JPH10318965A - BOD biosensor measuring device and standard solution for the measuring device - Google Patents
BOD biosensor measuring device and standard solution for the measuring deviceInfo
- Publication number
- JPH10318965A JPH10318965A JP9125235A JP12523597A JPH10318965A JP H10318965 A JPH10318965 A JP H10318965A JP 9125235 A JP9125235 A JP 9125235A JP 12523597 A JP12523597 A JP 12523597A JP H10318965 A JPH10318965 A JP H10318965A
- Authority
- JP
- Japan
- Prior art keywords
- standard solution
- bod
- measuring device
- biosensor
- solution
- 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.)
- Withdrawn
Links
Landscapes
- Investigating Or Analysing Biological Materials (AREA)
- Sampling And Sample Adjustment (AREA)
Abstract
(57)【要約】
【課題】BODバイオセンサ測定装置には、グルコース
とL−グルタミン酸の等量混合液が校正用標準溶液とし
て用いられているが、標準溶液の調製後時間が経つと劣
化が進行して検量線の傾きが変化し、測定精度の低下の
原因となる。本発明はこの課題を解決し、精度の高いB
ODバイオセンサ測定装置を提供することにある。
【解決手段】標準溶液としてグルコースとL−グルタミ
ン酸の等量混合液にアジ化ナトリウムを添加した水溶液
を使用する。これは標準溶液中への雑菌の繁殖やかび類
の発生を抑制して標準溶液が劣化しないために、BOD
の測定値が長期間安定しており、長期間の連続測定など
が実施可能となった。(57) [Problem] In a BOD biosensor measuring device, a mixture of equal amounts of glucose and L-glutamic acid is used as a standard solution for calibration, but deterioration occurs after a lapse of time after preparation of the standard solution. As the process proceeds, the slope of the calibration curve changes, causing a decrease in measurement accuracy. The present invention solves this problem and provides a highly accurate B
An OD biosensor measuring device is provided. An aqueous solution obtained by adding sodium azide to a mixture of equal amounts of glucose and L-glutamic acid is used as a standard solution. This is because the standard solution is not degraded by suppressing the growth of fungi and fungi in the standard solution.
The measured value of is stable for a long time, and a long-term continuous measurement can be performed.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、下水処理場、工
場、事業所などからの排水、および河川、湖沼などの環
境水域における検水を用いて、検水中の有機物汚染の尺
度である生物化学的酸素要求量(BOD)を、バイオセ
ンサにより測定する装置の校正用に用いる標準溶液の組
成に関する。BACKGROUND OF THE INVENTION The present invention relates to biochemistry, which is a measure of organic matter contamination in water samples using effluents from sewage treatment plants, factories, business establishments, and environmental water areas such as rivers and lakes. The standard oxygen demand (BOD) relates to the composition of a standard solution used for calibration of an instrument for measurement by a biosensor.
【0002】[0002]
【従来の技術】BODは、20℃、5日間という条件
で、好気性微生物によって検水中の有機物を資化する際
に消費される水中溶存酸素量をmg/Lの単位で表した
ものであり、最も代表的な水質汚濁の指標として極めて
重要なものである。BODは通常、日本工業規格(JI
S K0102)や、日本下水道協会の下水試験方法
(1984年)により、公定法として手分析によって測
定されている。2. Description of the Related Art BOD is the amount of dissolved oxygen in water consumed when aerobic microorganisms assimilate organic matter in a test water at 20 ° C. for 5 days, expressed in units of mg / L. It is extremely important as the most representative index of water pollution. The BOD is usually based on Japanese Industrial Standards (JI
SK0102) and by the Japan Sewerage Association Sewage Test Method (1984).
【0003】また、これら手分析によるBOD測定法と
は別に、簡便性、迅速性を特徴とするバイオセンサを用
いたBODの測定法があり、例えば特公昭61−725
8号公報などに記載されている。このバイオセンサとし
て微生物を用いたBODバイオセンサ測定装置は、排水
中のBODを約20〜40分程度で測定することができ
る非常に有効なBOD測定方法であり、平成2年には日
本工業規格「JISK3602:微生物電極による生物
化学的酸素要求量( BODS ) 計測器」に採用され、既
に製品化、実用化されている。In addition to the BOD measurement method based on manual analysis, there is a BOD measurement method using a biosensor characterized by its simplicity and speed. For example, Japanese Patent Publication No. 61-725.
