JPH06304589A - Treatment of return water - Google Patents

Treatment of return water

Info

Publication number
JPH06304589A
JPH06304589A JP9613893A JP9613893A JPH06304589A JP H06304589 A JPH06304589 A JP H06304589A JP 9613893 A JP9613893 A JP 9613893A JP 9613893 A JP9613893 A JP 9613893A JP H06304589 A JPH06304589 A JP H06304589A
Authority
JP
Japan
Prior art keywords
return water
phosphorus
tank
water
sludge
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
JP9613893A
Other languages
Japanese (ja)
Inventor
Kiwamu Matsubara
極 松原
Shigehiro Suzuki
重浩 鈴木
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP9613893A priority Critical patent/JPH06304589A/en
Publication of JPH06304589A publication Critical patent/JPH06304589A/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

  • Activated Sludge Processes (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To provide the method for treatment of return water to be generated from a secondary treatment stage of a sewer treatment plant capable of removing the phosphorus in the return water and decreasing the burden of a water treatment system. CONSTITUTION:The excess sludge after the secondary treatment of the sewer is separated to the return water and thickened sludge by a gravity thickening vessel 4. A part of the thickened sludge is added to the return water at such a ratio at which the concn. of the MLSS thereof attains >=100mg/L. The return water is then aerated in a phosphorus removing vessel 6. As a result, the thickened sludge changes from an anaerobic to aerobic state and, therefore, the phosphorus in the return water can excessively be taken, by which the phosphorus in the return water is removed.

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、下水処理場の二次処理
工程から発生する返流水の処理方法に関するものであ
り、特に返流水からのリン除去を目的とした返流水の処
理方法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 for treating return water generated from a secondary treatment process in a sewage treatment plant, and more particularly to a method for treating return water for removing phosphorus from the return water. Is.

【0002】[0002]

【従来の技術】図4に示すように、下水を最初沈澱池
1、曝気槽2、最終沈澱池3に順次通過させ、最終沈澱
池3の上澄水を二次処理水として放流することは従来か
ら知られている。そして最終沈澱池3から出た汚泥は、
一部が返送汚泥として曝気槽2に返送されるが、大部分
は余剰汚泥として重力濃縮槽4で重力濃縮により固液分
離され、濃縮汚泥は脱水機5で脱水処理される一方、返
流水は曝気槽2へそのまま返流されていた。
2. Description of the Related Art As shown in FIG. 4, sewage is first passed through a first settling tank 1, an aeration tank 2, and a final settling tank 3, and the supernatant water of the final settling tank 3 is discharged as secondary treated water. Known from. And the sludge from the final sedimentation pond 3
Part of it is returned to the aeration tank 2 as return sludge, but most of it is subjected to solid-liquid separation by gravity concentration in the gravity concentration tank 4 as excess sludge, and the concentrated sludge is dehydrated by the dehydrator 5, while the return water is It was returned to the aeration tank 2 as it was.

【0003】しかし、余剰汚泥が重力濃縮槽4で重力濃
縮される際に嫌気状態となるため、余剰汚泥に取り込ま
れていたリンが返流水中に放出される現象が生じ、この
ために返流水中のリン濃度が高くなって曝気槽2へ返流
した場合に水処理系の負荷を増加させるという問題があ
った。
However, since the excess sludge becomes anaerobic when it is gravity-concentrated in the gravity thickening tank 4, there occurs a phenomenon in which phosphorus taken up in the excess sludge is released into the return water, which causes the return flow. There is a problem that the load of the water treatment system is increased when the phosphorus concentration in the water becomes high and the phosphorus is returned to the aeration tank 2.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決して、返流水中のリンを除去して水処理
系の負荷を軽減させることができる返流水の処理方法を
提供するために完成されたものである。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned conventional problems and provides a method for treating return water by removing phosphorus in the return water to reduce the load on the water treatment system. It was completed in order to do.

