WO1999010739A1 - Instrument de mesure de l'activite de methanation - Google Patents
Instrument de mesure de l'activite de methanation Download PDFInfo
- Publication number
- WO1999010739A1 WO1999010739A1 PCT/JP1998/003768 JP9803768W WO9910739A1 WO 1999010739 A1 WO1999010739 A1 WO 1999010739A1 JP 9803768 W JP9803768 W JP 9803768W WO 9910739 A1 WO9910739 A1 WO 9910739A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- gvss
- amount
- sludge
- production activity
- methane production
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M21/00—Bioreactors or fermenters specially adapted for specific uses
- C12M21/04—Bioreactors or fermenters specially adapted for specific uses for producing gas, e.g. biogas
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
- C12M41/00—Means for regulation, monitoring, measurement or control, e.g. flow regulation
- C12M41/30—Means for regulation, monitoring, measurement or control, e.g. flow regulation of concentration
- C12M41/36—Means for regulation, monitoring, measurement or control, e.g. flow regulation of concentration of biomass, e.g. colony counters or by turbidity measurements
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
- G01N33/18—Water
- G01N33/186—Water using one or more living organisms, e.g. a fish
- G01N33/1866—Water using one or more living organisms, e.g. a fish using microorganisms
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Definitions
- the present invention relates to an apparatus for measuring methane production activity of granular sludge used in an anaerobic wastewater treatment method.
- a conventionally known measuring device for the methane generation activity of sludge As a conventionally known measuring device for the methane generation activity of sludge, a method called “water replacement method” described in a published publication “Water and Wastewater Vol. 37 No. 7 (1995)” is used. Some of these are shown in Figures 12 and 13 and will be explained.
- a plurality of narrow-mouthed bottles 62 to which a gas conduit 61 is detachably mounted are left standing in water in a constant temperature water tank 63, and a stirring member 66 and a heater 67 are mounted in the constant temperature water tank 63, and The distal end of the conduit 61 is inserted into a cleansing bottle 68 filled with 1 N, Na , H.
- the cleansing bottle 68 and the gas holder 69 are connected by the gas conduit 61, and the scale 72 is attached to the gas holder 69. Have been.
- the measurement of sludge methane generation activity does not take into account the gas phase replacement and requires a long time to increase the anaerobicity of the device. It takes a long time of 44 hours from the start to the end, during which time the operator has to be close to the measuring device and continuously monitor the instrument, which requires a great deal of effort, and the measured value of the scale is Because of the visual inspection, the readings tend to be inaccurate, care must be taken to keep the reaction bottles still, and When measuring low sludge, the NaOH aqueous solution may flow back from the gas holder into the narrow-mouthed bottle, and the methane production activity must be calculated manually by the operator. There are various problems such as the inability to calculate quickly and the inability to determine the quality of the methane production activity.
- the present invention solves the above-mentioned problems of the conventional methane production activity measuring device, and requires only a short time to increase the anaerobicity of the device.
- the process can be completed, and the instrument itself can automatically record the measurement results. During this time, the operator does not need to continuously monitor the instruments by the side of the measuring device. In addition to not requiring a burden, accurate measurement results can be obtained, and there is no need to pay attention to keeping the reaction vessel stationary.
- the Na 0 H aqueous solution does not flow back to the reaction vessel, and the methane production activity does not need to be calculated manually by the operator. It is an object of the present invention to provide a methane generation activity measuring device that can easily calculate the methane generation activity value quickly and can determine the quality of the methane generation activity value.
- the invention according to claim 1 includes a measuring unit and a recording unit for measuring methane production activity of sludge or soil in anaerobic wastewater treatment.
- a pressure vessel having a lid detachably mounted, a carbon dioxide absorption vessel detachably accommodated in the pressure vessel, and a detachably accommodated pressure vessel
- the lid is equipped with a pressure-electric conversion type pressure sensor connected to a recorder, and a support member for supporting the carbon dioxide gas absorbing container is provided on the outer bottom surface of the carbon dioxide gas absorbing container.
