CN108201784A - A kind of grate-type biomass power plant boiler flue gas purification tapping equipment and its method - Google Patents
A kind of grate-type biomass power plant boiler flue gas purification tapping equipment and its method Download PDFInfo
- Publication number
- CN108201784A CN108201784A CN201810177320.2A CN201810177320A CN108201784A CN 108201784 A CN108201784 A CN 108201784A CN 201810177320 A CN201810177320 A CN 201810177320A CN 108201784 A CN108201784 A CN 108201784A
- Authority
- CN
- China
- Prior art keywords
- flue gas
- desulfurization
- power plant
- grate
- desulfurizing
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/75—Multi-step processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D50/00—Combinations of methods or devices for separating particles from gases or vapours
- B01D50/20—Combinations of devices covered by groups B01D45/00 and B01D46/00
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/54—Nitrogen compounds
- B01D53/56—Nitrogen oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/80—Semi-solid phase processes, i.e. by using slurries
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C9/00—Combustion apparatus characterised by arrangements for returning combustion products or flue gases to the combustion chamber
- F23C9/06—Combustion apparatus characterised by arrangements for returning combustion products or flue gases to the combustion chamber for completing combustion
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
- F23J15/022—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow
- F23J15/025—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow using filters
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
- F23J15/04—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material using washing fluids
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/10—Oxidants
- B01D2251/104—Ozone
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Biomedical Technology (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Treating Waste Gases (AREA)
- Chimneys And Flues (AREA)
Abstract
本发明公开了一种炉排式生物质电站锅炉烟气净化排放装置及其方法,包括:生物质锅炉、氧化混合装置、脱硫塔、布袋除尘器、以及烟囱,生物质锅炉上设置有一次风口以及二次风口,生物质锅炉的出口通过氧化混合装置与脱硫塔相连接,脱硫塔的出口与布袋除尘器相连,布袋除尘器的出口第一支路与烟囱相连接,第二支路通过再循环风机与生物质锅炉一次风口以及二次风口相连接,形成循环回路;通过对脱硫、脱硝、除尘工艺的优化,实现生物质锅炉烟气二氧化硫、氮氧化物和粉尘等污染物超低排放。本发明对锅炉影响较小,根据负荷和实际污染物情况灵活运行,方便整个生物质电厂系统的运行管理,操作灵活,节水、节约运行成本。
The invention discloses a grate type biomass power plant boiler flue gas purification and discharge device and method thereof, comprising: a biomass boiler, an oxidation mixing device, a desulfurization tower, a bag filter, and a chimney, and a primary tuyere is arranged on the biomass boiler And the secondary air outlet, the outlet of the biomass boiler is connected to the desulfurization tower through the oxidation mixing device, the outlet of the desulfurization tower is connected to the bag filter, the first branch of the outlet of the bag filter is connected to the chimney, and the second branch passes through The circulation fan is connected with the primary tuyere and the secondary tuyere of the biomass boiler to form a circulation loop; through the optimization of desulfurization, denitration and dust removal processes, ultra-low emissions of pollutants such as sulfur dioxide, nitrogen oxides and dust in the flue gas of the biomass boiler are realized. The invention has little influence on the boiler, operates flexibly according to the load and actual pollutant conditions, facilitates the operation management of the whole biomass power plant system, is flexible in operation, saves water and saves operating costs.
Description
技术领域technical field
本发明涉及电站尾气排放领域,尤其涉及一种一种炉排式生物质电站锅炉烟气净化排放装置及其方法。The invention relates to the field of power station tail gas discharge, in particular to a grate type biomass power plant boiler flue gas purification and discharge device and method thereof.
背景技术Background technique
生物质锅炉是以生物质能源如农作物秸秆(玉米秸、高粱秸、麦秸、稻草、豆秸和棉秆等)、农业加工业的废弃物(稻壳)等作燃料的锅炉。生物质能源特点是可再生性、低污染性、广泛分布性、总量十分丰富。生物质锅炉排放烟气中二氧化硫、氮氧化物含量较低,但随着国家对锅炉烟气排放环保标准的提高,生物质锅炉已经不适应新的环保要求。Biomass boilers are boilers that use biomass energy such as crop stalks (corn stalks, sorghum stalks, wheat straw, rice straw, bean stalks, and cotton stalks, etc.), agricultural processing industry waste (rice husks), etc. as fuel. Biomass energy is characterized by renewability, low pollution, wide distribution and abundant total amount. The content of sulfur dioxide and nitrogen oxides in the exhaust gas of biomass boilers is relatively low, but with the improvement of national environmental protection standards for boiler flue gas emissions, biomass boilers have not adapted to the new environmental protection requirements.
