CN1243232C - Photochemical and biochemical microorganic membrane dynamic responding sensor for COD with optical fiber - Google Patents
Photochemical and biochemical microorganic membrane dynamic responding sensor for COD with optical fiber Download PDFInfo
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- CN1243232C CN1243232C CN 200410045500 CN200410045500A CN1243232C CN 1243232 C CN1243232 C CN 1243232C CN 200410045500 CN200410045500 CN 200410045500 CN 200410045500 A CN200410045500 A CN 200410045500A CN 1243232 C CN1243232 C CN 1243232C
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Abstract
The present invention discloses a microorganism membrane dynamics response sensor for optical fiber photochemical biochemical oxygen demand (BOD) and relates to a microbial sensor. A sensitive membrane of the microbial sensor is provided with a transparent sheet, an oxygen transduction membrane and a bacterial membrane, wherein the oxygen transduction membrane is arranged on the transparent sheet, and the bacterial membrane is fixed on the oxygen transduction membrane. When the microbial sensor is prepared, the oxygen transduction membrane is prepared on the transparent sheet, and mixed bacteria are fixed on the surface of the oxygen transduction membrane. The microbial sensor is provided with a sample cell, a sensitive membrane, a light emitting diode and an optical fiber, wherein the light emitting diode irradiates on the bacterial membrane, the sample cell is provided with an optical window, and one end of the optical fiber is connected with the optical window. When the BOD value of sea water is measured, GGA standard solution is added in the sea water, the light emitting diode irradiates on the bacterial membrane, and signal after responded enter a photomultiplier tube by the optical fiber. Finally, the signal is converted into a voltage signal by a microphotometer. Compared with a microbial membrane electrode method, the present invention is still more suitable for fast carrying out real-time and online monitoring. The method does not need stirring and is still more suitable for carrying out online monitoring. In addition, the present invention has the advantages of better reproducibility and stability, and short period, namely that the time from once sampling to next sampling is less than 30 minutes. The present invention can fast analyze the BOD of the sea water by selecting single bacterium or mixed bacterium according to different water quality.
Description
Technical field
The present invention relates to a kind of microbiological sensor, especially a kind of fiber optical chemical sensor BOD microbial film dynamic response sensor that can be used in the microbiological sensor that biochemical oxygen demand (BOD) measures.
Background technology
(Biochemical Oxygen Demand BOD) is one of the most frequently used in the water quality assessment process, most important index to biochemical oxygen demand.The 5d biochemical oxygen demand standard dilution metering that widely adopts is the standard method of being formulated in 1936 by American Public Health Association at present.But traditional measuring method not only needs the program of 5 days many complexity such as cultivation, and the accuracy of measuring has much relations with operator's skill level and operation skill, therefore can't realize the real-time and on-line monitoring to environment.In today of environmental analysis high development, a kind of instrument of the BOD of being referred to as microbiological sensor grows up gradually.Its principle, is measured BOD and is only related to initial oxidation speed, thereby can finish the mensuration of a sample in 10～15min organic oxygen consumption metabolism based on microorganism, has shortened the required time of measuring greatly.
The BOD microbiological sensor relate to selection, the bacterium of responsive bacterial classification fixing, secondary sensing, measure the core technologies such as selection of mode.Now domestic existing correlation technique and deficiency thereof are done simple introduction:
The selection of bacterial classification: at present, domestic BOD microbiological sensor mainly selects for use following bacterial classification making sensing membrane: the Deng Jiaqi of Fudan University etc. to select for use unusual Hansenula anomala bacterium, bacillus licheniformis as inoculation bacterium (Deng Jiaqi, Deng, analytical chemistry, 1994,7:647～651), the Du Xiaoyan of Harbin Medical University etc. selects for use skin shape trichosporon cutaneum bacterium and the pseudomonas that separates from active sludge to make different biological membranes (Du Xiaoyan, Deng, Chinese Journal of Preventive Medicine, 2003,37:125～127).Owing to all select single culture for use, therefore be difficult to the different organic substance of various character in the metabolism water sample to be measured.