- a gas generating pipe for ventilation that penetrates the internal bottom face is attached to the inner bottom face, and a vent pipe with a gas-phase replacement valve is attached to the lid of the pressure vessel, respectively.
- Pressure A magnetic stirrer is attached to the bottom inside the container.
- the time required to increase the anaerobicity of the apparatus is short, and the entire measurement process can be completed in a short time from the collection of sludge, and the apparatus itself can automatically record the measurement results During this time, the operator does not need to continuously monitor the instrument by the measuring device, so that the operator is not burdened and can obtain accurate measurement results. No need to pay attention to keeping the application vessel stationary, and when measuring sludge with low methane generation activity, the Na0H aqueous solution flows back to the reaction vessel. There is an effect that there is no such thing as.
- the invention according to claims 3 to 8 is characterized in that, as the recording means, the methane production activity amount per day ( g C0D / gVSS) is obtained from the pressure information detected by the pressure-electric conversion type pressure sensor in the measuring means. / d), and a display unit for displaying the calculated value processed by the calculation processing unit, and the calculation processing unit is configured to perform the calculation based on the pressure signal from the pressure sensor in the measurement unit.
- a unit that can measure the pressure change during a predetermined judgment time, convert the gradient of the pressure change into the time change of the gas generation amount, and express it as a load corresponding to the amount of methane gas per hour X [ml] [gC0D / h And the converted amount of methane gas X [gCOD / h] is divided by the total amount of sludge used for measurement [gVSS] to calculate the amount of methane gas per day per unit of sludge per unit Methane production activity per day ( g C0D / gVSS / d], and an A / D converter that converts the pressure signal from the pressure sensor in the measuring means to a digital signal as a calculation processing unit, and manually sets the judgment time to time the judgment time.
- a judgment time counter for displaying the judgment time numerically, a gVSS counter for manually setting the gVSS amount of the sludge, and a numerical display of the gVSS amount of the sludge, and a pressure signal from the A / D converter and the judgment time counter
- a control unit for controlling the calculation of the methane production activity per day [gC0D / gVSS / d] based on the data of the determination time of the sludge and the gVSS amount of the sludge from the gVSS counter, respectively.
- a keyboard for inputting and setting the judgment time and the amount of sludge gVSS, and the judgment time and the amount of sludge gVSS input from the keyboard are displayed on a screen.
- the display unit, the calculation processing unit A plurality of lamps that compare the calculated value of methane production activity [gC0D / gVSS / d] with a judgment criterion and illuminate the quality of this comparison step by step to display the results.
- This is a screen display device that compares the value of the amount of methane generation activity [gCOD / gVSS / d] calculated by the above with a criterion and displays the quality on a screen.
- the determination means in the methane production activity measuring device automatically calculates the daily methane production activity [gC0D / gVSS / d] from the pressure information detected by the pressure-electric conversion type pressure sensor in the measurement means.
- the calculated amount is displayed. That is, a pressure change at a predetermined judgment time is measured based on a pressure signal from the pressure sensor, and a gradient of the pressure change is converted into a time change of the gas generation amount. Then, it is converted into a unit [gC0D / h] that can be expressed as a load corresponding to the amount of methane gas X [ml] per hour.
- the converted amount of methane gas X [gCOD / h] is divided by the total amount of sludge used for measurement [gVSS] to calculate the amount of methane gas per day in the amount of sludge per unit, and the amount of methane generated per day Since the amount of activity [gCOD / gVSS / d] is calculated, it is not necessary to calculate the methane production activity manually, and it is possible to calculate it easily and quickly. There is an effect that the judgment can be made.
- FIG. 1 is a partially cutaway front view of the first embodiment of the present invention
- Fig. 2 is a longitudinal sectional front view of the carbon dioxide absorption container of the above
- Fig. 3 is an operation flow diagram of the same
- Fig. 4 is a method of measuring sludge of the same.