【0005】[0005]

【課題を解決するための手段】上記の課題を解決するた
めになされた本発明は、下水を二次処理した後の余剰汚
泥を重力濃縮槽で返流水と濃縮汚泥とに固液分離した
後、返流水にそのMLSS濃度が1000mg/L以上となるよ
うに濃縮汚泥の一部を添加してリン除去槽で曝気し、濃
縮汚泥に返流水中のリンを過剰摂取させることによって
返流水中のリンを除去することを特徴とするものであ
る。
The present invention, which has been made to solve the above-mentioned problems, has a method of solid-liquid separating excess sludge after secondary treatment of sewage into return water and concentrated sludge in a gravity concentration tank. , A part of the concentrated sludge is added to the returned water so that the MLSS concentration is 1000 mg / L or more, and aeration is performed in the phosphorus removal tank, and the concentrated sludge is excessively ingested with phosphorus in the returned water. It is characterized by removing phosphorus.

【0006】以下に本発明を図1のフローシートによっ
て更に詳細に説明する。図1に示すように、最初沈澱池
1、曝気槽2、最終沈澱池3によって下水を二次処理し
た後の余剰汚泥は、従来と同様に重力濃縮槽4で重力濃
縮されて返流水と濃縮汚泥とに分離される。なおここで
濃縮される汚泥には、最初沈澱池1から発生する初沈汚
泥を一部含ませてもよい。
The present invention will be described in more detail below with reference to the flow sheet of FIG. As shown in FIG. 1, the excess sludge after the secondary treatment of the sewage by the first settling tank 1, the aeration tank 2, and the final settling tank 3 is gravity-concentrated in the gravity thickening tank 4 in the same manner as the conventional one, and is condensed with the return water. It is separated into sludge. The sludge concentrated here may include a part of the initial sludge generated from the first settling basin 1.

【0007】本発明では、この返流水に濃縮汚泥の一部
を添加する。その添加量は返流水のMLSS濃度が1000
mg/L以上となるようにする。またその添加量は濃縮汚泥
の総体積の1/4 〜1/5 程度が適当である。そして濃縮汚
泥が添加された返流水は次のリン除去槽6で1〜3時間
程度曝気される。このときのDOは約2ppm 以上が好ま
しい。前記したように重力濃縮槽4においては汚泥は嫌
気状態となり、飢餓状態にあるが、リン除去槽6で曝気
されて好気状態に変化すると返流水中のリンを過剰摂取
し、返流水中のリンは除去される。
In the present invention, a part of the concentrated sludge is added to this return water. The amount of addition is 1000 MLSS concentration of the return water.
It should be more than mg / L. Also, it is appropriate to add about 1/4 to 1/5 of the total volume of concentrated sludge. Then, the returned water to which the concentrated sludge is added is aerated in the next phosphorus removing tank 6 for about 1 to 3 hours. At this time, DO is preferably about 2 ppm or more. As described above, the sludge becomes anaerobic and starved in the gravity concentration tank 4, but when it is aerated in the phosphorus removal tank 6 and changes to an aerobic state, it excessively ingests phosphorus in the return water, and Phosphorus is removed.

【0008】重力濃縮槽4から出た濃縮汚泥は脱水機5
で脱水処理され、脱水ケーキと脱水ろ液とに分離される
が、破線で示すようにこの脱水ろ液を返流水とともにリ
ン除去槽6へ送ることもできる。
The concentrated sludge discharged from the gravity thickening tank 4 is a dehydrator 5.
The dehydrated cake is separated into a dehydrated cake and a dehydrated filtrate, but this dehydrated filtrate can be sent to the phosphorus removing tank 6 together with the return water as shown by a broken line.

【0009】リン除去槽6を出た返流水は固液分離槽7
で処理水とリン除去槽余剰汚泥とに分離され、処理水は
曝気槽2へ返流される。この処理水はリンが除去された
ものであるから、水処理系の負荷を従来よりも軽減する
ことができる。なお、固液分離槽7で嫌気状態となると
リンの放出が起こるので、汚泥が嫌気状態とならない遠
心濃縮等を用いることが好ましい。
Returned water from the phosphorus removal tank 6 is a solid-liquid separation tank 7
Is separated into treated water and excess sludge in the phosphorus removal tank, and the treated water is returned to the aeration tank 2. Since this treated water is one from which phosphorus has been removed, the load on the water treatment system can be reduced more than before. Since phosphorus is released when the solid-liquid separation tank 7 becomes anaerobic, it is preferable to use centrifugal concentration or the like, which does not make the sludge anaerobic.

