CN104896470A - Pulverized coal fired boiler with ultralow nitric oxide emission - Google Patents
Pulverized coal fired boiler with ultralow nitric oxide emission Download PDFInfo
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- 239000003245 coal Substances 0.000 title claims abstract description 31
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title abstract description 29
- 239000003054 catalyst Substances 0.000 claims abstract description 48
- 238000010438 heat treatment Methods 0.000 claims abstract description 32
- 239000003638 chemical reducing agent Substances 0.000 claims abstract description 30
- 238000006243 chemical reaction Methods 0.000 claims abstract description 18
- 229910002091 carbon monoxide Inorganic materials 0.000 claims abstract description 17
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 13
- 239000003546 flue gas Substances 0.000 claims abstract description 13
- 238000006722 reduction reaction Methods 0.000 claims abstract description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 7
- 238000002485 combustion reaction Methods 0.000 claims description 23
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 9
- 239000007789 gas Substances 0.000 claims description 8
- 229910052760 oxygen Inorganic materials 0.000 claims description 7
- 238000000034 method Methods 0.000 claims description 6
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 5
- 238000007254 oxidation reaction Methods 0.000 claims description 5
- 239000001301 oxygen Substances 0.000 claims description 5
- 230000003197 catalytic effect Effects 0.000 claims description 4
- 229910052761 rare earth metal Inorganic materials 0.000 claims description 3
- 238000005507 spraying Methods 0.000 claims description 3
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 2
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims description 2
- 229910052782 aluminium Inorganic materials 0.000 claims description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 2
- 238000006555 catalytic reaction Methods 0.000 claims description 2
- 239000010941 cobalt Substances 0.000 claims description 2
- 229910017052 cobalt Inorganic materials 0.000 claims description 2
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims description 2
- 229910052802 copper Inorganic materials 0.000 claims description 2
- 239000010949 copper Substances 0.000 claims description 2
- 229910052742 iron Inorganic materials 0.000 claims description 2
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims description 2
- 229910044991 metal oxide Inorganic materials 0.000 claims description 2
- 150000004706 metal oxides Chemical class 0.000 claims description 2
- 239000000203 mixture Substances 0.000 claims description 2
- 229910052759 nickel Inorganic materials 0.000 claims description 2
- 230000003647 oxidation Effects 0.000 claims description 2
- 150000002910 rare earth metals Chemical class 0.000 claims description 2
- 239000010936 titanium Substances 0.000 claims description 2
- 229910052719 titanium Inorganic materials 0.000 claims description 2
- 238000003466 welding Methods 0.000 claims description 2
- GQPLMRYTRLFLPF-UHFFFAOYSA-N Nitrous Oxide Chemical class [O-][N+]#N GQPLMRYTRLFLPF-UHFFFAOYSA-N 0.000 claims 9
- 206010021143 Hypoxia Diseases 0.000 claims 1
- 238000001994 activation Methods 0.000 claims 1
- 239000004411 aluminium Substances 0.000 claims 1
- 230000008859 change Effects 0.000 claims 1
- 230000008021 deposition Effects 0.000 claims 1
- 239000002737 fuel gas Substances 0.000 claims 1
- 208000018875 hypoxemia Diseases 0.000 claims 1
- 229910001404 rare earth metal oxide Inorganic materials 0.000 claims 1
- 238000005728 strengthening Methods 0.000 claims 1
- 238000004519 manufacturing process Methods 0.000 abstract description 9
- 238000005516 engineering process Methods 0.000 abstract description 8
- 125000002924 primary amino group Chemical group [H]N([H])* 0.000 abstract description 4
- 230000007613 environmental effect Effects 0.000 abstract description 3
