JPH07214089A - Waste water treatment - Google Patents

Waste water treatment

Info

Publication number
JPH07214089A
JPH07214089A JP6016565A JP1656594A JPH07214089A JP H07214089 A JPH07214089 A JP H07214089A JP 6016565 A JP6016565 A JP 6016565A JP 1656594 A JP1656594 A JP 1656594A JP H07214089 A JPH07214089 A JP H07214089A
Authority
JP
Japan
Prior art keywords
sludge
waste water
biological activity
excess sludge
settling basin
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
JP6016565A
Other languages
Japanese (ja)
Inventor
Setsuo Takeuchi
節夫 竹内
Masahito Kunugi
正仁 功刀
Yasujirou Aoshika
安司郎 青鹿
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.)
Honshu Paper Co Ltd
Original Assignee
Honshu Paper 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 Honshu Paper Co Ltd filed Critical Honshu Paper Co Ltd
Priority to JP6016565A priority Critical patent/JPH07214089A/en
Publication of JPH07214089A publication Critical patent/JPH07214089A/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)

Abstract

PURPOSE:To effecively utilize the residual biological activity of excess sludge to lower BOD, etc., and to improve the efficiency in treating waste water by adding the excess sludge generated after activated-sludge treatment to the raw water in the initial settling basin while the biological activity of the excess sludge still remains. CONSTITUTION:Raw waste water is transferred from the initial settling basin to the final settling basin through an aerator. A part of the activated sludge separated from liq. in the final settling basin is recycled as return sludge in accordance with the operational condition of the aerator. Meanwhile, the remainder of activated sludge is dehydrated as return sludge, used in reclamation or incinerated. In this case, the excess sludge is added to the raw waste water in the initial settling basin when the biological activity of the sludge still remains. Consequently, the residual biological activity of the excess sludge is effectively utilized, BOD, etc., are lowered, and the efficiency in treating waste water is improved.

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、活性汚泥法による排水
処理方法の改良に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to improvement of a wastewater treatment method by the activated sludge method.

【0002】[0002]

【従来の技術】通常、活性汚泥法による排水処理におい
ては、標準活性汚泥法、分注法、完全混合法、再曝気法
などが用いられている。いずれも原排水を最初沈殿池か
らエアレーションタンクを経て最終沈殿池に至るのが処
理工程の中心であり、最終沈殿池で固液分離した活性汚
泥はエアレーションタンクの運転条件に合わせて一部は
返送汚泥として再利用されるが、残余は余剰汚泥として
汚泥処理工程へ排出し、脱水後埋め立て、もしくは焼却
処分されている。
2. Description of the Related Art Usually, in the wastewater treatment by the activated sludge method, a standard activated sludge method, a dispensing method, a complete mixing method, a re-aeration method and the like are used. In both cases, the main process is to pass the raw wastewater from the first settling tank to the final settling tank through the aeration tank.The activated sludge that is solid-liquid separated in the final settling tank is partially returned according to the operating conditions of the aeration tank. It is reused as sludge, but the rest is discharged as excess sludge to the sludge treatment process, and is dehydrated for landfill or incinerated.

【0003】[0003]

【発明が解決しようとする課題】本発明は、活性汚泥排
水処理からの余剰汚泥の利用に関するものであり、余剰
汚泥の持つ生物的活性を最後まで生かして、排水処理の
効率を向上させることを目的とするものである。
DISCLOSURE OF THE INVENTION The present invention relates to the use of surplus sludge from activated sludge wastewater treatment, and aims to improve the efficiency of wastewater treatment by fully utilizing the biological activity of excess sludge. It is intended.

【0004】[0004]

【課題を解決するための手段】本発明は、余剰汚泥を曝
気などの手段をもちいることなく、単に原排水へ添加す
るのみで主としてBODなどの数値を低下せしめる効果
があることを発見して完成したものである。
DISCLOSURE OF THE INVENTION It has been found that the present invention has an effect of mainly reducing numerical values such as BOD by simply adding excess sludge to raw wastewater without using means such as aeration. It has been completed.

【0005】通常、活性汚泥法による排水処理では、エ
アレーションタンク内のMLSSを略一定に保つように
運転条件が設定されるため、余剰汚泥の発生は避けられ
ず、これを無視して最終沈殿池で生じた活性汚泥を全て
エアレーションタンクへ戻すと、生物処理に必要なタン
ク内での滞留時間が短くなることと、曝気量に余裕が無
く生物を生かすための酸素量が不足するなどのために、
かえって処理性能が低下する。
[0005] Usually, in the wastewater treatment by the activated sludge method, operating conditions are set so as to keep the MLSS in the aeration tank substantially constant. Therefore, the generation of excess sludge is unavoidable. If all the activated sludge generated in step 2 is returned to the aeration tank, the retention time in the tank required for biological treatment will be shortened, and the amount of aeration will be insufficient and the amount of oxygen for living organisms will be insufficient. ,
On the contrary, the processing performance decreases.

【0006】[0006]

【実施例】本発明は、エアレーションタンクは正しい運
転条件に維持しておき、余剰汚泥を最初沈殿池に入る原
排水に添加、混合し、最初沈殿池での滞留中に残存生物
活性を利用して排水中の負荷成分を減じることにより、
排水処理の効率を向上させるものである。
EXAMPLE The present invention is to maintain the aeration tank under the correct operating conditions, add excess sludge to the raw wastewater entering the first settling tank, mix it, and utilize the residual biological activity during the retention in the first settling tank. By reducing the load components in the drainage by
It improves the efficiency of wastewater treatment.

