Tungsten trioxide/carbon nitride/bismuth oxide double-Z type photocatalyst and preparation method and application thereof
A technology of tungsten trioxide and photocatalyst, applied in the field of photocatalysis, can solve the problem of poor light absorption ability, photogenerated electron-hole separation rate and photocatalytic activity, difficulty in generating superoxide radicals and hydroxyl radicals, photogenerated electron-holes Fast recombination rate and other issues, to achieve the effect of good stability of photocatalytic performance, strong redox ability, and easy industrial utilization
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Embodiment 1
[0037] A tungsten trioxide / carbon nitride / bismuth oxide double-Z photocatalyst. The tungsten trioxide / carbon nitride / bismuth oxide double-Z photocatalyst uses carbon nitride as a carrier, and the carbon nitride is modified with tungsten trioxide and Bismuth oxide.
[0038] In this embodiment, in the tungsten trioxide / carbon nitride / bismuth oxide double Z photocatalyst, the mass percentage of tungsten trioxide is 2.4%, the mass percentage of bismuth oxide is 4.6%, and the mass percentage of carbon nitride is The mass percentage content is 93.0%.
[0039] In this embodiment, tungsten trioxide has a flake structure; bismuth oxide has a microsphere structure; and carbon nitride has a slate block structure.
[0040] A method for preparing the tungsten trioxide / carbon nitride / bismuth oxide double Z-type photocatalyst of the present embodiment includes the following steps:
[0041] (1) Put 100 mg of tungstic acid, 100 mg of bismuth nitrate pentahydrate and 4 g of melamine in an agate mortar...
Embodiment 2
[0061] The application of a tungsten trioxide / carbon nitride / bismuth oxide double-Z photocatalyst in the degradation of antibiotic wastewater includes the following steps:
[0062] Weigh 0.1g CN (Comparative Example 1), WO 3 (Comparative Example 2), Bi 2 O 3 (Comparative Example 3), CW (Comparative Example 4), CB (Comparative Example 5), WB (Comparative Example 6), WCB (Example 1), respectively added to 100mL, a concentration of 10mg / L tetracycline (TC) antibiotics In the wastewater, magnetically stirred for one hour in the dark (that is, under dark conditions) to reach adsorption equilibrium; then turn on the light source and irradiate it under visible light (λ≥420nm) for photocatalytic reaction for 60 minutes to complete the degradation of dye wastewater.
[0063] At the same time, in order to eliminate the influence of tetracycline wastewater self-degradation on the degradation effect, a control group without any catalyst was also set up, and the tetracycline wastewater was irrad...
Embodiment 3
[0078] To investigate the corrosion resistance and stability of the tungsten trioxide / carbon nitride / bismuth oxide double-Z photocatalyst during the photocatalytic degradation process, including the following steps:
[0079] (1) Weigh 0.1 g of the tungsten trioxide / carbon nitride / bismuth oxide double-Z photocatalyst (WCB) in Example 1, and add it to 100 mL of tetracycline wastewater with a concentration of 10 mg / L to obtain a reaction system.
[0080] (2) Place the reaction system (tetracycline wastewater with WCB added) obtained in step (1) on a magnetic stirrer, stir for 1 hour in the dark to reach adsorption equilibrium, and take out 4 mL of solution to represent the initial liquid to be degraded, namely When the reaction time is 0 min, the concentration of the solution is measured with an ultraviolet-visible spectrophotometer and recorded as C 0 .
[0081] (3) The remaining solution in step (2) is subjected to a photocatalytic reaction under visible light. After 60 minutes of rea...
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