- FIG. 5 is an explanatory diagram showing an initial state of the embodiment
- FIG. 5 is an explanatory diagram showing a middle stage of the embodiment of the method for measuring sludge
- FIG. 6 is a diagram showing a method for measuring the sludge.
- FIG. 7 is a front view of a second embodiment of the present invention
- FIG. 8 is a block diagram showing the configuration of an automatic determination means
- FIG. 9 is a front view of the external appearance of FIG. 0 is an operation flow diagram of the above
- FIG. 11 is an operation timing diagram of the above
- FIG. 12 is a slope view of a conventional example of the same type as the present invention
- FIG. 13 is an operation flow diagram of the above.
- the first embodiment of the present invention shown in FIGS. 1 and 2 has a measuring means 1 and a recording means 2, wherein the measuring means 1 comprises a pressure vessel 4 to which a lid 3 is detachably mounted, and a pressure vessel 4 It has a carbon dioxide gas absorbing container 6 detachably housed therein and a thermostatic water tank 7 with a stirrer and a pressure vessel 4 detachably housed therein, and a lid 3 has a pressure electricity connected to the recording means 2.
- a conversion type pressure sensor 8 is connected to a pair of gas phase replacement valves 9, 10, and ventilation pipes 11, 12 with a gas exchange valve. Is installed.
- a plurality of support pipes 14 for supporting the carbon dioxide absorption container 6 are mounted on the outer bottom surface of the carbon dioxide absorption container 6, and a generated gas pipe 16 for ventilating through the inner bottom surface is mounted at the center of the inner bottom surface. ing. Magnetic stirrer in water bath 7
- a stirrer switch 17 for operating an actuator (not shown) for operating 13 is provided.
- both the gas phase replacement valves 9 and 10 are closed, the pressure vessel 4 is immersed in the constant temperature water tank 7 at 35 ° C, the stirrer switch 17 is turned on, and the magnetic stirrer 13 is operated to turn on the pressure.
- the sludge and the reaction solution inside the container 4 are stirred, and the temperature inside the pressure container 4 becomes constant temperature in about 3 minutes.
- the measurer turns on the switch of the recording means 2 and inputs the pressure detected by the pressure-electrical conversion type pressure sensor 8 to the recorder 5 for 4 hours, for example, to finish the measurement.
- the amount of methanogenic activity (gC0D / gVSS / d) per day was calculated over 24 hours, and all measurement steps were completed.
- the time required for the entire process is about 28 hours and 34 minutes.
- the pressure information detected by the pressure-electric conversion type pressure sensor 8 disposed between the pressure vessel 4 and the recording means 2 is recorded by the recording means 2
- This information can be collected automatically without any operation by the measurer, and the measurement results are good. In this way, not only can the measurer's effort be significantly reduced, but also accurate measurement information can be obtained.
- Solution B 2.5% aqueous sodium sulfide solution, which is used to make the reaction solution anaerobic,
- Solution C 2.5% aqueous solution of stin hydrochloride used to make the reaction solution anaerobic
- the calculation procedure of the methane production activity amount [gC0D / gVSS / d] in the above case is as follows.
- the measuring means 1 is provided with a heating switch 18.
- the automatic judging means 20 is a judging means main body.
- the determination means main body 21 includes an amplifier 22 for amplifying the pressure signal output from the pressure sensor 8 as shown in FIG. 8, and converts the amplified pressure signal from the amplifier 22 into a digital signal.
- the control unit 26 performs control to calculate the daily methane production amount [gC0D / gVSS / d] based on the respective data of the determination time and the gVSS amount of the sludge from the gVSS counter.