【0010】[0010]

【実施例】以下に本発明の実施例を示す。図1の最終沈
澱池3から出た5000mg/Lの余剰汚泥を重力濃縮槽4で24
時間重力濃縮して固液分離し、20000mg/L に汚泥を濃縮
した。この濃縮汚泥の1/5 を重力濃縮槽4から出る返流
水および脱水ろ液に加え、リン除去槽6で曝気して処理
水を得た。曝気時間は2時間であり、このときのMLS
Sは1200mg/Lである。その結果、返流水中のリンは15pp
m であったが処理水中のリンは1ppm まで減少し、また
返流水中のBODは100ppmであったが処理水中のBOD
は10ppm まで減少した。
EXAMPLES Examples of the present invention will be shown below. The excess sludge of 5000 mg / L discharged from the final settling tank 3 in Fig.
Gravity concentration was carried out for an hour to perform solid-liquid separation, and the sludge was concentrated to 20000 mg / L. One-fifth of this concentrated sludge was added to the return water and the dehydrated filtrate from the gravity concentration tank 4 and aerated in the phosphorus removal tank 6 to obtain treated water. Aeration time is 2 hours and MLS at this time
S is 1200 mg / L. As a result, phosphorus in return water is 15pp
Although it was m, the phosphorus in the treated water decreased to 1 ppm, and the BOD in the return water was 100 ppm, but the BOD in the treated water was
Was reduced to 10 ppm.

【0011】図2はこの場合におけるリン除去槽6の曝
気時間と処理水中のリン濃度との関係を示すグラフであ
り、曝気時間が1時間以下では十分なリンの摂取が行わ
れず、逆に3時間以上曝気してもリンの除去率はほとん
ど変わらないことを示している。
FIG. 2 is a graph showing the relationship between the aeration time of the phosphorus removal tank 6 and the phosphorus concentration in the treated water in this case. When the aeration time is 1 hour or less, sufficient phosphorus intake is not performed, and conversely 3 This indicates that the phosphorus removal rate remains almost unchanged even after aeration for a longer time.

【0012】また、図3はリン除去槽6におけるMLS
Sと処理水中のリン濃度との関係を示すグラフであり、
MLSSは1000mg/L以上と高い方が除去量は多いが、10
00〜1500mg/Lで十分であることが分かる。MLSSを必
要以上に高くすると後段の固液分離工程の負荷が高くな
るので好ましくない。
Further, FIG. 3 shows the MLS in the phosphorus removing tank 6.
It is a graph which shows the relationship between S and the phosphorus concentration in treated water,
The higher the MLSS is 1000 mg / L or more, the larger the removal amount is, but 10
It turns out that 00 to 1500 mg / L is sufficient. If the MLSS is made higher than necessary, the load of the solid-liquid separation step in the latter stage becomes high, which is not preferable.

【0013】[0013]

【発明の効果】以上に説明したように、本発明によれば
下水の二次処理工程からの返流水に濃縮汚泥の一部を添
加してリン除去槽で曝気し、濃縮汚泥に返流水中のリン
を過剰摂取させるようにしたので、返流水中のリンを除
去して水処理系の負荷を軽減させることができる利点が
ある。
As described above, according to the present invention, a part of the concentrated sludge is added to the return water from the secondary treatment step of the sewage and aerated in the phosphorus removal tank, and the concentrated sludge is returned to the return water. Since it was made to excessively ingest phosphorus, there is an advantage that phosphorus in the return water can be removed to reduce the load on the water treatment system.

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

【図1】本発明の処理工程を示すフローシートである。FIG. 1 is a flow sheet showing the processing steps of the present invention.

【図2】実施例におけるリン除去槽の曝気時間と処理水
中のリン濃度との関係を示すグラフである。
FIG. 2 is a graph showing the relationship between the aeration time of a phosphorus removal tank and the phosphorus concentration in treated water in an example.