Fixing of bacterium: at present, the fixing means of the bacterium that domestic report is crossed mainly contains following several: cellulose acetate film sandwich method, sodium alginate to embed method, cross-linking method etc. (Deng Jiaqi, etc., environmental science, 1994,15:8～11; Wang Xiutong, etc., Qingdao College of Architectural Engineering journal, 2003,24:96～98).Because the membrane stability that the cellulose acetate sandwich method is fixed is relatively poor, very easily run off, active higher in a week, active later on rapid decay; In addition, because sodium alginate is soluble in phosphate solution, therefore also be unsuitable for long-term use.The fixing microbial film of sodium alginate to embed method must be dipped in the glycerine, preserves relatively because of difficulty, and swelling and leakage takes place easily when measuring, and is unsuitable for practical application.Have only the fixing membrane stability of cross-linking method better, the life-span can reach 40d, and this moment, its relative activity still kept 90%.
Secondary sensing and assay method: the signal after the mycoderm of BOD microbiological sensor responds in water sample will be converted into discernible signal through the secondary sensing.Existing BOD microbiological sensor is because the difference of secondary sensing can be divided into two kinds: microbial film oxygen electrode method and fiber optical chemical sensor BOD microbial sensitive method.According to the difference of measuring mode, fiber optical chemical sensor BOD microbiological sensor method can be divided into fluorescence intensity stable state difference mensuration (claim not only aeration) and fluorescence intensity rate of change mensuration (but also claiming film dynamic response sensing method).The modal secondary sensing device of report is microbial film oxygen electrode method (Jing Liu et al.Biosensors ﹠amp both at home and abroad at present; Bioelectronic 2000,14:883～893; Gal-Joo Chee et al.AnalyticaChimica Acta 1999,379:185～191; Du Xiaoyan, etc., sensor technology, 1998,17:27～32; An Lichao, etc., Environmental Pollution and Control, 18:32～46; Chen Ning, etc., Chinese environmental monitoring, 2002,18:48～50; Zhang Yue, etc., hi-tech communication, 2001,8:37～39.) etc.
No matter the patent of more existing relevant BOD biology sensor is based on the microbial film electrode method or the fiber optical chemical sensor microbiological sensor method of three-electrode system, what assay method used mostly is traditional aeration.Mensuration will stir in constant speed, carry out under the constant aeration condition, is mainly used in the detection of waste water and sanitary sewage BOD value, fail to embody to greatest extent microbiological sensor in real time, the characteristics of on-line monitoring.
The principle of microorganism oxygen electrode method (assay method is an aeration) is that the sensor of instrument is a microorganism electrode, the microorganism that domestication is good is fixed in the film of making of macromolecular material, constitute microbial film, microbial film is covered on the ventilated membrane of dissolved oxygen electrode, form the microbial film electrode.During measurement, with the standard buffer solution calibration, make oxygen electrode export a base current earlier; Inject water sample to be measured then, aqueous sample stream is behind microbial film, because the degradation of microorganism consumes the dissolved oxygen DO in the water sample, thereby the amount that is diffused into the oxygen on oxygen electrode surface correspondingly reduces, and causes the oxygen electrode output current to reduce.Reach balance through oxygen electrode output current behind the certain hour, at this moment there is quantitative relationship in the organic concentration value in oxygen electrode output current value and the water sample.Measure current value and can calculate the BOD value.Compare with traditional BOD5 short, favorable reproducibility of cycle and the high characteristics of precision are arranged.The detectability of microbial film electrode method can reach 5mg/L, the response time: 2～10min, measuring period: 30min.Its deficiency be (1) for the ease of controlling common use single culture, single culture is to different organic matter degradation ability differences, thereby the response of biology sensor is different with reappearance.Therefore be applicable to the fixedly one-point measurement of water system.(2) response time of microbial film electrode longer, in order to shorten the response time, need select new bacterial classification and immobilization material for use.(3) activity that is fixed on the bacterium in the microbial film progressively reduces, and needs " activation " to handle after each the measurement.And consistance, the interchangeability of microbial film are poor, thereby the automaticity of instrument is not high.
Summary of the invention
The object of the present invention is to provide a kind of fiber optical chemical sensor BOD microbial film dynamic response sensor sensing film and preparation method thereof.
Another object of the present invention is to provide a kind of fiber optical chemical sensor BOD microbial film dynamic response sensor and assay method thereof, to replace conventional microbial film oxygen electrode aeration etc., raising BOD microbiological sensor is real-time, the characteristic of on-line monitoring, and is used for the mensuration of seawater BOD value.
The said fiber optical chemical sensor BOD of the present invention microbial film dynamic response sensor sensing film is made up of slide, the oxygen sensing film and mycoderm, and the oxygen sensing film is located on the slide, and mycoderm is fixed on the oxygen sensing film.Said mycoderm is preferably mixed mycoderm.Slide is selected transparent glass sheet for use.
