CN202289834U - High-efficiency denitration device for circulating fluidized bed boiler - Google Patents
High-efficiency denitration device for circulating fluidized bed boiler Download PDFInfo
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- CN202289834U CN202289834U CN2011204180467U CN201120418046U CN202289834U CN 202289834 U CN202289834 U CN 202289834U CN 2011204180467 U CN2011204180467 U CN 2011204180467U CN 201120418046 U CN201120418046 U CN 201120418046U CN 202289834 U CN202289834 U CN 202289834U
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- cyclone separator
- denitrfying agent
- flue
- boiler
- smoke
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Abstract
The utility model discloses a high-efficiency denitration device for a circulating fluidized bed boiler, and belongs to the technical field of high-efficiency denitration for coal-fired boilers. The high-efficiency denitration device for the circulating fluidized bed boiler is characterized in that the originally-arranged cyclone separator of a boiler is utilized and a denitration device is arranged on the cyclone separator; after being led out of a hearth, the smoke of the boiler enters the cyclone separator along the tangent direction of a flue; and nozzles are respectively arranged on the flue and on the top of the cyclone separator and used for spraying a denitrifying agent. After the denitrifying agent and the smoke enter into the cyclone separator along the tangent direction of the flue, a strong rotational flow is formed, so that the speed for mixing the denitrifying agent and oxynitride in the smoke is enhanced, and the reduction of oxynitride in the smoke is promoted, and the content of oxynitride in the smoke is reduced obviously; and furthermore, the flue of the boiler is not required to be improved deeply. The high-efficiency denitration device has the advantages of simple structure, high denitration efficiency and low cost.
Description
Technical field
The utility model relates to a kind of efficient denitrification apparatus of CFBB, belongs to the efficient denitration technology of coal-burning boiler field.
Background technology
In the denitration scheme of general no catalysis, utilize through adding denitrfying agent such as liquefied ammonia, ammonia or urea liquid in 800-1100 ℃ of flue gas treating process and reduce nitrogen oxide (NO
X) discharge capacity, this method to a certain extent can be with nitrogen oxide (NO
X) be reduced into N
2, but its denitration efficiency is difficult to above 50%, especially for large-sized boiler.Main cause is that denitration efficiency receives following factor affecting: 1) nitrogen oxide and denitrfying agent can not get sufficient mixing in the combustion chamber; 2) the flue-gas temperature skewness in denitration reaction zone; 3) nitrogen oxide in denitration zone and the ratio of denitrfying agent concentration do not match.Therefore, nowadays a lot of traditional SNCR methods can not satisfy the strict demand to the exhaustion of nitrogen oxides from coal-fired boiler amount.
Occur a kind of new method 70 with the eighties,, utilize catalytic specie to promote reaction with the ammonia removal nitrogen oxide promptly at 300-400 ℃ of left and right sides low-temperature region.Present many coal-burning power plants are provided with selective catalytic reactor (SCR) between the economizer at boiler flue rear portion and air preheater, this place's cigarette temperature drop is between 300-400 ℃.This denitrfying agent is anhydrous ammonia, liquefied ammonia or urea mostly, and the place sprays in the flue gas in economizer exit, and gets into selective catalytic reactor immediately in (SCR).But the efficient of selective catalytic reactor and performance are very sensitive to the various procedures factor, and many shortcomings are arranged, and sum up as follows:
1. the catalytic specie life-span is too short.Catalytic specie life-span length depends on flying dust concentration and the contaminated thing chocking-up degree thereof in the flue gas.Coal combustion produces a large amount of flying dusts can be caused accelerating to stop up Catalytic Layer, and can significantly reduce the catalytic specie activity in operation after 5000 hours.Every two years changing a Catalytic Layer is through common occurrence.
2. with high investment and high operating cost.The SCR system builds and the operating cost costliness.One of main expensive operating cost is relevant with the material of normal replacing catalytic materials.
3. the design of good catalytic bed is unusual The key factor, but in the good design reducing smoke flying dust the accumulation of catalytic materials and caused active reduction of obstruction of hole thereof.
4. good SCR design is very important, especially to factor such as cigarette temperature, and dustiness, nitrogen oxide and the denitrfying agent concentration ratio in flue gas.These factors must evenly distribute before getting into the SCR catalyst converter.Not good enough SCR designs denitration efficiency will be reduced, and the life-span of shortening catalytic specie and the potential possibility that forms a large amount of sulfate of ammoniacs---a kind of stickum can stop up catalytic specie air gap and obstruct smoke circulation.