No. 8, for example. The BOD biosensor measuring device using a microorganism as a biosensor is a very effective BOD measuring method capable of measuring BOD in wastewater in about 20 to 40 minutes. It has been adopted in “JISK3602: Biochemical oxygen demand (BOD S ) measuring device using a microbial electrode” and has already been commercialized and put into practical use.
【0004】[0004]
【発明が解決しようとする課題】しかしながら、上記の
微生物センサを用いたBODバイオセンサ測定装置は、
校正に用いる標準溶液の経時変化が大きいという問題点
がある。即ち、校正用標準溶液は、調製後に時間が経つ
と共に劣化が進行し、BODとして測定される有機物の
濃度が減少してしまう。このため、調製後長時間置いた
標準溶液では、調整直後のものに比べてBODバイオセ
ンサ測定装置の出力が低下し、検量線の傾きが低下する
結果、検水の測定値が正常値より上昇し、また測定精度
が悪化してしまう。したがって、長期間連続的に測定を
続ける必要のある場合には、校正用標準溶液を新しく調
製し直したものに頻繁に交換しなければならない。これ
は測定装置の操作に手間がかかるということであり、ま
た測定精度も問題があるため、厳密にはこの測定装置で
は、長期間連続の測定ができないことになる。However, a BOD biosensor measuring device using the above-mentioned microorganism sensor is
There is a problem that the standard solution used for calibration has a large change with time. That is, the calibration standard solution deteriorates with time after preparation, and the concentration of the organic substance measured as BOD decreases. For this reason, the output of the BOD biosensor measuring device in the standard solution left for a long time after preparation is lower than that of the standard solution immediately after the adjustment, and the slope of the calibration curve is reduced. In addition, the measurement accuracy deteriorates. Therefore, when it is necessary to continue measurement for a long period of time, the calibration standard solution must be frequently replaced with a freshly prepared one. This means that it takes time and effort to operate the measuring device, and there is also a problem with the measurement accuracy. Strictly, this measuring device cannot perform continuous measurement for a long period of time.
【0005】[0005]
【課題を解決するための手段】BOD標準溶液の劣化を
防ぐという上記の問題を解決するために、本発明では、
アジ化ナトリウムを添加したグルコース・グルタミン酸
標準溶液をBODバイオセンサ測定装置用標準溶液とす
ることとする。このアジ化ナトリウムを従来のグルコー
ス・L−グルタミン酸等量混合溶液に添加することによ
って、標準溶液中での雑菌の繁殖や、かび類の発生を抑
制することができる。この結果、標準溶液中のBOD濃
度の低下が抑制され、精度の良いBOD測定が可能とな
る。さらに、標準溶液を調製し直す頻度も少なくでき、
長期間の連続測定にも適用が可能となる。Means for Solving the Problems In order to solve the above-mentioned problem of preventing the deterioration of the BOD standard solution, the present invention provides:
The glucose / glutamic acid standard solution to which sodium azide has been added is used as a standard solution for a BOD biosensor measurement device. By adding this sodium azide to a conventional mixed solution of equal amounts of glucose and L-glutamic acid, it is possible to suppress the propagation of various bacteria in a standard solution and the occurrence of mold. As a result, a decrease in the BOD concentration in the standard solution is suppressed, and accurate BOD measurement can be performed. Furthermore, the frequency of re-preparing the standard solution can be reduced,
It can be applied to long-term continuous measurement.
【0006】[0006]
【発明の実施の形態】以下、本発明をBODバイオセン
サ測定装置を用いた実施例にもとづき説明する。図1は
BODバイオセンサ測定装置の要部構成の一例を示す模
式図である。この測定装置は、容器に貯蔵された測定、
校正、洗浄、緩衝用の5種類の溶液と、送液制御用の電
磁弁、送液ポンプ、エアポンプと、測定系としての微生
物センサ、恒温槽、熱交換器と、制御部、表示部、記録
計とから構成されている。DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the present invention will be described based on an embodiment using a BOD biosensor measuring device. FIG. 1 is a schematic diagram illustrating an example of a main configuration of a BOD biosensor measurement device. This measuring device is a measurement stored in a container,
Five types of solutions for calibration, washing and buffering, solenoid valves for liquid supply control, liquid supply pumps, air pumps, microbial sensors as measurement systems, thermostats, heat exchangers, control units, display units, records It consists of a total.
