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Process and device for carrying out flue gas denitrification by utilizing solid organic denitrifying agent

A denitration agent and organic technology, applied in the field of industrial flue gas denitration, to achieve the effect of improving denitration efficiency, advanced equipment and technology, and high safety

Inactive Publication Date: 2015-03-04
天津天和环能科技有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0004] At present, the industrial flue gas denitrification technology mainly adopts the selective catalytic reduction method (SCR method) and the selective non-catalytic reduction method (SNCR method), both of which are harmful to the boiler combustion Due to the requirements of the working conditions, the traditional technology is still in the technical blind spot for the chain furnace
The SCR method is suitable for large pulverized coal furnaces, using catalysts for denitrification, long-term use will easily lead to air preheater blockage
This method usually requires the modification of the induced draft fan and the air preheater. Because the installation location is between the economizer and the air preheater, it is subject to many conditions and has high requirements for the flue gas flow field, which has investment and operating costs. Disadvantages such as high height, large floor area, complex system operation and maintenance
The SNCR method is suitable for circulating fluidized bed boilers, and requires a higher temperature (900~1100°C). Its investment cost is low, but the ammonia escape rate is relatively high, and the denitrification efficiency is relatively low, which cannot meet the requirements and discharge standards
The traditional denitrification process usually uses ammonia water or urea as the reducing agent, which has low storage and transportation safety and a large ammonia escape rate, which increases water consumption and brings great difficulties to subsequent wastewater treatment.
On the other hand, the ammonium sulfate (aerosol) produced during the flue gas treatment and the solid particles adsorbed by the saturated steam formed by a large amount of water will affect the subsequent dust removal device and affect the air volume.

Method used

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  • Process and device for carrying out flue gas denitrification by utilizing solid organic denitrifying agent
  • Process and device for carrying out flue gas denitrification by utilizing solid organic denitrifying agent
  • Process and device for carrying out flue gas denitrification by utilizing solid organic denitrifying agent

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0035] NO in flue gas to be treated x The initial concentration of 450 mg / m 3 , the flue temperature is within the range of 850°C~950°C, spray 53.30kg of solid organic denitration agent into the flue reactor every hour, and its specific components are 34.65kg of acetamide, 5.33kg of ammonium bicarbonate, 13.32kg of active calcium carbonate, with NO x The mass ratio of the reaction is 1.2:1, and the treated flue gas enters the online monitoring system for real-time monitoring.

[0036] Table 1 Flue gas denitrification efficiency in different periods

[0037]

Embodiment 2

[0039] As described in Example 1, the difference is: when the flue temperature is within the range of 650°C to 800°C, 63.79kg of solid organic denitration agent is sprayed into the flue reactor every hour, and its specific composition is 41.46kg of triammonium citrate, Ammonium bicarbonate 6.38kg, active calcium carbonate 15.95kg, and NO x The mass ratio of the reaction is 1.5:1, and the treated flue gas enters the online monitoring system for real-time monitoring.

[0040] Table 2 Flue gas denitrification efficiency in different periods

[0041]

Embodiment 3

[0043] NO in flue gas to be treated x The initial concentration of 750 mg / m 3, the flue temperature is within the range of 850°C~950°C, spray 232.88kg of solid organic denitration agent into the flue reactor every hour, and its specific components are 151.37kg of acetamide, 23.29kg of ammonium bicarbonate, 58.22kg of active calcium carbonate, with NO x The mass ratio of the reaction is 1.5:1, and the treated flue gas enters the online monitoring system for real-time monitoring.

[0044] Table 3 Flue gas denitrification efficiency in different time periods

[0045]

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Abstract

The invention discloses a process and a device for carrying out flue gas denitrification by utilizing a solid organic denitrifying agent. According to the process, an organic denitrifying reducing agent is sprayed into a reaction area at the fume temperature of 500-950 DEG C and gasified and is subjected to selective uncatalyzed reaction with NOx contained in smoke gas, so that the purpose of denitrification is achieved. The core device of the process is highly-integrated integral equipment, is designed according to unit system and mainly comprises a denitrifying agent delivery supply system, a metering distribution system, a fluidic system, a gas delivery system, a chemical agent injection system and an on-line monitoring system. According to the smoke gas denitrification technology of the solid organic denitrifying agent, no change needs to be made on a boiler, and only the injection system needs to be added to the position at the fume temperature of 500-950 DEG C and between the smoke gas outlet of the boiler and a superheater. The process and the device which are disclosed by the invention have the characteristics of low operating cost, high safety, obviousness in denitrification effect and the like.

Description

technical field [0001] The invention relates to the technical field of denitrification of industrial flue gas, and provides a process and a device for denitrification of flue gas by using a solid organic denitrification agent. Background technique [0002] The energy structure dominated by coal is the main factor affecting the quality of my country's atmospheric environment, and coal-burning pollution is the main feature of air pollution. With the improvement of people's awareness of environmental protection and the promulgation and implementation of the government's policy on the maximum allowable emission concentration of sulfur dioxide and nitrogen oxides from boilers, the SO in flue gas 2 and NO x Control has become a very urgent task. [0003] According to the newly promulgated "Emission Standards of Air Pollutants for Thermal Power Plants" (GB13223-2011), starting from July 1, 2014, the emission standard of nitrogen oxide pollutants for existing coal-fired thermal p...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01D53/83B01D53/56
Inventor 沈渭清王嫒
Owner 天津天和环能科技有限公司
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