JP2000069955A - Activity evaluation testing system - Google Patents

Activity evaluation testing system

Info

Publication number
JP2000069955A
JP2000069955A JP10243479A JP24347998A JP2000069955A JP 2000069955 A JP2000069955 A JP 2000069955A JP 10243479 A JP10243479 A JP 10243479A JP 24347998 A JP24347998 A JP 24347998A JP 2000069955 A JP2000069955 A JP 2000069955A
Authority
JP
Japan
Prior art keywords
reactor
mixture
concentration
activity evaluation
tank
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.)
Granted
Application number
JP10243479A
Other languages
Japanese (ja)
Other versions
JP3567453B2 (en
Inventor
Hideaki Kawahara
英明 川原
Keisuke Nakamura
啓介 中村
Hironori Nakamura
裕紀 中村
Hitoshi Yoshikawa
均 吉川
Masahiro Midorikawa
正博 緑川
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 Plant Technologies Ltd
Original Assignee
Hitachi Plant Technologies 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 Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Technologies Ltd
Priority to JP24347998A priority Critical patent/JP3567453B2/en
Publication of JP2000069955A publication Critical patent/JP2000069955A/en
Application granted granted Critical
Publication of JP3567453B2 publication Critical patent/JP3567453B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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

  • Apparatus Associated With Microorganisms And Enzymes (AREA)
  • Activated Sludge Processes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide an activity evaluation testing system by promptly metering the oxygen consumption rate with high accuracy. SOLUTION: The reactor (4) is equipped with a means metering the oxygen dissolved (DO) in the liquid in the reactor (4) and a means metering the oxygen (O2) in the upper gas phase and a certain amount of a microorganism mixture is introduced into the reactor (4) from the microorganism mixing tank (2) on the outside by evacuating the inside of the reactor (4). The activity of a microorganism is evaluated by metering the DO concentration in the culture mixture and the O2 concentration in the gas tightly closed in the upper part (4a) of the reactor (4).

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、活性評価試験装置
に係り、特に廃水の生物学的処理において処理装置の状
態監視や微生物の有機物酸化、硝化などの活性を評価す
るために必要な微生物の酸素消費速度を計測する活性評
価試験装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an activity evaluation test apparatus, and more particularly to an activity evaluation test apparatus for monitoring the condition of a treatment apparatus and evaluating the activity of microorganisms such as organic matter oxidation and nitrification in biological treatment of wastewater. The present invention relates to an activity evaluation test device for measuring an oxygen consumption rate.

【0002】[0002]

【従来の技術】廃水中の有機物や窒素成分を生物学的に
処理する方法では、一般に有機物の酸化やアンモニア性
窒素の硝化反応が利用される。これらの反応には、微生
物による酸素消費が伴うため、酸素消費速度をもとに、
処理装置の状態監視や微生物の有機物酸化、硝化などの
活性を評価することができる。
2. Description of the Related Art In a method of biologically treating organic substances and nitrogen components in wastewater, oxidation of organic substances and nitrification reaction of ammonia nitrogen are generally used. Because these reactions involve oxygen consumption by microorganisms, based on the rate of oxygen consumption,
It is possible to monitor the condition of the processing apparatus and evaluate the activity of microorganisms such as oxidation of organic substances and nitrification.

【0003】廃水処理装置における微生物の酸素消費速
度を計測する方法として、処理槽から微生物混合液を槽
外の小型反応器に採取し、反応器内で微生物反応を回分
で進行させ、その際の酸素消費速度を求める方法が知ら
れている。反応器内に採取した微生物混合液の酸素消費
速度を求める方法としては、溶存酸素濃度計(DO計)
および/または気相中の酸素濃度計(O2 計)を用いた
以下の方法が知られている。
[0003] As a method of measuring the oxygen consumption rate of microorganisms in a wastewater treatment apparatus, a mixture of microorganisms is collected from a treatment tank into a small reactor outside the tank, and the microbial reaction proceeds in the reactor in batches. Methods for determining the rate of oxygen consumption are known. As a method for obtaining the oxygen consumption rate of the microorganism mixture collected in the reactor, a dissolved oxygen concentration meter (DO meter)
The following method using an oxygen concentration meter (O 2 meter) in the gas phase is known.

【0004】a)反応器に空気を供給し、微生物混合液
から気相部に排出されるガス中のO 2 濃度を数mg/L
程度またはそれ以上に高めた後、空気の供給を止め、微
生物混合液を攪拌しながらDO計によりDO濃度の減少
速度を計測する。 b)反応器に空気を供給し、微生物混合液から気相部に
排出されるガス中のO 2 濃度をO2 計で計測し、供給空
気(大気)中のO2 濃度との差および供給空気量から酸
素消費速度を算出する。なお、DO濃度が変化する場合
は、DO計によりDO濃度の変化速度を計測し、酸素消
費速度を補正する。
A) Air is supplied to the reactor, and a mixture of microorganisms is supplied.
In the gas discharged from the gas into the gas phase TwoThe concentration is several mg / L
After increasing the air supply to about
DO concentration reduction by DO meter while stirring biological mixture
Measure the speed. b) Supply air to the reactor to convert the microorganism mixture into the gas phase.
O in exhaust gas TwoO concentrationTwoMeter and supply empty
O in the atmosphereTwoFrom the difference from the concentration and the amount of air supplied, acid
Calculate the elementary consumption speed. When the DO concentration changes
Measures the rate of change of the DO concentration with a DO meter,
Correct the speed.

