JPH11698A - Sludge concentration treatment method - Google Patents
Sludge concentration treatment methodInfo
- Publication number
- JPH11698A JPH11698A JP9171150A JP17115097A JPH11698A JP H11698 A JPH11698 A JP H11698A JP 9171150 A JP9171150 A JP 9171150A JP 17115097 A JP17115097 A JP 17115097A JP H11698 A JPH11698 A JP H11698A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- aeration tank
- concentration
- sewage
- performance
- 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
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Activated Sludge Processes (AREA)
- Treatment Of Sludge (AREA)
Abstract
(57)【要約】
【課題】 小規模の設備に対しても適用でき、運転管理
が容易で安定した濃縮性能が得られるとともに、水処理
性能に対しても悪影響を及ぼすことのない汚泥の濃縮処
理方法を提供する。
【解決手段】 下水等の汚水を曝気槽2の活性汚泥によ
り生物処理を行い、余剰汚泥Dを濃縮減容化する汚水処
理設備において、曝気機7の運転時間帯に曝気槽2から
直接、余剰汚泥Dを引き抜いて機械式濃縮装置に導き、
水処理設備への1日当たりの積算処理水量に応じて、汚
泥濃縮装置5の運転時間を設定して運転することを特徴
とする。
(57) [Summary] PROBLEM TO BE SOLVED: Applicable to small-scale equipment, easy operation management and stable concentration performance are obtained, and sludge concentration that does not adversely affect water treatment performance. Provide a processing method. SOLUTION: In a sewage treatment facility for subjecting wastewater such as sewage to biological treatment using activated sludge in an aeration tank 2 and concentrating and reducing excess sludge D, excess waste is directly discharged from the aeration tank 2 during the operation time of the aerator 7. Pull out the sludge D and guide it to the mechanical concentrator
It is characterized in that the operation time of the sludge concentrating device 5 is set and operated according to the integrated amount of treated water per day to the water treatment facility.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、下水等の汚水を活
性汚泥により生物処理を行う汚水処理設備において、発
生する余剰汚泥の前処理手段として広く利用することが
できるようにした汚泥の濃縮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 sludge concentration treatment which can be widely used as a pretreatment means for excess sludge generated in a sewage treatment facility for biologically treating sewage or other sewage with activated sludge. It is about the method.
【0002】[0002]
【従来の技術】従来、標準法やオキシデーションディッ
チ法等の活性汚泥による汚水処理設備において汚泥の前
処理用として、重力式の濃縮槽が広く使用されてきた。2. Description of the Related Art Conventionally, gravity type thickening tanks have been widely used for pretreatment of sludge in a sewage treatment facility using activated sludge such as a standard method or an oxidation ditch method.
【0003】[0003]
【発明が解決しようとする課題】上記従来汚泥の濃縮処
理方法には、下水管の分流化や食生活の変化に伴う発生
汚泥の性状変化等により、汚泥の濃縮性が悪化してお
り、また小規模の設備ほど処理量が少ないのに対し、ポ
ンプの閉塞等の面から配管はあまり細くできず、過大な
ポンプで短時間の処理を行うため、安定した濃縮性能を
得るのが難しいという問題点があった。本発明は、上記
従来の汚泥の濃縮処理方法の有する問題点を解決し、小
規模の設備に対しても適用でき、運転管理が容易で安定
した濃縮性能が得られるとともに、水処理性能に対して
も悪影響を及ぼすことのない汚泥の濃縮処理方法を提供
することを目的とする。In the above-mentioned conventional method for concentrating sludge, the sludge condensing property is deteriorated due to a change in the properties of the generated sludge due to the separation of sewer pipes and changes in eating habits. The problem is that the smaller the equipment, the smaller the throughput, but the pipes cannot be made very thin due to the blockage of the pump, etc. There was a point. The present invention solves the above-mentioned problems of the conventional sludge concentration treatment method, can be applied to small-scale facilities, and can achieve stable concentration performance with easy operation management and water treatment performance. It is an object of the present invention to provide a sludge concentration treatment method which does not adversely affect the sludge.
