CN100491822C - Denitrification method using biomass direct combustion and re-combustion and flue gas recirculation process - Google Patents
Denitrification method using biomass direct combustion and re-combustion and flue gas recirculation process Download PDFInfo
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技术领域 technical field
本发明涉及到煤粉锅炉低NOx燃烧技术,尤其涉及到利用生物质直燃再燃脱硝的燃烧方法。The invention relates to a low NOx combustion technology for a pulverized coal boiler, in particular to a combustion method utilizing biomass direct combustion and then combustion for denitrification.
背景技术 Background technique
煤粉燃烧是形成氮氧化物排放的重要来源,现有的低过量空气系数、空气分级燃烧技术和浓淡燃烧技术等低NOx燃烧技术的脱硝效率一般低于50%,因此不能满足日益严格的环保要求。再燃技术又称为燃料分级或炉内还原(IFNR)技术,它是降低NOx排放的诸多炉内方法中最有效的措施之一,再燃技术的脱硝效率可以达到60%以上。目前国内外现有的再燃脱硝项目大都以天然气作为再燃燃料,还有部分以细煤粉作为再燃燃料的。我国的天然气资源主要分布在西部,且储量有限,采用天然气作为再燃燃料,运行成本较高。细煤粉再燃脱硝技术对再燃煤粉的煤种及粒度都有严格的要求。Pulverized coal combustion is an important source of nitrogen oxide emissions. The denitrification efficiency of existing low-excess air ratio, air-staged combustion technology, and dense-lean combustion technology and other low-NOx combustion technologies is generally lower than 50%, so they cannot meet the increasingly stringent environmental protection requirements. Require. Reburning technology, also known as fuel classification or in-furnace reduction (IFNR) technology, is one of the most effective measures among many in-furnace methods to reduce NOx emissions. The denitrification efficiency of reburning technology can reach more than 60%. At present, most of the existing reburning and denitrification projects at home and abroad use natural gas as the reburning fuel, and some use fine coal powder as the reburning fuel. my country's natural gas resources are mainly distributed in the west, and the reserves are limited. The use of natural gas as reburning fuel has high operating costs. Fine pulverized coal reburning and denitrification technology has strict requirements on the coal type and particle size of reburning pulverized coal.
公开号为CN415891A的专利申请文件中公开了一种用生物质热解气再燃脱硝的燃烧方法及其装置,它采用生物制热解气作为再燃燃料,并在装置中增加了用于将生物质进行热解气化的气化炉及热解气的传输装置。由于已有的生物质气化技术产存在技术风险,并且所生产的生物质热解气的热值都是比较低的,并且其中只含有少量的CH4,而CH4是最有效的脱硝成分,所以采用生物质热解气进行脱销的效果并不理想,并且在生物质在气化过程中还损失了生物质的一部分能量,使得生物质的能量不能得到充分利用。该专利申请在装置中增加的气化炉及热解气的传输装置,使系统结构复杂,增加了系统的成本。The patent application document with the publication number CN415891A discloses a combustion method and device for reburning denitrification with biomass pyrolysis gas, which uses biomass pyrolysis gas as the reburning fuel, and adds an A gasifier for pyrolysis gasification and a transmission device for pyrolysis gas. Due to the technical risk of the existing biomass gasification technology, and the calorific value of the produced biomass pyrolysis gas is relatively low, and it only contains a small amount of CH 4 , and CH 4 is the most effective denitrification component , so the effect of using biomass pyrolysis gas for destocking is not ideal, and part of the energy of biomass is lost in the process of biomass gasification, so that the energy of biomass cannot be fully utilized. The gasifier and pyrolysis gas transmission device added to the device in this patent application complicate the structure of the system and increase the cost of the system.