【0005】c)反応器に空気を供給しながら、微生物
の混合液のDO濃度を測定し、その変化速度と総括酸素
移動容量係数(KLa)から酸素消費速度を算出する。 a)の方法は、混合液のDO濃度が0mg/Lになった
時点で計測が終了するため、反応器における混合液の初
期の酸素消費速度のみを測定するために用いられる。
C) While supplying air to the reactor, the DO concentration of the mixture of microorganisms is measured, and the oxygen consumption rate is calculated from the change rate and the overall oxygen transfer capacity coefficient (K La ). The method a) is used to measure only the initial oxygen consumption rate of the mixed solution in the reactor, since the measurement ends when the DO concentration of the mixed solution becomes 0 mg / L.

【0006】これに対し、b)およびc)の方法は、空
気を継続して供給するため、反応器内の微生物反応に伴
う酸素消費速度の推移を継続して計測することができ
る。しかし、b)の方法は、反応器を小型容器とした場
合、排気ガス中のO2 濃度と大気中のそれとの差はごく
僅かであり、酸素消費速度の測定誤差が比較的大きいと
いう問題がある。c)の方法は、間接指標であるKLa
用いて酸素消費速度を換算するためDO計のみを備えれ
ばよく、装置が簡単であるが、水温や空気量その他のパ
ラメータとの相関を把握する必要があるので、計測が煩
雑になるという問題がある。
On the other hand, in the methods b) and c), since the air is continuously supplied, the transition of the oxygen consumption rate accompanying the microbial reaction in the reactor can be continuously measured. However, the method b) has a problem that when the reactor is a small vessel, the difference between the O 2 concentration in the exhaust gas and that in the atmosphere is very small, and the measurement error of the oxygen consumption rate is relatively large. is there. Method c) requires only a DO meter to convert the oxygen consumption rate using K La which is an indirect index, and the apparatus is simple. However, the correlation with water temperature, air flow and other parameters can be grasped. Therefore, there is a problem that the measurement becomes complicated.

【0007】[0007]

【発明が解決しようとする課題】さて、処理槽の微生物
混合液を反応器に採取する場合、微生物の活性および混
合液の水質は刻々と変化するため、高速流で短時間に採
取工程を終了させる必要がある。そのため、混合液の採
取には、通常、高速流の送液ポンプが用いられるが、そ
の際、ポンプの高速回転部に混合液が直接接触するた
め、混合液内の微生物のフロックが破壊される場合があ
った。さらに、混合液が、微生物を表面または内部に固
定化した担体を含む場合には、担体表面からの微生物の
剥離や場合により担体自体の磨耗、破壊を生じかねない
問題もあった。
When the mixed liquid of microorganisms in the treatment tank is collected in the reactor, the activity of the microorganisms and the water quality of the mixed liquid change every moment. Need to be done. For this reason, a high-speed flow pump is usually used to collect the mixed solution. At this time, the mixed solution comes into direct contact with the high-speed rotating part of the pump, so that the flocs of microorganisms in the mixed solution are destroyed. There was a case. Further, when the mixture contains a carrier having microorganisms immobilized on the surface or inside thereof, there has been a problem that the microorganisms may be peeled off from the surface of the carrier, and in some cases, the carrier itself may be worn or destroyed.

【0008】送液ポンプを用いずに、反応器内に混合液
を採取する方法として、減圧ポンプによって反応器内を
減圧し、その負圧で混合液を反応器内に吸引する方法が
知られている。この方法を実施する装置は、反応器を減
圧状態にし、流入弁を開くことにより、外部の液を反応
器内に吸引し、反応器に設置された液面計に液位が達し
た時点で流入弁を閉じ、さらに大気弁を開き、気相部を
大気圧に戻すように構成されている。そして計測後は、
内部の液を排出弁から排出させ、次の液の採取工程に移
る。この装置によれば、ポンプの高速回転部に混合液が
直接接触することがなく、混合液内の微生物のフロック
が破壊されることなく、さらに、混合液が、微生物を表
面または内部に固定化した担体を含む場合に、担体表面
からの微生物の剥離や場合により担体自体の磨耗、破壊
を生じることなく、外部の液を高流速で容器内に採取す
ることができる。
As a method of collecting a mixed solution in a reactor without using a liquid sending pump, there is known a method of reducing the pressure in the reactor by a pressure reducing pump and sucking the mixed solution into the reactor at the negative pressure. ing. The apparatus for carrying out this method is that, when the reactor is depressurized and the inflow valve is opened, the external liquid is sucked into the reactor, and when the liquid level reaches the level gauge installed in the reactor, The inflow valve is closed, the atmosphere valve is opened, and the gas phase is returned to atmospheric pressure. And after the measurement,
The liquid inside is discharged from the discharge valve, and the process proceeds to the next liquid collecting step. According to this device, the mixed solution does not directly contact the high-speed rotating part of the pump, the flocs of the microorganisms in the mixed solution are not destroyed, and the mixed solution further fixes the microorganisms on the surface or inside. When a carrier is used, an external liquid can be collected into the container at a high flow rate without peeling of microorganisms from the surface of the carrier and in some cases abrasion or destruction of the carrier itself.

