Carbon-based electrochemical sensor for detecting heavy metal lead ions and application thereof
A carbon-based electrochemical and lead ion technology, which is applied in the field of environmental pollutant analysis and heavy metal ion detection, can solve the problems of increasing the detection signal, achieve the effects of reducing background current, improving selectivity and sensitivity, and stabilizing load performance
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[0027] The invention provides a method for preparing a carbon-based electrochemical sensor for detecting heavy metal lead ions, the method comprising the following steps:
[0028] 1) Pretreat the hydrophobic carbon paper, and then use cyclic voltammetry to electrodeposit and reduce graphene oxide to obtain a CP / rGO electrode;
[0029] 2) The dsDNA solution was drip-coated on the surface of the CP / rGO electrode, and then dried to obtain the CP / rGO / DNA carbon-based electrochemical sensor.
[0030] In step 1), the pretreatment process of the hydrophobic carbon paper is: ultrasonically cleaning the hydrophobic carbon paper with ethanol and water in sequence, and sealing the non-deposition area of the hydrophobic carbon paper with insulating glue after drying. The process of using cyclic voltammetry to electrodeposit and reduce graphene oxide is as follows: immerse the pretreated hydrophobic carbon paper in the graphene oxide suspension, use cyclic voltammetry to electrodeposit a...
Embodiment 1
[0035] The preparation method of the carbon-based electrochemical sensor for detecting heavy metal lead ions is as follows:
[0036](1) Pretreatment of carbon paper. The 0.9 cm × 1.7 cm hydrophobic carbon paper was ultrasonically cleaned in absolute ethanol and deionized water for 5 min, and dried to obtain a clean carbon paper surface. Seal the other parts of the carbon paper with insulating glue, leaving a conductive area of 2 mm × 2 mm to obtain a CP electrode.
[0037] (2) Preparation of CP / rGO electrode. Graphene oxide (GO) was ultrasonically dispersed in 0.1 mol / L PBS buffer solution with pH=9.18 for 1.5 h to form a homogeneous suspension with a concentration of 0.5 mg / mL. The obtained CP electrode was immersed in the above GO suspension, and rGO was electrodeposited by cyclic voltammetry (CV) with a scanning range of -0.96-0.78V and a scanning speed of 0.1V / s for 5 cycles. After scanning, the electrode was immersed in deionized water to wash off the unstable GO on ...
Embodiment 2
[0041] The CP / rGO / DNA electrochemical sensor prepared in Example 1 was used for electrochemical detection of lead ions.
[0042] Differential pulsed anodic stripping voltammetry (DPASV) was used to detect lead ions. A three-electrode system was used. The CP / rGO / DNA electrochemical sensor was used as the working electrode, the saturated calomel electrode was used as the reference electrode, and the platinum sheet was used as the counter electrode. First, a series of lead ion standard buffer solutions with different concentrations were deposited at a constant potential under stirring conditions, with a deposition potential of -0.1V and a deposition time of 360s. Then, it is dissolved in a blank buffer solution without lead ions, and the stripping potential scanning range is -0.8-0V, and the peak current of anodic stripping is obtained. When the concentration of lead ions increases, the peak current value increases accordingly, because the amount of lead ions deposited on the ele...
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