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JPH05237487A - Treating apparatus for water - Google Patents

Treating apparatus for water

Info

Publication number
JPH05237487A
JPH05237487A JP4073297A JP7329792A JPH05237487A JP H05237487 A JPH05237487 A JP H05237487A JP 4073297 A JP4073297 A JP 4073297A JP 7329792 A JP7329792 A JP 7329792A JP H05237487 A JPH05237487 A JP H05237487A
Authority
JP
Japan
Prior art keywords
tank
sludge
contact aeration
water
aeration tank
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
JP4073297A
Other languages
Japanese (ja)
Inventor
Kazuo Fujita
一男 藤田
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.)
Nihon Kentetsu Co Ltd
Original Assignee
Nihon Kentetsu Co Ltd
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 Nihon Kentetsu Co Ltd filed Critical Nihon Kentetsu Co Ltd
Priority to JP4073297A priority Critical patent/JPH05237487A/en
Publication of JPH05237487A publication Critical patent/JPH05237487A/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

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Activated Sludge Processes (AREA)

Abstract

PURPOSE:To decrease generation of foaming and excess sludge and to improve treating performance by positioning alternatively a pair of aeration tanks and a pair of precipitation tanks and returning a sludge from the first precipitation tank to the first aeration tank and returning the sludge from the second precipitation tank to the second aeration tank. CONSTITUTION:The first precipitation tank 21 is placed between the contact aeration tank 11 and the second tank 12 and the second precipitation tank 22 is provided next to the second contact aeration tank. Sludges in the first and the second precipitation tanks are respectively returned to the first and the second contact, aeration tanks. The organism phases of a pair of the contact aeration tanks are made thereby to be independent each other and self-digestion is promoted and excess sludge is made less. In addition floating sludges are made more by returning the sludges and foaming is made less.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は接触曝気法によって廃水
を浄化する水処理装置に関し、とくに都市廃水もしくは
生活廃水など比較的多量の有機物を含む廃水の浄化に好
適に用い得る水処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a water treatment apparatus for purifying wastewater by a contact aeration method, and more particularly to a water treatment apparatus which can be suitably used for purifying wastewater containing a relatively large amount of organic substances such as urban wastewater or domestic wastewater.

【0002】[0002]

【従来の技術】従来、接触曝気法によって水を浄化する
水処理装置は接触曝気槽および処理水を受け入れて上澄
水を放流する沈澱槽から成り、さらに場合によってはそ
の前後に備えられて導入廃水の流量調整を行なう原水ピ
ットが設置される。図2はそのような従来の水処理装置
を示すものであって、この従来例では接触曝気槽は第1
室1と第2室2に区分され、該第2室に隣接して沈澱槽
3が在る。接触曝気槽の各室には生物接触濾材4および
ブロワ5から送られる空気を槽内に放出する散気装置6
が設けられている。7は廃水導入管であり、8は放流管
である。
2. Description of the Related Art Conventionally, a water treatment apparatus for purifying water by a contact aeration method comprises a contact aeration tank and a settling tank for receiving treated water and discharging supernatant water. A raw water pit will be installed to adjust the flow rate. FIG. 2 shows such a conventional water treatment apparatus. In this conventional example, the contact aeration tank is the first
It is divided into a chamber 1 and a second chamber 2, and a precipitation tank 3 is adjacent to the second chamber. An air diffuser 6 that discharges the air sent from the biological contact filter 4 and the blower 5 into each chamber of the contact aeration tank 6
Is provided. Reference numeral 7 is a wastewater introduction pipe, and 8 is a discharge pipe.

【0003】接触曝気槽の各室内に充填される接触濾材
4には微生物が付着し、ブロワ5から送られる空気を各
散気装置6から吐出することにより槽内の廃水を撹拌し
且つ微生物に酸素を送り、廃水中の有機物を微生物の接
触酸化作用によって分解し、処理する。接触曝気槽の第
2室で生物処理された水は沈澱槽3に導入され、そこで
汚泥と上澄水に分離され、上澄水は放流される。
Microorganisms adhere to the contact filter media 4 filled in each chamber of the contact aeration tank, and the air sent from the blower 5 is discharged from each air diffuser 6 to agitate the waste water in the tank and transform the microorganisms into microorganisms. Oxygen is sent to decompose organic matter in wastewater by catalytic oxidation of microorganisms for treatment. The water biologically treated in the second chamber of the contact aeration tank is introduced into the precipitation tank 3, where it is separated into sludge and supernatant water, and the supernatant water is discharged.