【0004】[0004]
【課題を解決するための手段】上記目的を達成するた
め、本発明の汚泥の濃縮処理方法は、濃縮装置への供給
汚泥濃度を一定にして、安定した濃縮性能を確保するた
め、曝気機が運転されて槽内が十分攪拌混合されている
時間帯に曝気槽から定量ポンプにより引き抜き、機械濃
縮を行い、また機械濃縮の適用が好ましい生活排水主体
の汚水では、汚泥発生量が流入水量にほぼ比例すること
から、流入水量を計測する流量計を設け、流量計の測定
値から算出される1日当たりの積算処理水量に比例する
時間だけ濃縮装置を運転することを特徴とする。Means for Solving the Problems To achieve the above object, the method for concentrating sludge of the present invention uses an aerator to stabilize the concentration of sludge supplied to a concentrating apparatus and secure stable concentrating performance. During operation and during the time when the inside of the tank is sufficiently agitated and mixed, it is withdrawn from the aeration tank by a quantitative pump, and mechanical concentration is performed. Since the flow rate is proportional, a flow meter for measuring the amount of inflow water is provided, and the concentrator is operated for a time proportional to the integrated treated water amount per day calculated from the measured value of the flow meter.
【0005】上記の構成からなる本発明の汚泥の濃縮処
理方法は、発生汚泥量に見合っただけの余剰汚泥を濃縮
処理するため、曝気槽の汚泥混合液(MLSS)の濃度
が安定化し、これによって濃縮装置に供給する汚泥濃度
の日変動も小さくなるため、供用開始から計画流入水量
に達するまでの間においても、負荷変動に係わらず水処
理性能及び濃縮処理性能の安定化が図られる。In the sludge concentration treatment method of the present invention having the above-mentioned structure, the concentration of the sludge mixture (MLSS) in the aeration tank is stabilized because excess sludge is concentrated in accordance with the amount of generated sludge. As a result, the daily fluctuation of the concentration of sludge supplied to the concentrator becomes small, so that the water treatment performance and the concentration treatment performance are stabilized regardless of the load fluctuation from the start of operation to the time when the planned inflow water amount is reached.
【0006】[0006]
【発明の実施の形態】以下、本発明の汚泥の濃縮処理方
法の実施の形態を図面に基づいて説明する。図1は本発
明を適用する汚水処理設備の処理フローを示したもの
で、該図において1は前処理装置、2はこの前処理装置
1に流入管8を介して接続した曝気槽で、この曝気槽2
は長円形で中央長手方向に仕切板21を配設して循環水
路22を形成するとともに、この循環水路22内に1台
若しくは複数台の曝気機7を配設する。BEST MODE FOR CARRYING OUT THE INVENTION An embodiment of the sludge concentration treatment method of the present invention will be described below with reference to the drawings. FIG. 1 shows a processing flow of a sewage treatment facility to which the present invention is applied. In the figure, reference numeral 1 denotes a pretreatment device, and 2 denotes an aeration tank connected to the pretreatment device 1 via an inflow pipe 8. Aeration tank 2
Is provided with a partition plate 21 in the central longitudinal direction in the shape of an oval to form a circulation channel 22 and one or more aerators 7 are disposed in the circulation channel 22.
【0007】3は沈殿槽で、流出管9を介して前記曝気
槽2と接続するとともに、この沈殿槽3から曝気槽2に
返送汚泥管13をも配設する。4は沈殿槽3から流出す
る上澄水を導くように配設した消毒槽で、この消毒槽4
の後段に流量計11を設けるとともに、この流量計11
に制御装置10を電気的に接続し、水量計11の検出値
を制御装置10に印可し、汚泥濃縮装置5を制御する。
これは小規模処理設備における汚泥の発生量が流入水量
にほぼ比例することから、流入水量を計測する流量計を
別途設け、流量計の測定値から算出される1日当たりの
積算流入水量に比例する時間だけ汚泥濃縮装置5を運転
するように制御するものである。Reference numeral 3 denotes a sedimentation tank, which is connected to the aeration tank 2 via an outflow pipe 9 and also has a sludge pipe 13 returned from the sedimentation tank 3 to the aeration tank 2. Reference numeral 4 denotes a disinfecting tank arranged to guide supernatant water flowing out of the sedimentation tank 3.
A flow meter 11 is provided at the subsequent stage, and the flow meter 11
The control unit 10 is electrically connected to the control unit 10, and the detection value of the water meter 11 is applied to the control unit 10 to control the sludge concentrator 5.
Since the amount of sludge generated in the small-scale treatment equipment is almost proportional to the amount of inflow water, a flow meter for measuring the amount of inflow water is separately provided, and is proportional to the integrated amount of inflow water per day calculated from the measured value of the flow meter. The control is performed so that the sludge concentration device 5 is operated only for a certain time.