The preparation method of the said fiber optical chemical sensor BOD of the present invention microbial film dynamic response sensor sensing film is:
1) on slide, adopt the sol-gel investment to prepare the oxygen sensing film;
2) adopt organic modification sol gel-PVA (polyvinyl alcohol (PVA)) investment fixing Mixed Microbes on the oxygen sensing film surface.
Can be with TMOS (tetramethoxy-silicane) and DiMe-DMOS (dimethyldimethoxysil,ne) by volume 1 during the oxygen sensing film in preparation: the proportional quantities of (1.5～2.0) be taken in the open bottles, and adding 0.8～1.2ml0.001g/L is dissolved with [Ru (dpp) 3]
2+THF (tetrahydrofuran) solution of (4,7-diphenyl-1,10 phenanthroline ruthenium), behind vortex vibration 0.8～1.5min, dropwise the pH value of vibration adding 0.01mol/LHCl regulation system is 3～4 again, and 60～80 ℃ of lower open mouth magnetic of bottle are stirred water-bath heating 2～3h.Get above prepared coagulant liquid 50～100 μ L, evenly coat film forming on the glass sheet of ethanol and nitric acid treatment in advance, standby behind dry 12～24h in baking oven.
The preparation of the oxygen sensing film can be taken at TMOS (tetramethoxy-silicane) and 1: 1.8 by volume proportional quantities of DiMe-DMOS (dimethyldimethoxysil,ne) in the open bottles, the THF solution that adds [Ru (dpp) 3] 2+ of an amount of concentration, behind the vortex vibration 1min, dropwise vibrating adds the pH of 0.01mol/L HCl regulation system again, and 60 ℃ of lower open mouth magnetic of bottle are stirred water-bath heating 3h.Get above prepared coagulant liquid 60 μ L, evenly coat film forming on the glass sheet of ethanol and nitric acid treatment in advance, standby behind the dry 12h in baking oven.
The fixing organic modification sol gel-PVA investment that can adopt of bacterium is in the shop, surface of oxygen film system Mixed Microbes, concrete grammar is: by volume 1: (1～1.5) measures TMOS and DiMe-DMOS in open bottles, dropwise add 0.01mol/LHCl when sonic oscillation is even as catalyzer, bottle is stirred water-bath heating 0.5～1.5h at 50～70 ℃ of lower open mouth magnetic, after resulting coagulant liquid is cooled to room temperature, mixed in 1: 1 by volume with 4%～6%PVA aqueous solution, the bacteria suspension that adds 150～250 μ L again, fully vibration evenly, paint even thin layer on the oxygen sensing film surface, room temperature ventilation drying and forming-film.This microbial film thickness is 0.60～0.65mm.Its advantage: adopt the mycoderm good mechanical property of organic modification sol gel-PVA investment shop system, dry back easily is shaped, and thalline is active to keep good, and the response time is short, reaches 1 year serviceable life.
The said fiber optical chemical sensor BOD of the present invention microbial film dynamic response sensor is provided with sample cell, sensitive membrane, light emitting diode and optical fiber, sensitive membrane and light emitting diode place in the sample cell, the exciting light direct irradiation of light emitting diode is on the mycoderm of sensitive membrane, sample cell is provided with optical window, one termination optical window of optical fiber, the external measurement mechanism of the other end of optical fiber.The mycoderm of said sensitive membrane is advisable to mix mycoderm.
The assay method that the said fiber optical chemical sensor BOD of the present invention microbial film dynamic response sensor is used for seawater BOD value is:
1) the sample method at fiber optical chemical sensor BOD microbial film dynamic response sensor is: add GGA solution in the pond;
2) on the mycoderm of light beam direct irradiation in sample cell of light emitting diode, the fluorescence signal that the response back produces enters photomultiplier by fiber optic conduction;
3) current signal by photomultiplier output is converted into voltage signal through the low-light-level measurement instrument, is converted to digital signal by chromatographic work station again, by computer recording, analysis and processing.
Said GGA solution is settled to 100mL for accurately taking by weighing each 0.0750g of analytically pure glucose and glutamic acid with above phosphate buffer solution, join solution be called the BOD value and be the GGA solution of 1000mg/L.
Description of drawings
Fig. 1 is a sensitive membrane front view (FV) of the present invention.
Fig. 2 is a sensitive membrane outboard profile of the present invention.
Fig. 3 is a determinator synoptic diagram of the present invention.