【0009】しかしながら、この反応器に、内部の混合
液中のDO濃度と上部ガス中のO2濃度を計測するため
のDO計とO2 計を導入する場合には、混合液の採取時
にDO計が混合液に接触する時間が短く、混合液のDO
濃度に十分に応答できない。そのため、採取終了後に混
合液のDO濃度変化の計測を開始する際に、応答の遅れ
が生じて精度の良い計測ができない。また、混合液の採
取時に容器内が減圧状態になり、ガス中のO2 濃度およ
びO2 計の指示値が低下するため、採取終了後に気相部
を大気圧にしてガス中のO2 濃度変化の計測を開始する
際に、応答の遅れが生じて精度の良い計測ができない。
さらに、この反応器に、隔膜内に電解液が保持された従
来のDO電極を導入する場合には、混合液を採取するた
めに、反応器内を減圧状態(600Toor以下)にし
た際、DO電極の指示値が一時的に、極端に高い数値を
示すなど異常がみられ、採取された混合液のDO濃度に
十分に応答できない場合があり、採取終了後に混合液の
DO濃度変化の計測を開始する際に、応答の遅れが生
じ、精度の良い計測ができなかった。
However, when introducing a DO meter and an O 2 meter for measuring the DO concentration in the internal mixture and the O 2 concentration in the upper gas into this reactor, the DO at the time of collecting the mixture is required. The time for the meter to contact the mixture is short,
Inadequate response to concentration. Therefore, when the measurement of the DO concentration change of the mixed solution is started after the end of the collection, a delay in response occurs and accurate measurement cannot be performed. Further, it becomes vessel is depressurized state during collection of the liquid mixture, the O 2 concentration for the indicated value of the O 2 concentration and O 2 meter in the gas is decreased, and the gas phase to atmospheric pressure after collection finished gas When the measurement of the change is started, a response delay occurs, and accurate measurement cannot be performed.
Further, when a conventional DO electrode in which an electrolyte is held in a diaphragm is introduced into this reactor, when the inside of the reactor is depressurized (600 Toor or less) to collect a mixed solution, DO Abnormalities such as an extremely high reading temporarily appearing on the electrode may not be enough to respond to the DO concentration of the sampled liquid mixture. When starting, a response delay occurred, and accurate measurement could not be performed.

【0010】本発明は、このような事情に鑑みてなされ
たもので、上記従来技術の欠点を解消して、微生物混合
液を反応器に採取し、微生物の酸素消費速度を測定する
装置において、混合液内の微生物のフロックの破壊や担
体表面または内部に固定化した微生物の剥離および担体
自体の磨耗、破壊を生じることなく、さらには反応器に
採取した微生物混合液のDO濃度と上部気相部のO2
度の変化の計測開始時に、DO計とO2 計の指示値を、
それぞれ混合液の初期のDO濃度と大気中のO 2 濃度に
確実に合わせることにより、精度良く酸素消費速度を計
測することができる活性評価試験装置を提供することを
目的とする。
The present invention has been made in view of such circumstances.
It eliminates the disadvantages of the prior art described above,
Collect the liquid in a reactor and measure the rate of oxygen consumption by microorganisms
In the device, the destruction and burden of microbial flocs in the mixture
Exfoliation and carrier of microorganisms immobilized on or in the body
Without causing wear and tear of itself, and even in the reactor
DO concentration of collected microorganism mixture and O in upper gas phaseTwoDark
At the start of the measurement of the degree change, the DO meter and OTwoMeter reading,
The initial DO concentration of the mixture and the O TwoTo the concentration
Accurate measurement of oxygen consumption rate
To provide an activity evaluation test device capable of measuring
Aim.

【0011】[0011]

【課題を解決するための手段】本発明は前記目的を達成
するために、本発明の請求項1の活性評価試験装置は、
反応器が内部液中の溶存酸素(DO)濃度と上部ガス中
の酸素(O2 )濃度を計測する手段を有し、前記反応器
内を減圧状態とすることにより、外部の微生物混合槽か
ら微生物混合液を前記反応器内に一定量採取するように
構成され、前記反応器への混合液の採取終了時から、前
記反応器上部に密閉されたガスを混合液内に循環しなが
ら混合液のDO濃度とガス中のO2 濃度の変化を計測す
ることにより微生物活性を評価することを特徴としてい
る。
In order to achieve the above object, the present invention provides an activity evaluation test apparatus according to claim 1 of the present invention.
The reactor has means for measuring the concentration of dissolved oxygen (DO) in the internal liquid and the concentration of oxygen (O 2 ) in the upper gas. It is configured to collect a fixed amount of the microorganism mixture into the reactor, and from the end of collection of the mixture into the reactor, while circulating the gas sealed in the upper part of the reactor into the mixture, The microbial activity is evaluated by measuring changes in the DO concentration and the O 2 concentration in the gas.