发明内容 Contents of the invention
本发明提供的利用生物质直燃再燃与烟气再循环工艺脱硝的方法是基于下面的装置来实现的,所述装置包括煤粉锅炉,它还包括生物质给料装置、以及所述生物质给料装置与煤粉锅炉之间的连接装置和再循环引风机,所述生物质给料装置的出料口和一次风进风管道连通,一次风进风管道的一端和再燃燃料喷口连通,再循环引风机的进风口和煤粉锅炉的尾部烟道连通,再循环引风机的出风口和一次风进风管道连通,所述再循环引风机的入口和空气预热器与除尘器之间的尾部烟道连通,或者和空气预热器之前的尾部烟道段连通,所述方法的步骤为:The method for denitrification using biomass direct combustion and reburning and flue gas recirculation process provided by the present invention is realized based on the following device, which includes a pulverized coal boiler, which also includes a biomass feeding device, and the biomass The connecting device between the feeding device and the pulverized coal boiler and the recirculation induced draft fan, the outlet of the biomass feeding device is connected with the primary air inlet pipe, and one end of the primary air inlet pipe is connected with the reburning fuel nozzle, The air inlet of the recirculation induced draft fan is connected with the tail flue of the pulverized coal boiler, the air outlet of the recirculation induced draft fan is connected with the primary air inlet pipe, and the inlet of the recirculation induced draft fan is connected with the air preheater and the dust collector The tail flue is communicated with, or communicated with the tail flue section before the air preheater, and the steps of the method are:
A、煤粉通过煤粉锅炉的燃烧器进入煤粉锅炉炉膛底部主燃区燃烧形成含有NOx的烟气;A. Pulverized coal enters the main combustion zone at the bottom of the pulverized coal boiler furnace through the burner of the pulverized coal boiler to burn to form flue gas containing NOx;
B、利用一次风混合再循环的尾部烟气的混合物将生物质颗粒喷入炉膛中部,形成再燃还原区;B. Use the mixture of primary air to mix and recirculate the tail flue gas to spray biomass particles into the middle of the furnace to form a reburning reduction zone;
C、生物质颗粒在再燃还原区低化学当量比条件下析出碳氢基、氨基等活性基团,与煤粉锅炉主燃区形成的NOx反应形成N2,同时生物质焦炭与NOx在再燃还原区发生异相还原反应,将主燃区产生的NOx还原成N2;C. Biomass particles precipitate active groups such as hydrocarbon groups and amino groups under the condition of low stoichiometric ratio in the reburning reduction zone, and react with NOx formed in the main combustion zone of the pulverized coal boiler to form N 2 . At the same time, biomass coke and NOx are in the reburning reduction A heterogeneous reduction reaction occurs in the main combustion zone, reducing the NOx produced in the main combustion zone to N 2 ;
D、从煤粉锅炉炉膛的再燃还原区上部燃尽风喷口喷入燃尽风,形成燃尽区,使未完全燃烧的可燃物完全燃烧。D. Inject the burn-out air from the burn-out air nozzle on the upper part of the reburning reduction zone of the pulverized coal boiler furnace to form a burn-off zone, so that the incompletely burned combustibles can be completely burned.
其中步骤A中所述的主燃区过量空气系数为0.8~1.0。Wherein the excess air ratio in the main combustion zone described in step A is 0.8-1.0.
在步骤B中所述的一次风30混合再循环的尾部烟气的混合物中的尾部烟气的比例为0%~100%。The proportion of the tail gas in the mixture of the
其中步骤C中所述的再燃还原区过量空气系数为0.8~0.9。Wherein the excess air ratio in the reburning reduction zone described in step C is 0.8-0.9.
其中步骤D中所述的燃尽区过量空气系数为1.15~1.2。Wherein the excess air ratio in the burnout zone described in step D is 1.15-1.2.
在上述方法中,煤粉锅炉炉膛内煤的发热量占80~90%,生物质的发热量占10~20%。In the above method, the calorific value of coal in the furnace of the pulverized coal boiler accounts for 80-90%, and the calorific value of biomass accounts for 10-20%.
在本发明的步骤B中,利用一次风与再循环尾部烟气的混合物一起将生物质喷入再燃还原区,这样不但有利于形成再燃所需的低化学当量比的条件,还能够强化生物质射流刚性和再燃还原区混合条件。In step B of the present invention, the biomass is sprayed into the reburning reduction zone together with the mixture of primary air and recirculated tail flue gas, which not only helps to form the conditions of low stoichiometric ratio required for reburning, but also can strengthen the biomass Jet rigidity and mixed conditions in the reburn reduction zone.