【0004】[0004]

【発明が解決しようとする課題】従来の装置では付着汚
泥が殆どであり、浮遊汚泥が少ないため全体の換算汚泥
(MLSS)が少なく、従って処理性能が良くなかっ
た。また、活性汚泥法と異なり、浮遊汚泥が少ないこと
から、食品や洗剤などの界面活性剤を含む生活廃水また
は都市廃水では発泡が多く、且つ汚泥の自己消化は全体
の換算汚泥量に比例するため汚泥の自己消化が進まず、
余剰汚泥が多く発生し、その発生量は30〜40%に達
する等の問題点があった。さらに接触曝気槽の各室が独
立の系になっていないため生物相が単一であり、従って
食物連鎖が進まず、この面からも余剰汚泥が多くなる。
In the conventional apparatus, most of the sludge is adhered, and the amount of suspended sludge is small, so that the total converted sludge (MLSS) is small, and therefore the treatment performance is not good. In addition, unlike the activated sludge method, since there is little floating sludge, foaming is large in domestic wastewater or urban wastewater containing surfactants such as food and detergent, and the self-extinction of sludge is proportional to the total converted sludge amount. Self-extinguishment of sludge does not proceed,
There was a problem that a large amount of excess sludge was generated and the generated amount reached 30 to 40%. Furthermore, since each chamber of the contact aeration tank does not have an independent system, there is a single biota, so the food chain does not progress, and excess sludge also increases from this aspect.

【0005】本発明は上記従来技術の問題点を解消する
ことであって、それ故、界面活性剤を含む廃水の処理に
おいても発泡および余剰汚泥の発生を少なくし、処理性
能を向上し得る接触曝気法による水処理装置を提供する
ことである。
The present invention is to eliminate the above-mentioned problems of the prior art. Therefore, even in the treatment of waste water containing a surfactant, the generation of foaming and excess sludge can be reduced, and the treatment performance can be improved. An object of the present invention is to provide a water treatment device by an aeration method.

【0006】[0006]

【課題を解決するための手段】本発明による水処理装置
の特徴は接触曝気槽が一対の槽11、12からなり、且
つその間に第1の沈澱槽21が配置され、第1の接触曝
気槽の処理水は第1の沈澱槽に送られ且つ第1の沈澱槽
の上澄水が第2の接触曝気槽に導入され、さらに第2の
接触曝気槽の処理水を受け入れる第2の沈澱槽22と、
第1の沈澱槽から第1の接触曝気槽に汚泥を返送する装
置および第2の沈澱槽から第2の接触曝気槽に汚泥を返
送する装置によって構成される。
A feature of the water treatment apparatus according to the present invention is that the contact aeration tank comprises a pair of tanks 11 and 12, and a first settling tank 21 is arranged between them, and a first contact aeration tank is provided. Treated water is sent to the first settling tank, the supernatant water of the first settling tank is introduced to the second contact aeration tank, and the second settling tank 22 for receiving the treated water of the second contact aeration tank 22. When,
It comprises a device for returning sludge from the first settling tank to the first contact aeration tank and a device for returning sludge from the second settling tank to the second contact aeration tank.

【0007】[0007]

【作用】この水処理装置では沈澱槽から各接触曝気槽に
汚泥を返送し、該汚泥は浮遊汚泥となるため、接触濾材
に生息する付着汚泥のほか可成りの浮遊汚泥が存在し、
全体の換算汚泥が多くなる。そのため汚泥の自己消化が
進み、且つ第1の接触曝気槽および第1の沈澱槽と第2
の接触曝気槽および第2の沈澱槽とは互に生物的に独立
した系となるため互に独立した生物相を形成し、従って
生物の食物連鎖が進み、それ故、余剰汚泥の発生量が少
なくなる。また、返送により浮遊汚泥が多くなるため発
泡も大幅に減少し、さらに処理性能が向上する。
In this water treatment device, sludge is returned from the settling tank to each contact aeration tank, and since the sludge becomes floating sludge, there is considerable floating sludge in addition to the adhered sludge inhabiting the contact filter medium.
The total conversion sludge increases. Therefore, the sludge self-extinguishes, and the first contact aeration tank, the first settling tank and the second sludge
The contact aeration tank and the second settling tank of the plant are biologically independent of each other, so that they form mutually independent biota, thus promoting the food chain of the organisms, and thus the amount of excess sludge generated. Less. Moreover, since the amount of suspended sludge increases due to the return, foaming is also greatly reduced, and the treatment performance is further improved.

