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Embedded SCR + SNCR flue gas denitration device and method for grate rotary kiln

A chain grate and rotary kiln technology, applied in separation methods, chemical instruments and methods, gas treatment, etc., can solve the problems of difficulty in meeting ultra-low emission requirements, waste, high operating costs and energy, etc. Utilization rate, the effect of reducing the escape of ammonia

Pending Publication Date: 2021-05-07
BEIJING SHOUGANG INT ENG TECH
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  • Abstract
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  • Claims
  • Application Information

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Problems solved by technology

In the traditional flue gas denitrification method, the denitrification efficiency of SNCR is generally 20% to 40%, and the denitrification efficiency of activated carbon method is generally 30% to 60%, which is difficult to meet the ultra-low emission requirements. %, becoming the preferred process method
[0003] At present, the treatment of pellet flue gas mostly adopts the process route of adding SCR denitrification device to the main exhaust system. Since the catalytic reaction temperature range of SCR denitrification process is 260 ° C ~ 400 ° C, and the temperature of pellet main exhaust gas is between 150 ° C ~ 180 ° C Therefore, a flue gas heating system must be equipped, resulting in high operating costs and energy waste

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  • Embedded SCR + SNCR flue gas denitration device and method for grate rotary kiln
  • Embedded SCR + SNCR flue gas denitration device and method for grate rotary kiln

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Embodiment Construction

[0035] A chain grate-rotary kiln embedded SCR+SNCR flue gas denitrification method, mainly including: 1# ring cooling fan 1, 2# ring cooling fan 2, 3# ring cooling fan 3, SNCR atomizing spray gun 4, multi-tube Dust collector 5, electric damper 6, low-leakage airtight damper 7, ammonia injector 8, SCR denitrification reactor 9, heat recovery fan 10, main exhaust air box 11, main extractor electrostatic precipitator 12, desulfurization device 13, main exhaust Machine 14, drying air blower 15, chimney 16.

[0036] Open a hole on the side wall of the fume hood at the top of the grate preheating section II, and install the SNCR atomizing spray gun 4; the position of the spray gun should be selected so that the injected reducing agent and the flue gas are fully mixed, and the sprayed reductant is fully mixed with the flue gas, and at the reaction temperature (850 ~ 1050 ℃) Zones have a dwell time of not less than 0.5s. The reducing agent is sprayed into the top fume hood of the pre...

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Abstract

The invention discloses an embedded SCR + SNCR flue gas denitration device and method for a grate rotary kiln, and belongs to the technical field of sintering and pelletizing flue gas denitration. According to the SCR denitration method, the denitration efficiency is guaranteed, and a flue gas heating system does not need to be arranged. According to a main source of NOX in flue gas discharged by a chain grate-rotary kiln, an SNCR denitration system is arranged at a preheating section II for primary denitration by combining a principle of a pellet air flow system; an SCR denitration device is arranged between a multi-pipe dust remover and a backheating fan in a pelletizing process air flow system and is used for secondary fine denitration. The flue gas with NOx removed returns to an air draft drying section of the chain grate through the heat return fan, production requirements can be met, denitration treatment on the pellet flue gas can be achieved, and compared with an existing most commonly-adopted after-main-exhaust full-flue-gas denitration system, the flue gas does not need to be subjected to heat compensation, and the operation cost can be reduced by about 3 / 4.

Description

technical field [0001] The invention relates to a grate-rotary kiln embedded SCR+SNCR flue gas denitrification device and method, belonging to the technical field of sintering and pelletizing flue gas denitrification. Background technique [0002] NO in the waste gas discharged from the main exhaust system of pellet production X The concentration reaches 250~500mg / Nm 3 , and the oxygen content is as high as 17% to 19%, and the latest ultra-low emission standards require NO X Emission concentration≤50mg / Nm 3 , and the emission concentration should be converted into a benchmark oxygen content of 16%, and the actual denitrification efficiency is required to reach more than 85%. In the traditional flue gas denitrification method, the denitrification efficiency of SNCR is generally 20% to 40%, and the denitrification efficiency of activated carbon method is generally 30% to 60%, which is difficult to meet the ultra-low emission requirements. %, become the preferred process me...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01D53/76B01D53/56B01D53/86F27D17/00
CPCB01D53/56B01D53/76B01D53/8625B01D2251/2062B01D2258/0283F27D17/004F27D17/008
Inventor 李长兴王波颜晓光寇彦德孙照燕杨帆王飞刘东生
Owner BEIJING SHOUGANG INT ENG TECH