【図3】実施例におけるリン除去槽のMLSSと処理水
中のリン濃度との関係を示すグラフである。
FIG. 3 is a graph showing the relationship between the MLSS of the phosphorus removal tank and the phosphorus concentration in the treated water in the examples.

【図4】従来の下水処理工程を示すフローシートであ
る。
FIG. 4 is a flow sheet showing a conventional sewage treatment process.

【符号の説明】 1 最初沈澱池 2 曝気槽 3 最終沈澱池 4 重力濃縮槽 5 脱水機 6 リン除去槽 7 固液分離槽[Explanation of code] 1 First settling tank 2 Aeration tank 3 Final settling tank 4 Gravity concentration tank 5 Dehydrator 6 Phosphorus removal tank 7 Solid-liquid separation tank

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 下水を二次処理した後の余剰汚泥を重力
濃縮槽で返流水と濃縮汚泥とに固液分離した後、返流水
にそのMLSS濃度が1000mg/L以上となるように濃縮汚
泥の一部を添加してリン除去槽で曝気し、濃縮汚泥に返
流水中のリンを過剰摂取させることによって返流水中の
リンを除去することを特徴とする返流水の処理方法。
1. The excess sludge after the secondary treatment of sewage is subjected to solid-liquid separation into return water and concentrated sludge in a gravity concentration tank, and then the concentration of MLSS in the return water is 1000 mg / L or more. A method for treating return water, which comprises removing part of the return water by aeration in a phosphorus removal tank and causing the concentrated sludge to excessively ingest phosphorus in the return water.
JP9613893A 1993-04-22 1993-04-22 Treatment of return water Pending JPH06304589A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9613893A JPH06304589A (en) 1993-04-22 1993-04-22 Treatment of return water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9613893A JPH06304589A (en) 1993-04-22 1993-04-22 Treatment of return water

Publications (1)

Publication Number Publication Date
JPH06304589A true JPH06304589A (en) 1994-11-01

Family

ID=14157035

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9613893A Pending JPH06304589A (en) 1993-04-22 1993-04-22 Treatment of return water

Country Status (1)

Country Link
JP (1) JPH06304589A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08117788A (en) * 1994-10-21 1996-05-14 Ngk Insulators Ltd Treatment of return water
KR100410896B1 (en) * 2000-12-28 2003-12-24 경기도(보건환경연구원) Intermittently aerating dewatered filtrate injection method for treatment of organic matter, N and P
CN110436712A (en) * 2012-11-27 2019-11-12 汉普顿道路环境卫生区 Method and apparatus for the wastewater treatment for using weight to select
US11999641B2 (en) 2021-03-12 2024-06-04 Hampton Roads Sanitation District Method and apparatus for multi-deselection in wastewater treatment

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56150493A (en) * 1980-04-22 1981-11-20 Ebara Infilco Co Ltd Disposal of organic waste water
JPS59112900A (en) * 1982-12-21 1984-06-29 Ebara Infilco Co Ltd Treatment of organic waste water
JPH02293094A (en) * 1989-05-02 1990-12-04 Inax Corp Method for removing phosphorus in sewage

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56150493A (en) * 1980-04-22 1981-11-20 Ebara Infilco Co Ltd Disposal of organic waste water
JPS59112900A (en) * 1982-12-21 1984-06-29 Ebara Infilco Co Ltd Treatment of organic waste water
JPH02293094A (en) * 1989-05-02 1990-12-04 Inax Corp Method for removing phosphorus in sewage

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08117788A (en) * 1994-10-21 1996-05-14 Ngk Insulators Ltd Treatment of return water
KR100410896B1 (en) * 2000-12-28 2003-12-24 경기도(보건환경연구원) Intermittently aerating dewatered filtrate injection method for treatment of organic matter, N and P
CN110436712A (en) * 2012-11-27 2019-11-12 汉普顿道路环境卫生区 Method and apparatus for the wastewater treatment for using weight to select
US11999641B2 (en) 2021-03-12 2024-06-04 Hampton Roads Sanitation District Method and apparatus for multi-deselection in wastewater treatment

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