生物质锅炉烟气具有以下的特点:Biomass boiler flue gas has the following characteristics:
(1)炉内温度差别大,生物质锅炉主要有炉排炉和循环流化床炉,每种炉型又分为中温中压炉、次高温次高压炉、高温高压炉,炉膛温度分别为700~760℃、800~950℃、850~1100℃;(1) The temperature in the furnace varies greatly. Biomass boilers mainly include grate furnace and circulating fluidized bed furnace. 700~760℃, 800~950℃, 850~1100℃;
(2)烟气含湿量高,因生物质中氢元素含量较高,烟气中湿含量也高,可达到15%~30%左右,而燃煤锅炉烟气湿含量不会超过10%;(2) The moisture content of the flue gas is high. Because the hydrogen content in the biomass is high, the moisture content in the flue gas is also high, which can reach about 15% to 30%, while the moisture content of the flue gas from a coal-fired boiler will not exceed 10%. ;
(3)烟气粉尘量很大,生物质燃烧后的灰渣比在(10:0~8:2),由于燃烧粉尘粒径小,比电阻大两个原因,燃生物质锅炉除尘只适合袋式除尘器,堆积密度一般在0.18-0.5t/m3。研究表明生物质燃烧排放颗粒物的主要成分有K2SO4、KCl和K2CO3,排放浓度一般在200mg/m3左右。烟尘中碱金属含量高,可达8%以上。(3) The amount of flue gas dust is very large, and the ash-slag ratio after biomass combustion is (10:0-8:2). Due to the small particle size of the combustion dust and the large specific resistance, the dust removal of biomass-fired boilers is only suitable For bag filter, the bulk density is generally 0.18-0.5t/m 3 . Studies have shown that the main components of particulate matter emitted by biomass combustion are K2SO4, KCl and K2CO3, and the emission concentration is generally around 200mg/m3. The content of alkali metal in the soot is high, which can reach more than 8%.
(4)二氧化硫、氮氧化物浓度低、且波动大,燃烧纯生物质时二氧化硫、氮氧化物含量在100~250mg/m3之间波动,如燃料中掺杂模板、木材、树皮等,烟气中二氧化硫、氮氧化物含量会在250~600mg/m3之间波动,瞬时也可达1000mg/m3以上;(4) The concentrations of sulfur dioxide and nitrogen oxides are low and fluctuate greatly. When burning pure biomass, the contents of sulfur dioxide and nitrogen oxides fluctuate between 100 and 250mg/m3. The content of sulfur dioxide and nitrogen oxides in the air will fluctuate between 250-600mg/m3, and it can reach more than 1000mg/m3 instantaneously;
(5)烟气中烟尘易二次燃烧,燃烧易结焦。由于生物质不能在炉内完全燃烧,在烟道里也由于氧含量不够不能再次燃烧,较大粉尘由于烟气热交换时间很短会保持着燃烧温度,所以一旦在氧条件具备,比如放置于空气中会再次燃烧。燃烧后灰分含有焦油等物质,设备一旦温度降低,就可能产生结焦现象,造成堵塞现象,由于考虑到锅炉结焦及腐蚀问题,排烟温度可能会在160-190℃。(5) The soot in the flue gas is easy to burn again, and the combustion is easy to coke. Since biomass cannot be completely combusted in the furnace, it cannot be re-combusted in the flue due to insufficient oxygen content. The larger dust will maintain the combustion temperature due to the short heat exchange time of the flue gas. Therefore, once the oxygen condition is met, such as placed in the air will burn again. The ash after combustion contains tar and other substances. Once the temperature of the equipment drops, it may cause coking and blockage. Considering the coking and corrosion of the boiler, the exhaust gas temperature may be 160-190 °C.