【0007】図1において、同一組成で濃度の異なる2
種類の校正用標準溶液1A、標準溶液1B、洗浄液2、
検水3、緩衝溶液4をそれぞれの容器に満たしておき、
制御部14のプログラムに従って、標準溶液1A、1
B、洗浄液2、測定検水3、のそれぞれの溶液の流路に
設けた電磁弁5A〜5Dを切り替えて、選択した一種類
の溶液と、緩衝溶液4とを、送液ポンプ6Aおよび6B
を用いて混合し、エアポンプ7からのエアにより送液中
の溶存酸素を飽和させる。[0007] In FIG.
Calibration standard solution 1A, standard solution 1B, cleaning solution 2,
The test sample 3 and the buffer solution 4 are filled in each container,
According to the program of the control unit 14, the standard solutions 1A, 1A
The electromagnetic valves 5A to 5D provided in the flow paths of the solution B, the washing solution 2, and the measurement sample 3 are switched so that the selected one type of solution and the buffer solution 4 are transferred to the solution sending pumps 6A and 6B.
And the dissolved oxygen in the solution is saturated by the air from the air pump 7.
【0008】この時使用する校正用標準溶液1Aと1B
は、JIS K0102の手分析法および日本下水道協
会の下水試験方法で定められたBOD標準溶液であり、
グルコースとL−グルタミン酸の等量混合液である(以
下、従来の標準溶液と記載する)。この標準溶液は微生
物センサ10の検量線の作成に用いられる。また、洗浄
液2は配管系に残った標準溶液1A,1Bや検水3の洗
浄と、微生物センサ10の出力を内生呼吸(餌の無い)
状態に戻すために用い、他の溶液を送液して測定が終了
する都度、洗浄液2を送って配管系を洗浄する。The calibration standard solutions 1A and 1B used at this time
Is a BOD standard solution defined by the manual analysis method of JIS K0102 and the sewage test method of the Japan Sewerage Association,
It is a mixture of equal amounts of glucose and L-glutamic acid (hereinafter referred to as a conventional standard solution). This standard solution is used for preparing a calibration curve of the microorganism sensor 10. Further, the washing liquid 2 is used for washing the standard solutions 1A and 1B and the sample 3 remaining in the piping system and for the endogenous respiration of the output of the microorganism sensor 10 (without food).
It is used to return to the state, and every time the measurement is completed by sending another solution, the washing liquid 2 is sent to wash the piping system.
【0009】微生物センサ10は、微生物を多孔質膜に
固定化した微生物膜12と、溶存酸素電極11およびフ
ローセル13とから成り、測定時の溶液の温度を一定に
する熱交換器9と共に、設定温度に温度制御された恒温
槽8内に組込んである。溶存酸素が飽和状態の溶液は、
エアと共に恒温槽8内の熱交換器9を通過し、設定温度
に保たれた後、微生物センサ10へ送られる。ここで、
多孔質膜に固定化された微生物と溶存酸素電極とによっ
て、送液された溶液中の有機物を資化する際に消費され
る溶存酸素量(呼吸量)に応じた電気信号(電圧または
電流)を出力する。この時、消費される溶存酸素量は測
定溶液中の有機物量と比例するので、あらかじめ2種類
の濃度既知のBOD標準溶液を測定して検量線を作成し
ておき、これに対して測定検水を測定したときの電気出
力信号を、制御部14により比較、演算して測定検水の
BOD濃度を算出し、一連のデータを表示部15に表示
し、また記録部14で印字する。The microorganism sensor 10 includes a microorganism membrane 12 in which microorganisms are immobilized on a porous membrane, a dissolved oxygen electrode 11 and a flow cell 13, and is set together with a heat exchanger 9 for keeping the temperature of the solution at the time of measurement constant. It is incorporated in a thermostat 8 whose temperature is controlled to a temperature. Solutions with saturated dissolved oxygen are:
After passing through the heat exchanger 9 in the thermostat 8 together with the air and being kept at the set temperature, it is sent to the microorganism sensor 10. here,
An electric signal (voltage or current) corresponding to the amount of dissolved oxygen (respiration) consumed when assimilating the organic matter in the solution sent by the microorganism immobilized on the porous membrane and the dissolved oxygen electrode Is output. At this time, the amount of dissolved oxygen consumed is proportional to the amount of organic matter in the measurement solution. Therefore, a calibration curve is prepared by measuring two types of BOD standard solutions having known concentrations in advance, and a measurement sample is prepared. The control unit 14 compares and calculates the electrical output signal obtained when measuring the BOD concentration to calculate the BOD concentration of the measured test water, displays a series of data on the display unit 15, and prints the data on the recording unit 14.
