5内の液体から分離したガスの酸素濃度は下だ
かなり高いので、ブロワ23を有するパイプ24からこ
のガスを取出し、パイプ12に供給して再使用すること
が望才しく、これによって酸素の利用効率が向上する。
Since the oxygen concentration of the gas separated from the liquid in the cylinder body 5 is quite high at the bottom, it is desirable to extract this gas from the pipe 24 having the blower 23 and supply it to the pipe 12 for reuse. Oxygen usage efficiency improves.

以上のようにこの発明の汚水浄化装置によれば処理すべ
き汚水は処理槽と曝気機構との間で連続的に循環し、そ
の一部が分離室に移行し、分離室内で活性汚泥が沈降分
離されたのち、上澄液が処理水さして取出される。
As described above, according to the sewage purification device of the present invention, the sewage to be treated is continuously circulated between the treatment tank and the aeration mechanism, a part of which is transferred to the separation chamber, and activated sludge settles in the separation chamber. After separation, the supernatant liquid is removed from the treated water.

したがって曝気槽で曝気した液体の全量を沈、穀槽に送
り、この沈殿槽で沈降分離された活性汚泥の一部を曝気
槽に返送する従来の方法と比較して、処理効率がきわめ
て高くまた得られた処理水の清澄度も良好である。
Therefore, compared to the conventional method in which the entire amount of liquid aerated in the aeration tank is sent to the grain tank where it settles and a part of the activated sludge that has been settled and separated in this settling tank is returned to the aeration tank, the treatment efficiency is extremely high. The clarity of the obtained treated water is also good.

しかも分離室で沈降分離された活性汚泥は、分離室内に
長時間にわたって滞留することなく、液体の流れを利用
して曝気機構に返送されるので、活性汚泥の活性度は常
に高い水準に保たれ、これも処理効率の向上をもたらす
要因となる。
In addition, the activated sludge that has been sedimented and separated in the separation chamber does not remain in the separation chamber for a long time and is returned to the aeration mechanism using the liquid flow, so the activity of the activated sludge is always maintained at a high level. , this is also a factor that improves processing efficiency.

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

第1図はこの発明の一実施例による汚水浄化装置の概略
的縦断面図、第2図および第3図はそれぞれ他の実施例
による装置を示す概略的縦断面図である。 1・・・・・・処理槽、2・・・・・・曝気機構、6・
・・・・・1次曝気室、7・・・・・・セトラー、8・
・・・・・2次曝気室、9゜10・・・・・・ティフユ
ーザ、13・・・・・・分離室、14・・・・・・セパ
レータ、16・・・・・・汚泥パイプ、21・・・・・
・取出管、22・・・・・・返送管。
FIG. 1 is a schematic longitudinal cross-sectional view of a sewage purification apparatus according to one embodiment of the present invention, and FIGS. 2 and 3 are schematic longitudinal cross-sectional views showing apparatuses according to other embodiments, respectively. 1... treatment tank, 2... aeration mechanism, 6.
...Primary aeration chamber, 7...Settler, 8.
...Secondary aeration chamber, 9゜10...Tif user, 13...Separation chamber, 14...Separator, 16...Sludge pipe , 21...
・Takeout pipe, 22...Return pipe.

Claims (1)