- 238000010248 power generation Methods 0.000 abstract description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 12
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 9
- 229910052757 nitrogen Inorganic materials 0.000 description 7
- 229910021529 ammonia Inorganic materials 0.000 description 5
- 238000010531 catalytic reduction reaction Methods 0.000 description 4
- 230000009467 reduction Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000010586 diagram Methods 0.000 description 2
- 238000009418 renovation Methods 0.000 description 2
- AKEJUJNQAAGONA-UHFFFAOYSA-N sulfur trioxide Chemical compound O=S(=O)=O AKEJUJNQAAGONA-UHFFFAOYSA-N 0.000 description 2
- 230000009471 action Effects 0.000 description 1
- 230000009849 deactivation Effects 0.000 description 1
- 238000004134 energy conservation Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
Abstract
一种超低氮氧化物排放的煤粉锅炉,属于燃煤发电环保技术领域,该煤粉锅炉包括炉膛、锅炉燃烧器、炉内水冷壁受热面、屏式受热面和对流受热面,锅炉燃烧器为带有还原剂发生装置的锅炉燃烧器,能够生成还原剂CO,使得NO和CO发生还原反应,实现烟气脱硝;锅炉燃烧器包括低氮燃烧器LNB和燃尽风OFA,利用低氮燃烧器LNB深度空气分级以减少NO的原始生成量,利用燃尽风OFA调节还原剂CO与NO的摩尔比;炉内水冷壁受热面、屏式受热面和对流受热面沿烟气流程方向附着催化剂层或在尾部烟道设置独立催化剂层;本发明系统结构简单、运行稳定,无需使用氨基还原剂即可完成脱硝反应,脱硝效率高、显著降低脱硝成本,广泛适用于不同规模等级的煤粉锅炉。
A pulverized coal boiler with ultra-low nitrogen oxide emissions belongs to the field of environmental protection technology for coal-fired power generation. The burner is a boiler burner with a reducing agent generator, which can generate CO as a reducing agent, so that NO and CO can undergo a reduction reaction to achieve flue gas denitrification; Burner LNB deep air classification to reduce the original production of NO, and use the overfired air OFA to adjust the molar ratio of reducing agent CO to NO; the heating surface of the water wall, panel heating surface and convection heating surface in the furnace are attached along the flow direction of the flue gas A catalyst layer or an independent catalyst layer is set in the tail flue; the system of the present invention has a simple structure and stable operation, and can complete the denitrification reaction without using an amino reducing agent. The denitrification efficiency is high, and the denitrification cost is significantly reduced. boiler.
Description
技术领域technical field
本发明属于燃煤发电环保技术领域,具体涉及一种超低氮氧化物排放的煤粉锅炉。The invention belongs to the technical field of coal-fired power generation and environmental protection, and in particular relates to a pulverized coal boiler with ultra-low emission of nitrogen oxides.
背景技术Background technique
随着国家对环保的日益重视,火电厂的污染物排放控制越来越严格。根据《煤电节能减排升级与改造行动计划(2014-2020年)》,中东部地区新建燃煤发电机组NOx排放要达到燃气机组排放限值(50mg/m3),超低排放将是未来燃煤电站发展的趋势。With the country's increasing emphasis on environmental protection, the control of pollutant emissions from thermal power plants is becoming more and more stringent. According to the "Coal Power Energy Conservation and Emission Reduction Upgrading and Transformation Action Plan (2014-2020)", the NO x emission of new coal-fired power generation units in the central and eastern regions must reach the emission limit of gas-fired units (50mg/m 3 ), and the ultra-low emission will be The development trend of coal-fired power stations in the future.
目前,煤粉锅炉的脱硝方式主要采用低氮燃烧技术结合选择性催化还原脱硝技术(SCR)或选择性非催化还原脱硝技术(SNCR)。选择性非催化还原脱硝技术(SNCR)无需使用催化剂,对锅炉本体改动少、成本低,但由于煤粉锅炉中还原剂与NO混合均匀性差,反应时间短,脱硝效率仅为30~40%。只有循环流化床锅炉上才能实现70~80%的脱硝效率,因此其在使用上受到了很大的限制。At present, the denitrification method of pulverized coal boiler mainly adopts low nitrogen combustion technology combined with selective catalytic reduction denitrification technology (SCR) or selective non-catalytic reduction denitrification technology (SNCR). Selective non-catalytic reduction denitrification technology (SNCR) does not require the use of catalysts, requires few changes to the boiler body, and is low in cost. However, due to the poor mixing uniformity of the reducing agent and NO in the pulverized coal boiler, the reaction time is short, and the denitrification efficiency is only 30-40%. Only circulating fluidized bed boilers can achieve 70-80% denitrification efficiency, so its use is greatly restricted.