【0012】また、本発明の請求項2の活性評価試験装
置は、請求項1において、前記反応器がその容積よりも
大きい容積をもつ減圧タンクに連結され、微生物混合液
の採取時に、前記減圧タンクを減圧し、微生物混合液を
外部から前記反応器内、次いで前記減圧タンク内に吸引
することにより、前記反応器内の混合液を外部からの混
合液と入れ換えながら、反応器に備えたDO計の指示値
を混合液のDO濃度に合わせるように構成したことを特
徴としている。
According to a second aspect of the present invention, there is provided an activity evaluation test apparatus according to the first aspect, wherein the reactor is connected to a pressure reducing tank having a larger volume than the reactor, and the pressure reduction tank is used when collecting the microorganism mixture. By depressurizing the tank and sucking the microorganism mixture from the outside into the reactor and then into the vacuum tank, the DO in the reactor was replaced while replacing the mixture in the reactor with the mixture from the outside. It is characterized in that the reading of the meter is adapted to the DO concentration of the mixture.

【0013】また、本発明の請求項3の活性評価試験装
置は、請求項2において、前記反応器と前記減圧タンク
を連結する連結管の位置を前記反応器内の混合液の液位
と合わせることにより、前記反応器に混合液を一定量採
取するように構成したことを特徴としている。また、本
発明の請求項4の活性評価試験装置は、請求項1、2ま
たは3において、微生物混合液の採取終了時に、前記反
応器の上部ガス部に外気を吸引することにより、減圧さ
れていたガス部の圧力を大気圧に戻すことを特徴として
いる。
According to a third aspect of the present invention, in the activity evaluation test apparatus according to the second aspect, the position of the connecting pipe connecting the reactor and the pressure reducing tank is adjusted to the level of the mixed solution in the reactor. This is characterized in that a fixed amount of the mixed solution is collected in the reactor. Further, in the activity evaluation test device according to claim 4 of the present invention, the pressure is reduced by sucking outside air into the upper gas portion of the reactor at the end of the collection of the microorganism mixture in claim 1, 2 or 3. It is characterized by returning the pressure of the gas part to atmospheric pressure.

【0014】反応器を減圧状態にした際にDO電極の指
示値が異常を示す原因として、電極の隔膜内に保持され
た電解液が、隔膜を介して反応器内に吸引されることに
より、電解液内でキャビテーションを生じるためである
ことが種々の検討から推測された。そこで、電解液部か
ら反応器の同じく減圧された気相部に通じる連通管を取
付け、隔膜を介した吸引力を打ち消す方向に電解液に引
力を生じさせるように構成したものである。
The cause of the abnormality in the indicated value of the DO electrode when the reactor is depressurized is that the electrolyte held in the diaphragm of the electrode is sucked into the reactor through the diaphragm. It was inferred from various studies that this is because cavitation occurs in the electrolytic solution. Therefore, a communication pipe is provided from the electrolytic solution part to the gas phase part of the reactor, which is also depressurized, so that an attractive force is generated in the electrolytic solution in a direction to cancel the suction force through the diaphragm.

【0015】[0015]

【発明の実施の形態】以下、添付図面に従って本発明の
活性評価試験装置の好ましい実施の形態について詳説す
る。図1は、本発明係る活性評価試験装置の一実施の形
態を示している。この装置は、微生物混合槽2、反応器
4、減圧タンク6等によって構成されている。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of the activity evaluation test apparatus of the present invention will be described below in detail with reference to the accompanying drawings. FIG. 1 shows an embodiment of the activity evaluation test apparatus according to the present invention. This apparatus includes a microorganism mixing tank 2, a reactor 4, a decompression tank 6, and the like.

【0016】反応器4は、その下部に流入管8の一端が
接続されている。この流入管8は、中間部が立ち上げら
れ、他端が微生物混合槽2の微生物混合液10内に浸漬
されている。そして、流入管8の中間部には流入弁12
が配設されている。また、反応器4の上部には連結管1
4の一端が配置されており、該連結管14の他端は減圧
タンク6の上部(気相部)6aに配置されている。さら
に、反応器4の上部には、DO計16が設置されてい
る。このDO計16は、その先端に隔膜18を備え、該
隔膜18を上記連結管14の一端よりも僅かに低い位置
に配置させている。このDO計16は一端を内部に接続
し、他端を上記連結管14の一端よりも高く位置させた
連通管20を備えている。また、この反応器4には、上
部(気相部)4aと底部とを接続する循環ライン22が
形成され、該循環ライン22の中間には循環ポンプ24
が介在され、該循環ポンプ24と反応器4の上部4aと
の間に切換え弁26、また循環ポンプ24と反応器4の
底部との間に切換え弁28がそれぞれ介在されている。
上記切換え弁26は、反応器4の上部4aを大気または
循環ライン22に選択的に連通させるもので、上記切換
え弁28は、循環ライン22を反応器4の底部または大
気に選択的に連通するものである。さらに、循環ライン
22における循環ポンプ24と切換え弁26との間には
2 計30が配設されている。
The lower end of the reactor 4 is connected to one end of an inlet pipe 8. The inflow pipe 8 has an intermediate portion raised and the other end immersed in the microorganism mixture 10 in the microorganism mixture tank 2. An inflow valve 12 is provided at an intermediate portion of the inflow pipe 8.
Are arranged. In addition, a connecting pipe 1 is provided above the reactor 4.
The other end of the connecting pipe 14 is arranged at the upper part (gas phase part) 6 a of the pressure reducing tank 6. Further, a DO meter 16 is provided above the reactor 4. The DO meter 16 has a diaphragm 18 at its tip, and the diaphragm 18 is arranged at a position slightly lower than one end of the connection pipe 14. The DO meter 16 includes a communication pipe 20 having one end connected to the inside and the other end positioned higher than one end of the connection pipe 14. A circulation line 22 connecting the upper part (gas phase part) 4a and the bottom part is formed in the reactor 4, and a circulation pump 24 is provided in the middle of the circulation line 22.
A switching valve 26 is interposed between the circulation pump 24 and the upper portion 4a of the reactor 4, and a switching valve 28 is interposed between the circulation pump 24 and the bottom of the reactor 4.
The switching valve 26 selectively connects the upper portion 4a of the reactor 4 to the atmosphere or the circulation line 22, and the switching valve 28 selectively communicates the circulation line 22 to the bottom of the reactor 4 or the atmosphere. Things. Further, an O 2 meter 30 is disposed between the circulation pump 24 and the switching valve 26 in the circulation line 22.

