Method for determining copper ions by selenium film modified electrode
A technology for modifying electrodes and copper ions, which is applied in the electrochemical analysis of copper ions, and in the field of measuring copper ions with selenium film modified electrodes, can solve the problems of low sensitivity of anodic stripping method, influence on analytical performance, poor reproducibility, etc., and achieve improvement Reproducibility and accuracy, improved sensitivity, low cost effect
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Embodiment 1
[0021] This embodiment adopts Potentiostat / Galvanostat BAS-100A chronopotential analyzer and electrochemical three-electrode test system, uses pyrolytic graphite (EPPG) as the electrode substrate, reduces the selenium film formed by co-enrichment as the working electrode, and platinum wire as the counter electrode , Ag / AgCl is the reference electrode, and the copper ion content in the sample is tested by anodic stripping differential chronopotential method. Reduction co-enrichment and anodic stripping conditions are respectively: the enrichment potential is -200mV, the enrichment time is 180s, and the resting time is 20s; during the test, the anodic stripping current is +2.0μA, and the scan rate is 20mV s -1 , the frequency is 20Hz.
[0022] See attached figure 1 , curve 1 in the figure is for 0.01molL by the above method -1 HCl+5.0gL -1 The results obtained from the KCl solution test; Curve 2 is the addition of 20.0 μgL to the solution described in Curve 1 -1 After Cu(II)...
Embodiment 2
[0026] This embodiment adopts Potentiostat / Galvanostat BAS-100A chronopotential analyzer and electrochemical three-electrode test system, uses pyrolytic graphite (EPPG) as the electrode substrate, reduces the selenium film formed by co-enrichment as the working electrode, and platinum wire as the counter electrode , Ag / AgCl as the reference electrode, using anodic stripping differential chronopotentiometry to measure different concentrations of copper ions in simulated water samples; at the same time, 1.0 μg L -1Cu(II) for the anti-interference detection of different ions. Reduction co-enrichment and anodic stripping conditions are respectively: the enrichment potential is -300mV, the enrichment time is 180s, and the resting time is 20s; during the test, the anodic stripping current is +2.0μA, and the scan rate is 20mV s -1 , the frequency is 20Hz.
[0027] See attached figure 2 And attached image 3 , for containing 0.01mol L -1 HCl, 10.0gL -1 KCl, 1.0 mg L -1 Cu(II) o...
Embodiment 3
[0032] This embodiment adopts Potentiostat / Galvanostat BAS-100A chronopotential analyzer and electrochemical three-electrode test system, uses pyrolytic graphite (EPPG) as the electrode substrate, reduces the selenium film formed by co-enrichment as the working electrode, and platinum wire as the counter electrode , Ag / AgCl as the reference electrode, using the anodic stripping differential chronopotential method to determine the copper ion content of simulated water samples, spiked seawater and tap water samples. Reduction co-enrichment and anodic stripping conditions are respectively: the enrichment potential is -300mV, the enrichment time is 180s, and the resting time is 20s; during the test, the anodic stripping current is +2.0μA, and the scan rate is 20mV s -1 , the frequency is 20Hz.
[0033] Simulation sample: adopt the test method of embodiment 1 or 2, be 0.40 μ g L to known Cu (II) concentration -1 The simulated sample 1, the known Cu(II) concentration is 3.0μg L -1...
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