Summary of the invention
In order to solve the problem that exists in the prior art; The utility model provides a kind of efficient denitrification apparatus of CFBB; It is a significant improvement to the SNCR system; Powerful eddy current in unique location through some denitrfying agent nozzles and the cyclone separator significantly improves the denitration reaction effect, increases NO in the flue gas
XWith the mixing of denitrfying agent with contact, to reach efficient denitration effect.
The technical scheme of the utility model is: a kind of efficient denitrification apparatus of CFBB; CFBB is connected with a denitrification apparatus; Said denitrification apparatus adopts a cyclone separator, and this cyclone separator becomes the tangential to be connected with the boiler exhaust gas road of CFBB, and the bottom is provided with an air-returen flue that is connected with CFBB; Top is provided with a smoke outlet flue, and the bottom of smoke outlet flue is provided with an inner flue that stretches in the cyclone separator; On said boiler exhaust gas road, be provided with the first denitrfying agent nozzle, on said cyclone separator, be provided with the second denitrfying agent nozzle.
A first denitrfying agent nozzle that in the boiler exhaust gas road, sprays denitrfying agent is set on said boiler exhaust gas road at least.
Between the shell and inner flue of said cyclone separator, the annular chamber top of formation is provided with second a denitrfying agent nozzle that in cyclone separator, sprays denitrfying agent at least.
Said denitrfying agent adopts liquefied ammonia, ammonia or urea liquid.
Adopt above-mentioned technical scheme, the flue-gas temperature of coming out from boiler furnace is between 800-1100 ℃, and flue gas tangentially gets in the cyclone separator through the boiler exhaust gas road, forms one strong flue gas eddy flow.Denitrfying agent (like ammonia or urea liquid etc.) is installed the nozzle injection from the top of boiler exhaust gas road, cyclone separator or simultaneously from these two positions.Denitrfying agent can spread rapidly with the eddy flow in the separator after getting into flue gas, and in the eddy flow district, forms aerosol post diaphragm.This aerosol post diaphragm can impel contacting of nitrogen oxide and denitrfying agent and prevent the nitrogen oxide escape.When the cigarette temperature was within 800-1100 ℃ optimum range, the quick and reaction of nitrogen oxides of ammonia compound meeting in the flue gas impelled NO
XBe reduced into nitrogen, thereby improve denitration efficiency, reduce the discharging of nitrogen oxide.
The beneficial effect of the utility model is: the efficient denitrification apparatus of this CFBB is installed nozzle with the top of cyclone separator and is injected denitrfying agent on the boiler exhaust gas road; Through the cyclonic action of flue gas in separator; Strengthened the mixing velocity of nitrogen oxide in denitrfying agent and the flue gas; Promote the reduction of nitrogen oxide in the flue gas, significantly reduced the amount of nitrogen oxides of flue gas.And need not boiler flue is carried out deep transformation, simple in structure, with low cost, denitration efficiency is high.
Description of drawings
Fig. 1 is a kind of efficient denitrification apparatus fundamental diagram of CFBB.
Fig. 2 is that the boiler exhaust gas road is connected sketch map with the tangential of cyclone separator.
Among the figure: 1, CFBB, 2, cyclone separator, 3, the boiler exhaust gas road, 4, the first denitrfying agent nozzle; 5, the second denitrfying agent nozzle, 6, boiler smoke, 6a, flue gas eddy flow, 7, the denitrfying agent pipeline; 8, denitrfying agent supply pump, 9, smoke outlet flue, 9a, inner flue, 10, air-returen flue.
The specific embodiment
Fig. 1,2 shows a kind of efficient denitrification apparatus fundamental diagram of CFBB.Among the figure; Denitrification apparatus adopts a cyclone separator 2; This cyclone separator 2 is connected with 3 one-tenth tangentials, boiler exhaust gas road of CFBB 1; The bottom is provided with an air-returen flue 10 that is connected with CFBB 1, and top is provided with a smoke outlet flue 9, and the bottom of smoke outlet flue 9 is provided with an inner flue 9a who stretches in the cyclone separator 2.4 first denitrfying agent nozzles 4 that in boiler exhaust gas road 3, spray denitrfying agent are being set on the boiler exhaust gas road 3.Between the shell 2 and inner flue 9a of cyclone separator, the annular chamber top of formation is provided with 4 second denitrfying agent nozzles 5 that in cyclone separator 2, spray denitrfying agent.Denitrfying agent adopts liquefied ammonia, ammonia or urea liquid.
