JP2001079586A - Operation of sewage treating equipment - Google Patents

Operation of sewage treating equipment

Info

Publication number
JP2001079586A
JP2001079586A JP25992899A JP25992899A JP2001079586A JP 2001079586 A JP2001079586 A JP 2001079586A JP 25992899 A JP25992899 A JP 25992899A JP 25992899 A JP25992899 A JP 25992899A JP 2001079586 A JP2001079586 A JP 2001079586A
Authority
JP
Japan
Prior art keywords
sludge
sewage
water level
facility
aerator
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
JP25992899A
Other languages
Japanese (ja)
Inventor
Hideaki Hamada
英明 浜田
Takaaki Otsuka
貴章 大塚
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.)
Hitachi Kiden Kogyo Ltd
Nihon HELS Industry Corp
Original Assignee
Hitachi Kiden Kogyo Ltd
Nihon HELS Industry Corp
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 Hitachi Kiden Kogyo Ltd, Nihon HELS Industry Corp filed Critical Hitachi Kiden Kogyo Ltd
Priority to JP25992899A priority Critical patent/JP2001079586A/en
Publication of JP2001079586A publication Critical patent/JP2001079586A/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

PROBLEM TO BE SOLVED: To provide an operating method of sewage treating equipment capable of preventing the flowing-out of sludge out of a system before a maintenance manager reaches a treatment plant by controlling to automatically work a sludge over-flow preventing system when a water level reaches the warning level of the high water level. SOLUTION: In the operating method of the sewage treating equipment constituted of a sewage receiving tank 1, an aeration tank 2 and a final settling tank 3 and the incidental equipments such as an aerator 21, a sludge scraper 31 and a returned sludge pump 32 and for treating the sewage such as domestic waste water, the over flow of the sludge out of facility is prevented by automatically stopping one kind or plural equipments of the aerator 21, the sludge scraper 31 and the returned sludge pump 32 when the water level of the facility reaches the set warning level of the high water level.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、生活排水等の汚水
を浮遊性の汚泥により生物処理する汚水処理設備の運転
方法に関し、特に、雨水や地下水等の不明水が多く流入
する施設であって、汚泥が軽く、重力沈降しにくい場合
においても、施設の外に汚泥が溢流することを未然に防
止し、安定した汚水の処理を行うようにした汚水処理設
備の運転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 of operating a sewage treatment facility for biologically treating sewage such as domestic wastewater with floating sludge, and more particularly to a facility into which a large amount of unknown water such as rainwater or groundwater flows. Also, the present invention relates to a method of operating a sewage treatment facility that prevents sludge from overflowing out of the facility and performs stable sewage treatment even when the sludge is light and hard to settle by gravity.

【0002】[0002]

【従来の技術】近年、下水道設備は大都市から中小都市
に移行し、その規模は小さくなっており、処理の安定
性、維持管理性からオキデーションディッテ法(以下、
「OD法」といい、OD法を実施する設備を「OD設
備」という。)が多く採用されている。このOD法の主
要機器は、汚水ポンプ、曝気機、汚泥掻寄機、返送汚泥
ポンプ等の多くの機器から構成される。そしてその運転
は、通常、汚水ポンプが水位運転、曝気機がタイマー運
転又は溶存酸素値(DO値)等をフィードバックする自
動制御運転(以下、溶存酸素値に基づいて行う自動制御
を「DO制御」という。)、汚泥掻寄機が連続運転、返
送汚泥ポンプが連続運転又はタイマー運転であり、それ
ぞれが自動的に運転がなされている。
2. Description of the Related Art In recent years, sewerage facilities have shifted from large cities to small and medium-sized cities, and their scale has been reduced.
The equipment that implements the OD method is called “OD equipment”. ) Is often adopted. The main equipment of the OD method is composed of many equipment such as a sewage pump, an aerator, a sludge scraper, and a return sludge pump. Normally, the operation is a water level operation of a sewage pump, a timer operation of an aerator, or an automatic control operation of feeding back a dissolved oxygen value (DO value) (hereinafter, “DO control” is an automatic control performed based on a dissolved oxygen value). ), The sludge scraper is a continuous operation, the return sludge pump is a continuous operation or a timer operation, and each is automatically operated.

