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JPS5930158B2 - How to treat sewage - Google Patents
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JPS5930158B2 - How to treat sewage - Google Patents

How to treat sewage

Info

Publication number
JPS5930158B2
JPS5930158B2 JP55185776A JP18577680A JPS5930158B2 JP S5930158 B2 JPS5930158 B2 JP S5930158B2 JP 55185776 A JP55185776 A JP 55185776A JP 18577680 A JP18577680 A JP 18577680A JP S5930158 B2 JPS5930158 B2 JP S5930158B2
Authority
JP
Japan
Prior art keywords
sewage
inflow
cycle
treatment
discharge
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
JP55185776A
Other languages
Japanese (ja)
Other versions
JPS57110385A (en
Inventor
登 早川
茂 稲見
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.)
NISHIHARA KANKYO EISEI KENKYUSHO KK
Original Assignee
NISHIHARA KANKYO EISEI KENKYUSHO 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 NISHIHARA KANKYO EISEI KENKYUSHO KK filed Critical NISHIHARA KANKYO EISEI KENKYUSHO KK
Priority to JP55185776A priority Critical patent/JPS5930158B2/en
Publication of JPS57110385A publication Critical patent/JPS57110385A/en
Publication of JPS5930158B2 publication Critical patent/JPS5930158B2/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

  • Activated Sludge Processes (AREA)

Description

【発明の詳細な説明】 この発明は、汚水の活性スラッジ処理方法の改良に関す
るものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a method for treating wastewater with activated sludge.

工場廃水、家庭廃水、下水、し尿等の廃水の処理方法と
して活性スラッジ処理方法が広(普及されている。
Activated sludge treatment methods are becoming widespread as a treatment method for wastewater such as factory wastewater, domestic wastewater, sewage, and human waste.

そして、活性スラッジ処理の方法の一つとじてバッチ処
理があり、バッチ処理は返送手段を必要とせず、ばつ気
槽と沈殿槽が一つの槽でよ(、さらに完全静止状態で沈
殿処理が行える等の多くの長所がある。
Batch processing is one of the activated sludge processing methods. Batch processing does not require a return means, and the aeration tank and sedimentation tank are all in one tank (furthermore, the sedimentation process can be carried out in a completely still state). It has many advantages such as

しかし、従来のバッチ処理は、ばつ気工程の間のみに汚
水を流入するのが一般的であり流入時間が限定されない
汚水を対象とする場合は、放流サイクルから次の放流サ
イクルまでの流入水を貯留する必要があり、特にこの容
量は最大流入量に応じて定めるため、大容量の貯留槽が
必須要件となっていた。
However, in conventional batch processing, wastewater generally flows in only during the aeration process, and when dealing with wastewater whose inflow time is not limited, the inflow water from one discharge cycle to the next discharge cycle is processed. It is necessary to store the water, and in particular, this capacity is determined according to the maximum inflow, so a large-capacity storage tank has become an essential requirement.

このためこのような廃水処理には、バッチ処理は採用さ
れず、昼間のみに汚水が発生するような工場廃水等、汚
水の流入が特定の条件にあてはまる時のみわずかに利用
されて(・た。
For this reason, batch processing is not used for such wastewater treatment, and is only used to a limited extent when specific conditions are met for the inflow of sewage, such as factory wastewater where sewage is generated only during the day.

また、汚水の流入を処理サイクルに合せて制限しない連
続流入とし、槽内をばつ気、沈殿、放流のサイクルを繰
り返す処理が提案され、この方法によれば沈殿室や汚泥
の返送が必要ないというバッチ処理の効果はそのままで
連続的に流入する一般の汚水を効率よ(処理することが
できる。
In addition, a treatment method has been proposed in which the inflow of sewage is made to flow continuously without being restricted according to the treatment cycle, and the cycle of aeration, sedimentation, and discharge is repeated in the tank.With this method, there is no need for a settling chamber or return of sludge. Continuously flowing general wastewater can be efficiently treated while retaining the effects of batch processing.

つまりこの方法によれば、汚水の貯留槽を設ける必要が
殆んどな(、一槽で処理できるという効果を有する。
In other words, this method has the advantage that there is almost no need to provide a wastewater storage tank (it can be treated in one tank).

