Microcystic toxin-LR electrochemical detection method with amplified graphene signals
A technology of microcystin and signal amplification, applied in electrochemical variables of materials, measuring devices, scientific instruments, etc., can solve the problems of high cost, high cycle, complex process, etc., and achieve good electrical conductivity, sensitive electrochemical signals, and more The effect of electrochemically active area
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[0032] Example 1
[0033] A graphene signal amplification microcystin-LR electrochemical detection method, in which the specific manufacturing process of the sensor involved is as follows:
[0034] (1) First, pre-treat the gold electrode. The processing method is as follows: Place the surface of the gold electrode on a freshly configured piranha (H 2 SO 4 / H 2 O 2 =7:3v / v) Soak in the lotion for 10-15 minutes, after taking it out, rinse with ultrapure water, and use aluminum oxide with particle size of 1.0μm, 0.3μm, and 0.05μm in sequence with the word "8" Carefully polish to a smooth surface. Then rinse the aluminum oxide on the surface of the electrode with ultra-pure water, and place the electrodes in ultra-pure water, ethanol, and ultra-pure water for 5 to 10 minutes. After the ultrasound is completed, take out the electrode immediately, use it as the working electrode, the platinum wire electrode as the counter electrode, and the SCE as the reference electrode to perform cycl...
Example Embodiment
[0037] Example 2
[0038] Before measuring the concentration of MC-LR, take out the prepared MCH / Au NPs / Au electrode, and drop 10μL of endonuclease (DNase I) reaction buffer (pH=7.0, containing 100mmol / L) on the surface of the electrode. NaCl), 5μL of graphene-aptamer complex, 3μL of MC-LR at the test concentration, 2μL of DNase I solution (1000U / mL), put the electrode in a biochemical incubator at 30°C for one hour take out. Gently rinse the electrode surface with ethanol and ultrapure water to remove the weakly bound graphene. The electrode was then dried under a nitrogen atmosphere, and then taken out for DPV detection. The electrochemical detection was carried out in a 20 mmol / L phosphate buffer solution (pH=7.0) containing 5 mmol / L ferrocene formic acid and 0.1 mol / L sodium perchlorate.
[0039] The change of current and the concentration of MC-LR are at 1.0×10 -12 ~1.0×10 -10 There is a good linear relationship in the range of mol / L, the correlation coefficient is about 0....
Example Embodiment
[0040] Example 3
[0041] Put the prepared electrochemical aptamer sensor into 1.0×10 -11 mol / L MC-LR and the concentration of 1.0×10 -9 mol / L interfering substances are mixed in pairs for determination. The interference experiments of three common environmental pollutants of omethoate, glyphosate, paraquat, dimetrodin, acetamiprid and trichlorfon on the determination of MC-LR were investigated. Using the test conditions in Example 2 to determine the current response, the results of the study show that other interferences with a concentration of 100 times the MC-LR have an impact on the MC-LR current by less than 10.0%. It can be seen that the prepared aptamer sensor has high selectivity to MC-LR.
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