Preparation method of high-overpotential electrode and solar energy and electric energy denitrification device comprising high-overpotential electrode
A technology of potential electrode and graphite electrode, which is applied in energy wastewater treatment, chemical instruments and methods, water pollutants, etc., and can solve the problems of lead oxide secondary pollution, not being an electrode material, and high energy consumption
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[0018] The preparation of high overpotential electrode comprises the following steps:
[0019] Step 1) Add SnCl to the beaker 4、 SbCl 3 , add concentrated hydrochloric acid, n-butanol solution, stir to dissolve, then add Nd(NO 3 ) 3 , stir to dissolve;
[0020] Step 2) Put the graphite electrode into the beaker for soaking, take it out, and dry it at 50°C for half an hour;
[0021] Step 3) Then put it into a muffle furnace, crystallize at 420°C, take it out and cool it, and repeat the operation 12 times to obtain a neodymium-doped tin oxide graphite electrode.
[0022] Further, the soaking time in step 2 is set to 2 hours, and the crystallization time in step 3 is set to 2 hours.
[0023] The solar energy and electric energy denitrification device constructed by high overpotential electrodes includes a solar electrochemical denitrification device and an electrochemical oxidation denitrification device; the solar electrochemical denitrification device includes a solar cell...
Embodiment 1
[0025] Use neodymium-doped tin oxide graphite electrodes as anode and cathode respectively, put it into the first 100mL reaction tank 5, the electrode effective area is 6.8cm2, and the distance between the two electrodes is 3.5cm, and the solar electrolysis device is assembled as figure 1 shown. Take 100ml of a solution with an ammonia nitrogen concentration of 150mg / L, and add NaCl supporting electrolyte to make the concentration 0.1mol / L. Turn on the power supply, adjust the electrode voltage to 2.4 volts, conduct photolysis for 62 hours, and the ammonia nitrogen content is reduced to 6.0 mg / L as measured by Nessler's reagent method. This value is far lower than the national emission standard of 15mg / L.
Embodiment 2
[0027] Use neodymium-doped tin oxide graphite electrodes as the anode and the cathode respectively, put it into the second reaction tank 9 of 100mL, the effective area of the electrode is 6.8cm2, and the distance between the two electrodes is 3.5cm, and the assembled electrochemical electrolysis device is as follows: figure 2 shown. Take 100ml of a solution with an ammonia nitrogen concentration of 100mg / L, and add NaCl supporting electrolyte to make the concentration 0.1mol / L. Turn on the power supply, adjust the electrode voltage to 2.4 volts, perform electrochemical electrolysis for 62 hours, and use Nessler's reagent method to measure the ammonia nitrogen content from 100mg / L to 9.0mg / L, reaching the national emission standard.
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