しかし、この方法でも槽内体が放流サイクルから次の放
流サイクルまでの流入水を貯留するので、このための余
裕容積を必要とし、この余裕容積も最大流入量に応じて
定める必要があるので、流入量の変動が大きい場合に槽
内体の容積を太きくしなければならないという欠点があ
った。
However, even with this method, since the tank interior stores inflow water from one discharge cycle to the next discharge cycle, a surplus volume is required for this purpose, and this surplus volume also needs to be determined according to the maximum inflow volume. There was a drawback that the volume of the tank interior had to be increased when there were large fluctuations in the inflow amount.

この発明は、上記の問題点を除去し、汚水を流入する槽
体内で汚水をばつ気、沈殿、上澄放流の連続工程を繰り
返し制御し、且つこの工程の1サイクル時間を流入量に
合せて変更し、槽容量を小さくできる汚水処理方法を提
供することを目的とする。
This invention eliminates the above problems by repeatedly controlling the continuous process of aeration, sedimentation, and supernatant discharge of wastewater in a tank body into which wastewater flows, and also by adjusting the cycle time of this process to match the inflow amount. The purpose of the present invention is to provide a sewage treatment method that can be modified to reduce tank capacity.

以下この発明の実施例を図面に基づき説明する。Embodiments of the present invention will be described below based on the drawings.

第1図は、この発明の汚水の処理方法に用いられる汚水
処理装置の断面図を示し、第3図は、第1図の汚水処理
装置を制御する制御装置の説明図である。
FIG. 1 shows a sectional view of a sewage treatment device used in the sewage treatment method of the present invention, and FIG. 3 is an explanatory diagram of a control device that controls the sewage treatment device of FIG. 1.

はぼ長方形の鉄筋コンクリートその他適当な材料から成
る槽体1の一端1aに汚水を連続流入するために汚水流
入口2が設けられ、この一端1aに近接して短絡(ショ
ートサーキット)防止のための仕切壁3が下端を約30
07W7M位の高さの開口部3aを形成上て配置されて
いる。
A sewage inlet 2 is provided for continuous flow of sewage into one end 1a of a rectangular tank body 1 made of reinforced concrete or other suitable material, and a partition is provided adjacent to this end 1a to prevent short circuits. Wall 3 has a lower end of about 30
It is arranged to form an opening 3a with a height of about 07W7M.

そしてこの仕切壁3と一端1aとで流入ゾーン4が構成
されると共に仕切壁3と槽体1の他端1bとでばつ気室
5が構成される。
The partition wall 3 and one end 1a constitute an inflow zone 4, and the partition wall 3 and the other end 1b of the tank body 1 constitute an air chamber 5.

この槽体1内に収容された汚水の表面から上澄液を放流
するために、汚水流入口20反対側の他端1bにて隣接
してデカンタ6が配置されている。
In order to discharge supernatant liquid from the surface of the sewage contained in the tank body 1, a decanter 6 is disposed adjacent to the other end 1b on the opposite side of the sewage inlet 20.

このデカンタ6は適当な形状をとりうるが、この例では
排出バイブロaの両側にスカムバッフルの役目をするフ
ロー)6bが固定され、曲管6Cにより軸パイプ7に接
続され、この軸パイプ7は槽壁を貫通し放流溝に適して
いる。
This decanter 6 can take any suitable shape, but in this example, flow pipes 6b serving as scum baffles are fixed on both sides of the discharge vibro a, and are connected to a shaft pipe 7 by a bent pipe 6C. Penetrates the tank wall and is suitable for a drainage ditch.

デカンタ6は、軸パイプ7で支持され高さ位置を駆動装
置8で前記軸パイプを回転させることによって上下動す
るようになっている。
The decanter 6 is supported by a shaft pipe 7, and its height can be moved up and down by rotating the shaft pipe with a drive device 8.

又この槽体1の底部には、空気供給器9が多数配置され
、所定時間のばつ気処理を施すため外部から空気を圧送
できるようになっている。
Further, a large number of air supply devices 9 are arranged at the bottom of the tank body 1, so that air can be fed under pressure from the outside in order to carry out aeration treatment for a predetermined period of time.

しかもこの槽体1内は連続して流入した汚水に空気を所
定の時間にわたって散気拡散させるばつ気処理工程及び
所定の時間にわたって沈殿させる沈殿処理工程、上澄液
体を所定の時間にわたって放流する上澄放流処理工程の
一連のサイクルを(り返すように制御される。
In addition, the inside of this tank body 1 includes an aeration process in which air is diffused and diffused over a predetermined period of time into the wastewater that has continuously flowed in, a precipitation treatment process in which air is precipitated over a predetermined period of time, and a supernatant liquid is discharged over a predetermined period of time. It is controlled to repeat a series of cycles of the clear discharge treatment process.