【0010】制御部14のプログラムは次の通りであ
る。最初に微生物センサ10の出力を標準状態にするた
めに、洗浄液2を送り出すように電磁弁5Cを開く。標
準状態になった時や、既に標準状態になっている時に
は、電磁弁5A、5C、5B、5Cがこの順で開いて、
2種類の濃度の標準溶液1A、1Bや洗浄液2を送り、
校正のための測定と洗浄を行う。その後、原点とこの2
種類の校正値を用いて検量線を作成すると共に、データ
を表示部15に表示し、また記録部14で印字する。The program of the control unit 14 is as follows. First, in order to set the output of the microorganism sensor 10 to the standard state, the electromagnetic valve 5C is opened so as to send out the cleaning liquid 2. When it is in the standard state or when it is already in the standard state, the solenoid valves 5A, 5C, 5B and 5C are opened in this order,
Send two types of standard solutions 1A and 1B and cleaning solution 2,
Perform measurement and cleaning for calibration. Then, the origin and this 2
A calibration curve is created using the types of calibration values, the data is displayed on the display unit 15 and printed by the recording unit 14.
【0011】次に検水3を電磁弁5Dを開いて送液し、
濃度未知の検水3のBOD濃度を検量線から演算してデ
ータを表示部15に表示し、また記録部14で印字す
る。設定した回数の検水測定が終わり、センサ出力が標
準状態になった時点で再び校正を開始する。これらのそ
れぞれの測定の間には、必ず洗浄液2を送液して微生物
センサ10の出力を内生呼吸状態に戻している。各バル
ブの開閉時間、および検水の測定回数などの設定は、プ
ログラムの調整で容易に変更することができる。Next, the sample 3 is sent by opening the solenoid valve 5D.
The BOD concentration of the test water 3 whose concentration is unknown is calculated from the calibration curve, and the data is displayed on the display unit 15 and printed by the recording unit 14. Calibration is started again when the set number of water sample measurements has been completed and the sensor output has reached the standard state. During each of these measurements, the washing liquid 2 is always sent to return the output of the microorganism sensor 10 to the endogenous respiration state. Settings such as the opening / closing time of each valve and the number of times of water measurement can be easily changed by adjusting the program.
【0012】以上の構成の装置を用いて、従来のBOD
値33mg/Lの標準溶液を連続して測定した結果を図
2の破線に示す。図2では、本発明の標準溶液との差を
明確にするために初期のセンサ出力で規格化した値とセ
ンサ連続運転日数との関係で示した。破線で示した従来
の標準溶液では、4日目から劣化によるセンサ出力低下
が始まり、9日目で初期のセンサ出力の50%以下に減
少してしまうことがわかる。一方、本発明の1mM−ア
ジ化ナトリウムを添加したBOD33mg/L標準溶液
を適用した場合は、図2の実線で示すように20日以上
経過してもセンサ出力は初期の70%以上を保持してい
る。[0012] Using the apparatus having the above configuration, the conventional BOD
The result of continuously measuring a standard solution having a value of 33 mg / L is shown by a broken line in FIG. FIG. 2 shows the relationship between the value normalized by the initial sensor output and the number of continuous sensor operation days in order to clarify the difference from the standard solution of the present invention. It can be seen that the sensor output of the conventional standard solution indicated by the broken line starts to decrease due to deterioration from the fourth day, and decreases to 50% or less of the initial sensor output on the ninth day. On the other hand, when the BOD 33 mg / L standard solution to which 1 mM sodium azide of the present invention is added is applied, the sensor output retains 70% or more of the initial value even after 20 days or more as shown by the solid line in FIG. ing.