【0003】[0003]

【発明が解決しようとする課題】ところで、OD法の活
性汚泥は、長時間曝気型の汚泥であり、加えて機械式曝
気撹拌機により活性汚泥フロックが壊されて小さくなり
がちで、標準活性汚泥法の汚泥より沈降しにくくなって
いる。一方、OD設備の維持管理体制は、処理規模によ
って異なり、大きい施設では、昼間は維持管理者が常駐
し、夜間は無人の場合が多く、また小さい規模の施設で
は、1週間に1乃至2回の巡回点検が行われる程度の内
容となっている。このような状況下において、大雨等が
原因で、計画汚水量を超える水が処理施設内に流入した
場合、曝気槽の活性汚泥が最終沈殿池に大量に移行し、
そこで十分な沈殿時間が得られず、処理水に混ざって、
処理場の系外に出て行くことになる。このことは、処理
水質が悪化するだけでなく、汚泥の溢流の程度によって
は、再度、活性汚泥を育成しなおさなければならない
し、放流先の水環境に悪影響が及ぶという問題があっ
た。
By the way, the activated sludge of the OD method is a long-time aerated type sludge. In addition, the activated sludge floc tends to be broken down by a mechanical aeration stirrer and becomes small. It is harder to settle than sludge of the law. On the other hand, the maintenance system for OD equipment varies depending on the processing scale. In large facilities, maintenance managers are resident during the day and unmanned at night in many cases, and in smaller facilities once or twice a week. It is a content that the patrol inspection of is performed. Under such circumstances, when water exceeding the planned amount of wastewater flows into the treatment facility due to heavy rain, etc., a large amount of activated sludge in the aeration tank moves to the final sedimentation tank,
Therefore, sufficient precipitation time was not obtained, mixed with treated water,
You will be out of the treatment plant. This not only deteriorates the quality of the treated water, but also has to raise the activated sludge again depending on the degree of sludge overflow, which has a problem of adversely affecting the water environment of the discharge destination.

【0004】また、これを防止するシステムとして、図
3に示すように、処理場には水位計を設置して、高水位
の警戒レベルに水位が達した時点で、非常通報装置によ
る連絡が維持管理者に入るようになっているが、非常通
報装置による警報の連絡があっても、夜間や休日の場合
は、処理場より離れた位置に待機している維持管理者
が、処理場に到着するまでに時間がかかり、必要な処置
を施すまでに曝気槽の活性汚泥が最終沈殿池に大量に移
行して、そこで十分な沈殿時間が得られずに処理水に混
ざって、処理場の系外に、汚泥が溢流してしまうという
問題があった。
As a system for preventing this, as shown in FIG. 3, a water level gauge is installed in the treatment plant, and when the water level reaches the high water level warning level, communication by the emergency notification device is maintained. Even if there is an alert notification from the emergency notification device, at night or on holidays, the maintenance manager who is waiting at a location away from the treatment plant arrives at the treatment plant. It takes a long time to perform the treatment, and the activated sludge in the aeration tank migrates in large quantities to the final sedimentation basin before the necessary treatment is performed. Outside, there was a problem that sludge overflowed.

【0005】本発明は、従来の汚水処理設備の運転方法
の有する問題点を解決し、高水位の警戒レベルに水位が
達した時、自動的に汚泥溢流防止システムが働くように
して、維持管理者が処理場に到着するまでの間にも、汚
泥が系外に流れ出ないようにすることができる汚水処理
設備の運転方法を提供することを目的とする。
[0005] The present invention solves the problems of the conventional method of operating a sewage treatment facility, and automatically activates and maintains a sludge overflow prevention system when a water level reaches a high water level alert level. It is an object of the present invention to provide a method of operating a sewage treatment facility that can prevent sludge from flowing out of the system even before a manager arrives at a treatment plant.