【0017】減圧タンク6は、上部(気相部)6aに吸
引管32の一端が接続されており、該吸引管32には減
圧ポンプ34が設置されている。この減圧タンク6の底
部には、排液管36の一端が接続され、該排液管36の
他端は上記微生物混合槽2に接続されている。そして、
該排液管36には、排出弁38が介在されている。さら
に、この減圧タンク6の上部には、液面計40および開
放弁42が設置されている。
One end of a suction pipe 32 is connected to an upper part (gas phase part) 6a of the decompression tank 6, and a decompression pump 34 is installed in the suction pipe 32. One end of a drain pipe 36 is connected to the bottom of the decompression tank 6, and the other end of the drain pipe 36 is connected to the microorganism mixing tank 2. And
A drain valve 38 is interposed in the drain pipe 36. Further, a liquid level gauge 40 and an opening valve 42 are provided above the decompression tank 6.

【0018】本発明に係る活性評価試験装置は、反応器
4の気相部(上部)4aを密閉構造とし、反応器4内の
微生物混合液からの排出ガスを循環ポンプ24により反
応器4内の混合液中に供給し、その際のDO濃度とO2
濃度のそれぞれの変化を計測するものである。そしてD
O濃度とO2 濃度のそれぞれの変化速度および混合液、
気相部の容積から酸素消費速度を算出する。
In the activity evaluation test apparatus according to the present invention, the gas phase part (upper part) 4a of the reactor 4 has a closed structure, and the exhaust gas from the mixture of microorganisms in the reactor 4 is supplied to the reactor 4 by the circulation pump 24. And the DO concentration and O 2
It measures each change in concentration. And D
The rate of change of each of the O concentration and the O 2 concentration and the mixture;
The oxygen consumption rate is calculated from the volume of the gas phase.

【0019】本装置により試料(微生物混合液)を採取
し、その酸素消費速度を計測する運転例を、図1に基づ
いて各工程ごとに示すと以下のようになる。 試料採取 反応器4の切換え弁26によって反応器4を大気から遮
断するとともに、開放弁42を閉じて減圧タンク6を大
気から遮断して、減圧ポンプ34を作動させると、減圧
タンク6および反応器4は減圧ポンプ34によって減圧
される。そこで、流入管8の流入弁12を開けると、微
生物混合槽2から混合液10が反応器4、次いで減圧タ
ンク6に吸引される。減圧タンク6に混合液が所定量満
たされ、液面が液面計40の接触子先端に至ると、流入
弁12を閉じて混合液の採取を終了する。続いて、切換
え弁26を操作して反応器4を大気に開放するととも
に、開放弁42を開き減圧タンク6を大気に開放する。
すると、反応器4上部の気相部4aが外気と入れ替わ
り、減圧タンク6の気相部6aとともに大気圧に戻る。
その結果、反応器4内には連結管14の開口位置と同じ
液位で、混合液が一定量採取される。また、減圧タンク
6に残った余分の混合液は、その後、適当な時間に排出
弁38を開放することによって微生物混合槽2へ戻され
る。なお、混合液の採取時には、反応器4の気相部4a
から反応器4の底部に至る循環ライン22は切換え弁2
6と切換え弁28によって反応器4から遮断され、かつ
それらの切り換え弁26、28を介して大気に連通さ
れ、同時に、循環ポンプ24によって外気をライン中の
2 計30に通過させ、O2 計30のキャリブレーショ
ンを行なう。
An operation example in which a sample (mixture of microorganisms) is collected by the present apparatus and the rate of oxygen consumption is measured based on FIG. 1 for each process is as follows. Sampling The reactor 4 is shut off from the atmosphere by the switching valve 26 of the reactor 4, the opening valve 42 is closed to shut off the depressurizing tank 6 from the atmosphere, and the depressurizing pump 34 is operated. 4 is depressurized by the decompression pump 34. Then, when the inflow valve 12 of the inflow pipe 8 is opened, the mixed solution 10 is sucked from the microorganism mixing tank 2 into the reactor 4 and then into the decompression tank 6. When the pressure-reducing tank 6 is filled with a predetermined amount of the liquid mixture and the liquid level reaches the contact tip of the liquid level gauge 40, the inflow valve 12 is closed to terminate the collection of the liquid mixture. Subsequently, the switching valve 26 is operated to open the reactor 4 to the atmosphere, and the opening valve 42 is opened to open the pressure reducing tank 6 to the atmosphere.
Then, the gas phase part 4a in the upper part of the reactor 4 is exchanged with the outside air, and returns to the atmospheric pressure together with the gas phase part 6a of the pressure reducing tank 6.
As a result, a certain amount of the mixed liquid is collected in the reactor 4 at the same liquid level as the opening position of the connection pipe 14. The excess mixed solution remaining in the decompression tank 6 is thereafter returned to the microorganism mixing tank 2 by opening the discharge valve 38 at an appropriate time. When the mixed solution is collected, the gas phase 4a of the reactor 4
A circulation line 22 extending from the reactor to the bottom of the reactor 4 is provided with a switching valve 2
It is isolated from the reactor 4 by 6 and the switching valve 28, and communicates with the atmosphere via their switching valves 26 and 28, at the same time, passed through the outside air into O 2 meter 30 in the line by the circulating pump 24, O 2 A total of 30 calibrations are performed.