【0008】[0008]

【実施例】次に図面を参照のもとに本発明の実施例に関
し説明する。図1はこの水処理装置の一例を示すもので
あって、図示のようにこの装置では一対の接触曝気槽1
1、12を含むほか、一対の沈澱槽21、22が備えら
れる。一方の沈澱槽、即ち第1の沈澱槽21は一対の接
触曝気槽の間に配置され、第1の接触曝気槽11の処理
水が該沈澱槽21に導入され且つその沈澱槽21の上澄
水が第2の接触曝気槽12に導入されるようになってい
る。
Embodiments of the present invention will now be described with reference to the drawings. FIG. 1 shows an example of this water treatment apparatus. As shown in the figure, this apparatus has a pair of contact aeration tanks 1
In addition to 1 and 12, a pair of precipitation tanks 21 and 22 are provided. One settling tank, that is, the first settling tank 21 is arranged between a pair of contact aeration tanks, and the treated water of the first contact aeration tank 11 is introduced into the settling tank 21 and the supernatant water of the settling tank 21. Is introduced into the second contact aeration tank 12.

【0009】従って、一対の接触曝気槽はその間に沈澱
槽21が介在するので生物的に互に独立した系になって
いる。他の沈澱槽22は第2の接触曝気槽12に隣接
し、第2の接触曝気槽12の処理水を受け入れ、上澄水
を放流するようになっている。これらの一対の接触曝気
槽および一対の沈澱槽は好ましくは図示のように一つの
大きな槽を区分することによって構成されるが、所望に
より別個の槽で構成されてもよい。なお、従来と同様に
各接触曝気槽内には生物接触濾材4および散気装置6が
設置され、各散気装置にはブロワ5から空気が送られ
る。処理すべき廃水は導入管7によって第1の接触曝気
槽11に送入され、第2の沈澱槽22の最終処理水は放
流管8によって放流される。
Therefore, the pair of contact aeration tanks are biologically independent from each other because the precipitation tank 21 is interposed therebetween. The other settling tank 22 is adjacent to the second contact aeration tank 12, receives the treated water of the second contact aeration tank 12, and discharges the supernatant water. The pair of contact aeration tanks and the pair of precipitation tanks are preferably constructed by dividing one large tank as shown in the figure, but may be composed of separate tanks if desired. As in the conventional case, the biological contact filter 4 and the air diffuser 6 are installed in each contact aeration tank, and air is sent from the blower 5 to each air diffuser. The waste water to be treated is fed into the first contact aeration tank 11 by the introduction pipe 7, and the final treated water in the second precipitation tank 22 is discharged by the discharge pipe 8.

【0010】さらに、この水処理装置では第1の沈澱槽
21内の汚泥を第1の接触曝気槽11に返送するため沈
澱槽21内にポンプ23が設置され、且つ該ポンプの吐
出側に接続され、そこから該槽を越えて第1の接触曝気
槽11の廃水入口側に延びる配管13が備えられる。第
2の沈澱槽22内の汚泥を第2の接触曝気槽12に返送
するため該沈澱槽内にポンプ24が設置され、且つ該ポ
ンプ24の吐出側に接続され、そこから該槽を越えて第
2の接触曝気槽12の流入側に延びる配管14が備えら
れる。
Further, in this water treatment apparatus, a pump 23 is installed in the settling tank 21 for returning the sludge in the first settling tank 21 to the first contact aeration tank 11, and is connected to the discharge side of the pump. And a pipe 13 extending from there to the wastewater inlet side of the first contact aeration tank 11 beyond the tank. A pump 24 is installed in the second settling tank 22 for returning the sludge in the second settling tank 22 to the second contact aeration tank 12, and is connected to the discharge side of the pump 24. A pipe 14 extending to the inflow side of the second contact aeration tank 12 is provided.

【0011】処理すべき原水は導入管7より第1の接触
曝気槽11に導入され、そこで散気装置6からの曝気に
より生物処理され、処理水は第1の沈澱槽21に送られ
る。沈澱槽21では大きな汚泥は沈降して分離され、上
澄水は第2の接触曝気槽12に導入され、そこで再度生
物処理される。第2の接触曝気槽12での処理水は第2
の沈澱槽22に送られ、汚泥は沈降し、上澄水が放流管
8により放流される。
Raw water to be treated is introduced into a first contact aeration tank 11 through an introduction pipe 7, where it is biologically treated by aeration from an air diffuser 6, and the treated water is sent to a first settling tank 21. In the settling tank 21, large sludge is settled and separated, and the supernatant water is introduced into the second contact aeration tank 12 where it is biologically treated again. The treated water in the second contact aeration tank 12 is the second
The sludge is sent to the sedimentation tank 22 and the supernatant water is discharged through the discharge pipe 8.

