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Smoke denitration catalyst by catalytic oxidation, and preparation method thereof

A technology for oxidation catalysts and denitrification catalysts, applied in physical/chemical process catalysts, metal/metal oxides/metal hydroxide catalysts, chemical instruments and methods, etc., can solve unfavorable SCR reactor installation, catalyst corrosion and wear, Nitrogen emissions and other issues, to achieve good catalytic oxidation activity, simple and feasible method, simple preparation process effect

Active Publication Date: 2011-09-21
BEIJING UNIV OF CHEM TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0003] Take NH 3 Selective catalytic reduction (SCR) technology as a reducing agent is the current treatment of NO in flue gas X The most commonly used method. However, this method has the following four disadvantages ① SCR method uses ammonia as an important chemical raw material, but generates useless nitrogen emissions, resulting in high SCR operating costs; ② The stoichiometric ratio of ammonia and NO needs to be strictly controlled , otherwise the penetration of unreacted ammonia will cause secondary pollution; ③ due to H 2 O and SO 2 It is an inevitable component in the flue gas. The surface of the catalyst is easily blocked and covered by the generated ammonium salt, so the reaction temperature must be above 350°C to decompose the ammonium salt and maintain good activity.
For this reason, the reactor must be placed in a high-temperature and high-dust area, and the catalyst is vulnerable to corrosion and wear of high-concentration smoke; ④The economizer and air preheater of boilers in my country are assembled in one piece, which is not conducive to the installation of SCR reactors, and is difficult Direct application on existing boilers

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0022] Add 5g of Na-montmorillonite into a mixture of acetone and water with a volume ratio of 2:1 to obtain a suspension with a mass concentration of 0.8%, cross-link with 40g of acidic n-butyl titanate at room temperature for 3 hours, wash with distilled water, dry and pulverize Afterwards, as a carrier, 1.6g Cu(NO 3 ) 2 ·3H 2 O and an oxalic acid solution of 0.35 g ammonium metavanadate were put into a muffle furnace for activation at 500° C. to obtain a catalyst. When the volume fraction of NO is 500ppm, O 2 Volume fraction 15%, the rest is N 2 , Airspeed 13000h -1 , the oxidation degree of NO can reach 45%, in the presence of saturated water vapor at 40°C and 500ppm SO 2 In the environment, it can keep the activity above 43% stably.

Embodiment 2

[0024] Add 5g of Na-montmorillonite into a mixture of acetone and water with a volume ratio of 1:1 to obtain a suspension with a mass concentration of 0.7%, cross-link with 40g of acidic n-butyl titanate at room temperature for 3 hours, wash with distilled water, dry and pulverize Afterwards, it was used as a carrier to adsorb 1.2g Cu(NO 3 ) 2 ·3H 2 O and an oxalic acid solution of 0.22g ammonium metavanadate were put into a muffle furnace for activation at 500°C to obtain a catalyst. When the volume fraction of NO is 500ppm, O 2 Volume fraction 10%, the rest is N 2 , Airspeed 12000h -1 , the oxidation degree of NO can reach 48%, in the presence of 40 ℃ saturated water vapor and 500ppm SO 2 In the environment, it can keep the activity above 45% stably.

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Abstract

The invention discloses a smoke denitration NO (Nitric Oxide) oxidation catalyst by catalytic oxidation, and a preparation method thereof. The NO oxidation catalyst is prepared from titanium crosslinking clay as a carrier and copper oxide and vanadium oxide as active ingredients, wherein the titanium crosslinking clay carrier is prepared by taking acetone as a dispersing agent and crosslinking and aging titanic acid butyl acetate and sodium base montmorillonite turbid liquid under an acid condition. Copper nitrate and ammonium metavanadate solutions are used as the precursors of the active ingredients, are fixed on the carrier by an immersion method, and are dried and calcined by program heating to obtain the smoke denitration catalyst by catalytic oxidation. In the catalyst, the copper capacity is 2-10%, and the vanadium capacity is 0.5-5%. The smoke denitration catalyst by catalytic oxidation has the advantages of good sulfur and water tolerance, good reproducibility and good denitration effect.

Description

technical field [0001] The invention relates to a NO oxidation catalyst used for catalytic oxidation flue gas denitrification and a preparation method thereof. Background technique [0002] Nitrogen oxides (NO X ) is one of the main air pollutants and an important precursor for inducing photochemical smog and acid rain. Now the world's annual NO X The emissions have reached 35-58Mt, of which more than 95% come from the combustion process of fossil fuels. [0003] Take NH 3 Selective catalytic reduction (SCR) technology as a reducing agent is the current treatment of NO in flue gas X The most commonly used method. But this method has the following four disadvantages ① SCR method uses ammonia as an important chemical raw material, but generates useless nitrogen emissions, resulting in high SCR operating costs; ② The stoichiometric ratio of ammonia and NO needs to be strictly controlled , otherwise the penetration of unreacted ammonia will cause secondary pollution; ③ due ...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01J23/847B01J21/16B01D53/86B01D53/56
Inventor 赵青涛童华王京刚徐仲均刘欣
Owner BEIJING UNIV OF CHEM TECH
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