【0006】[0006]

【課題を解決するための手段】上記目的を達成するた
め、本発明の汚水処理設備の運転方法は、汚水受水槽、
曝気槽及び最終沈殿池並びにそれに付帯する曝気機、汚
泥掻寄機、返送汚泥ポンプ等の機器から構成され、生活
排水などの汚水を処理する汚水処理設備の運転方法にお
いて、施設の水位が設定された高水位の警戒レベルに達
した時に、曝気機、汚泥掻寄機、返送汚泥ポンプのいず
れか1種若しくは複数の機器を自動的に停止して、施設
外に汚泥が溢流するのを未然に防止するようにしたこと
を特徴とする。
In order to achieve the above object, a method for operating a sewage treatment plant according to the present invention comprises a sewage receiving tank,
The aeration tank and final sedimentation basin and the associated aerators, sludge scrapers, return sludge pumps, and other equipment are used to set the water level of the facility in the method of operating sewage treatment equipment that treats sewage such as domestic wastewater. When the high water level alert level is reached, one or more of the aerator, sludge scraper and return sludge pump are automatically stopped to prevent sludge from overflowing the facility. It is characterized by being prevented.

【0007】上記の構成からなる本発明の汚水処理設備
の運転方法は、激しい降雨時等において、汚水受水槽、
曝気槽、最終沈殿池等の施設内の汚水処理量以上の汚水
が流入して、汚水受水槽内で予め設定した高水位の警戒
レベルに水位が達した時、自動的に汚泥溢流防止システ
ムが働くようにしているので、維持管理者が処理場に到
着するまでの間にも、汚泥が系外に流れ出ないようにす
ることができ、どのように状態でも安定した汚水の処理
を行うことができる。
[0007] The method of operating the sewage treatment equipment of the present invention having the above-described structure is capable of receiving a sewage receiving tank,
Sludge overflow prevention system automatically when sewage exceeding the amount of sewage treatment in the aeration tank, final sedimentation basin, etc. flows in and the water level reaches a preset high water level in the sewage receiving tank. Works so that the sludge can be prevented from flowing out of the system before the maintenance manager arrives at the treatment plant, and the wastewater can be treated stably in any condition. Can be.

【0008】また、この場合、施設の水位が設定された
高水位の警戒レベル以下になった時に、停止している曝
気機、汚泥掻寄機、返送汚泥ポンプのいずれか1種若し
くは複数の機器を、自動的に通常運転に復帰するように
することができる。
In this case, when the water level of the facility falls below the set high water level alert level, any one or more of the stopped aerators, sludge scrapers and return sludge pumps are provided. Can be automatically returned to the normal operation.

【0009】これにより、施設内への汚水処理量が減少
し、汚水受水槽の水位が設定された高水位の警戒レベル
以下になると自動的に通常運転に切り替えられるので、
流入汚水量に関係なく常に安定した汚水の処理が行え
る。
As a result, the amount of sewage treated into the facility decreases, and when the water level of the sewage receiving tank falls below the set high water level alert level, the operation is automatically switched to the normal operation.
Stable sewage treatment can always be performed regardless of the amount of inflow sewage.

【0010】[0010]

【発明の実施の形態】以下、本発明の汚水処理設備の運
転方法の実施の形態を図面に基づいて説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the method for operating a sewage treatment plant according to the present invention will be described below with reference to the drawings.

【0011】図1〜図2は、本発明の第1実施例を示
し、図1は、オキシデーションディッテ法の水処理フロ
ーである。図において1は、汚水受水槽であり、通常、
汚水受水槽1には複数台の汚水ポンプ11と水位計12
とが設置され、汚水受水槽1に導入される汚水を、水位
計12で検知しつつ、通常運転用の汚水ポンプ11を連
続的又は間欠的さらには選択的に運転して曝気槽2へ送
水されように構成される。また、この汚水受水槽1に複
数台設置される汚水ポンプ11は、そのうち少なくとも
1台を予備若しくは非常運転用として使用される。
FIGS. 1 and 2 show a first embodiment of the present invention, and FIG. 1 shows a flow of water treatment by the oxidation ditter method. In the figure, reference numeral 1 denotes a sewage receiving tank.
The sewage receiving tank 1 has a plurality of sewage pumps 11 and water level gauges 12.
Is installed, and while detecting the sewage introduced into the sewage receiving tank 1 with the water level gauge 12, the sewage pump 11 for normal operation is continuously or intermittently or selectively operated to supply water to the aeration tank 2. It is configured to be. Further, at least one of the sewage pumps 11 installed in the sewage receiving tank 1 is used for spare or emergency operation.

