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MnO<x>@Eu-CeO<x> low-temperature SCR flue gas denitration catalyst and preparation method and application thereof

A denitration catalyst and flue gas technology, applied in chemical instruments and methods, heterogeneous catalyst chemical elements, physical/chemical process catalysts, etc., can solve problems such as poor resistance to sulfur poisoning, improve catalytic activity and improve dispersibility , the effect of excellent NH3-SCR performance

Active Publication Date: 2020-06-09
JIANGXI AGRICULTURAL UNIVERSITY
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

However, Mn-based catalysts have poor resistance to sulfur poisoning

Method used

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  • MnO&lt;x&gt;@Eu-CeO&lt;x&gt; low-temperature SCR flue gas denitration catalyst and preparation method and application thereof
  • MnO&lt;x&gt;@Eu-CeO&lt;x&gt; low-temperature SCR flue gas denitration catalyst and preparation method and application thereof
  • MnO&lt;x&gt;@Eu-CeO&lt;x&gt; low-temperature SCR flue gas denitration catalyst and preparation method and application thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0032] (1) MnO x Preparation of nanorods: 1.2156 g KMnO 4 Add to 157.4 mL of deionized water and stir to dissolve. After dissolving, add 2.6 mL of 37 wt% hydrochloric acid, continue stirring, and finally dilute to 160 mL. The solution was transferred to a 200 mL reactor, heated to 140 °C, and reacted for 12 h. Naturally cooled to room temperature, the product was taken out, washed to neutrality, and dried at 80°C for 12 h to obtain a powdery solid product.

[0033] (2) MnO x @Eu-CeO x Preparation: 1.14g of MnO x Add the nanorod powder into 60 mL of absolute ethanol, ultrasonically stir and disperse evenly, then add hexamethylenetetramine solution, cerium nitrate hexahydrate solution and europium nitrate hexahydrate solution in sequence, and control the addition rate of the three solutions The reaction was carried out under heating and stirring in a water bath at 75°C for 3 hours (the addition rates of hexamethylenetetramine solution, cerium nitrate hexahydrate solution a...

Embodiment 2

[0035] (1) MnO x Preparation of nanorods: 1.2156 g KMnO 4 Add to 157.4 mL of deionized water and stir to dissolve. After dissolving, add 2.0 mL of 37 wt% hydrochloric acid, continue stirring, and finally dilute to 160 mL. The solution was transferred to a 200 mL reactor, heated to 140 °C, and reacted for 6 h. Naturally cooled to room temperature, the product was taken out, washed to neutrality, and dried at 80°C for 6 h to obtain a powdery solid product.

[0036] (2) MnO x @Eu-CeO x Preparation: 0.7g of MnO x Add the nanorod powder into 40 mL of absolute ethanol, ultrasonically stir and disperse evenly, then add hexamethylenetetramine solution, cerium nitrate hexahydrate solution and europium nitrate hexahydrate solution in sequence, and control the addition rate of the three solutions The reaction was carried out under heating and stirring in a water bath at 70°C for 4 hours (the addition rates of hexamethylenetetramine solution, cerium nitrate hexahydrate solution and ...

Embodiment 3

[0038] (1) MnO x Preparation of nanorods: 1.2156 g KMnO 4 Add it into 157.4 mL of deionized water and stir to dissolve; after dissolving, add 3 mL of 37 wt% hydrochloric acid and continue stirring, and finally set the volume to 160 mL; transfer the solution to a 200 mL reactor, heat up to 140 °C, and react for 24 h; naturally cool to room temperature, take out the product, wash the product to neutrality, and dry at 80°C for 24 h to obtain a powdery solid product;

[0039] (2) MnO x @Eu-CeO x Preparation: 2.5g of MnO x Add the nanorod powder into 80 mL of absolute ethanol, ultrasonically stir and disperse evenly, then add hexamethylenetetramine solution, cerium nitrate hexahydrate solution and europium nitrate hexahydrate solution in sequence, and control the addition rate of the three solutions The reaction was carried out under heating and stirring in a water bath at 80°C for 2 h (the addition rates of hexamethylenetetramine solution, cerium nitrate hexahydrate solution, ...

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Abstract

The invention discloses a MnO<x>@Eu-CeO<x> low-temperature SCR flue gas denitration catalyst and a preparation method and application thereof. According to the invention, an MnO<x> nanorod prepared byusing a hydrothermal method is used as an inner core, the outer layer of the MnO<x> nanorod is wrapped with a precursor of Eu-CeO<x> through an improved chemical precipitation method, and then roasting is carried out so as to prepare the MnO<x>-Eu-CeO<x> low-temperature SCR flue gas denitration catalyst with a core-shell structure. In the prepared MnO<x>@Eu-CeO<x> low-temperature SCR flue gas denitration catalyst, a molar mass ratio of the MnO<x> nanorod to CeO<x> to EuO<x> is 1: (0.4-1.2): (0.2-0.8). The MnO<x>@Eu-CeO<x> low-temperature SCR flue gas denitration catalyst disclosed by the invention has the core-shell structure, and the shell is a composite oxide shell, so the oxidation-reduction capability of active components and interaction between the active components are greatly improved, and the catalyst presents excellent NO<x> catalytic reduction activity and low-temperature strong sulfur poisoning resistance at a temperature of 100-200 DEG C.

Description

technical field [0001] The invention belongs to the field of environmental protection and environmental catalysis, in particular to MnO x @Eu-CeO x Low-temperature SCR flue gas denitrification catalyst, preparation method and application thereof. Background technique [0002] Nitrogen oxides (NO x ) is one of the main air pollutants that cause acid rain, photochemical smog, and ozone layer damage. It has serious harm to human health and the ecological environment. How to effectively control and reduce NO x The emissions have attracted the attention of researchers from various countries. According to statistics, 70.9% of China's nitrogen oxide emissions in 2014 came from industrial sources of nitrogen oxide emissions such as electric power, thermal power production and supply industries, among which the nitrogen oxide emissions from thermal power plants accounted for 10% of the total nitrogen oxide emissions from industrial enterprises. 62.1%, which is the largest emitter ...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01J23/34B01D53/90B01D53/56
CPCB01D53/56B01D53/90B01J23/002B01J23/34B01J2523/00B01J2523/3743B01J2523/72B01J2523/3712
Inventor 喻成龙
Owner JIANGXI AGRICULTURAL UNIVERSITY