本发明与现有技术比较具有的优点有:Compared with the prior art, the present invention has the following advantages:
将尾部再循环烟气作为生物质再燃燃料的输送介质,有利于形成再燃还原区要求的低化学当量比条件,同时可增强再燃喷口生物质射流的刚性,强化再燃还原区的混合条件,降低对生物质种类和物性参数的要求,有利于CHi、NHi等活性基团与主燃区形成的NOx的还原反应。Using tail recirculation flue gas as the transport medium of biomass reburning fuel is conducive to the formation of low stoichiometric ratio conditions required in the reburning reduction zone. Requirements for biomass types and physical parameters are conducive to the reduction reaction of CHi, NHi and other active groups with NOx formed in the main combustion zone.
本发明直接利用生物质粉碎后的颗粒作为再燃燃料,符合国家关于生物质能的高效综合开发和利用政策,将生物质合理利用与再燃技术结合起来,降低了生物质转化过程的技术风险及成本,在基本不影响煤粉锅炉原来燃烧状况的条件下,有效的降低氮氧化物的排放。The invention directly uses the crushed biomass particles as the reburning fuel, conforms to the national high-efficiency comprehensive development and utilization policy of biomass energy, combines the rational utilization of biomass with reburning technology, and reduces the technical risk and cost of the biomass conversion process , effectively reducing the emission of nitrogen oxides under the condition of basically not affecting the original combustion conditions of pulverized coal boilers.
本发明适用于新建锅炉,以及对在运锅炉的改造。The invention is suitable for newly-built boilers and the transformation of boilers in operation.
附图说明 Description of drawings
图1是本发明的利用生物质直燃再燃与烟气再循环工艺脱硝的装置的结构示意图。Fig. 1 is a schematic structural diagram of a device for denitrification using biomass direct combustion and reburning and flue gas recirculation processes according to the present invention.
具体实施方式 Detailed ways
具体实施方式一:本实施方式的利用生物质直燃再燃与烟气再循环工艺脱硝的方法,具体步骤为:Specific implementation mode 1: The method for denitrification using biomass direct combustion and re-combustion and flue gas recirculation process in this embodiment, the specific steps are:
A、煤粉通过煤粉锅炉的燃烧器21进入煤粉锅炉炉膛底部主燃区X燃烧形成含有NOx的烟气;A. The pulverized coal enters the main combustion zone X at the bottom of the furnace of the pulverized coal boiler through the
B、利用一次风30混合再循环的尾部烟气的混合物将生物质颗粒喷入炉膛中部,形成再燃还原区Y;B. Use the mixture of
C、生物质颗粒在再燃还原区Y低化学当量比条件下析出碳氢基、氨基等活性基团,与煤粉锅炉主燃区X形成的NOx反应形成N2,同时生物质焦炭与NOx在再燃还原区Y发生异相还原反应,将主燃区X产生的NOx还原成N2;C. Biomass particles precipitate active groups such as hydrocarbon groups and amino groups under the condition of low stoichiometric ratio in the reburning reduction zone Y, and react with NOx formed in the main combustion zone X of the pulverized coal boiler to form N 2 , and at the same time, biomass coke and NOx are in A heterogeneous reduction reaction occurs in the reburning reduction zone Y, and the NOx produced in the main combustion zone X is reduced to N 2 ;
D、从煤粉锅炉炉膛的再燃还原区Y上部的燃尽风喷口23喷入燃尽风31,形成燃尽区Z,使未完全燃烧的可燃物完全燃烧。D. Inject the overburning
在步骤A中所述的主燃区X过量空气系数为0.8~1.0。The excess air ratio of the main combustion zone X described in step A is 0.8-1.0.
在步骤B中所述的一次风30混合再循环的尾部烟气的混合物中的尾部烟气的比例为0%~100%。The proportion of the tail gas in the mixture of the
在步骤C中所述的再燃还原区Y过量空气系数为0.8~0.9。The excess air ratio in the reburning reduction zone Y in step C is 0.8-0.9.
在步骤D中所述的燃尽区Z过量空气系数为1.15~1.2。The excess air ratio of the burnout zone Z in step D is 1.15-1.2.