选择性催化还原脱硝技术(SCR)是目前煤粉锅炉的主流脱硝技术,市场占有率超过95%,脱硝效率一般能达到80~90%,但其在使用中也存在一些问题:Selective catalytic reduction denitration technology (SCR) is currently the mainstream denitrification technology for pulverized coal boilers, with a market share of more than 95%, and the denitrification efficiency can generally reach 80-90%, but there are some problems in its use:
⑴需要在锅炉尾部烟道布置催化剂层,改造项目施工难度大,且催化剂层存在本体阻力、影响了机组的运行经济性;(1) It is necessary to arrange a catalyst layer in the flue at the tail of the boiler. The reconstruction project is difficult to construct, and the catalyst layer has body resistance, which affects the operating economy of the unit;
⑵催化剂有使用寿命,失活后需要定期更换,后续成本高,且失活脱硝催化剂难再生和处理,容易造成环境污染;(2) The catalyst has a service life, and needs to be replaced regularly after deactivation, resulting in high follow-up costs, and it is difficult to regenerate and dispose of the deactivated denitrification catalyst, which is likely to cause environmental pollution;
⑶采用氨作为还原剂后容易发生氨逃逸,由于催化剂会氧化生成三氧化硫,与氨反应粘附在受热面上;(3) When ammonia is used as the reducing agent, it is easy to escape ammonia, because the catalyst will be oxidized to generate sulfur trioxide, which will react with ammonia and adhere to the heating surface;
⑷脱硝反应需要使用氨基还原剂,运行成本高、有潜在的安全问题,且氨基还原剂在生产过程中本身就需要消耗大量的能量,对环境也存在污染。(4) The denitrification reaction requires the use of an amino reducing agent, which has high operating costs and potential safety issues, and the amino reducing agent itself needs to consume a lot of energy in the production process, and also pollutes the environment.
发明内容Contents of the invention
为了解决上述现有技术存在的问题,本发明的目的在于提供一种超低氮氧化物排放的煤粉锅炉,结构简单、运行稳定,无需使用氨基还原剂即可完成脱硝反应,脱硝效率高、不增加运行成本,可用于现有煤粉锅炉改造,也可用于新建煤粉锅炉的设计。In order to solve the problems existing in the above-mentioned prior art, the object of the present invention is to provide a pulverized coal boiler with ultra-low nitrogen oxide emissions, which has a simple structure and stable operation, and can complete the denitrification reaction without using an amino reducing agent, and has high denitrification efficiency, It does not increase operating costs, and can be used for the renovation of existing pulverized coal boilers, and can also be used for the design of new pulverized coal boilers.
为了达到上述目的,本发明采用如下技术方案:In order to achieve the above object, the present invention adopts following technical scheme:
一种超低氮氧化物排放的煤粉锅炉,包括炉膛1、锅炉燃烧器2以及设置在炉膛1内的水冷壁受热面3、屏式受热面4和对流受热面5;A pulverized coal boiler with ultra-low nitrogen oxide emissions, comprising a furnace 1, a boiler burner 2, and a water wall heating surface 3, a panel heating surface 4 and a convection heating surface 5 arranged in the furnace 1;
所述锅炉燃烧器2为带有还原剂发生装置的锅炉燃烧器,能够生成还原剂CO,使得NO和CO在锅炉本身带有的催化剂的催化作用下发生还原反应,实现烟气脱硝;同时催化剂能够促进烟气中的CO与O2发生氧化反应生成CO2,从而降低锅炉的可燃气体未完全燃烧热损失,提高锅炉热效率并使CO排放控制在允许范围;烟气中的NO与CO发生还原反应的主要反应方程式为2CO+2NO→N2+2CO2,有效反应温度区间为80℃~1400℃。The boiler burner 2 is a boiler burner with a reducing agent generating device, which can generate the reducing agent CO, so that NO and CO undergo a reduction reaction under the catalysis of the catalyst carried by the boiler itself, and realize flue gas denitrification; It can promote the oxidation reaction of CO and O 2 in the flue gas to generate CO 2 , thereby reducing the incomplete combustion heat loss of the boiler, improving the thermal efficiency of the boiler and controlling the CO emission within the allowable range; the reduction of NO and CO in the flue gas The main reaction equation of the reaction is 2CO+2NO→N 2 +2CO 2 , and the effective reaction temperature range is 80°C to 1400°C.