【0012】好ましくは図1に示すように第1の沈澱槽
21は第2の沈澱槽22より容量が小さくなっており、
従って第1の沈澱槽21での滞留時間は比較的短く、例
えば30分程度にとられ、大きな汚泥のみを沈降させ
る。一例では第1の沈澱槽21が30分の場合、第2の
沈澱槽22の滞留時間1.0〜1.5時間にとられる。第
1の沈澱槽内の沈降汚泥はポンプ23および配管13に
よって第1の接触曝気槽11に返送され且つ第2の沈澱
槽内の沈降汚泥はポンプ24および配管14によって第
2の接触曝気槽12に返送される。
Preferably, as shown in FIG. 1, the first settling tank 21 has a smaller capacity than the second settling tank 22,
Therefore, the residence time in the first settling tank 21 is relatively short, for example, about 30 minutes, and only large sludge is settled. In one example, when the first settling tank 21 is 30 minutes, the residence time of the second settling tank 22 is 1.0 to 1.5 hours. The settling sludge in the first settling tank is returned to the first contact aeration tank 11 by the pump 23 and the pipe 13, and the settling sludge in the second settling tank is set in the second contact aeration tank 12 by the pump 24 and the pipe 14. Will be returned to.

【0013】このように第1および第2の接触曝気槽1
1、12の間に第1の沈澱槽21が介在し且つ該沈澱槽
の上澄水が第2の接触曝気槽12に導入されるので、第
1の接触曝気槽11および第1の沈澱槽21に対し第2
の曝気槽12は生物的に独立の系となり、従って各接触
曝気槽では互に独立した生物相が発生する。そのため生
物の食物連鎖が進み、余剰汚泥が滅少する。
Thus, the first and second contact aeration tanks 1
Since the first precipitation tank 21 is interposed between the first and second tanks 12 and 12, and the supernatant water of the precipitation tank is introduced into the second contact aeration tank 12, the first contact aeration tank 11 and the first precipitation tank 21. Second against
The aeration tanks 12 are biologically independent systems, so that in each contact aeration tank, independent biota are generated. As a result, the food chain of living things progresses and excess sludge is reduced.

【0014】各接触曝気槽11、12には沈澱槽から汚
泥が返送されるので、接触濾材4に付着した汚泥のほ
か、多くの浮遊汚泥が加えられることになり、全体の換
算汚泥(MLSS)が増加する。従って、処理性能が向
上すると共に、汚泥の自己消化が進み、従って余剰汚泥
の発生量が大幅に減少する。とくに生活廃水などのよう
に界面活性剤を含む廃水の処理においても、返送による
多量の浮遊汚泥の存在により発泡が著しく減少する。
Since the sludge is returned from the settling tank to the contact aeration tanks 11 and 12, a large amount of floating sludge is added in addition to the sludge adhering to the contact filter medium 4, and the total converted sludge (MLSS) is added. Will increase. Therefore, the treatment performance is improved, and the self-extinction of the sludge is promoted, so that the amount of excess sludge generated is significantly reduced. Particularly in the treatment of wastewater containing a surfactant such as domestic wastewater, foaming is significantly reduced due to the presence of a large amount of suspended sludge caused by returning.

【0015】次に具体例を示すと、都市廃水の処理にお
いて従来技術では接触曝気槽第1室と第2室の合計滞留
時間6時間、沈澱槽での滞留が2時間であった。濾材と
してひも状のもので50%充填され、廃水(原水)BO
D100mg/Lで運転した場合、付着汚泥(換算ML
SS)2200mg/L、処理水質は平均BOD18m
g/Lであった。
As a concrete example, in the treatment of urban wastewater, in the prior art, the total residence time in the first and second chambers of the contact aeration tank was 6 hours, and the residence in the precipitation tank was 2 hours. 50% filled with string-like filter material, wastewater (raw water) BO
When operated at D100 mg / L, adhered sludge (converted ML
SS) 2200mg / L, average treated water quality is 18m
It was g / L.