【0012】汚水ポンプ11の運転は、通常、水位計1
2で検知される水位レベルにより、通常運転用の汚水ポ
ンプ11が、起動若しくは停止されて、間欠的に曝気槽
2へ汚水受水槽1から汚水が送水される。そして、この
曝気槽2には、曝気機21が設置され、曝気機21の運
転により曝気槽2内に供給された汚水中に空気(酸素)
を供給するとともに、曝気機21により生じる撹拌流に
より汚水と活性汚泥を均一に混合撹拌して、汚水を生物
処理するようにしている。この曝気機2の運転は、タイ
マーにより設定されるか、若しくはDO制御等による自
動運転がなされる。
The operation of the sewage pump 11 is usually performed by the water level meter 1.
The sewage pump 11 for normal operation is started or stopped according to the water level detected in 2, and sewage is intermittently sent from the sewage receiving tank 1 to the aeration tank 2. An aerator 21 is installed in the aeration tank 2, and air (oxygen) is contained in the sewage supplied into the aeration tank 2 by the operation of the aerator 21.
Is supplied, and the sewage and activated sludge are uniformly mixed and stirred by the stirring flow generated by the aerator 21 so that the sewage is biologically treated. The operation of the aerator 2 is set by a timer, or is automatically performed by DO control or the like.

【0013】さらに、曝気槽2内で処理された汚水と汚
泥の混合液は、通常、水路若しくは配管により最終沈殿
池3へ移送される。この最終沈殿池3では、水と汚泥が
比重差により重力分離されるが、比重の大きい汚泥は最
終沈殿池の底部に溜り、上澄水は消毒槽4へ送水され
て、滅菌後系外に放流される。一方、汚泥は、最終沈殿
池3内に配設された汚泥掻寄機31が連続的に運転され
ているので、集積部に掻寄せられた後に、大部分の汚泥
は最終沈殿池内又は外部に配設された返送汚泥ポンプ3
2により曝気槽2に返流され、その内の一部を余剰汚泥
として処分されるようにしている。
Further, the mixed liquid of the sewage and the sludge treated in the aeration tank 2 is usually transferred to the final sedimentation basin 3 by a water channel or a pipe. In this final sedimentation basin 3, water and sludge are separated by gravity due to a difference in specific gravity. However, sludge having a large specific gravity accumulates at the bottom of the final sedimentation basin, and supernatant water is sent to the disinfection tank 4 and discharged out of the system after sterilization. Is done. On the other hand, since the sludge scraper 31 disposed in the final sedimentation basin 3 is continuously operated, most of the sludge is collected inside or outside the final sedimentation basin after being scraped by the accumulation part. Returned sludge pump 3 installed
The wastewater is returned to the aeration tank 2 by the second and a part thereof is disposed of as excess sludge.

【0014】ところで、最近の処理場の汚水収集方式は
分流式であっても、配管の誤接合、破損、その他の理由
により、雨水や地下水が処理場に混入することもしばし
ばあり、これらの理由により、処理場に計画値以上の汚
水が流入することがある。このような場合は、汚水受水
槽1の水位が上昇し、通常運転の汚水ポンプ11だけで
は汚水受水槽1に流入する汚水を排除できずに、汚水受
水槽1の水位が上昇し続ける。この水位の上昇を防止す
るため、本発明では水位計12で予め設定した高水位の
警戒レベルに達したことを検知すると、非常用汚水ポン
プの起動だけでなく、施設内に配設された曝気機、返送
汚泥ポンプ、汚泥掻寄機等の機器の制御をも行うように
したものである。
By the way, even if a recent wastewater treatment system of a treatment plant is of a diversion type, rainwater or groundwater often enters the treatment plant due to erroneous connection of pipes, breakage, or other reasons. Therefore, sewage more than the planned value may flow into the treatment plant. In such a case, the water level in the sewage receiving tank 1 rises, and the sewage pump 11 in the normal operation alone cannot eliminate the sewage flowing into the sewage receiving tank 1, and the water level in the sewage receiving tank 1 keeps rising. In order to prevent the rise of the water level, in the present invention, when the water level gauge 12 detects that the warning level of the preset high water level has been reached, not only the emergency wastewater pump is started but also the aeration provided in the facility. It also controls equipment such as a sludge pump, a return sludge pump, and a sludge scraper.