Fig. 4 is a sensing membrane BOD response curve of the present invention.In Fig. 4, horizontal ordinate is time/min (t/min), and ordinate is electric current/millivolt (I/mv).
Fig. 5 is the aerial recovery curve of BOD sensitive membrane of the present invention.In Fig. 5, horizontal ordinate is time/min (t/min), and ordinate is fluorescence intensity (I
F).
Fig. 6 is the first derivation curve of BOD response curve of the present invention.In Fig. 6, horizontal ordinate is time/min (t/min), and ordinate is fluorescence intensity rate of change (dI/dt).
Fig. 7 is the linear response situation of mycoderm of the present invention in 0～30mg/L.In Fig. 7, horizontal ordinate is (C
GGA/ mgL
-1), ordinate is fluorescence intensity rate of change (dI/dt).
Embodiment
Following examples will the present invention is further illustrated in conjunction with the accompanying drawings.
As Fig. 1, shown in 2, fiber optical chemical sensor BOD microbial film dynamic response sensor sensing film is made up of transparent glass sheet 1, the oxygen sensing film 2 and mixed mycoderm 3, and the oxygen sensing film 2 is located on the transparent glass sheet 1, mixes mycoderm 3 and is fixed on the oxygen sensing film 2.
The selection of bacterial classification: existing method is all used single culture shop system mycoderm, and the present invention uses the seawater screening bacterial classification of separating in the seawater, the fresh water acclimatization bacillus of taming repeatedly in seawater etc. to mix the shop system by 1: 1 after cultivating and mixes mycoderm.Its advantage: owing to contain multiple bacterium in the mycoderm, various organic abilities obtain complementation in the metabolism water sample to be measured, can be more thorough, the organism in the metabolism water sample to be measured faster.
The preparation of the oxygen sensing film can be with TMOS (tetramethoxy-silicane) and DiMe-DMOS (dimethyldimethoxysil,ne) by volume 1: the proportional quantities of (1.5～2.0) is taken in the open bottles, the THF solution that adds [Ru (dpp) 3] 2+, behind the vortex vibration 1min, dropwise vibrating adds the pH of 0.01mol/LHCl regulation system again, and 60 ℃ of lower open mouth magnetic of bottle are stirred water-bath heating 3h.Get above prepared coagulant liquid 60 μ L, evenly coat film forming on the glass sheet of ethanol and nitric acid treatment in advance, standby behind the dry 12h in baking oven.
Fixing of bacterium: adopt organic modification sol gel-PVA investment in the shop, surface of oxygen film system Mixed Microbes, concrete grammar is: by volume 1: (1～1.5) measures TMOS and DiMe-DMOS in open bottles, dropwise add 0.01mol/LHCl when sonic oscillation is even as catalyzer, bottle is stirred water-bath heating 0.5～1.5h at 50～70 ℃ of lower open mouth magnetic, after resulting coagulant liquid is cooled to room temperature, with 4%～6%PVA aqueous solution by volume 1: mix (0.8～1.2), the bacteria suspension that adds 150～250 μ L again, fully vibration evenly, paint even thin layer on the oxygen sensing film surface, room temperature ventilation drying and forming-film.This microbial film thickness is 0.60～0.65mm.Its advantage: adopt the mycoderm good mechanical property of organic modification sol gel-PVA investment shop system, dry back easily is shaped, and thalline is active to keep good, and the response time is short, reaches 1 year serviceable life.
Measuring principle: fiber optical chemical sensor BOD microbial film dynamic response sensor device adopts single fiber optic conduction fluorescence signal and stabilized voltage supply 12.Select for use blue LED 4 as on the mycoderm 6 of exciting light (wavelength X max=460nm) direct irradiation in sample cell 5, the fluorescence signal that the response back produces enters photomultiplier 8 by optical fiber 7 conduction.Current signal by photomultiplier 8 outputs is converted into voltage signal through low-light-level measurement instrument 9, is converted to digital signal by chromatographic work station 10 again, by computing machine 11 records, analyzes and handles (referring to Fig. 3).In order to obtain better resolution, experiment utilizes the first order derivative function at data processing work station, and the signal of record is handled, and obtains first order derivative response collection of illustrative plates.Light emitting diode 4 is 90 ° of placements with optical fiber 7 in the system, can effectively eliminate the interference of exciting light like this, to realize high measuring accuracy and accuracy.During measurement, get the experiment mycoderm in sample cell, leave standstill in the air to output one constant digital signal.At this moment, the GGA standard solution that in sample cell, adds 20mL, do not stir, under the condition of not blowing air and measuring flume sealing, dissolved oxygen DO in the mensuration liquid around the mycoderm will promptly be consumed, and dissolved oxygen DO has little time to spread additional in the solution, cause mycoderm to present a kind of state of local anoxic on every side, the fluorescence intensity level that shows as the oxygen film through oxygen sensing film secondary sensing raises gradually.The size of this fluorescence intensity rate of change changes with the difference of organic concentration in the measuring cell, in certain BOD concentration range, exists certain linear between the two.