(6)一般燃料燃烧排放的NOx类型可分为快速型NOx、热力型NOx及燃料型NOx。快速型NOx一般占总量的比例<5%,影响不大;燃料型NOx主要来自于燃料中含氮化合物的氧化,其生成量与燃料中氮含量密切相关,当燃料中氮的含量超过0.1%时,燃料氮转化成的NOx量将占主要地位;热力型NOx主要是高温下(>1400℃)空气中的N2氧化形成NOx(NO是NOx主要存在形式,占NOx总物质的量的90%以上)。生物质锅炉燃烧温度均在800~1000℃,因此生物质锅炉燃烧产生的NOx类型主要是燃料型NOx。研究表明生物质中的氮元素主要以蛋白质、游离氨基酸等有机氮的形式存在,同时还有部分无机氮,因此生物质燃烧产生的NOx主要来源于有机氮的氧化反应。根据相关锅炉测试资料,当锅炉烟气中含氧量为12~15%时,NOx浓度约330~420mg/m3。(6) The types of NOx emitted by general fuel combustion can be divided into rapid NOx, thermal NOx and fuel NOx. Rapid NOx generally accounts for less than 5% of the total amount, and has little impact; fuel-type NOx mainly comes from the oxidation of nitrogen-containing compounds in the fuel, and its formation is closely related to the nitrogen content in the fuel. When the nitrogen content in the fuel exceeds 0.1 %, the amount of NOx converted from fuel nitrogen will dominate; thermal NOx is mainly formed by oxidation of N2 in the air at high temperature (>1400°C) to form NOx (NO is the main form of NOx, accounting for 90% of the total amount of NOx %above). The combustion temperature of biomass boilers is 800-1000°C, so the type of NOx produced by the combustion of biomass boilers is mainly fuel-type NOx. Studies have shown that nitrogen in biomass mainly exists in the form of organic nitrogen such as protein and free amino acids, as well as some inorganic nitrogen. Therefore, NOx produced by biomass combustion mainly comes from the oxidation reaction of organic nitrogen. According to relevant boiler test data, when the oxygen content in the boiler flue gas is 12-15%, the NOx concentration is about 330-420mg/m3.
基于以上的缺点,生物质锅炉烟气对环境造成了不良的影响,为环境带来了污染。Based on the above shortcomings, the flue gas of the biomass boiler has caused adverse effects on the environment and brought pollution to the environment.
发明内容Contents of the invention
针对上述缺陷或不足,本发明的目的在于提供一种一种炉排式生物质电站锅炉烟气净化排放装置及其方法。In view of the above defects or deficiencies, the object of the present invention is to provide a grate type biomass power plant boiler flue gas purification and discharge device and its method.
为达到以上目的,本发明的技术方案为:For achieving above object, technical scheme of the present invention is:
一种炉排式生物质电站锅炉烟气净化排放装置,包括:生物质锅炉、氧化混合装置、脱硫塔、布袋除尘器、以及烟囱,其中,所述生物质锅炉上设置有一次风口以及二次风口,所述生物质锅炉的出口通过氧化混合装置与脱硫塔相连接,脱硫塔的出口与布袋除尘器相连接,布袋除尘器的出口分为两路:第一支路与烟囱相连接,第二支路通过再循环风机与生物质锅炉一次风口以及二次风口相连接,形成循环回路;所述生物质锅炉上设置有脱硝雾化喷嘴,脱硝雾化喷嘴上依次通过计量分配装置以及脱硝剂泵与脱硝剂箱相连接;所述氧化混合装置上连接有臭氧发生器以及制氧机;所述脱硫塔上设置有脱硫雾化喷嘴,脱硫雾化喷嘴上连接有脱硫浆液箱、工艺水箱以及压缩空气罐,所述脱硫浆液箱上连接有脱硫剂仓。A grate-type biomass power plant boiler flue gas purification and discharge device, comprising: a biomass boiler, an oxidation mixing device, a desulfurization tower, a bag filter, and a chimney, wherein the biomass boiler is provided with a primary tuyere and a secondary The outlet of the biomass boiler is connected to the desulfurization tower through an oxidation mixing device, the outlet of the desulfurization tower is connected to the bag filter, and the outlet of the bag filter is divided into two paths: the first branch is connected to the chimney, and the second branch is connected to the chimney. The two branches are connected with the primary tuyere and the secondary tuyere of the biomass boiler through the recirculation fan to form a circulation loop; the biomass boiler is equipped with a denitrification atomizing nozzle, and the denitrification atomizing nozzle passes through the metering distribution device and the denitrification agent in turn. The pump is connected with the denitration agent tank; the oxidation mixing device is connected with an ozone generator and an oxygen generator; the desulfurization tower is provided with desulfurization atomizing nozzles, and the desulfurization atomizing nozzles are connected with desulfurization slurry tanks, process water tanks and A compressed air tank, the desulfurization agent tank is connected to the desulfurization slurry tank.