- the judgment means main body 21 has a D / A converter 27 for converting the data from the control section 26 into a recorder 5 hair analog signal and sending it out, manually setting the judgment time in the control section 26, and A judgment time counter 33 that measures the judgment time and displays the numerical value of the judgment time is provided, and a gVSS counter 34 that manually sets the gVSS amount of the sludge in the control unit 26 and displays the numerical value of the gVSS amount of the sludge is provided.
- the judgment means main body 21 has a DPM (corresponding to a digital panel meter, a digital display, and a screen display device in claims) for displaying the measured methane production activity value, etc. 43, and illuminates the operation state of the measurement.
- DPM corresponding to a digital panel meter, a digital display, and a screen display device in claims
- a power supply switch 32 to be turned on and off, and a power supply unit 45 for supplying a direct current to each part of the judgment means main body 21 are provided.
- various instruction switches (not shown) are provided. This instruction switch indicates, for example, a lamp test. And a reset switch for instructing completion of measurement and performing the next measurement.
- the lamps 30a to 30e indicate the operation status as shown in Fig. 9.
- the power lamp 30a lights up when the power is turned on, the failure display lamp 30b lights up and displays a fault, and the measurement is in progress.
- Means 2 1) In-measurement indicator lamp 30c, which lights up during operation to display the status, completion indicator lamp 30d, which lights up and displays the measurement completion, and lamp test which lights up and displays whether or not each lamp is normal It is composed of a display lamp 30 e.
- the lamps 40a to 40e compare the judgment contents of the methane generation activity value measured as shown in Fig. 9 with the judgment criteria set in the control unit 26 in advance, and illuminate the quality of the judgment in five steps.
- This 5-level display lamp lights up "HH extremely good” HH display lamp 40a, lights up “MH : Slightly good” MH display lamp 40b lights up and displays ML: Lights up “ML: Slightly bad” ML display Lamp 40 c, illuminates and displays “L : defective” L indicator lamp 40 d, illuminates and displays “LL: extremely poor” c Consists of LL indicator lamp 40 e, judgment time counter 33, gVSS counter 34 Uses a counter that sets the rotation from the panel surface, but other configurations may be used.
- a keyboard for inputting the judgment time and sludge gVSS amount for inputting the judgment time and sludge gVSS amount, a screen display for displaying the judgment time and sludge gVSS amount input from the keyboard, and a judgment input from the keyboard
- a timer for measuring the time a memory for storing the determination time and the gVSS amount of the sludge, and a memory for reading and storing the stored data by the control unit may be used.
- the power supply 45 When the power switch 32 is turned on, the power supply 45 The section is energized and automatic measurement of the methane production activity of the granular sludge is started.
- the pressure signal from the pressure sensor 8 is amplified by the amplifier 22, the amplified pressure signal is converted into a digital signal by the AZD converter 23, and transmitted to the control unit 26.
- the judgment time is set in the control unit 26 by the manual operation of the judgment time counter 33, and the judgment time is counted and the judgment time is displayed by a numeral.
- the gVSS amount of the sludge is set in the control unit 26 by manual operation of the gVSS counter 34, and the gVSS amount of the sludge is numerically displayed.
- control unit 26 executes the methane generation activity per day by the flow and operation timing shown in FIGS. Control to calculate the amount [gC0D / gVSS / d].
- the calculated amount of methane production activity [gC0D / gVSS / d] is converted into an analog signal by the D / A converter 27 and sent to the recorder 5, where the writing is performed on the recording paper with a pen or the like.
- the control unit 26 sets the lamp 30 (power lamp 30a, failure indicator lamp 30b, Control to individually turn on the display lamp 30c, the completion display lamp 30d, and the lamp test display lamp 30e).
- control unit 26 compares the control for displaying the measured methane generation activity value with the DP M43 and the content of the determination of the measured methane generation activity value with a determination criterion set in the control unit 26 in advance.
- the contents of the pass / fail status will be described in five steps using the lamp 40 (HH indicator lamp 40a, MH indicator lamp 40b, ML indicator lamp 40c, L The indicator lamp 40d and the LL indicator lamp 40e) are lit.