【0015】予め設定した高水位の警戒水位前後におけ
る曝気機、返送汚泥ポンプ、汚泥掻寄機等の機器の運転
フローを、図2に示す。以下、警戒水位前後の機器の運
転制御の説明を、図2に基づいて説明する。汚水受水槽
1に流入する汚水の水位が、予め設定した高水位の警戒
レベル以下を水位計12にて検出している場合は、通常
運転、即ち通常運転の汚水ポンプ11、曝気機21、汚
泥掻寄機31及び返送汚泥ポンプ32が運転され、非常
用汚水ポンプは停止した状態で、汚水受水槽1に流入す
る汚水は、曝気槽2、最終沈殿池3を順次経過して処理
されている。ところが、激しい降雨などにて汚水受水槽
1に流入する汚水量が増し、設定流入量以上となり、単
位時間当たりの処理量以上が流入するようになると、汚
水受水槽1の水位が次第に上昇し、やがて警戒レベルに
達する。この警戒レベルに達っしたことを水位計12に
て検知する。
FIG. 2 shows the operation flow of equipment such as an aerator, a return sludge pump, and a sludge scraper before and after a preset high water level warning water level. Hereinafter, the operation control of the devices before and after the warning water level will be described with reference to FIG. When the water level of the sewage flowing into the sewage receiving tank 1 is detected by the water level gauge 12 below a preset high water level warning level, the sewage pump 11, the aerator 21, and the sludge of the normal operation are used. While the scraper 31 and the return sludge pump 32 are operated and the emergency wastewater pump is stopped, the sewage flowing into the sewage receiving tank 1 is sequentially processed through the aeration tank 2 and the final sedimentation basin 3. . However, when the amount of sewage flowing into the sewage receiving tank 1 due to heavy rainfall increases and exceeds the set inflow amount, and the amount of treatment per unit time or more flows in, the water level of the sewage receiving tank 1 gradually increases, Eventually the alert level is reached. The water level gauge 12 detects that the alarm level has been reached.

【0016】従来の通常運転では、図3に示すように、
水位が警戒レベルに達した段階で、自動非常警報装置に
より維持管理者へ外部通報がなされるとともに、非常用
汚水ポンプが運転され、維持管理者が処理場で適当な処
置を行うようにしている。しかし、本発明においては、
図2に示すように、水位が警戒レベルに達してこの非常
用汚水ポンプが運転された段階で、関係するリレーの状
態を検出し、曝気機21、返送汚泥ポンプ32、汚泥掻
寄機31等の施設内の機器類を緊急停止させるようにす
る。この施設内の機器類を緊急停止は、リレーの状態を
検出する以外に、さらに別の手段として、水位計12の
信号により、直接、これらの機器を停止するようにする
こともできる。この機器類の停止方法は限定されるもの
ではなく、種々の方法で行うことができる。なお、本実
施例では、曝気機21、返送汚泥ポンプ32、汚泥掻寄
機31のすべてを停止させているが、必要に応じて、例
えば、時間当たりの流入量に合わせてこれらの機器の
内、少なくともいずれか1台を自動的に停止させ、汚泥
の溢流を未然にを防止させるようにすることもできる。
In conventional normal operation, as shown in FIG.
When the water level reaches the alert level, an external alarm is sent to the maintenance person by the automatic emergency alarm device, and the emergency sewage pump is operated so that the maintenance person can take appropriate measures at the treatment plant. . However, in the present invention,
As shown in FIG. 2, when the water level reaches the alert level and the emergency sewage pump is operated, the state of the related relay is detected, and the aerator 21, the return sludge pump 32, the sludge scraper 31, etc. Emergency stop of equipment in the facility. The emergency stop of the equipment in the facility can be performed by directly stopping the equipment by the signal of the water level gauge 12 as another means other than detecting the state of the relay. The method of stopping the devices is not limited, and can be performed by various methods. In this embodiment, the aerator 21, the return sludge pump 32, and the sludge scraper 31 are all stopped. However, if necessary, for example, any of these devices may be stopped according to the inflow per hour. It is also possible to automatically stop at least one of the units to prevent sludge from overflowing.