所述锅炉燃烧器2包括低氮燃烧器LNB和燃尽风OFA,利用低氧和空气深度分级燃烧不仅减少NO的原始生成量,而且在燃烧过程中产生CO还原剂,并利用燃尽风OFA调节还原剂CO与NO的摩尔比;The boiler burner 2 includes a low-nitrogen burner LNB and an overfired air OFA, utilizing low oxygen and deep air staged combustion to not only reduce the original production of NO, but also to produce a CO reducing agent during the combustion process, and utilize the overfired air OFA Adjust the molar ratio of reducing agent CO and NO;
所述水冷壁受热面3、屏式受热面4和对流受热面5表面的金属氧化物经过活化处理,具有良好的催化性能,能够促进烟气中的CO与O2发生氧化反应生成CO2,从而回收化学不完全损失q3,提高锅炉热效率并使CO排放控制在允许范围;同时促进烟气中的NO与CO等发生还原反应;The metal oxides on the surface of the water-cooled wall heating surface 3, the panel heating surface 4 and the convection heating surface 5 have been activated and have good catalytic performance, which can promote the oxidation reaction of CO and O 2 in the flue gas to generate CO 2 , In this way, the chemical incomplete loss q 3 can be recovered, the thermal efficiency of the boiler can be improved and the CO emission can be controlled within the allowable range; at the same time, the reduction reaction of NO and CO in the flue gas can be promoted;
对于难燃煤种,为加强脱硝反应效率,沿烟气流程方向的水冷壁受热面3、屏式受热面4和对流受热面5上设置附着催化剂层A或在尾部烟道设置独立催化剂层B;For difficult-to-combustible coals, in order to enhance the denitrification reaction efficiency, an attached catalyst layer A is installed on the water-cooled wall heating surface 3, panel heating surface 4, and convection heating surface 5 along the flue gas flow direction, or an independent catalyst layer B is installed on the tail flue. ;
所述锅炉排烟中氧浓度为0~4.5%,因此排烟热损失较常规煤粉锅炉低,锅炉排烟热损失为1%~4%;The oxygen concentration in the exhaust gas of the boiler is 0-4.5%, so the heat loss of the exhaust gas is lower than that of a conventional pulverized coal boiler, and the heat loss of the boiler exhaust gas is 1%-4%;
所述煤粉锅炉通过控制燃烧总氧量和空气深度分级燃烧,使锅炉排烟热损失q2及灰渣未完全燃烧热损失q4之和最小,而常规煤粉锅炉要求排烟热损失q2、灰渣未完全燃烧热损失q4及化学不完全燃烧热损失q3之和为最小;由于产生CO而形成的化学不完全燃烧热损失q3则通过在炉内的催化氧化形成CO2得以回收,从而提高锅炉热效率。The pulverized coal boiler minimizes the sum of the boiler exhaust heat loss q 2 and the incomplete combustion heat loss q 4 of the boiler by controlling the total amount of combustion oxygen and the air depth staged combustion, while the conventional pulverized coal boiler requires the exhaust heat loss q 2. The sum of the incomplete combustion heat loss q 4 of ash and slag and the chemical incomplete combustion heat loss q 3 is the minimum; the chemical incomplete combustion heat loss q 3 due to the generation of CO is formed by catalytic oxidation in the furnace to form CO 2 Can be recycled, thereby improving the thermal efficiency of the boiler.
所述燃尽风OFA调节还原剂CO与NO的摩尔比的方法为:增加燃尽风OFA是位于低氮燃烧器LNB上部的一股单独送入的热风,增加燃尽风OFA的总风量可以降低还原剂CO与NO的摩尔比,减少燃尽风OFA的总风量可以增加还原剂CO与NO的摩尔比。The method for adjusting the molar ratio of the reductant CO to NO by the overfired air OFA is as follows: increasing the overfired air OFA is a separately sent hot air located at the top of the low-nitrogen burner LNB, and increasing the total air volume of the overfired air OFA can Reducing the molar ratio of reducing agent CO to NO and reducing the total air volume of overfired air OFA can increase the molar ratio of reducing agent CO to NO.
所述还原剂CO与NO的摩尔比为(0.5~6):1。The molar ratio of the reducing agent CO to NO is (0.5-6):1.
所述锅炉燃烧器2生成的还原剂CO浓度为100~1000ppm,锅炉燃烧器2区域的过量空气系数为0.5~0.8,炉膛1出口过量空气系数为1.0~1.2。The reducing agent CO concentration generated by the boiler burner 2 is 100-1000 ppm, the excess air coefficient in the area of the boiler burner 2 is 0.5-0.8, and the excess air coefficient at the outlet of the furnace 1 is 1.0-1.2.
所述附着催化剂层A和独立催化剂层B的表面温度为200℃~1000℃。The surface temperature of the attached catalyst layer A and the independent catalyst layer B is 200°C to 1000°C.
所述附着催化剂层A和独立催化剂层B为铁、铜、镍、锰、钴、钛、铝或稀土金属及其氧化物的多种混合物,根据反应温度和布置位置的变化有所不同。The attached catalyst layer A and the independent catalyst layer B are various mixtures of iron, copper, nickel, manganese, cobalt, titanium, aluminum or rare earth metals and their oxides, which vary according to the reaction temperature and arrangement position.