- the measurer operates the judgment time counter 33 to set a judgment time (here, 4 hours) in the control unit 26 as shown in FIG. 11 (b). Is displayed.
- the measurer operates the gVSS counter 34 to input the gVSS amount of the sludge, and this amount is displayed on the gVSS counter 34.
- ⁇ P 2 is the pressure that is changed to between the time of determination after lapse operation ignore time
- V is Sorasunryou
- T the actual determination time (4 hours)
- T 4 the calculation ignores time (1 hour)
- gCOD the methanogenic activity (slope)
- GVSS is weight sludge.
- the operation ignoring time (T 4 ), for example, 1 hour is set.
- the calculation time ( 3 ) of the control unit 26 is set to be 0.2 hours (12 minutes) here.
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Description
Claims
Priority Applications (6)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
EP98938980A EP1008850B1 (en) | 1997-08-27 | 1998-08-25 | Methanation activity measuring instrument |
CA 2301824 CA2301824C (en) | 1997-08-27 | 1998-08-25 | Specific methanogenic activity measuring apparatus |
DE1998633766 DE69833766T2 (de) | 1997-08-27 | 1998-08-25 | Vorrichtung zum messen der methanisierungsaktivität |
AU87507/98A AU738448B2 (en) | 1997-08-27 | 1998-08-25 | Specific methanogenic activity measuring apparatus |
US09/485,953 US6416994B1 (en) | 1997-08-27 | 1998-08-25 | Methanation activity measuring instrument |
HK01102167A HK1031425A1 (en) | 1997-08-27 | 2001-03-26 | Methanation activity measuring instrument. |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9/231162 | 1997-08-27 | ||
JP23116297A JP3071405B2 (ja) | 1996-12-13 | 1997-08-27 | メタン生成活性測定装置 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO1999010739A1 true WO1999010739A1 (fr) | 1999-03-04 |
Family
ID=16919287
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/JP1998/003768 WO1999010739A1 (fr) | 1997-08-27 | 1998-08-25 | Instrument de mesure de l'activite de methanation |
Country Status (8)
Country | Link |
---|---|
US (1) | US6416994B1 (ja) |
EP (1) | EP1008850B1 (ja) |
CN (1) | CN1185489C (ja) |
AU (1) | AU738448B2 (ja) |
CA (1) | CA2301824C (ja) |
DE (1) | DE69833766T2 (ja) |
HK (1) | HK1031425A1 (ja) |
WO (1) | WO1999010739A1 (ja) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP2301573A1 (en) | 2002-10-01 | 2011-03-30 | Novartis Vaccines and Diagnostics, Inc. | Anti-cancer and anti-infectious disease compositions and methods for using same |
Families Citing this family (8)
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US20040261496A1 (en) * | 2003-04-18 | 2004-12-30 | Vickery Thomas P. | Method of evaluating safety of liquids for drum storage |
CN102787067B (zh) * | 2012-08-10 | 2014-04-30 | 中国科学院亚热带农业生态研究所 | 一种体外厌氧发酵温室气体实时检测装置及检测方法 |
CN104880540A (zh) * | 2015-06-11 | 2015-09-02 | 农业部环境保护科研监测所 | 一种测定有机固体废弃物生化产甲烷潜力的装置和方法 |
CN105136607A (zh) * | 2015-08-14 | 2015-12-09 | 中国科学院重庆绿色智能技术研究院 | 基于生物气检测的生物活性检测装置及方法 |
CN109266534B (zh) * | 2018-08-28 | 2022-04-22 | 暨南大学 | 一种用于测定生物膜呼吸速率的呼吸瓶、测定装置及测定方法 |
CN111320265A (zh) * | 2018-12-17 | 2020-06-23 | 中国石油化工股份有限公司 | 一种厌氧氨氧化污泥活性评价方法及应用 |