【0017】このように曝気槽2へ流入する汚水量が、
設定された計画値を超えた状況では、最終沈殿池3での
水量負荷が大きく、活性汚泥が十分に沈降・分離せず、
処理水と一緒に系外へ溢流するが、曝気機21、返送汚
泥ポンプ32、汚泥掻寄機31等の機器類の全停止又は
選択停止のいずれにしても、機器を停止することによ
り、曝気槽か最終沈殿池のいずれかに汚泥を沈殿・貯留
できるので、汚泥の溢流を防止することができる。その
中でも、特に、曝気機21を停止することが効果的であ
るが、これは、曝気槽が広大な沈殿面積を有するからで
ある。
As described above, the amount of wastewater flowing into the aeration tank 2 is
In the situation exceeding the set plan value, the water load in the final sedimentation basin 3 is large, and the activated sludge does not settle and separate sufficiently.
Although it overflows out of the system together with the treated water, the apparatus is stopped by stopping the apparatus regardless of whether all of the equipment such as the aerator 21, the return sludge pump 32, and the sludge scraper 31 is stopped or is selectively stopped. Since sludge can be settled and stored in either the aeration tank or the final sedimentation basin, the overflow of sludge can be prevented. Among them, stopping the aerator 21 is particularly effective, because the aeration tank has a large sedimentation area.

【0018】また、返送汚泥ポンプ32の停止は、曝気
槽2と最終沈殿池3の間の水循環を停止することにな
り、曝気槽2や最終沈殿池3への流入水量を減ずること
ができるので、汚泥の溢流防止に一層効果的である。さ
らに、汚泥掻寄機31の停止は、最終沈殿池内の流れを
弱め、汚泥の沈降速度を上げる効果がある。このよう
に、施設の水位が警戒レベルに達した段階で、自動的
に、設備内の機器の運転を停止すれば、維持管理者が非
常通報装置からの連絡を受けて、処理場に到着するまで
の間に、溢流する汚泥を未然に防止することができる。
Further, when the return sludge pump 32 is stopped, the water circulation between the aeration tank 2 and the final sedimentation basin 3 is stopped, and the amount of water flowing into the aeration tank 2 and the final sedimentation basin 3 can be reduced. It is even more effective in preventing sludge from overflowing. Furthermore, stopping the sludge scraper 31 has the effect of weakening the flow in the final sedimentation basin and increasing the sludge settling speed. As described above, when the water level of the facility reaches the alert level, if the operation of the equipment in the facility is automatically stopped, the maintenance manager receives a notification from the emergency notification device and arrives at the treatment plant. In the meantime, overflowing sludge can be prevented.

【0019】逆に、施設の水位が警戒レベル以下になっ
た段階においては、水位計12の信号、若しくは、非常
用汚水ポンプの運転停止の指令により、自動的にこれら
の機器の運転を通常運転に切り替えることができ、ロス
なく従来運転を再開できる。
Conversely, when the water level of the facility falls below the alert level, the operation of these devices is automatically performed in the normal operation mode by a signal from the water level gauge 12 or a command to stop the operation of the emergency sewage pump. The conventional operation can be resumed without loss.

【0020】なお、計画値以上の汚水が処理場に流入
し、汚泥の溢流が懸念される場合は、通常、曝気槽を最
終沈殿池代わりに使用して汚泥を曝気槽の底部に沈降せ
しめるとともに、上層部だけを流入水が流れるようにし
て、汚泥の溢流防止を図るが、この場合、曝気槽の面積
は最終沈殿池に比べて大きいため、かなりの汚泥が曝気
槽内に保持できる。また、曝気槽へ流入する水量を少し
でも低減したり、汚泥の沈降効率を高くすることが有効
である。
When sewage more than the planned value flows into the treatment plant and there is a possibility of sludge overflow, the aeration tank is usually used instead of the final sedimentation tank to settle the sludge at the bottom of the aeration tank. At the same time, the inflow water flows only in the upper layer to prevent the sludge from overflowing, but in this case, the area of the aeration tank is larger than the final sedimentation basin, so that considerable sludge can be retained in the aeration tank. . It is also effective to reduce the amount of water flowing into the aeration tank as much as possible and to increase the sludge settling efficiency.