所述附着催化剂层A附着在炉内水冷壁受热面3、屏式受热面4和对流受热面5的全部外表面或部分外表面。The attached catalyst layer A is attached to all or part of the outer surfaces of the water wall heating surface 3 , the panel heating surface 4 and the convection heating surface 5 in the furnace.
所述附着催化剂层A采用喷涂、熔敷或堆焊方式附着,附着层厚度为0.1~5mm。The attached catalyst layer A is attached by spraying, welding or surfacing, and the thickness of the attached layer is 0.1-5mm.
所述独立催化剂层B采用板式催化或蜂窝催化剂,布置一层或多层。The independent catalyst layer B adopts plate type catalyst or honeycomb catalyst, arranged in one or more layers.
本发明的核心内容是通过对炉膛燃烧工况的调整,即利用低氮燃烧器LNB深度空气分级以减少NO的原始生成量,利用燃尽风OFA调节还原剂CO与NO的摩尔比,促使还原反应发生,在保证与氨法脱硝技术相近的脱硝效率同时,大幅度降低脱硝装置成本和脱硝花费。The core content of the present invention is to adjust the combustion conditions of the furnace, that is, to use the low-nitrogen burner LNB deep air classification to reduce the original production of NO, and to use the overfired air OFA to adjust the molar ratio of the reducing agent CO and NO to promote the reduction. The reaction occurs, while ensuring the denitrification efficiency similar to that of the ammonia denitrification technology, the cost of the denitrification device and the cost of denitrification are greatly reduced.
和现有技术相比较,本发明具备如下优点:Compared with the prior art, the present invention has the following advantages:
1、采用深度分级燃烧等方式,在炉膛中实现更低的氮排放,降低生成的烟气NOx浓度。1. Adopt deep staged combustion and other methods to achieve lower nitrogen emissions in the furnace and reduce the NOx concentration of the generated flue gas.
2、采用CO替代NH3作为脱硝还原剂,避免了氨源的安全隐患,系统简单,CO为燃烧产物、运行成本低廉。2. Using CO instead of NH3 as the denitrification reducing agent avoids the safety hazard of ammonia source, the system is simple, CO is a combustion product, and the operating cost is low.
3、采用附着催化剂层方式时可以不设置独立催化剂床层,大幅度降低炉膛改造成本,高效利用有限的炉膛空间。3. When the method of attaching the catalyst layer is adopted, it is not necessary to set up an independent catalyst bed, which greatly reduces the cost of furnace renovation and efficiently utilizes the limited furnace space.
4、催化剂采用廉价金属及其氧化物,大幅度降低催化剂成本。4. The catalyst uses cheap metals and their oxides, which greatly reduces the cost of the catalyst.
5、催化剂不包含重金属,废弃后无处置问题。5. The catalyst does not contain heavy metals, and there is no disposal problem after being discarded.
附图说明Description of drawings
图1为本发明的实例1的布置示意图。Fig. 1 is a schematic layout diagram of Example 1 of the present invention.
图2为本发明的实例2的布置示意图。Fig. 2 is a schematic layout diagram of Example 2 of the present invention.
具体实施方式Detailed ways
下面结合附图和具体实施例对本发明做进一步详细说明。The present invention will be described in further detail below in conjunction with the accompanying drawings and specific embodiments.
实施例1Example 1
如图1所示的超低氮氧化物排放的煤粉锅炉,包括炉膛1、带有还原剂发生装置的锅炉燃烧器2以及设置在炉膛1内的水冷壁受热面3、屏式受热面4和对流受热面5。锅炉运行期间利用低氮燃烧器LNB深度空气分级,燃烧过量空气系数为0.6,NO的原始生成量为120ppm,利用燃尽风OFA调节CO与NO的摩尔比为2.5,CO生成浓度为300ppm,燃烧区域温度1100℃。为提高脱硝反应效率,在屏式受热面4上熔敷附着了1mm厚度的附着催化剂层A,屏式受热面4的表面温度为750℃,附着催化剂层的主要成份是Fe2O3和CuO。经过脱硝反应后NO排放浓度降低至20ppm,脱硝效率83%。The pulverized coal boiler with ultra-low nitrogen oxide emission as shown in Figure 1 includes a furnace 1, a boiler burner 2 with a reducing agent generator, and a water-cooled wall heating surface 3 and a panel heating surface 4 installed in the furnace 1 And convection heating surface 5. During the operation of the boiler, the low-nitrogen burner LNB deep air classification is used, the excess air coefficient of combustion is 0.6, the original production of NO is 120ppm, the molar ratio of CO and NO is adjusted to 2.5 by using the overfired air OFA, and the concentration of CO production is 300ppm. The regional temperature is 1100°C. In order to improve the efficiency of the denitration reaction, a 1mm-thick attached catalyst layer A is deposited on the screen-type heating surface 4. The surface temperature of the screen-type heating surface 4 is 750°C, and the main components of the attached catalyst layer are Fe 2 O 3 and CuO . After the denitration reaction, the NO emission concentration is reduced to 20ppm, and the denitration efficiency is 83%.