【特許請求の範囲】 1 被処理液体を収容する処理槽と、下端が上記処理槽
内に連通ずる垂直な第1曝気室を形成する筒体と、この
筒体の底部に流入汚水を導くパイプと、上記第1曝気室
内に酸素含有ガスを吹込むことによって上記第1曝気室
内の液体を上昇させながらこの液体中のCO2を追い出
すと同時に酸素を供給するためのディフューザと、上記
第1曝気室を通過した液体を受は入れ、この液体中の気
泡を分離するためのセトラーを形成する筒体と、下端が
上記セトラーに連なり、上端が上記処理槽の内部に連な
る第2曝気室を形成する筒体と、上記第2曝気室内に酸
素含有ガスを吹込むことによって上記第2曝気室内の液
体を上昇させながらこの液体中に酸素を溶解させるため
のディフューザと、上記処理槽の周縁部に形成された分
離室と、一端がこの分離室内に開口する汚泥パイプとを
備え、上記分離室は、上記処理槽内の液体を受入れるた
めに下端で上記処理槽内部に連通しているとともに、上
端が上澄液をオーバーフローさせるためのせきを形成し
、また上記汚泥パイプの一端は、上・記分離室内で分離
した汚泥層内に開口していることを特徴とする汚水浄化
装置。 2 上記汚泥パイプの他端は、上記第2曝気室の底部に
連通している特許請求の範囲第1項記載の汚水浄化装置
。 3 上記汚泥パイプの他端は、上記処理槽内の底部に開
口している特許請求の範囲第1項記載の汚水浄化装置。
[Scope of Claims] 1. A treatment tank containing a liquid to be treated, a cylinder forming a vertical first aeration chamber whose lower end communicates with the treatment tank, and a pipe that guides inflowing wastewater to the bottom of the cylinder. and a diffuser for blowing an oxygen-containing gas into the first aeration chamber to raise the liquid in the first aeration chamber while expelling CO2 in the liquid and at the same time supplying oxygen; A cylindrical body that forms a settler for receiving the liquid that has passed through and separating bubbles in the liquid, and a second aeration chamber that has a lower end connected to the settler and an upper end connected to the inside of the processing tank. a cylindrical body, a diffuser for dissolving oxygen in the liquid while raising the liquid in the second aeration chamber by blowing oxygen-containing gas into the second aeration chamber, and a diffuser formed at the peripheral edge of the processing tank. and a sludge pipe having one end opened into the separation chamber, the separation chamber having a lower end communicating with the inside of the treatment tank to receive the liquid in the treatment tank, and an upper end communicating with the inside of the treatment tank. A sewage purification device characterized in that a weir is formed for overflowing the supernatant liquid, and one end of the sludge pipe opens into a sludge layer separated in the separation chamber. 2. The sewage purification device according to claim 1, wherein the other end of the sludge pipe communicates with the bottom of the second aeration chamber. 3. The sewage purification device according to claim 1, wherein the other end of the sludge pipe opens at the bottom of the treatment tank.
JP55002820A 1980-01-14 1980-01-14 Sewage purification equipment Expired JPS5815037B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP55002820A JPS5815037B2 (en) 1980-01-14 1980-01-14 Sewage purification equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP55002820A JPS5815037B2 (en) 1980-01-14 1980-01-14 Sewage purification equipment

Publications (2)

Publication Number Publication Date
JPS56100697A JPS56100697A (en) 1981-08-12
JPS5815037B2 true JPS5815037B2 (en) 1983-03-23

Family

ID=11540042

Family Applications (1)

Application Number Title Priority Date Filing Date
JP55002820A Expired JPS5815037B2 (en) 1980-01-14 1980-01-14 Sewage purification equipment

Country Status (1)

Country Link
JP (1) JPS5815037B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63149299U (en) * 1987-09-17 1988-09-30

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5231557A (en) * 1975-09-05 1977-03-10 Kogyo Kaihatsu Kenkyusho Method of enriching oxygen and apparatus thereof
JPS5259955A (en) * 1975-11-11 1977-05-17 Kogyo Kaihatsu Kenkyusho Kk Waste water purifying method and its device
JPS5633091A (en) * 1979-08-29 1981-04-03 Kogyo Kaihatsu Kenkyusho Soil water purifying method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5231557A (en) * 1975-09-05 1977-03-10 Kogyo Kaihatsu Kenkyusho Method of enriching oxygen and apparatus thereof
JPS5259955A (en) * 1975-11-11 1977-05-17 Kogyo Kaihatsu Kenkyusho Kk Waste water purifying method and its device
JPS5633091A (en) * 1979-08-29 1981-04-03 Kogyo Kaihatsu Kenkyusho Soil water purifying method

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JPS56100697A (en) 1981-08-12

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