在上述方法中,煤粉锅炉炉膛内煤的发热量占80~90%,生物质的发热量占10~20%。In the above method, the calorific value of coal in the furnace of the pulverized coal boiler accounts for 80-90%, and the calorific value of biomass accounts for 10-20%.
在所述步骤B中,利用一次风30混合再循环的尾部烟气的混合物将生物质颗粒喷入再燃还原区Y,这样不但有利于形成再燃所需的低化学当量比的条件,还能够强化生物质射流刚性和再燃还原区Y混合条件。In the step B, the biomass particles are sprayed into the reburning reduction zone Y by using the mixture of the
用于该方法的利用生物质直燃再燃与烟气再循环工艺脱硝的装置,由生物质给料装置1、煤粉锅炉2以及其之间的连接和再循环引风机3组成,所述生物质给料装置1的出料口和一次风进风管道4连通,一次风进风管道4的一端和再燃燃料喷口22连通,再循环引风机3的进风口和煤粉锅炉2的尾部烟道27连通,再循环引风机3的出风口和一次风进风管道4连通。The device for denitrification using biomass direct combustion and reburning and flue gas recirculation process for this method is composed of
现有的煤粉锅炉2的炉膛分为主燃区X、再燃还原区Y和燃尽区Z。本实施方式利用廉价、易得的生物质进行简单的粉碎加工后作为再燃的原料,采用再循环尾部烟气和一次风30混合作为生物质的输送介质,不但能够增强再燃喷口22射流的刚性、强化再燃还原区Y的混合条件,还有利于CHi、NHi等活性基团与主燃区X形成NOx的还原反应。再燃还原区Y喷入的生物质在低过量空气系数条件下,不完全燃烧,形成稳定的再燃还原区Y还原性气氛,同时生物质中的钾、钠等碱金属氧化物对NOx还原反应具有良好的催化作用。煤粉锅炉2内主燃区X形成的含有NOx的烟气进入再燃还原区Y后,烟气中的NOx与再燃喷口22喷入的生物质析出的挥发分发生同相反应,与析出挥发分的生物质焦炭发生异相反应,形成含有N2的气体。该气体进入燃尽区Z后,由于有燃尽风31经燃尽风喷口23喷入该区,因此来自再燃还原区Y的烟气中未燃尽的可燃物质在该区进一步燃烧,热的烟气分别经过过热器24、省煤器25、空气预热器26进行热交换,最后经除尘器28净化,在排风机的作用下经过烟囱排出。再循环引风机3的入口可以和空气预热器26与除尘器28之间的尾部烟道连通,或者和空气预热器26之前的尾部烟道27段连通。由于生物质颗粒的部分输送介质补充了部分尾部烟气,所以本发明实现了生物质再燃脱硝和烟气再循环脱硝的双重功能。The furnace of the existing pulverized coal boiler 2 is divided into a main combustion zone X, a reburning reduction zone Y and a burnout zone Z. In this embodiment, cheap and easy-to-obtain biomass is used as a raw material for reburning after simple crushing and processing, and the mixture of recirculated tail flue gas and
具体实施方式二:本实施方式的利用生物质直燃再燃与烟气再循环工艺脱硝的装置与具体实施方式一的区别在于,所述给料装置1由给料仓11和绞龙12组成,所述绞龙12固定在给料仓11内的底部,绞龙12的出口与一次风进风管道4连通。Specific embodiment 2: The difference between the denitrification device using biomass direct combustion and reburning and flue gas recirculation process in this embodiment and the
具体实施方式三:本实施方式的利用生物质直燃再燃与烟气再循环工艺脱硝的装置与具体实施方式一的区别在于,还包括生物质粉碎装置5和埋刮板提升机6,所述生物质粉碎装置5的出口通过埋刮板提升机6与生物质给料装置1的入口连接。生物质通过生物质粉碎装置5粉碎之后,通过埋刮板提升机6输送到生物质给料装置1中。Specific embodiment three: The difference between the denitrification device using biomass direct combustion and reburning and flue gas recirculation process in this embodiment and specific embodiment one is that it also includes a
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2007
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CN102364246A (en) * | 2011-04-25 | 2012-02-29 | 南京师范大学 | Method and system for collectively removing NOx and mercury (Hg) in coal-fired flue gas by utilizing secondary combustion of biomass charcoal |
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