【0020】この活性評価試験装置では、減圧タンク6
の容積を反応器4のそれより大きく構成している。その
ため、反応器4内の混合液は完全に入れ換えられ、反応
器6に備えられたDO計16は、混合液採取の間、連続
して入れ替わる混合液と接触することができ、DO計1
6の指示値が混合液のDO濃度(初期値)と一致するよ
うになる。なお、採取が終了するまでの混合液とDO計
16の接触時間は、減圧タンク6の容積、液面計40の
高さ、減圧ポンプ34の吸引量、流入管8、連結管14
の内径、長さなどにより容易に調節することができ、通
常、0.5〜3分に設定される。 試料の酸素消費速度の計測 反応器4への混合液の採取後、切換え弁26および切換
え弁28を操作して、循環ライン22を反応器4に接続
し、循環ポンプ24により、密閉された反応器4の気相
部4aのガスをライン中のO2 計30に連通させた後、
反応器4の底部から反応器4内の混合液に供給する。混
合液の採取終了時に、DO計16は混合液の初期のDO
濃度を示しており、またO2 計30は外気を用いてキャ
リブレーションが終了し、反応器4の気相部4aのガス
も外気と入れ替わっているため、反応器4に採取した混
合液内の微生物反応による酸素消費に伴う、混合液のD
O濃度およびガス中のO2 濃度の変化を精度良く計測す
ることができる。
In this activity evaluation test apparatus, the pressure reducing tank 6
Is made larger than that of the reactor 4. Therefore, the mixture in the reactor 4 is completely exchanged, and the DO meter 16 provided in the reactor 6 can come into contact with the continuously exchanged mixture during the mixture sampling, and the DO meter 1
6 becomes equal to the DO concentration (initial value) of the mixed solution. The contact time between the mixed solution and the DO meter 16 until the collection is completed depends on the volume of the decompression tank 6, the height of the liquid level gauge 40, the suction amount of the decompression pump 34, the inflow pipe 8, the connection pipe 14 and the like.
Can be easily adjusted by the inner diameter, length, etc., and is usually set to 0.5 to 3 minutes. Measurement of Oxygen Consumption Rate of Sample After collecting the mixed solution in the reactor 4, the switching valve 26 and the switching valve 28 are operated to connect the circulation line 22 to the reactor 4, and the closed reaction is performed by the circulation pump 24. After the gas in the gas phase part 4a of the vessel 4 is communicated with the O 2 meter 30 in the line,
The mixed solution in the reactor 4 is supplied from the bottom of the reactor 4. At the end of the sampling of the mixture, the DO meter 16 indicates the initial DO of the mixture.
The concentration is shown, and the calibration of the O 2 meter 30 is completed using the outside air, and the gas in the gas phase portion 4 a of the reactor 4 is also replaced with the outside air. D of mixed solution accompanying oxygen consumption by microbial reaction
Changes in the O concentration and the O 2 concentration in the gas can be accurately measured.

【0021】なお、酸素消費速度は次式(1)から求め
られる。
The oxygen consumption rate can be obtained from the following equation (1).

【0022】[0022]

【数1】 なお、本発明の活性評価試験装置は、上記実施の形態に
限らず各種変更が可能である。例えば、流入弁12は流
入管8に介在させ、該流入弁12を開くことによって流
入管8を開通させ、流入弁12を閉じることによって流
入管8を閉止しているが、流入管8を大気弁とし、該弁
を開くことによって流入管8を大気に開放し、それによ
って微生物混合槽2の混合液が反応器4へ流入するのを
阻止することもできる。この場合には、大気弁の設置位
置を反応器4における連結管14の開口位置よりも高い
位置に設置する必要がある。また、各弁の作動タイミン
グは、本発明の目的を達成できる範囲で適宜変更するこ
ともできる。
(Equation 1) In addition, the activity evaluation test apparatus of the present invention is not limited to the above embodiment, and various changes can be made. For example, the inflow valve 12 is interposed in the inflow pipe 8, the inflow pipe 8 is opened by opening the inflow valve 12, and the inflow pipe 8 is closed by closing the inflow valve 12. By opening the valve, the inflow pipe 8 is opened to the atmosphere so that the mixture in the microorganism mixing tank 2 can be prevented from flowing into the reactor 4. In this case, it is necessary to install the atmospheric valve at a position higher than the opening position of the connecting pipe 14 in the reactor 4. Further, the operation timing of each valve can be appropriately changed within a range in which the object of the present invention can be achieved.