【0008】この汚泥濃縮装置5には曝気槽2よりポン
プ12を介して余剰汚泥を供給するよう送泥管14を配
設する。この汚泥濃縮装置5への供給汚泥濃度を一定に
して、安定した脱水性能を確保するため曝気槽から直接
余剰汚泥を引き抜くとともに、この汚泥濃縮装置5には
汚泥貯留槽6を接続する。The sludge concentration apparatus 5 is provided with a sludge pipe 14 so as to supply surplus sludge from the aeration tank 2 via a pump 12. To keep the concentration of sludge supplied to the sludge concentrator 5 constant and secure stable dehydration performance, excess sludge is directly drawn from the aeration tank, and a sludge storage tank 6 is connected to the sludge concentrator 5.
【0009】従って下水等の有機性汚水汚泥Aは、前処
理装置1を経て曝気槽2へと流入する。本実施例におい
て曝気槽2は、スクリュー形曝気機7を配備したオキシ
デーションディッチを示しているが、曝気槽の形状や曝
気装置は特に限定されるものではない。曝気槽2内の汚
泥混合液はオーバーフローして、沈澱槽3へと流入し汚
泥は沈降した後、返送汚泥Cとして曝気槽に戻され、上
澄水はオーバーフローして、消毒槽4で殺菌処理された
後、放流水Bとして系外に排出される。Accordingly, the organic wastewater sludge A such as sewage flows into the aeration tank 2 through the pretreatment device 1. In this embodiment, the aeration tank 2 shows an oxidation ditch provided with the screw type aerator 7, but the shape of the aeration tank and the aeration apparatus are not particularly limited. The sludge mixture in the aeration tank 2 overflows, flows into the sedimentation tank 3 and the sludge settles, and then returns to the aeration tank as returned sludge C. The supernatant water overflows and is sterilized in the disinfection tank 4. After that, it is discharged out of the system as discharge water B.
【0010】流量計11は、消毒槽4の後段に設けら
れ、消毒槽の放流流量を計測しているが、流量計の種類
や条件によっては、流入配管や消毒槽への流入部など、
別の位置に設けることも可能である。The flow meter 11 is provided at the subsequent stage of the disinfecting tank 4 and measures the discharge flow rate of the disinfecting tank. However, depending on the type and conditions of the flow meter, an inflow pipe, an inflow portion to the disinfecting tank, etc.
It is also possible to provide it at another position.
【0011】余剰汚泥Dは、曝気槽から直接引き抜き、
給泥ポンプ12により機械式の汚泥濃縮装置5へと送泥
する。尚、給泥ポンプ12は、図示したような槽外形に
限定されず、水中形のポンプを用いても良いが、小容量
でも流量の安定性の良いポンプを用いる必要がある。The excess sludge D is drawn directly from the aeration tank,
The mud is fed to the mechanical sludge concentrator 5 by the mud feed pump 12. In addition, the mud feed pump 12 is not limited to the tank outer shape as shown in the figure, and may be a submersible pump. However, it is necessary to use a pump having a small capacity and good flow rate stability.
【0012】脱水機の運転使令を与えるための制御装置
10は、流量計11の測定データのとり込みや演算機能
等を有する。そして、給泥ポンプ12は、通常濃縮装置
5に組み込まれた専用の制御盤により制御されるが、こ
の専用の制御盤の機能をすべて制御装置10に取り込み
濃縮装置付属の専用盤をなくすことも可能である。処理
された濃縮汚泥Eは、所定の期間汚泥貯留槽6に一時貯
留された後、場外に搬出される。A control device 10 for giving an operation instruction of the dehydrator has a function of acquiring measurement data of the flow meter 11 and an arithmetic function. The mud feed pump 12 is usually controlled by a dedicated control panel incorporated in the concentrating device 5, but it is also possible to incorporate all the functions of this dedicated control panel into the control device 10 and eliminate the dedicated panel attached to the concentrating device. It is possible. The treated concentrated sludge E is temporarily stored in the sludge storage tank 6 for a predetermined period, and then carried out of the site.
【0013】次に、本発明の作用を示す。小規模の汚
水、特に下水においては、流入水量が計画値に達するま
で少なくとも1年以上の期間を要することから、安定し
た処理性能を保つためには流入水量に応じて適宜、運転
時間を変更していく必要がある。本発明では、経時的に
変化する水量を流量計11で測定し、制御装置10に入
力される。制御装置内に設けられた演算装置では、1日
の流量の合計が積算され、この積算流量qと、計画流入
水量Qの比r(=q/Q)が求められる。次に、このr
をもとに、1日当たりの濃縮装置の運転時間が計算され
る。尚、濃縮条件は予め定めておき、単位時間当たりの
処理量が一定となるよう設定する。Next, the operation of the present invention will be described. For small-scale sewage, especially sewage, it takes at least one year for the inflow to reach the planned value. To maintain stable treatment performance, change the operation time as appropriate according to the inflow. It is necessary to go. In the present invention, the amount of water changing over time is measured by the flow meter 11 and input to the control device 10. In the arithmetic unit provided in the control device, the total of the daily flow rates is integrated, and a ratio r (= q / Q) of the integrated flow amount q and the planned inflow water amount Q is obtained. Next, this r
, The operating time of the concentrator per day is calculated. Note that the concentration conditions are determined in advance and set so that the processing amount per unit time is constant.