【0016】本発明の装置では接触曝気第1槽で4時
間、第1沈澱槽で0.5時間、接触曝気第2槽で2時
間、第2(最終)沈澱槽で1.5時間それぞれ滞留し、
返送率は第1槽、第2槽とも30%で運転した場合、廃
水BOD100mg/Lで処理水の平均BOD6.4m
g/L、付着汚泥2200mg/L、浮遊汚泥500m
g/L、合計汚泥(MLSS)2700mg/Lであっ
た。また余剰汚泥に関しても従来30%のものが16%
と大幅に減少した。さらに廃水BODが1000mg/
Lの場合も同様な結果を得ている。
In the apparatus of the present invention, the contact aeration first tank 4 hours, the first precipitation tank 0.5 hours, the contact aeration second tank 2 hours, the second (final) precipitation tank 1.5 hours respectively. Then
When the return rate is 30% in both the first tank and the second tank, the wastewater BOD is 100 mg / L and the average BOD is 6.4 m.
g / L, adhered sludge 2200 mg / L, floating sludge 500 m
The total sludge (MLSS) was 2700 mg / L. As for the excess sludge, the conventional 30% is 16%
And drastically decreased. Waste water BOD is 1000 mg /
Similar results are obtained for L as well.

【0017】[0017]

【発明の効果】上記のように、本発明によれば汚泥の返
送により全体の換算汚泥が増加するため処理性能が向上
すると共に、2つの接触曝気槽では互に独立した生物相
が形成されるので、自己消化が進み、余剰汚泥が少なく
なる。さらに多量の浮遊汚泥の存在により発泡を著しく
減少することができる。
As described above, according to the present invention, the total conversion sludge is increased by returning sludge, so that the treatment performance is improved and independent biota are formed in the two contact aeration tanks. Therefore, self-extinguishing progresses and excess sludge decreases. Further, the presence of a large amount of suspended sludge can significantly reduce foaming.

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

【図1】本発明による水処理装置を概略的に示す側面図
である。
FIG. 1 is a side view schematically showing a water treatment device according to the present invention.

【図2】従来の接触曝気法による水処理装置を概略的に
示す側面図である。
FIG. 2 is a side view schematically showing a conventional water treatment device by a contact aeration method.

【符号の説明】[Explanation of symbols]

11 第1の曝気槽 12 第2の曝気槽 21 第1の沈澱槽 22 第2の沈澱槽 13 配管 14 配管 23 ポンプ 24 ポンプ 11 First Aeration Tank 12 Second Aeration Tank 21 First Precipitation Tank 22 Second Precipitation Tank 13 Piping 14 Piping 23 Pump 24 Pump

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 接触曝気法により水を浄化する第1およ
び第2の接触曝気槽と、前記接触曝気槽の間に在って前
記第1の接触曝気槽からその処理水を受け入れ且つ上澄
水を前記第2の接触曝気槽に移流する第1の沈澱槽と、
前記第2の接触曝気槽からその処理水を受け入れる第2
の沈澱槽と、前記第1の沈澱槽より前記第1の接触曝気
槽に汚泥を返送するポンプおよび配管からなる第1の返
送装置と、前記第2の沈澱槽より前記第2の接触曝気槽
に汚泥を返送するポンプおよび配管からなる第2の返送
装置を含む水処理装置。
1. A first and second contact aeration tank for purifying water by a contact aeration method, and a treated water which is present between the first contact aeration tank and receives the treated water from the first contact aeration tank and which is a supernatant water. A first settling tank for advancing the gas to the second contact aeration tank;
A second for receiving the treated water from the second contact aeration tank
Settling tank, a first returning device comprising a pump and a pipe for returning sludge from the first settling tank to the first contact aeration tank, and the second contacting aeration tank from the second settling tank A water treatment device including a second returning device including a pump and a pipe for returning sludge to the inside.
JP4073297A 1992-02-25 1992-02-25 Treating apparatus for water Pending JPH05237487A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4073297A JPH05237487A (en) 1992-02-25 1992-02-25 Treating apparatus for water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4073297A JPH05237487A (en) 1992-02-25 1992-02-25 Treating apparatus for water

Publications (1)

Publication Number Publication Date
JPH05237487A true JPH05237487A (en) 1993-09-17

Family

ID=13514091

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4073297A Pending JPH05237487A (en) 1992-02-25 1992-02-25 Treating apparatus for water

Country Status (1)

Country Link
JP (1) JPH05237487A (en)

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