そしてこのために制御装置、例えばコントロールパネル
10が外部に配置してあり、この制御装置により流量計
で計測した流入量に応じて各工程の所要時間を制御する
For this purpose, a control device, for example, a control panel 10, is disposed outside, and this control device controls the time required for each step in accordance with the inflow amount measured by a flow meter.

たとえば第2図イ2口のサイクルパターン図に示すよう
にばつ気処理を4.5時間、沈殿処理を1時間、上澄放
流処理を0.5時間に設定する1サイクルに6時間を要
する6時間サイクル、ばつ気処理を1.5時間、沈殿処
理を1時間、上澄放流処理を0.5時間に設定する1サ
イクルに3時間を要する3時間サイクルの2つのサイク
ルパターンをもち、これを適宜選定するようになってい
る。
For example, as shown in the 2-port cycle pattern diagram in Figure 2, it takes 6 hours for one cycle in which the aeration treatment is set for 4.5 hours, the sedimentation treatment is set for 1 hour, and the supernatant discharge treatment is set for 0.5 hours6. It has two cycle patterns: a 3-hour cycle, in which the aeration treatment is set to 1.5 hours, the sedimentation treatment is set to 1 hour, and the supernatant discharge treatment is set to 0.5 hours. It is designed to be selected appropriately.

通常時6時間サイクルとすれば槽体1内の上部の余裕容
積Vは6時間の流入量に対する余裕容積になるが、これ
を3時間サイクルとすれば、前記Vは、3時間の流入水
に対する余裕容積となるため流入量が2倍となっても処
理は可能となる。
If the normal cycle is 6 hours, then the upper part of the tank body 1 has an extra volume V for the inflow amount for 6 hours, but if this is a 3 hour cycle, then the above V is the extra volume for the inflow water for 3 hours. Because of the extra capacity, processing is possible even if the inflow volume is doubled.

なお、沈殿時間、放流時間は、物理的に最短時間がきま
るため、はぼ一定とした方がよい。
Note that the precipitation time and discharge time should be kept approximately constant because the minimum time is determined physically.

また必要な場合、サイクルの変更に伴ないばつ気処理の
ばつ気強度を変更してもよいが、これは一定としても一
日の全除去有機物量が大きく変化しなければ問題とはな
らない。
Furthermore, if necessary, the aeration intensity of the aeration treatment may be changed as the cycle is changed, but even if this is constant, it will not be a problem as long as the total amount of organic matter removed per day does not change significantly.

但し、全て6時間サイクルの場合はばつ気晴間は1日に
′ 18時間、全て3時間サイクルの場合は1日に12
時間、になるのでサイクルパターンの変更を流入パター
ン等に合せて計画することが望ましい。
However, if all 6-hour cycles are used, the distraction period will be 18 hours per day, and if all 3-hour cycles are used, the distraction period will be 12 hours per day.
Therefore, it is desirable to plan changes to the cycle pattern according to the inflow pattern, etc.

尚前記槽体1内の仕切壁3の下端開口部3a高さを30
0mmに設定したのは、ばつ気室5の攪拌の際流入ゾー
ン4との汚水の混合度が適当となるためである。
Note that the height of the lower end opening 3a of the partition wall 3 in the tank body 1 is set to 30
The reason why it is set to 0 mm is that the degree of mixing of wastewater with the inflow zone 4 during agitation in the aeration chamber 5 is appropriate.

こうすると汚泥は、流入ゾーン4で有機物負荷が非常に
高い状態におかれるため、沈殿性が改善され処理効果が
高くなる。
In this way, the sludge is placed in a state where the organic matter load is very high in the inflow zone 4, so that the settling property is improved and the treatment effect is enhanced.

以上の如く、この発明の汚水の処理方法によれば、汚水
をばつ気、沈殿、上澄放流するという1サイクルの所要
時間を流入量に合せて変更できるようにし、流入量が多
いときには1サイクルの時間を短かくし、流入量が少な
いときは1サイクルの時間を長くすることによって汚水
の流入量が変動しても汚水貯留のための槽容積を小さく
でき、かつ十分な処理ができる。
As described above, according to the sewage treatment method of the present invention, the time required for one cycle of aeration, sedimentation, and supernatant discharge of sewage can be changed according to the inflow amount, and when the inflow amount is large, one cycle By shortening the time for sewage and lengthening the time for one cycle when the amount of inflow is small, the volume of the tank for storing sewage can be reduced even if the amount of sewage flowing in fluctuates, and sufficient treatment can be achieved.