【0021】[0021]

【発明の効果】本発明の汚水処理設備の運転方法によれ
ば、激しい降雨時等において、汚水受水槽、曝気槽、最
終沈殿池等の施設内の汚水処理量以上の汚水が流入し
て、汚水受水槽内で予め設定した高水位の警戒レベルに
水位が達した場合でも、自動的に汚泥溢流防止システム
が働くようにしているので、維持管理者が処理場に到着
するまでの間にも、汚泥が系外に流れ出ないようにする
ことができ、どのように状態でも安定した汚水の処理を
行うことができる。
According to the method for operating the sewage treatment equipment of the present invention, during heavy rainfall, etc., sewage in excess of the sewage treatment amount in the sewage receiving tank, aeration tank, final sedimentation basin, etc., flows in, Even if the water level reaches the preset high water level warning level in the sewage receiving tank, the sludge overflow prevention system is automatically activated. Also, sludge can be prevented from flowing out of the system, and stable treatment of sewage can be performed in any state.

【0022】また、施設の水位が設定された高水位の警
戒レベル以下になった時に、停止している曝気機、汚泥
掻寄機、返送汚泥ポンプのいずれか1種若しくは複数の
機器を、自動的に通常運転に復帰するようにすることに
より、施設内への汚水処理量が減少し、汚水受水槽の水
位が設定された高水位の警戒レベル以下になると自動的
に、停止している曝気機等機器を運転して通常運転に切
り替えられるので、流入汚水量に関係なく常に安定した
汚水の処理が行える。
When the water level of the facility falls below the set high water level alert level, one or more of the stopped aerator, sludge scraper and return sludge pump are automatically turned on. By returning to normal operation, the amount of sewage treatment into the facility is reduced, and when the water level in the sewage receiving tank falls below the set high water level alert level, the aeration is automatically stopped. The apparatus can be switched to the normal operation by operating the apparatus such as the apparatus, so that the sewage can be always stably treated regardless of the amount of inflow sewage.

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

【図1】本発明の汚水処理設備の運転方法の実施の形態
を示すオキシデーションディッテ法の水処理フローであ
る。
FIG. 1 is a water treatment flow of an oxidation ditter method showing an embodiment of a method for operating a sewage treatment facility of the present invention.

【図2】本発明の汚水処理設備の運転方法を実施する設
備における機器類の運転フローである。
FIG. 2 is an operation flow of equipment in equipment for implementing the operation method of the wastewater treatment equipment of the present invention.

【図3】従来の設備における機器類の運転フローであ
る。
FIG. 3 is an operation flow of equipment in a conventional facility.

【符号の説明】[Explanation of symbols]

1 汚水受水槽 11 汚水ポンプ 12 水位計 2 曝気槽 21 曝気機 3 最終沈殿池 31 汚泥掻寄機 32 返送汚泥ポンプ 4 消毒槽 DESCRIPTION OF SYMBOLS 1 Sewage receiving tank 11 Sewage pump 12 Water level gauge 2 Aeration tank 21 Aerator 3 Final sedimentation basin 31 Sludge scraper 32 Return sludge pump 4 Disinfection tank

フロントページの続き Fターム(参考) 4D028 BB03 BC18 BD11 BD16 CA00 CA09 CA11 CC01 CD05 Continuation of the front page F term (reference) 4D028 BB03 BC18 BD11 BD16 CA00 CA09 CA11 CC01 CD05