实施例2Example 2
如图2所示的超低氮氧化物排放的煤粉锅炉,为提高脱硝效率设置了独立的独立催化剂层B,独立催化剂层B采用蜂窝催化剂,布置1层,附着催化剂层的主要成份是Fe2O3和稀土元素的氧化物。经过脱硝反应后NO排放浓度降低至10ppm,脱硝效率提高至92%。As shown in Figure 2, the pulverized coal boiler with ultra-low nitrogen oxide emissions is equipped with an independent independent catalyst layer B to improve the denitrification efficiency. The independent catalyst layer B adopts honeycomb catalysts and is arranged in one layer. The main component of the attached catalyst layer is Fe 2 O 3 and oxides of rare earth elements. After the denitration reaction, the NO emission concentration is reduced to 10ppm, and the denitration efficiency is increased to 92%.
实施例3Example 3
本实施例超低氮氧化物排放的煤粉锅炉,低氮燃烧器LNB燃烧过量空气系数为0.8,NO的原始生成量为200ppm,利用燃尽风OFA调节CO与NO的摩尔比为3,对应CO生成浓度为600ppm,燃烧区域温度1200℃。在屏式受热面4和对流受热面5上采用熔敷附着了1.5mm厚度的附着催化剂层A,屏式受热面4的表面温度为800℃,对流受热面5的表面温度为600℃,附着催化剂层的主要成份是Fe2O3和CuO。经过脱硝反应后NO排放浓度降低至50ppm,脱硝效率75%。In the pulverized coal boiler with ultra-low nitrogen oxide emissions in this embodiment, the excess air coefficient of the low-nitrogen burner LNB combustion is 0.8, the original production amount of NO is 200ppm, and the molar ratio of CO and NO is adjusted to 3 by using the overfired air OFA, corresponding to The CO generation concentration is 600ppm, and the combustion zone temperature is 1200°C. On the panel heating surface 4 and the convection heating surface 5, a catalyst layer A with a thickness of 1.5mm is welded and attached. The surface temperature of the panel heating surface 4 is 800°C, and the surface temperature of the convection heating surface 5 is 600°C. The main components of the catalyst layer are Fe 2 O 3 and CuO. After the denitration reaction, the NO emission concentration is reduced to 50ppm, and the denitration efficiency is 75%.
实施例4Example 4
本实施例超低氮氧化物排放的煤粉锅炉,NO的原始生成量为100ppm,CO与NO的摩尔比为2,对应CO生成浓度为200ppm。在对流受热面5上采用喷涂附着了0.5mm厚度的附着催化剂层A。经过脱硝反应后NO排放浓度降低至40ppm,脱硝效率60%。In the pulverized coal boiler with ultra-low nitrogen oxide emission in this embodiment, the original production amount of NO is 100ppm, the molar ratio of CO to NO is 2, and the corresponding CO production concentration is 200ppm. On the convective heating surface 5, a 0.5 mm-thick adhesion catalyst layer A was applied by spraying. After the denitration reaction, the NO emission concentration is reduced to 40ppm, and the denitration efficiency is 60%.
实施例5Example 5
本实施例超低氮氧化物排放的煤粉锅炉,在屏式受热面4喷涂了0.5mm的附着催化剂层A,其主要成分是Fe2O3和CuO。在对流受热面5上喷涂了1mm的附着催化剂层A,其主要成分是Fe2O3和Ni。In the pulverized coal boiler with ultra-low nitrogen oxide emissions in this embodiment, a 0.5mm adhered catalyst layer A is sprayed on the panel heating surface 4, and its main components are Fe 2 O 3 and CuO. On the convection heating surface 5, a 1 mm adhered catalyst layer A, whose main components are Fe 2 O 3 and Ni, was sprayed.
Claims (9)
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