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Water quality toxicity biosensor microorganism electrode preparation method

A biosensor, microbial electrode technology, applied in biochemical equipment and methods, microbial determination/inspection, instruments, etc., can solve the problem of inability to objectively reflect the true toxic effects of pollutants, poor sensitivity and repeatability of toxicity analysis, and bacterial flora composition. Large structural differences and other problems, to achieve the effect of true toxicity analysis results, reduce instrument analysis costs, and achieve the effect of repeated use

Inactive Publication Date: 2008-09-10
TONGJI UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

At present, in the research of CellSense biosensor, single strains such as Escherichia coli (E.coli), Pseudomonas putida (Pseudomonas putida), Vibrio fischeri (V.fischeri), or mixed strains such as activated sludge have been used. (Activated sludge) as the research report of the tested microorganisms (Marinella et al. : 41-54; Wang et al. Chinese Chemical Letters 2008, 19: 211-214), but in actual water quality toxicity analysis, because wastewater is often a complex pollution system in which multiple pollutants coexist, and different types of microorganisms Therefore, the CellSense biosensor based on a single strain has the disadvantages of poor sensitivity and reproducibility of toxicity analysis
At the same time, from the perspective of environmental pollution ecotoxicology, the toxicity evaluation based on a single strain has the limitation that it cannot objectively reflect the true toxic effect of pollutants
The CellSense biosensor using activated sludge as the tested microorganism has the characteristics of wide detection range of pollutants and true toxicity analysis results, but due to the large differences in the composition and structure of the bacterial flora of different activated sludge, it has caused differences among laboratories. The toxicity test results are difficult to compare with each other. The above problems greatly limit the development of this type of microbial sensor
[0005] The microbial electrodes currently used by CellSense biosensors are prepared by pre-printing adhesives around the working area of ​​the carbon electrodes and pasting polycarbonate membranes to directly cover and fix the tested microorganisms. The microbial electrodes prepared by this method are disposable. The electrode is discarded after completing a water toxicity analysis, which leads to high analysis costs and affects its promotion and application
[0006] Therefore, in order to improve the performance of CellSense biosensor toxicity analysis and reduce the cost of analysis, the development and immobilization of test microorganisms need further research

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0017] Take 50 parts of freeze-dried Escherichia coli (E.coli), 20 parts of yeast (yeast) and 40 parts of Nitrosomonas sp., and carry out strain mixing and compounding; take 0.6g of compounded mixed bacteria Add 250 μL of 0.85% sodium chloride solution to the solution, and stir the wet bacteria with a sterilized toothpick; paste double-sided tape around the working area of ​​the carbon electrode of the cleaned CellSense biosensor, and use a pipette to draw 7 μL of the mixed bacteria solution to apply In the working area of ​​the CellSense carbon electrode, air it in the dark at room temperature for 1 hour, then cover the polycarbonate film on the mixed bacteria, and seal and fix the bacteria in the working area of ​​the carbon electrode with double-sided adhesive tape to obtain a microbial electrode. The prepared microbial electrode was placed in a refrigerator at 4°C for 48 hours before use.

[0018] Adopt the above-mentioned CellSense biosensor based on the microbial electro...

Embodiment 2

[0020] Take 80 parts of freeze-dried Escherichia coli (E.coli), 20 parts of yeast (yeast) and 50 parts of Nitrosomonas sp., and carry out strain mixing and compounding; take 0.5g of the compounded mixed bacteria Add 200 μL of 0.85% sodium chloride solution, and stir the wet bacteria with a sterilized toothpick; paste double-sided tape around the working area of ​​the carbon electrode of the cleaned CellSense biosensor, and use a pipette gun to draw 5 μL of the bacteria solution and apply it on In the working area of ​​the CellSense carbon electrode, after airing in the dark at room temperature for 0.5h, cover the polycarbonate film on the mixed bacteria, and seal and fix the bacteria in the electrode working area by double-sided adhesive to make a microbial electrode. The prepared microbial electrode was placed in the refrigerator at 4°C for 24 hours before use.

[0021] Using the CellSense biosensor of the microbial electrode of the present invention, biotoxicity analysis was...

Embodiment 3

[0023] Take the microbial electrode used in Example 2, remove the previously fixed microbial cells with pure water, sterilize and dry in the ultra-clean workbench, and perform the re-fixation of the microorganisms according to the operation steps in Example 2. And used for the toxicity analysis of 2,4-dichlorophenol, 20 times of repeated tests were analyzed to obtain 2,4-dichlorophenol EC 50 The deviation of the value is less than 8%, which can meet the needs of actual analysis. The biosensor microbial electrode not only has a simple preparation method, but also can realize the repeated use of the carbon working electrode, thereby reducing the instrument analysis cost by more than 90%.

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PUM

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Abstract

The invention relates to a microorganism electrode preparation method of a water quality toxicity biosensor, which is characterized in that: 40 to 100 parts of freezing and drying colon bacillus, 20 to 80 parts of microzyme and 40 to 60 parts of nitrosomonas are taken according to weight and the three germs are blended to get a blended germ; then 0.3 to 1.0g of blended germ is taken and added into 200 to 500 Mu L of 0.85 percent chlorine solution and a sterilized toothpick is used for mixing well the germ , thus blended germ solution is available; a diprosopia tape is stuck to the round of the working area of the carbon electrode; 5 to 10 Mu L of blended germ solution is drawn with a liquid relief gun, which is smeared to the working area of the carbon electrode and is air-cured for 0.5 to 2.0h in dark under room temperature; then a Makrolan film is covered on the air-cured blended solution, thus the microorganism electrode is made by fixing the germ through the diprosipia tape, which is at last arranged in a fridge of 4 DEG C for 24 to 48h ready for use. The microorganism electrode obtained from the invention improves largely the sensitivity and repetitiveness of the water quality toxicity analysis of the biosensor. The microorganism electrode preparation method of the water quality toxicity biosensor has the advantages of easy techniques and easy operation, can realize the reusage of the biosensor electrode, thus largely reducing the instrument analysis cost.

Description

technical field [0001] The invention relates to a method for preparing a microbial electrode of a CellSense biosensor used for water quality toxicity analysis. The microbial electrode prepared by the method can not only improve the toxicity analysis performance of the CellSense biosensor, but also reduce the analysis cost. It belongs to the technical field of environmental monitoring. Background technique [0002] At present, there are mainly two types of methods for the determination of wastewater toxicity, one is physical and chemical methods, and the other is biological methods. Traditional physical and chemical analysis methods can quantitatively analyze the content of main components in pollutants, but they cannot directly and comprehensively reflect the comprehensive impact of various toxic substances on the environment. Biological testing can make up for the lack of physical and chemical testing methods, so in water pollution research, it has become one of the import...

Claims

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Application Information

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IPC IPC(8): G01N27/327G01N33/18C12Q1/18
Inventor 王学江夏四清陈玲赵红宁王虹
Owner TONGJI UNIV
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