【0014】次に、流入水の濃度や水処理の運転条件か
ら計画流入水量における濃縮装置の必要運転時間をTと
すると、積算流量がqにおける濃縮装置の運転時間t
は、t=r・Tとなる。ただし、実際にはqがある程度
の幅の中でバラツキをもちながら、除々に増加していく
ため、日々変化するqに対して、tを設定変更する必要
はないため、1週間〜1カ月程度の期間におけるqの平
均値を求め、この値をもとに、次の期間のtを設定変更
することが好ましい。Next, assuming that the required operation time of the concentrator at the planned inflow water amount is T based on the concentration of the inflow water and the operating conditions of the water treatment, the operation time t of the concentrator at the integrated flow rate q is t.
Becomes t = r · T. However, actually, since q gradually increases while having a certain range of variation, it is not necessary to change the setting of t for q that changes daily, so that it is about one week to one month. It is preferable to obtain the average value of q in the period, and to change the setting of t in the next period based on this value.
【0015】タイマーの時間設定は、積算機能を備えた
流量計の値をもとに上記計算を手計算または、制御装置
内の演算装置によりtを求めた後、手動でタイマーを設
定しても良いが、制御装置内蔵のタイマーを自動で変更
できる装置とすることがより望ましい。The time of the timer can be set by manually calculating the above calculation based on the value of the flow meter having the integrating function, or by calculating t by an arithmetic unit in the control device, and then manually setting the timer. Good, but more desirably a device that can automatically change the timer built into the control device.
【0016】尚、汚泥濃縮装置の種類は特に限定されな
いが、少なくとも運転開始及び運転停止の信号さえ与え
れば、自動で運転でき、小規模で低濃度の汚泥混合液
(MISS)濃度においても安定した処理性能が得られ
る装置を用いる必要がある。また、安定した濃縮性能を
得るためには安定した濃度の余剰汚泥を供給する必要が
あることから曝気槽が曝気機により充分撹拌混合されて
いる時間帯に行う。したがって、曝気機を間欠運転する
設備においては、計画流入水量時の汚泥濃縮装置運転時
間Tと、1サイクル当りの曝気時間を比較し、Tが大き
い場合には汚泥濃縮装置の運転を1日複数回行うように
分割し、すべての運転が曝気時間帯に行われるよう設定
する必要がある。The type of the sludge concentrator is not particularly limited, but it can be operated automatically as long as at least a signal for starting and stopping the operation is given, and is stable even in a small-scale low-concentration sludge mixture (MISS). It is necessary to use a device that can provide processing performance. Further, since it is necessary to supply a surplus sludge having a stable concentration in order to obtain a stable concentration performance, it is performed during a time period when the aeration tank is sufficiently stirred and mixed by the aerator. Therefore, in the equipment that intermittently operates the aerator, the operation time T of the sludge concentrator at the time of the planned inflow water amount is compared with the aeration time per cycle. It is necessary to divide the operation so that all operations are performed during the aeration period.
【0017】[0017]
【発明の効果】本発明の汚泥の濃縮処理方法によれば、
汚泥濃度が安定している曝気槽から余剰汚泥を引き抜
き、流入水量を計測して水量に比例する時間だけ濃縮処
理を行うため、発生汚泥量に見合った汚泥が余剰汚泥と
して引き抜かれて、安定した濃縮性能を保持できるとと
もに、曝気槽のMLSS濃度の安定化が図られるため、
供用開始から計画流入水量に達する間においても、負荷
変動に係わらず、安定した水処理性能を得ることができ
る。According to the sludge concentration treatment method of the present invention,
Excess sludge is withdrawn from the aeration tank where the sludge concentration is stable, the inflow is measured, and the enrichment treatment is performed for a time proportional to the amount of water.Thus, the sludge corresponding to the amount of generated sludge is extracted as surplus sludge, and stable. Since the concentration performance can be maintained and the MLSS concentration in the aeration tank is stabilized,
Even during the period from the start of operation to the planned inflow water amount, stable water treatment performance can be obtained regardless of load fluctuation.