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 汚水受水槽、曝気槽及び最終沈殿池並び
にそれに付帯する曝気機、汚泥掻寄機、返送汚泥ポンプ
等の機器から構成され、生活排水などの汚水を処理する
汚水処理設備の運転方法において、施設の水位が設定さ
れた高水位の警戒レベルに達した時に、曝気機、汚泥掻
寄機、返送汚泥ポンプのいずれか1種若しくは複数の機
器を自動的に停止して、施設外に汚泥が溢流するのを未
然に防止するようにしたことを特徴とする汚水処理設備
の運転方法。
1. Operation of sewage treatment equipment for treating sewage such as domestic wastewater, comprising a sewage receiving tank, an aeration tank, a final sedimentation basin, and associated equipment such as an aerator, a sludge scraper, and a return sludge pump. In the method, when the water level of the facility reaches the set high water level alert level, one or more devices of the aerator, sludge scraper and return sludge pump are automatically stopped, and A method for operating a sewage treatment facility, characterized in that sludge is prevented from overflowing in advance.
【請求項2】 施設の水位が設定された高水位の警戒レ
ベル以下になった時に、停止している曝気機、汚泥掻寄
機、返送汚泥ポンプのいずれか1種若しくは複数の機器
を、自動的に通常運転に復帰するようにしたことを特徴
とする請求項1記載の汚水処理設備の運転方法。
2. When the water level of the facility falls below the set high water level alert level, one or more of the stopped aerator, sludge scraper and return sludge pump are automatically turned on. The method for operating sewage treatment equipment according to claim 1, wherein the normal operation is returned to normal operation.
JP25992899A 1999-09-14 1999-09-14 Operation of sewage treating equipment Pending JP2001079586A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP25992899A JP2001079586A (en) 1999-09-14 1999-09-14 Operation of sewage treating equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP25992899A JP2001079586A (en) 1999-09-14 1999-09-14 Operation of sewage treating equipment

Publications (1)

Publication Number Publication Date
JP2001079586A true JP2001079586A (en) 2001-03-27

Family

ID=17340887

Family Applications (1)

Application Number Title Priority Date Filing Date
JP25992899A Pending JP2001079586A (en) 1999-09-14 1999-09-14 Operation of sewage treating equipment

Country Status (1)

Country Link
JP (1) JP2001079586A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009028673A (en) * 2007-07-30 2009-02-12 Miike Iron Works Co Ltd Apparatus for reducing sludge volume
JP2010247127A (en) * 2009-04-20 2010-11-04 Kobelco Eco-Maintenance Co Ltd Method of operating organic waste water treatment facility
CN113958518A (en) * 2021-11-17 2022-01-21 刘小军 Internet water pump station and automatic adjusting method thereof

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009028673A (en) * 2007-07-30 2009-02-12 Miike Iron Works Co Ltd Apparatus for reducing sludge volume
JP2010247127A (en) * 2009-04-20 2010-11-04 Kobelco Eco-Maintenance Co Ltd Method of operating organic waste water treatment facility
CN113958518A (en) * 2021-11-17 2022-01-21 刘小军 Internet water pump station and automatic adjusting method thereof
CN113958518B (en) * 2021-11-17 2024-03-22 北京三友卓越科技有限公司 Internet water pump station and automatic adjusting method thereof

Similar Documents

Publication Publication Date Title
US5006232A (en) Sewage treatment plant
HU222677B1 (en) Method and apparatus for sewage water treatment
KR20050043855A (en) Self controlling sewage or wastewater treatment process
CN104703927B (en) Waste water outflow system and method
EP1136449B1 (en) Waste water processing system
JP2001079586A (en) Operation of sewage treating equipment
JP2010155184A (en) Support feeding type biological reaction apparatus
JP2004188255A (en) Oxidation ditch
JP2000110733A (en) Control system for pump of storage facility
JP2003027533A (en) Rainwater and bathtub water recycling apparatus
JP7437144B2 (en) water treatment plant
JP3908927B2 (en) Sewage disinfection method
SU1091128A1 (en) System for control of process for primary separating of sewage
JPH10296251A (en) Method for regulating sludge in sewage treatment tank
JP7103598B2 (en) Water treatment control device and water treatment system
JP3257946B2 (en) Sewage treatment method and sewage treatment apparatus
JP2002242238A (en) Reclaimed water facility
JP2002239569A (en) Facilities for reclaimed water
Kirschenman et al. A regulatory guide to sequencing batch reactors
BG109696A (en) Method and installation for biological sewage treatment
JP3739203B2 (en) Waste water treatment apparatus and operation method thereof
JP2002239552A (en) Reclaimed water facility
JP2002242899A (en) Water supply device
JP2022021204A (en) Modification method for activated sludge treatment facilities
JP2002239548A (en) Reclaimed water facility