Do not containing under the organic condition, the bacterium endogenous respiration reaches passive steady state (SS) in the mycoderm, and promptly the oligopnea state is put in detection cell with the sensitive membrane for preparing, after pouring the GGA standard solution of 20mL into, do not stirring, detecting under the condition of not blowing air and detection cell sealing.The dissolved oxygen DO that measure around the sensing membrane in the liquid this moment will be consumed rapidly, and dissolved oxygen DO has little time diffusion and replenishes in the solution, causes presenting local anaerobic condition around the mycoderm, and the fluorescence intensity level that oxygen sensing film secondary sensing is shown as the oxygen film raises gradually.Its process mainly is divided into three phases (referring to Fig. 4): the initial stage (a) bacterium be in induction period (inertia phase), it is less that fluorescence intensity signals changes, mid-term, (b) bacterium entered positive breathing state, a large number of nutrients is absorbed decomposition, O
2Content descends rapidly thereupon, and fluorescence intensity signals increases sharply.Present local anaerobic condition around later stage (c) mycoderm, bacterium enters the endogenous stationary phase of suppressing breathing once more in the film, and this moment, fluorescence signal increased slowly, and curve enters the commentaries on classics flat spot gradually.The BOD response curve as shown in Figure 4, experiment condition: T:25 ℃; PH:7.0; NaCl%:3.5%; GGA concentration: 10mg/L.
The selection of sensing membrane response reset mode: after the fluorescence intensity level of sensitive membrane rises to maximal value and finishes the mensuration of a BOD value, sensitive membrane must be returned to and measure preceding initial conditions, carry out the mensuration of another BOD value again.The air restoring method is exactly after test finishes the water sample in the measuring cell to be got rid of, make sensitive membrane exposed to air a period of time, make sensitive membrane return to a kind of method (referring to Fig. 5) of original state with airborne oxygen, whole process is divided into three phases, the a stage is responsive to measuring the response curve of liquid, and its response speed arrives from slow to fast again and keeps balance; The b stage represent responsive get rid of measure liquid, open Chi Gai after aerial recovery curve, the fluorescence signal of sensitive membrane descends rapidly until a stationary value, a stage and the signal of b between the stage increase suddenly to opening the pond and cover that extraneous light intensity causes; The c stage is sensitive membrane fluorescence intensity change curve after adding blank solution again in the measuring flume and covering Chi Gai, and after extraneous influence of light disappeared, the fluorescence signal intensity of sensitive membrane returned to the original state before measuring.Experimental results show that the air restoring method can be used for the recovering state of sensitive membrane.In usually measuring, after a BOD pH-value determination pH finishes, only need pour out mensuration liquid, with sensitive membrane be exposed to treat in the air fluorescence intensity level return to stable after, can add and measure the mensuration that liquid carries out another BOD value.Experiment condition: T, 30 ℃; PH, 7.2; NaCl%, 3.2%; GGA concentration, 10mg/L.
The BOD response curve is behind first derivation, one maximal value (referring to Fig. 6) appears in fluorescence intensity rate of change (dIF/dt), the size of this fluorescence intensity rate of change, difference with organic concentration in the measuring cell changes, in certain BOD concentration range, exist certain linear (referring to Fig. 7) between the two.Experiment condition: T, 35 ℃; PH, 7.2; NaCl%, 3.2%; GGA concentration, 0～30mg/L.
This shows that advantage of the present invention is that (1) fiber optical chemical sensor BOD microbial film dynamic response sensing method compares microorganism The membrane electrode method is more suitable in real time, quick, on-line monitoring; (2) owing to need not in the testing process to stir, more be adapted to online prison Survey; (3) favorable reproducibility, good stability, the cycle is short, and the time from single injected sampling to next sample introduction is less than 30min; (4) can According to different choice list-bacterial classification or the mixed bacterium of water quality, can carry out fast B OD to seawater and analyze.