【0013】このような標準溶液の劣化の原因として考
えられるものに、標準溶液中への雑菌の繁殖やかび類の
発生が考えられる。雑菌の繁殖やかび類の発生を抑制す
るものにはアジ化ナトリウム、銅錯塩(ボルドー液)、
サリチル酸、多硫化カルシウムがあるが、本発明者らは
アジ化ナトリウムについてはBODバイオセンサの微生
物膜に用いる微生物である前述のJIS K3602で
既定されている酵母菌トリコスポロン・クタネウムに対
する影響を与えないことを実験により確認している。こ
のため、アジ化ナトリウムがBOD標準溶液の劣化の抑
制に効果があると認められる。Probable causes of such deterioration of the standard solution include propagation of various bacteria and generation of molds in the standard solution. Sodium azide, copper complex (Bordeaux solution),
Although there are salicylic acid and calcium polysulfide, the present inventors have determined that sodium azide has no effect on the yeast Trichosporone ctaneum specified in JIS K3602, which is a microorganism used for the microbial membrane of the BOD biosensor. Has been confirmed by experiments. For this reason, it is recognized that sodium azide is effective in suppressing deterioration of the BOD standard solution.
【0014】[0014]
【発明の効果】BODバイオセンサに用いる従来の標準
溶液は劣化の進行が早く、連続運転を行うためには3日
おき程度の頻繁な試薬交換が必要であり、また、間欠運
転を行う場合でも、測定精度を保つためには標準溶液の
交換が重要な項目となる。しかし、本発明の標準溶液を
適用すれば、標準溶液の劣化が低減されるので、標準溶
液の再調整や、交換の頻度を低減させ、長時間連続的に
安定な測定を実施することができる。According to the present invention, the conventional standard solution used for the BOD biosensor rapidly deteriorates, and requires frequent reagent replacement about every three days for continuous operation, and even when performing intermittent operation. In order to maintain the measurement accuracy, replacement of the standard solution is an important item. However, if the standard solution of the present invention is applied, deterioration of the standard solution is reduced, so that readjustment of the standard solution or the frequency of replacement can be reduced, and stable measurement can be performed continuously for a long time. .
【図1】BODバイオセンサ測定装置の要部構成の一例
を示す模式図FIG. 1 is a schematic diagram showing an example of a main configuration of a BOD biosensor measurement device.
【図2】本発明の標準溶液と従来の標準溶液を適用した
場合のBODバイオセンサ測定装置の出力比較図FIG. 2 is an output comparison diagram of a BOD biosensor measuring device when a standard solution of the present invention and a conventional standard solution are applied.
1A: 校正用標準溶液A 1B: 校正用標準溶液B 2: 洗浄液 3: 検水 4: 緩衝溶液 5A〜5D: 電磁弁 6A〜6B: 送液ポンプ 7: エアポンプ 8: 恒温槽 9: 熱交換器 10: 微生物センサ 11: 溶存酸素電極 12: 微生物膜(酵母菌トリコスポロン・クタ
ネウム) 13: フローセル 14: 制御部 15: 表示部 16: 記録計 17: 排水1A: Calibration standard solution A 1B: Calibration standard solution B 2: Cleaning solution 3: Water sample 4: Buffer solution 5A to 5D: Solenoid valve 6A to 6B: Liquid sending pump 7: Air pump 8: Thermostat 9: Heat exchanger 10: Microbial sensor 11: Dissolved oxygen electrode 12: Microbial membrane (trichosporone ctaneum, yeast) 13: Flow cell 14: Control unit 15: Display unit 16: Recorder 17: Drainage
Claims (3)
定する装置において、校正に使用する標準溶液が、グル
コース・L−グルタミン酸等量混合溶液にアジ化ナトリ
ウムを添加することを特徴とするBODバイオセンサ測
定装置。An apparatus for measuring BOD in water using a biosensor, wherein a standard solution used for calibration is obtained by adding sodium azide to a mixed solution of glucose and L-glutamic acid in equal amounts. Biosensor measurement device.
センサであり、酵母菌トリコスポロン・クタネウムを固
定化した微生物膜と、溶存酸素電極と、フローセルとか
ら成るBODバイオセンサ測定装置。2. The BOD biosensor measuring device according to claim 1, wherein the biosensor is a microbial sensor, and the biosensor comprises a microbial membrane on which the yeast Trichosporone ctaneum is immobilized, a dissolved oxygen electrode, and a flow cell.
液にアジ化ナトリウムを添加することを特徴とするBO
Dバイオセンサ測定装置用標準溶液。3. A BO, wherein sodium azide is added to a mixed solution of equal amounts of glucose and L-glutamic acid.