【図1】本発明の汚泥の濃縮処理方法の第1実施例を示
すフローチャート図である。FIG. 1 is a flowchart showing a first embodiment of a sludge concentration treatment method of the present invention.
1 前処理装置 2 曝気槽 22 循環水路 3 沈殿槽 4 消毒槽 5 汚泥濃縮装置 6 汚泥貯蓄槽 7 曝気機 8 流入管 9 流出管 10 制御装置 11 流量計 12 給泥ポンプ 13 返送汚泥管 14 送泥管 A 有機性汚水汚泥 B 放流水 C 返送汚泥 D 余剰汚泥 E 濃縮汚泥 DESCRIPTION OF SYMBOLS 1 Pre-processing apparatus 2 Aeration tank 22 Circulation channel 3 Sedimentation tank 4 Disinfection tank 5 Sludge concentrator 6 Sludge storage tank 7 Aerator 8 Inflow pipe 9 Outflow pipe 10 Controller 11 Flow meter 12 Sludge pump 13 Return sludge pipe 14 Pipe A Organic wastewater sludge B Discharge water C Return sludge D Excess sludge E Condensed sludge
Claims (1)
生物処理を行い、余剰汚泥を濃縮減容化する汚水処理設
備において、曝気機の運転時間帯に曝気槽から直接、余
剰汚泥を引き抜いて機械式濃縮装置に導き、水処理設備
への1日当たりの積算処理水量に応じて、汚泥濃縮装置
の運転時間を設定して運転することを特徴とする汚泥の
濃縮処理方法。Claims: 1. In a sewage treatment facility for subjecting wastewater such as sewage to biological treatment with activated sludge in an aeration tank and concentrating and reducing excess sludge, the excess sludge is drawn directly from the aeration tank during the operation time of the aerator. Characterized in that the sludge concentrator is operated by setting the operation time of the sludge concentrator according to the integrated amount of treated water per day to the water treatment facility.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9171150A JPH11698A (en) | 1997-06-11 | 1997-06-11 | Sludge concentration treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9171150A JPH11698A (en) | 1997-06-11 | 1997-06-11 | Sludge concentration treatment method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH11698A true JPH11698A (en) | 1999-01-06 |
Family
ID=15917925
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9171150A Pending JPH11698A (en) | 1997-06-11 | 1997-06-11 | Sludge concentration treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH11698A (en) |
-
1997
- 1997-06-11 JP JP9171150A patent/JPH11698A/en active Pending
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JP3961835B2 (en) | Sewage treatment plant water quality controller | |
| JP4334317B2 (en) | Sewage treatment system | |
| JP2012200705A (en) | Nitrogen-containing wastewater treatment method and apparatus | |
| JP2001353496A (en) | Sewage treatment system and measurement system | |
| JP5276279B2 (en) | Operation control method for aeration apparatus | |
| JP6818951B1 (en) | Water treatment equipment and water treatment method | |
| JP2002126779A (en) | Sewage treatment method and apparatus used therefor | |
| CN115231738B (en) | Fenton process wastewater treatment method | |
| JP3067993B2 (en) | Method and apparatus for biological dephosphorization of wastewater | |
| JPH07115025B2 (en) | Bulking control method using SVI | |
| JP3654742B2 (en) | Sludge dewatering method | |
| JP4620391B2 (en) | Sewage treatment equipment | |
| JP2003260484A (en) | Wastewater treatment apparatus | |
| JPH05253597A (en) | Nitrification reaction control device in activated sludge treatment | |
| JPH11683A (en) | Operation method of small-scale sewage treatment equipment | |
| JPH08192179A (en) | Sludge retention time setting device in activated sludge method | |
| JP2021183313A (en) | Dilution treatment method and dilution treatment apparatus for diluted material containing ammonia nitrogen | |
| JP2015217375A (en) | Sewage treatment apparatus and sewage treatment method | |
| JPS5898190A (en) | Method of controlling amount of sludge | |
| JP3303475B2 (en) | Operation control method of activated sludge circulation method | |
| JP2000084585A (en) | Operation control method of aeration device and sludge extraction pump | |
| JP3690537B2 (en) | Intermittent aeration | |
| JP2001259682A (en) | Wastewater treatment equipment | |
| JP2000015279A (en) | Continuous treatment of sewage | |
| JP2000185296A (en) | Sludge extraction pump operation control method |