Claims (5)
1, fiber optical chemical sensor biological oxygen demand microbe film dynamic response sensor sensing film, it is characterized in that being made up of slide, the oxygen sensing film and mycoderm, the oxygen sensing film is located on the slide, and mycoderm is fixed on the oxygen sensing film, said mycoderm is for mixing mycoderm, and slide is selected transparent glass sheet for use.
2, the preparation method of fiber optical chemical sensor biological oxygen demand microbe film dynamic response sensor sensing film as claimed in claim 1 is characterized in that the steps include:
1) on slide, adopts the sol-gel investment to prepare the oxygen sensing film, the proportional quantities of tetramethoxy-silicane and dimethyldimethoxysil,ne 1: 1.5 by volume～2.0 is taken in the open bottles, add 0.8～1.2ml 0.001g/L and be dissolved with [Ru (dpp) 3]
2+Tetrahydrofuran solution, behind vortex vibration 0.8～1.5min, dropwise the vibration pH value that adds 0.01mol/L HCl regulation system is 3～4 again, 60～80 ℃ of lower open mouth magnetic of bottle is stirred water-bath heat 2～3h; Get above prepared coagulant liquid 50～100 μ L, evenly coat film forming on the glass sheet of ethanol and nitric acid treatment in advance, standby behind dry 12～24h in baking oven;
2) adopt organic modification sol gel-PVA investment fixing Mixed Microbes on the oxygen sensing film surface.
3, the preparation method of fiber optical chemical sensor biological oxygen demand microbe film dynamic response sensor sensing film as claimed in claim 2, the preparation that it is characterized in that the oxygen sensing film can be taken at tetramethoxy-silicane and 1: 1.8 by volume proportional quantities of dimethyldimethoxysil,ne in the open bottles, adds [Ru (dpp) 3] of an amount of concentration
2+Tetrahydrofuran solution, behind the vortex vibration 1min, dropwise vibrate again and add the pH of 0.01mol/L HCl regulation system, 60 ℃ of lower open mouth magnetic of bottle are stirred water-bath heating 3h, get above prepared coagulant liquid 60 μ L, evenly coat film forming on the glass sheet of ethanol and nitric acid treatment in advance, standby behind the dry 12h in baking oven.
4, the preparation method of fiber optical chemical sensor biological oxygen demand microbe film dynamic response sensor sensing film as claimed in claim 2, it is characterized in that fixing 1: 1 by volume～1.5 of bacterium measures tetramethoxy-silicane and dimethyldimethoxysil,ne in open bottles, dropwise add 0.01mol/LHCl when sonic oscillation is even as catalyzer, bottle is stirred water-bath heating 0.5～1.5h at 50～70 ℃ of lower open mouth magnetic, after resulting coagulant liquid is cooled to room temperature, mixed in 1: 1 by volume with 4%～6%PVA aqueous solution, the bacteria suspension that adds 150～250 μ L again, fully vibration evenly, paint even thin layer on the oxygen sensing film surface, room temperature ventilation drying and forming-film.
5, fiber optical chemical sensor biological oxygen demand microbe film dynamic response sensor, it is characterized in that being provided with sample cell, sensitive membrane, light emitting diode and optical fiber, sensitive membrane and light emitting diode place in the sample cell, the exciting light direct irradiation of light emitting diode is on the mycoderm of sensitive membrane, sample cell is provided with optical window, one termination optical window of optical fiber, the external measurement mechanism of the other end of optical fiber, the mycoderm of said sensitive membrane is for mixing mycoderm.
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| CN100441695C (en) * | 2005-12-16 | 2008-12-10 | 厦门大学 | Biological oxygen demand microbe sensor sensitive membrane activating process and automatic activating apparatus |
| CN101285774B (en) * | 2008-05-27 | 2010-06-09 | 厦门大学 | Visualized oxygen sensing detection biosensor preparation method |
| CN100593688C (en) * | 2008-10-20 | 2010-03-10 | 重庆工学院 | Method for on-line measuring microbiological film thickness by fiber prague grating sensor |
| CN102650597B (en) * | 2012-04-28 | 2015-08-05 | 浙江工业大学 | A kind of the oxygen sensing film based on Fluorescence Quenching Principle |
| CN110849858A (en) * | 2019-12-09 | 2020-02-28 | 天津大学 | Dissolved oxygen sensitive film light sensing device and fluorescence efficiency detection system |
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