所述脱硫塔上设置有旋风除尘器,所述旋风除尘器的出口上连接有下料器一方面与脱硫灰仓相连接,脱硫灰仓通过螺旋下料器收集灰尘;另一方通过循环灰箱与脱硫塔相连接形成回路。The desulfurization tower is equipped with a cyclone dust collector, and the outlet of the cyclone dust collector is connected with a feeder. On the one hand, it is connected with the desulfurization ash bin, and the desulfurization ash bin collects dust through the screw feeder; It is connected with the desulfurization tower to form a loop.
所述布袋除尘器的下方设置有集灰槽,集灰槽通过下料装置与脱硫灰仓相连接。An ash collecting tank is arranged below the bag filter, and the ash collecting tank is connected with the desulfurization ash bin through the unloading device.
所述脱硫剂仓的出口依次通过螺旋给料机、称重计量装置以及消化器与脱硫浆液箱入口相连接,脱硫剂仓的气体入口与压缩空气罐相连接。The outlet of the desulfurizing agent bin is connected to the inlet of the desulfurizing slurry tank through a screw feeder, a weighing and measuring device and a digester in sequence, and the gas inlet of the desulfurizing agent bin is connected to a compressed air tank.
所述消化器以及脱硫浆液箱上均连接有水源。Both the digester and the desulfurization slurry tank are connected with a water source.
所述脱硫浆液箱通过脱硫剂输送泵与脱硫雾化喷嘴相连接;所述工艺水箱通过给水泵与脱硫雾化喷嘴相连接。The desulfurization slurry tank is connected to the desulfurization atomizing nozzle through a desulfurizing agent delivery pump; the process water tank is connected to the desulfurization atomizing nozzle through a feed water pump.
所述布袋除尘器的出口处设置有引风机;第二支路通过再循环风机还与脱硫塔的入口相连接。An induced draft fan is installed at the outlet of the bag filter; the second branch is also connected to the inlet of the desulfurization tower through a recirculation fan.
所述脱硫塔的出口处设置有脱硫灰收集槽。A desulfurization ash collection tank is arranged at the outlet of the desulfurization tower.
一种炉排式生物质电站锅炉烟气净化排放方法,包括:A method for purifying and discharging flue gas from a grate type biomass power plant boiler, comprising:
1)、生物质锅炉内进行SNCR脱硝处理后,采用EAS-FGR处理工艺,将排放气体经过脱硫塔进行脱硫处理;1) After the SNCR denitrification treatment is carried out in the biomass boiler, the EAS-FGR treatment process is adopted, and the exhaust gas is desulfurized through the desulfurization tower;
2)、脱硫塔脱硫处理后的气体通过布袋除尘器除尘后,脱硫脱硝处理后的净烟气一部分通过烟囱排出,另一部分通过再循环风机送入二次风口进入炉膛二次燃烧;2) After the gas desulfurized by the desulfurization tower is dedusted by the bag filter, part of the clean flue gas after desulfurization and denitrification is discharged through the chimney, and the other part is sent to the secondary tuyere by the recirculation fan and enters the furnace for secondary combustion;
3)、臭氧发生器产生的臭氧送至氧化混合装置与烟气进行湍流混合,臭氧与烟气中的NO发生氧化还原反应,NO被转化为易吸收脱除的NO2;反应后的烟气与再循环风机的出口排出的脱硫脱硝处理后的净烟气混合,保证低负荷下流化床稳定运行、不塌床。3) The ozone generated by the ozone generator is sent to the oxidation mixing device for turbulent mixing with the flue gas, and the ozone and the NO in the flue gas undergo a redox reaction, and the NO is converted into NO2 that is easy to absorb and remove; the flue gas after the reaction is mixed with the flue gas The desulfurized and denitrified net flue gas discharged from the outlet of the recirculation fan is mixed to ensure the stable operation of the fluidized bed under low load and not to collapse the bed.
所述脱硫塔上连接有脱硫浆液箱,脱硫浆液箱中配制有浓度为10~15%脱硫浆液,脱硫浆液通过脱硫剂输送泵至脱硫雾化喷嘴,雾化后的脱硫浆液在脱硫塔与烟气污染物反应后再经去除旋风除尘器和布袋除尘器进一步除尘后进入烟囱达标排放。The desulfurization tower is connected with a desulfurization slurry tank, and the desulfurization slurry tank is prepared with a desulfurization slurry with a concentration of 10-15%. After the air pollutants are reacted, they are further dedusted by the cyclone dust collector and the bag filter, and then enter the chimney to meet the emission standards.