The first denitrfying agent nozzle 4 is connected with denitrfying agent supply pump 8 through denitrfying agent pipeline 7 with the second denitrfying agent nozzle 5.When CFBB 1 work, after boiler smoke 6 gets into boiler exhaust gas road 3, get into cyclone separator 2 with the tangential again, form one very strong flue gas eddy flow 6a.In boiler exhaust gas road 3, spray into denitrfying agent at 4 first denitrfying agent nozzles 4; Or in cyclone separator 2, spray into denitrfying agent at 4 second denitrfying agent nozzles 5; Or spray into denitrfying agent simultaneously at above-mentioned two places; Denitrfying agent receives heating evaporation in high-temperature flue gas, and under cyclonic action, denitrfying agent and nitrogen oxide are fully mixed and carries out reduction reaction.
Adopt above-mentioned efficient denitrification apparatus; Denitrfying agent is heated, evaporates, spreads in 800-1100 ℃ of high-temperature flue gas; And under strong cyclonic action, denitrfying agent forms the aerosol post at the inner chamber of cyclone separator 2, and the nitrogen oxide in the flue gas can fully contact and mix with denitrfying agent aerosol post.The quick and reaction of nitrogen oxides of denitrfying agent meeting in the flue gas impels NOx to be reduced into nitrogen, thereby improves denitration efficiency.
Claims (4)
1. the efficient denitrification apparatus of a CFBB; CFBB (1) is connected with a denitrification apparatus; It is characterized in that: said denitrification apparatus adopts a cyclone separator (2); This cyclone separator (2) becomes the tangential to be connected with the boiler exhaust gas road (3) of CFBB (1); The bottom is provided with an air-returen flue (10) that is connected with CFBB (1), and top is provided with a smoke outlet flue (9), and the bottom of smoke outlet flue (9) is provided with an inner flue (9a) that stretches in the cyclone separator (2); On said boiler exhaust gas road (3), be provided with the first denitrfying agent nozzle (4), on said cyclone separator (2), be provided with the second denitrfying agent nozzle (5).
2. the efficient denitrification apparatus of a kind of CFBB according to claim 1 is characterized in that: first a denitrfying agent nozzle (4) that in boiler exhaust gas road (3), sprays denitrfying agent is being set on the said boiler exhaust gas road (3) at least.
3. the efficient denitrification apparatus of a kind of CFBB according to claim 1; It is characterized in that: between the shell (2) and inner flue (9a) of said cyclone separator, the annular chamber top of formation is provided with second a denitrfying agent nozzle (5) that in cyclone separator (2), sprays denitrfying agent at least.
4. according to the efficient denitrification apparatus of claim 2 or 3 described a kind of CFBBs, it is characterized in that: said denitrfying agent adopts liquefied ammonia, ammonia or urea liquid.
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CN2011204180467U CN202289834U (en) | 2011-10-28 | 2011-10-28 | High-efficiency denitration device for circulating fluidized bed boiler |
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CN2011204180467U CN202289834U (en) | 2011-10-28 | 2011-10-28 | High-efficiency denitration device for circulating fluidized bed boiler |
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102357339A (en) * | 2011-10-26 | 2012-02-22 | 中能东讯新能源科技(大连)有限公司 | Efficient denitrifying device of circular fluidized bed boiler |
CN102974204A (en) * | 2012-12-13 | 2013-03-20 | 江苏百灵天地环境设计研究院有限公司 | Reaction device for SNCR (selective non-catalytic reduction) denitration system of circulating fluid bed |
CN103949148A (en) * | 2014-05-20 | 2014-07-30 | 国家电网公司 | Enhanced absorption device in wet desulfurization absorption tower and wet desulfurization absorption tower |
TWI504843B (en) * | 2013-08-30 | 2015-10-21 | Automotive Res & Testing Ct | Apparatus and method for treating exhaust gas from vehicle |
-
2011
- 2011-10-28 CN CN2011204180467U patent/CN202289834U/en not_active Expired - Fee Related
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102357339A (en) * | 2011-10-26 | 2012-02-22 | 中能东讯新能源科技(大连)有限公司 | Efficient denitrifying device of circular fluidized bed boiler |
CN102974204A (en) * | 2012-12-13 | 2013-03-20 | 江苏百灵天地环境设计研究院有限公司 | Reaction device for SNCR (selective non-catalytic reduction) denitration system of circulating fluid bed |
TWI504843B (en) * | 2013-08-30 | 2015-10-21 | Automotive Res & Testing Ct | Apparatus and method for treating exhaust gas from vehicle |
CN103949148A (en) * | 2014-05-20 | 2014-07-30 | 国家电网公司 | Enhanced absorption device in wet desulfurization absorption tower and wet desulfurization absorption tower |
CN103949148B (en) * | 2014-05-20 | 2017-03-08 | 国家电网公司 | Strengthening absorption plant and wet desulphurization absorption tower in a kind of wet desulphurization absorption tower |
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Granted publication date: 20120704 Termination date: 20151028 |
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