Low-temperature flue gas denitrification catalyst for selective reduction of NO by CO and its application
A denitrification catalyst and low-temperature flue gas technology, applied in molecular sieve catalysts, catalyst activation/preparation, physical/chemical process catalysts, etc., can solve problems such as decreased NO removal rate, unsuitable catalyst preparation, and low specific surface area
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Embodiment 1
[0032] The low-temperature flue gas denitrification catalyst utilizing CO to selectively reduce NOx in this embodiment was prepared according to the following steps:
[0033] A. Add Cu(NO 3 ) 2 0.20mol / L, Mn(NO 3 ) 2 2.0L of 0.20mol / L aqueous solution (mass 2110g), pH3.5; start stirring, heat up to 90°C, add 1280g of newly prepared ammonium-type SSZ-13 molecular sieve water-containing suction filter cake (550g in terms of solid matter), control Treat at 85°C for 1.5h for ion exchange, filter with suction, rinse with 2400g of water three times and filter with suction, dry the filter cake at 120°C for 5h, then roast it in an air-conditioned muffle furnace at 570°C for 6h, and crush it to -600 mesh to obtain Cu -Mn / SSZ-13 molecular sieve calcined powder; in the Cu-Mn / SSZ-13 molecular sieve calcined powder obtained by testing, in terms of oxide mass content, CuO2.6% and MnO1.7% were converted; ammonium-type SSZ-13 was prepared The sodium type SSZ-13 molecular sieve raw powder ...
Embodiment 2
[0039]Basically repeat the steps A-C of Example 1 to prepare the low-temperature flue gas denitrification catalyst using CO to selectively reduce NOx in this example, the difference is that the amount of basic copper carbonate in step B is 160 g, and the aluminum phosphate sol-pseudoboehmite composite glue The consumption of liquid is 1300g, and the water absorption rate of the obtained roasted bar is 0.42ml / g; step C sprinkles 84ml of acetic acid aqueous solution of mass concentration 75%.
[0040] The mass percentages of the main components in the low-temperature flue gas denitrification catalyst in this example are estimated to be about 37.7% of the SSZ-13 molecular sieve as hydrogen, 9.5% of copper as CuO, and 5.0% of manganese as MnO.
Embodiment 3
[0042] Basically repeat the steps A-C of Example 2 to prepare the low-temperature flue gas denitrification catalyst using CO to selectively reduce NOx in this example, the difference is that the amount of basic manganese carbonate in step B is 180g, and the aluminum phosphate sol-pseudoboehmite composite glue The consumption of liquid is 1400g, and the water absorption rate of the obtained roasted bar is 0.43ml / g; step C sprinkles 86ml of acetic acid aqueous solution of mass concentration 80%.
[0043] The mass percentages of the main components in the low-temperature flue gas denitrification catalyst in this example are estimated to be about 36.0% of the SSZ-13 molecular sieve as hydrogen, 10.0% of copper as CuO, and 8.0% of manganese as MnO.
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Abstract
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