与现有技术比较,本发明的有益效果为:Compared with prior art, the beneficial effects of the present invention are:
本发明提供了一种炉排式生物质电站锅炉烟气净化排放装置及其方法,用于生物质锅炉烟气净化,通过对脱硫、脱硝、除尘尤其是脱硝工艺的优化设计,可实现生物质锅炉烟气二氧化硫、氮氧化物和粉尘等污染物超低排放。本发明对锅炉影响较小,既可根据负荷和实际污染物情况灵活运行,也可进行各分系统协同处理,方便整个生物质电厂系统的运行管理,其中,脱硫脱硝系统协同处理,操作灵活,便于维护,节水、节约运行成本,还能够根据生物质锅炉的烟气特点,采用源头NOx控制、SNCR脱硝、氧化强化脱硝和半干法脱硫脱硝协同NOx控制技术,解决了采用SCR脱硝工艺投资成本高、容易堵塞、运行维护困难等问题;另外,脱硫脱硝产物可作为生物质灰的Ca、S、N元素的有益补充,用作复合肥料,无二次污染。本发明性能可靠,操作灵活,便于维护,具有很好的经济效益和环境效益。The invention provides a grate-type biomass power plant boiler flue gas purification and discharge device and method thereof, which are used for biomass boiler flue gas purification. Ultra-low emissions of pollutants such as sulfur dioxide, nitrogen oxides and dust in boiler flue gas. The present invention has little influence on the boiler, and can operate flexibly according to the load and actual pollutant conditions, and can also carry out coordinated processing of each sub-system, which facilitates the operation and management of the entire biomass power plant system, wherein the coordinated processing of the desulfurization and denitrification system is flexible in operation, It is easy to maintain, save water, and save operating costs. It can also adopt source NOx control, SNCR denitrification, oxidation enhanced denitrification and semi-dry desulfurization and denitrification synergistic NOx control technology according to the flue gas characteristics of the biomass boiler, which solves the problem of adopting SCR denitrification process investment. High cost, easy blockage, difficult operation and maintenance, etc.; in addition, desulfurization and denitrification products can be used as a beneficial supplement of Ca, S, and N elements in biomass ash, and can be used as compound fertilizers without secondary pollution. The invention has reliable performance, flexible operation, convenient maintenance and good economic and environmental benefits.
附图说明Description of drawings
图1是本发明装置结构示意图。Fig. 1 is a schematic diagram of the structure of the device of the present invention.
图中,1-二次风口,2-脱硝雾化喷嘴,3-计量分配装置,4-脱硝泵,5-脱硝剂箱,6-压缩空气罐,7-脱硫剂仓,8-螺旋给料机,9-称重计量装置,10-消化器,11-脱硫浆液箱,12-脱硫剂输送泵,13-脱硫雾化喷嘴,14-脱硫塔,15-给水泵,16-工艺水箱,17-旋风除尘器,18-下料器,19-循环灰箱,20-脱硫灰仓,21-螺旋下料器,22-集灰槽,23-布袋除尘器,24-引风机,25-再循环风机,26-脱硫灰收集槽,27-氧化混合装置,28-臭氧发生器,29-制氧机,30-一次风口,31-烟囱;32-生物质锅炉。In the figure, 1-secondary air outlet, 2-denitration atomizing nozzle, 3-metering and distribution device, 4-denitration pump, 5-denitration agent box, 6-compressed air tank, 7-desulfurization agent warehouse, 8-screw feeding Machine, 9-weighing and metering device, 10-digester, 11-desulfurization slurry tank, 12-desulfurization agent delivery pump, 13-desulfurization atomizing nozzle, 14-desulfurization tower, 15-feed water pump, 16-process water tank, 17 -cyclone dust collector, 18-feeder, 19-circulating ash box, 20-desulfurization ash bin, 21-screw feeder, 22-ash collection tank, 23-bag dust collector, 24-induced fan, 25-recycling Circulation fan, 26-desulfurization ash collection tank, 27-oxidation mixing device, 28-ozone generator, 29-oxygen generator, 30-primary tuyere, 31-chimney; 32-biomass boiler.
具体实施方式Detailed ways
下面将结合附图对本发明做详细描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明的保护范围。The present invention will be described in detail below in conjunction with the accompanying drawings. Apparently, the described embodiments are only some, not all, embodiments of the present invention. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.