【0007】したがって、余剰汚泥の添加、混合は最初
沈殿池の入り口以前であればどこでもよく、パイプなど
の接合で簡単に対応できる。最初沈殿池への液送でポン
プが使用されている場合にはポンプの入り口に接合する
ことが、混合を均一にする点で好ましいが、これに限る
ものではない。
Therefore, the excess sludge can be added and mixed anywhere before the entrance of the sedimentation tank, and it can be easily handled by joining pipes or the like. When the pump is first used to transfer the liquid to the settling tank, joining to the inlet of the pump is preferable in terms of uniform mixing, but it is not limited to this.

【0008】最初沈殿池での滞留時間中に、溶存酸素が
有効な範囲の時間は生物活性は持続しており、排水中の
負荷成分に対して生物処理が行われるため、例えばBO
Dでは10〜30%程度の減少がある。これは余剰汚泥
の混合比率、水温、滞留時間により変動する。
During the initial residence time in the settling tank, the biological activity is maintained for a time period within which dissolved oxygen is effective, and the load components in the wastewater are biologically treated.
In D, there is a reduction of about 10 to 30%. This varies depending on the mixing ratio of excess sludge, water temperature, and residence time.

【0009】[実施例1]テーブルテストの結果で示す
と、洋紙および板紙系混合排水に対し、余剰汚泥を体積
%で5%添加した場合、滞留時間1時間で26.3%、
2時間で31.7%、10%添加では、同じく1時間で
30.3%、2時間で38.5%のBODカット率が得
られた。原排水のBODは100mg/lである。
[Example 1] The results of the table test show that, when 5% by volume of excess sludge was added to the mixed wastewater of paper and board, 26.3% by residence time 1 hour,
When 31.7% was added in 2 hours and 10% was added, a BOD cut rate of 30.3% in 1 hour and 38.5% in 2 hours was obtained. The BOD of raw wastewater is 100 mg / l.

【0010】[実施例2]テーブルテストの結果で示す
と、板紙系クリフローター処理水(原排水COD260
mg/l)に対し、体積%で2%添加した場合、滞留時
間1時間で13.8%、2時間で27.9%、4%添加
では、同じく1時間で15.3%、2時間で29.4%
のCODカット率が得られた。
[Embodiment 2] The results of the table test show that the paperboard-based clarifter treated water (the original wastewater COD260
(mg / l), when 2% by volume is added, the residence time is 13.8% for 1 hour, 27.9% for 2 hours, and for 4%, the same is 15.3% for 1 hour and 2 hours. 29.4%
The COD cut rate of was obtained.

【0011】[実施例3]テーブルテストの結果で示す
と、古紙パルプ処理工程の排水(原排水COD640m
g/l)に対し、体積%で4%添加した場合、滞留時間
1時間で4.7%、2時間で3.1%、8%添加では、
同じく1時間で10.9%、2時間で14.1%のCO
Dカット率が得られた。
[Embodiment 3] The results of the table test show that wastewater from the waste paper pulp treatment process (raw wastewater COD 640 m
g / l), when 4% by volume% is added, the residence time is 4.7% for 1 hour, 3.1% for 2 hours, and 8% is added.
Similarly, 10.9% CO for 1 hour and 14.1% CO for 2 hours
The D cut rate was obtained.

【0012】[0012]

【発明の効果】本発明によれば、余剰汚泥を有効に活用
し、正規のエアレーションタンクによる活性汚泥処理に
先立った事前の混合処理でBOD、COD成分を減少さ
せることができるため、エアレーションタンクでの負荷
を減らし、排水処理工程の効率を高めることが可能であ
る。
According to the present invention, since excess sludge can be effectively utilized and BOD and COD components can be reduced by a prior mixing process prior to the activated sludge process by a regular aeration tank, the aeration tank can be used. It is possible to reduce the load on the wastewater and increase the efficiency of the wastewater treatment process.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】活性汚泥処理後に発生する余剰汚泥を、そ
の生物的活性が残存している間に、活性汚泥処理工程の
最初沈殿池で原排水に添加し、余剰汚泥の残存生物活性
を利用することを特徴とする排水処理方法。
1. Excess sludge generated after treatment of activated sludge is added to raw wastewater in the first settling tank of the activated sludge treatment process while the biological activity remains, and the residual biological activity of the excess sludge is utilized. A wastewater treatment method characterized by:
JP6016565A 1994-02-10 1994-02-10 Waste water treatment Pending JPH07214089A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6016565A JPH07214089A (en) 1994-02-10 1994-02-10 Waste water treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6016565A JPH07214089A (en) 1994-02-10 1994-02-10 Waste water treatment

Publications (1)

Publication Number Publication Date
JPH07214089A true JPH07214089A (en) 1995-08-15

Family

ID=11919818

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6016565A Pending JPH07214089A (en) 1994-02-10 1994-02-10 Waste water treatment

Country Status (1)

Country Link
JP (1) JPH07214089A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102863078A (en) * 2012-10-16 2013-01-09 山东省环境保护科学研究设计院 Method for treating chemical industrial wastewater

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102863078A (en) * 2012-10-16 2013-01-09 山东省环境保护科学研究设计院 Method for treating chemical industrial wastewater

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