【0023】[0023]

【実施例】上記した活性評価試験装置による酸素消費速
度の計測例を図2に示す。本例は、下水の硝化、脱窒処
理プロセスの硝化槽から、硝化細菌を固定化した担体
(3mm角)と浮遊活性汚泥の混合液を採取したもので
ある。計測開始時(初期)に、反応器のガス中のO2
度(%表示)はほぼ大気と同じ21%を示し、微生物反
応の進行に伴って低下し、30分後に17%近くに達し
ている。DO濃度は、初期に5mg/L程度を示し、3
0分後に6mg/Lに達してしる。20秒毎の各計測値
とVL =1.6L、VG =0.4Lをもとに、酸素消費
速度Kr を算出した結果を同じく図2に示す。Kr は、
初期に30mg/L・h程度を示し、時間の経過ととも
に低下し、約20分後、10mg/L・h程度で安定す
る結果が得られた。
FIG. 2 shows an example of measuring the oxygen consumption rate by the above-described activity evaluation test apparatus. In this example, a mixed solution of a carrier (3 mm square) on which nitrifying bacteria were immobilized and floating activated sludge was collected from a nitrification tank in a sewage nitrification and denitrification process. At the start of measurement (initial stage), the O 2 concentration in the gas of the reactor (expressed in%) shows almost 21%, which is almost the same as the atmosphere, and decreases with the progress of the microbial reaction, reaching nearly 17% after 30 minutes. I have. The DO concentration initially shows about 5 mg / L,
It reaches 6 mg / L after 0 minutes. Each measured value every 20 seconds and the V L = 1.6 L, the V G = 0.4 L to the original, also shown in FIG. 2 the result of calculating the oxygen consumption rate K r. K r is
The initial value was about 30 mg / L · h, which decreased with the passage of time. After about 20 minutes, a stable result was obtained at about 10 mg / L · h.

【0024】また、上記した活性評価試験装置では、4
00〜600Torrの減圧状態において、従来装置に
みられたDO計の指示値の異常を解消することができ
た。なお、400Torr以下では、減圧状態が2分以
上続くと、反応器内の液中からO2 が析出し、液のDO
濃度そのものが変化するため、そのような運転を避ける
ことが好ましい。
In the above activity evaluation test apparatus,
Under the reduced pressure of 00 to 600 Torr, the abnormality of the indicated value of the DO meter, which was observed in the conventional apparatus, could be solved. At 400 Torr or less, if the depressurized state continues for 2 minutes or more, O 2 precipitates from the liquid in the reactor, and the DO
It is preferable to avoid such operation because the concentration itself changes.

【0025】[0025]

【発明の効果】以上のように、本発明の活性評価試験装
置では、ポンプを通過することなく負圧を利用すること
によって微生物混合槽の混合液を反応器へ導入している
ので、混合液内の微生物のフロックの破壊や担体表面ま
たは内部に固定化した微生物の剥離および担体自体の磨
耗、破壊を生じることなく、さらには反応器に採取した
微生物混合液のDO濃度と上部気相部のO2 濃度の変化
の計測開始時に、DO計とO2 計の指示値を、それぞれ
混合液の初期のDO濃度と大気中のO2 濃度に確実に合
わせることにより、迅速に精度良く酸素消費速度を計測
することができる。
As described above, in the activity evaluation test apparatus of the present invention, the mixture in the microorganism mixing tank is introduced into the reactor by utilizing the negative pressure without passing through the pump. The microbial floc is not destroyed, the microorganisms immobilized on the surface or inside of the carrier are not separated, and the carrier itself is not worn or destroyed. O 2 in the measurement starting concentration change, the indicated value of the DO meter and O 2 meter by reliably keying the O 2 concentration of the initial DO concentration in the atmosphere in each mixture, quickly and accurately the oxygen consumption rate Can be measured.

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

【図1】本発明に係る活性評価試験装置の一実施の形態
を示した構成図
FIG. 1 is a configuration diagram showing an embodiment of an activity evaluation test apparatus according to the present invention.

【図2】図1の活性評価試験装置によって得られた酸素
消費速度、DO濃度およびO2濃度を示した特性線図
FIG. 2 is a characteristic diagram showing the oxygen consumption rate, DO concentration and O 2 concentration obtained by the activity evaluation test apparatus of FIG.

【符号の説明】[Explanation of symbols]

2…微生物混合槽 4…反応器 4a…気相部 6…減圧タンク 6a…気相部 8…流入管 10…微生物混合液 12…流入弁 14…連結管 16…DO計 18…隔膜 20…連通管 22…循環ライン 24…循環ポンプ 26、28…切換え弁 30…O2 計 32…吸引管 34…減圧ポンプ 36…排液管 38…排出弁 40…液面計2 ... Microorganism mixing tank 4 ... Reactor 4a ... Gas phase 6 ... Decompression tank 6a ... Gas phase 8 ... Inflow pipe 10 ... Microorganism mixture 12 ... Inflow valve 14 ... Connecting pipe 16 ... DO meter 18 ... Diaphragm 20 ... Communication tube 22 ... circulation line 24 ... circulation pump 26, 28 ... switching valve 30 ... O 2 meter 32 ... suction pipe 34 ... vacuum pump 36 ... drain pipe 38 ... exhaust valve 40 ... liquid level meter