しかも沈殿槽、返送手段等の余分の設備の必要がない。Furthermore, there is no need for extra equipment such as a settling tank or return means.

なお、上記実施例では、処理サイクルに合せて制限する
ことな(連続流入する汚水処理方法のみについて説明し
たが、流入を制限する通常のバッチ処理方法においても
、その汚水貯留のための容積を小さくできるという同様
の効果が得られる。
In addition, in the above example, only the sewage treatment method in which the inflow is continuously inflowed without being restricted according to the treatment cycle, but even in the normal batch treatment method in which the inflow is restricted, the volume for storing the sewage can be reduced. A similar effect can be obtained.

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

第1図はこの発明の方法に用いる汚水処理装置の断面図
、第2図イ2口はこの発明の実施例を示すサイクルパタ
ーン図、第3図は第1図の処理装置の制御システム説明
図である。 1・・・・・・槽体、1a・・・・・・一端、1b・・
・・・・他端、2・・・・・・汚水流入口、3・・・・
・・仕切壁、4・・・・・・流入ゾーン、5・・・・・
・ばつ気室、6・・・・・・デカンタ、10・・・・・
・制御装置。
Figure 1 is a sectional view of a sewage treatment equipment used in the method of this invention, Figure 2 A is a cycle pattern diagram showing an embodiment of this invention, and Figure 3 is an explanatory diagram of the control system of the treatment equipment of Figure 1. It is. 1... Tank body, 1a... One end, 1b...
...Other end, 2...Sewage inlet, 3...
...Partition wall, 4...Inflow zone, 5...
・Air chamber, 6...Decanter, 10...
·Control device.

Claims (1)

【特許請求の範囲】[Claims] 1 槽体内に収容された汚水なばつ気処理するばつ気工
程と、前記槽体内に収容された汚水を沈殿処理する沈殿
工程と、この沈殿工程で得られた上澄液を放流する放流
工程を有し、これらの工程を繰返すことによって汚水処
理を行うバッチ式活性汚泥法による汚水の処理方法にお
いて、前記放流工程の1つから次の放流工程までの1サ
イクルの時間を汚水の流入量に応じて、流入量が多いと
きには短か(なるように、また流入量が少ないときには
長(なるように変更することを特徴とする汚水の処理方
法。
1. An aeration step for aerating the sewage contained in the tank body, a precipitation step for precipitating the sewage contained in the tank body, and a discharge step for discharging the supernatant liquid obtained in this precipitation step. In a sewage treatment method using a batch activated sludge method in which sewage is treated by repeating these steps, the time of one cycle from one of the discharge steps to the next discharge step is determined according to the amount of inflow of sewage. A method for treating sewage characterized by changing the length to be short when the inflow is large and to long when the inflow is small.
JP55185776A 1980-12-27 1980-12-27 How to treat sewage Expired JPS5930158B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP55185776A JPS5930158B2 (en) 1980-12-27 1980-12-27 How to treat sewage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP55185776A JPS5930158B2 (en) 1980-12-27 1980-12-27 How to treat sewage

Publications (2)

Publication Number Publication Date
JPS57110385A JPS57110385A (en) 1982-07-09
JPS5930158B2 true JPS5930158B2 (en) 1984-07-25

Family

ID=16176684

Family Applications (1)

Application Number Title Priority Date Filing Date
JP55185776A Expired JPS5930158B2 (en) 1980-12-27 1980-12-27 How to treat sewage

Country Status (1)

Country Link
JP (1) JPS5930158B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6417555U (en) * 1987-07-22 1989-01-27

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60183083A (en) * 1984-02-29 1985-09-18 Nishihara Environ Sanit Res Corp Sewage treatment apparatus
JPS6137293U (en) * 1984-08-07 1986-03-07 株式会社 西原環境衛生研究所 Scum discharge device
JPH0248079Y2 (en) * 1984-12-29 1990-12-17

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6417555U (en) * 1987-07-22 1989-01-27

Also Published As

Publication number Publication date
JPS57110385A (en) 1982-07-09

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