BR112021022594A2 (pt) * | 2019-06-17 | 2022-01-04 | Halliburton Energy Services Inc | Ferramenta de amostragem de fluido para amostra de fluido de uma formação subterrânea, método para amostrar fluidos de formação e sistema de teste para medição de componente |
CN110668565B (zh) * | 2019-09-11 | 2022-03-15 | 青岛理工大学 | 一种用于厌氧反应器的卷管式污泥取样与活性测评装置及其工作方法 |
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JPH01312999A (ja) * | 1988-05-06 | 1989-12-18 | John R Waters | 細菌の活性を検出する方法および装置 |
JPH08242887A (ja) * | 1995-03-15 | 1996-09-24 | Meidensha Corp | 酢酸資化性メタン生成菌濃度測定方法及び装置 |
JPH08285837A (ja) * | 1995-04-17 | 1996-11-01 | Kurita Water Ind Ltd | 汚泥活性度計測装置 |
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IT1269200B (it) * | 1994-01-28 | 1997-03-21 | Eniricerche Spa | Determinazione della tossicita' delle acque mediante l'uso di una coltura batterica anaerobica |
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JPH09242887A (ja) * | 1996-03-01 | 1997-09-16 | Yoshiya Okazaki | 定流量弁装置 |
DE19734154A1 (de) * | 1997-08-07 | 1999-02-25 | Umweltanalytik Und Forschungs | Verfahren und Vorrichtung zur getrennten oder kombinierten Erfassung des aeroben und anaeroben Abbaues von industriellen und kommunalen Abwässern |
-
1998
- 1998-08-25 DE DE1998633766 patent/DE69833766T2/de not_active Expired - Fee Related
- 1998-08-25 CA CA 2301824 patent/CA2301824C/en not_active Expired - Fee Related
- 1998-08-25 AU AU87507/98A patent/AU738448B2/en not_active Ceased
- 1998-08-25 CN CNB988085445A patent/CN1185489C/zh not_active Expired - Fee Related
- 1998-08-25 EP EP98938980A patent/EP1008850B1/en not_active Expired - Lifetime
- 1998-08-25 US US09/485,953 patent/US6416994B1/en not_active Expired - Fee Related
- 1998-08-25 WO PCT/JP1998/003768 patent/WO1999010739A1/ja active IP Right Grant
-
2001
- 2001-03-26 HK HK01102167A patent/HK1031425A1/xx not_active IP Right Cessation
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JPH01312999A (ja) * | 1988-05-06 | 1989-12-18 | John R Waters | 細菌の活性を検出する方法および装置 |
JPH08242887A (ja) * | 1995-03-15 | 1996-09-24 | Meidensha Corp | 酢酸資化性メタン生成菌濃度測定方法及び装置 |
JPH08285837A (ja) * | 1995-04-17 | 1996-11-01 | Kurita Water Ind Ltd | 汚泥活性度計測装置 |
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Title |
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See also references of EP1008850A4 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP2301573A1 (en) | 2002-10-01 | 2011-03-30 | Novartis Vaccines and Diagnostics, Inc. | Anti-cancer and anti-infectious disease compositions and methods for using same |
Also Published As
Publication number | Publication date |
---|---|
AU8750798A (en) | 1999-03-16 |
DE69833766T2 (de) | 2006-11-23 |
DE69833766D1 (de) | 2006-05-04 |
EP1008850B1 (en) | 2006-03-08 |
AU738448B2 (en) | 2001-09-20 |
CN1268223A (zh) | 2000-09-27 |
CA2301824C (en) | 2008-07-08 |
CA2301824A1 (en) | 1999-03-04 |
EP1008850A4 (en) | 2004-04-28 |
US6416994B1 (en) | 2002-07-09 |
EP1008850A1 (en) | 2000-06-14 |
CN1185489C (zh) | 2005-01-19 |
HK1031425A1 (en) | 2001-06-15 |
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