Standard solution for D biosensor measurement device.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9125235A JPH10318965A (en) | 1997-05-15 | 1997-05-15 | BOD biosensor measuring device and standard solution for the measuring device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9125235A JPH10318965A (en) | 1997-05-15 | 1997-05-15 | BOD biosensor measuring device and standard solution for the measuring device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH10318965A true JPH10318965A (en) | 1998-12-04 |
Family
ID=14905156
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9125235A Withdrawn JPH10318965A (en) | 1997-05-15 | 1997-05-15 | BOD biosensor measuring device and standard solution for the measuring device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH10318965A (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2001004626A1 (en) * | 1999-07-07 | 2001-01-18 | Korea Institute Of Science And Technology | An electrochemical method for enrichment of microorganism, a biosensor for analyzing organic substance and bod |
| KR20030003849A (en) * | 2001-07-04 | 2003-01-14 | 주식회사 에코아이티이십일 | Copper electrode-based electrochemical sensor for measurement of COD and the method of measuring of COD and the automatic analyzer thereof |
| CN103308575A (en) * | 2013-05-27 | 2013-09-18 | 中粮生化能源(龙江)有限公司 | Method for detecting content of glutamic acid by biosensing analyzer and applications of analyzer |
| CN116794131A (en) * | 2023-06-26 | 2023-09-22 | 南开大学 | BOD real-time on-line monitoring device |
-
1997
- 1997-05-15 JP JP9125235A patent/JPH10318965A/en not_active Withdrawn
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2001004626A1 (en) * | 1999-07-07 | 2001-01-18 | Korea Institute Of Science And Technology | An electrochemical method for enrichment of microorganism, a biosensor for analyzing organic substance and bod |
| KR20030003849A (en) * | 2001-07-04 | 2003-01-14 | 주식회사 에코아이티이십일 | Copper electrode-based electrochemical sensor for measurement of COD and the method of measuring of COD and the automatic analyzer thereof |
| CN103308575A (en) * | 2013-05-27 | 2013-09-18 | 中粮生化能源(龙江)有限公司 | Method for detecting content of glutamic acid by biosensing analyzer and applications of analyzer |
| CN116794131A (en) * | 2023-06-26 | 2023-09-22 | 南开大学 | BOD real-time on-line monitoring device |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US4350763A (en) | Method for determining biochemical oxygen demand | |
| CN102288653A (en) | Online biochemical oxygen demand (BOD) detector and detection method of same | |
| Li et al. | Effects of pre-conditioning and microbial composition on the sensing efficacy of a BOD biosensor | |
| JP3664888B2 (en) | BOD biosensor measuring device | |
| US6416652B1 (en) | Method for measuring ammonia in biochemical processes | |
| JP3289522B2 (en) | BOD measuring device | |
| US5518893A (en) | Quick biochemical oxygen demand test and apparatus for the same | |
| JPH10318965A (en) | BOD biosensor measuring device and standard solution for the measuring device | |
| US5017496A (en) | Method for determining the respiration rate of a respiring material in the form of a continuous process current, as well as a device suitable for such an application | |
| CN202083662U (en) | Biochemical Oxygen Demand BOD Online Tester | |
| EP0537210B1 (en) | Continuous rbcod measurement | |
| Harita et al. | BOD quick estimating system utilizing a microbial electrode | |
| WO2006030538A1 (en) | Method of wastewater treatment measurement and wastewater treatment measuring apparatus | |
| AU676362B2 (en) | Quick biochemical oxygen demand test and apparatus for the same | |
| CN120369781B (en) | Lactic acid bacteria pH inhibition method for online biotoxicity detection of water quality and detection device | |
| JPS5999353A (en) | Method and apparatus for measuring bod | |
| JPS5852558A (en) | Ammonia densitometer | |
| CN1130464C (en) | Method and instrument for quickly assaying oxygen requirement of organisms | |
| JP3651501B2 (en) | BOD automatic analysis method and BOD automatic analyzer | |
| JP3572031B2 (en) | BOD measurement method | |
| JP2001228110A (en) | Biosensor-based water quality meter | |
| JPH0735741A (en) | BOD measuring device | |
| JPWO2007020675A1 (en) | BOD measuring method and apparatus | |
| Ben-Hassan et al. | A microcomputer-based oxygen measurement and control system for fermentation processes | |
| CN1290859A (en) | Method and device for on-line monitoring waste water |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20040127 |
|
| A761 | Written withdrawal of application |
Free format text: JAPANESE INTERMEDIATE CODE: A761 Effective date: 20040331 |