───────────────────────────────────────────────────── フロントページの続き (72)発明者 中村 裕紀 東京都千代田区内神田1丁目1番14号 日 立プラント建設株式会社内 (72)発明者 吉川 均 東京都千代田区内神田1丁目1番14号 日 立プラント建設株式会社内 (72)発明者 緑川 正博 埼玉県坂戸市溝端町9番地(15−203) Fターム(参考) 4B029 AA02 AA07 BB01 CC01 CC03 CC13 DA10 DB17 DF03 DF04 DF05 DF09 FA12 FA15 4D028 BC15 BC17 BC26 BD00 BD10 BD17 CA01 CA04 CA10 CB03 CB08 CC00 CC07 CC09 CC15 CD04 CD05  ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Yuki Nakamura 1-1-1 Uchikanda, Chiyoda-ku, Tokyo Inside Hitachi Plant Construction Co., Ltd. (72) Hitoshi Yoshikawa 1-1-1, Uchikanda, Chiyoda-ku, Tokyo No. 14 Inside Hitachi Plant Construction Co., Ltd. (72) Inventor Masahiro Midorikawa 9-15 Mizobata-cho, Sakado-shi, Saitama (15-203) F-term (reference) 4B029 AA02 AA07 BB01 CC01 CC03 CC13 DA10 DB17 DF03 DF04 DF05 DF09 FA12 FA15 4D028 BC15 BC17 BC26 BD00 BD10 BD17 CA01 CA04 CA10 CB03 CB08 CC00 CC07 CC09 CC15 CD04 CD05

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】反応器が内部液中の溶存酸素(DO)濃度
と上部ガス中の酸素(O2 )濃度を計測する手段を有
し、前記反応器内を減圧状態とすることにより、外部の
微生物混合槽から微生物混合液を前記反応器内に一定量
採取するように構成され、前記反応器への混合液の採取
終了時から、前記反応器上部に密閉されたガスを混合液
内に循環しながら混合液のDO濃度とガス中のO2 濃度
の変化を計測することにより微生物活性を評価すること
を特徴とする活性評価試験装置。
1. The reactor has means for measuring the concentration of dissolved oxygen (DO) in the internal liquid and the concentration of oxygen (O 2 ) in the upper gas. Is configured to collect a fixed amount of a mixed solution of microorganisms from the microorganism mixing tank into the reactor, and from the end of collection of the mixture to the reactor, the gas sealed at the top of the reactor is mixed into the mixed solution. An activity evaluation test device for evaluating microbial activity by measuring changes in the DO concentration of a mixture and the O 2 concentration in a gas while circulating.
【請求項2】前記反応器がその容積よりも大きい容積を
もつ減圧タンクに連結され、微生物混合液の採取時に、
前記減圧タンクを減圧し、微生物混合液を外部から前記
反応器内、次いで前記減圧タンク内に吸引することによ
り、前記反応器内の混合液を外部からの混合液と入れ換
えながら、反応器に備えたDO計の指示値を混合液のD
O濃度に合わせるように構成したことを特徴とする請求
項1に記載の活性評価試験装置。
2. The method according to claim 1, wherein said reactor is connected to a vacuum tank having a larger volume than said volume,
By decompressing the decompression tank and sucking the microorganism mixture from the outside into the reactor and then into the decompression tank, the mixture in the reactor is replaced with the mixture from the outside while preparing the reactor. The indicated value of the DO meter
The activity evaluation test device according to claim 1, wherein the device is configured to be adjusted to the O concentration.
【請求項3】前記反応器と前記減圧タンクを連結する連
結管の位置を前記反応器内の混合液の液位と合わせるこ
とにより、前記反応器に混合液を一定量採取するように
構成したことを特徴とする請求項2に記載の活性評価試
験装置。
3. A fixed amount of the mixture is collected in the reactor by adjusting a position of a connecting pipe connecting the reactor and the pressure reducing tank to a level of the mixture in the reactor. The activity evaluation test device according to claim 2, wherein:
【請求項4】微生物混合液の採取終了時に、前記反応器
の上部ガス部に外気を吸引することにより、減圧されて
いたガス部の圧力を大気圧に戻すことを特徴とする請求
項1、2または3に記載の活性評価試験装置。
4. The method according to claim 1, wherein when the collection of the mixture of microorganisms is completed, outside air is sucked into the upper gas portion of the reactor to return the reduced pressure of the gas portion to the atmospheric pressure. 4. The activity evaluation test device according to 2 or 3.
JP24347998A 1998-08-28 1998-08-28 Activity evaluation test equipment Expired - Fee Related JP3567453B2 (en)

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JP2000069955A true JP2000069955A (en) 2000-03-07
JP3567453B2 JP3567453B2 (en) 2004-09-22

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7449113B2 (en) 2002-09-24 2008-11-11 Advanced Aeration Control, Llc Controlling wastewater treatment processes
JP2010124722A (en) * 2008-11-26 2010-06-10 Ihi Corp Measurement device and method, and apparatus and method for operating culture tank system

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7449113B2 (en) 2002-09-24 2008-11-11 Advanced Aeration Control, Llc Controlling wastewater treatment processes
EP1546045B1 (en) * 2002-09-24 2021-01-20 Advanced Aeration Control, LLC Controlling wastewater treatment processes
JP2010124722A (en) * 2008-11-26 2010-06-10 Ihi Corp Measurement device and method, and apparatus and method for operating culture tank system

Also Published As

Publication number Publication date
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