如图1所示,本发明提供了一种炉排式生物质电站锅炉烟气净化排放装置,包括:生物质锅炉32、氧化混合装置27、脱硫塔14、布袋除尘器23、以及烟囱31,其中,所述生物质锅炉32上设置有一次风口30以及二次风口1,所述生物质锅炉32的出口通过氧化混合装置27与脱硫塔14相连接,脱硫塔14的出口与布袋除尘器23相连接,布袋除尘器23的出口分为两路:第一支路与烟囱31相连接,第二支路通过再循环风机25与生物质锅炉32一次风口30以及二次风口1相连接,形成循环回路;所述生物质锅炉32上设置有脱硝雾化喷嘴2,脱硝雾化喷嘴2上依次通过计量分配装置3以及脱硝剂泵4与脱硝剂箱5相连接;所述氧化混合装置27上连接有臭氧发生器28以及制氧机29;所述脱硫塔14上设置有脱硫雾化喷嘴13,脱硫雾化喷嘴13上连接有脱硫浆液箱11、工艺水箱16以及压缩空气罐6,所述脱硫浆液箱11上连接有脱硫剂仓7。所述消化器10以及脱硫浆液箱11上均连接有水源,示例性的,所述水源为厂区的供水水源。As shown in Figure 1, the present invention provides a kind of grate type biomass power plant boiler flue gas purification and discharge device, comprising: biomass boiler 32, oxidation mixing device 27, desulfurization tower 14, bag filter 23, and chimney 31, Wherein, the biomass boiler 32 is provided with a primary tuyere 30 and a secondary tuyere 1, the outlet of the biomass boiler 32 is connected to the desulfurization tower 14 through an oxidation mixing device 27, and the outlet of the desulfurization tower 14 is connected to the bag filter 23 The outlet of the bag filter 23 is divided into two paths: the first branch is connected with the chimney 31, and the second branch is connected with the primary air outlet 30 and the secondary air outlet 1 of the biomass boiler 32 through the recirculation fan 25, forming circulation loop; the biomass boiler 32 is provided with a denitrification atomizing nozzle 2, and the denitrification atomizing nozzle 2 is connected to the denitrification agent tank 5 through the metering distribution device 3 and the denitration agent pump 4 in sequence; the oxidation mixing device 27 is An ozone generator 28 and an oxygen generator 29 are connected; the desulfurization tower 14 is provided with a desulfurization atomizing nozzle 13, and the desulfurization atomizing nozzle 13 is connected with a desulfurization slurry tank 11, a process water tank 16 and a compressed air tank 6. The desulfurization agent tank 7 is connected to the desulfurization slurry tank 11 . Both the digester 10 and the desulfurization slurry tank 11 are connected to a water source. Exemplarily, the water source is a water supply source of the factory area.
其中,所述脱硫塔14上设置有旋风除尘器17,所述旋风除尘器17的出口上连接有下料器18一方面与脱硫灰仓20相连接,脱硫灰仓20通过螺旋下料器21收集灰尘;另一方通过循环灰箱19与脱硫塔14相连接形成回路。所述脱硫塔14的出口处设置有脱硫灰收集槽26。Wherein, the desulfurization tower 14 is provided with a cyclone dust collector 17, and the outlet of the cyclone dust collector 17 is connected with a feeder 18. On the one hand, it is connected with the desulfurization ash bin 20, and the desulfurization ash bin 20 passes through the screw feeder 21. Dust is collected; the other side is connected to the desulfurization tower 14 through the circulating ash box 19 to form a loop. The outlet of the desulfurization tower 14 is provided with a desulfurization ash collection tank 26 .
优选地,所述布袋除尘器23的下方设置有集灰槽22,集灰槽22通过下料装置与脱硫灰仓20相连接。所述布袋除尘器23的出口处设置有引风机24;第二支路通过再循环风机25还与脱硫塔14的入口相连接。Preferably, an ash collection tank 22 is provided below the bag filter 23, and the ash collection tank 22 is connected with the desulfurization ash bin 20 through a feeding device. An induced draft fan 24 is provided at the outlet of the bag filter 23 ; the second branch is also connected to the inlet of the desulfurization tower 14 through a recirculation fan 25 .
具体的,所述脱硫剂仓7的出口依次通过螺旋给料机8、称重计量装置9以及消化器10与脱硫浆液箱11入口相连接,脱硫剂仓7的气体入口与压缩空气罐6相连接。Specifically, the outlet of the desulfurizer bin 7 is connected to the inlet of the desulfurization slurry tank 11 through a screw feeder 8, a weighing and metering device 9 and a digester 10 in sequence, and the gas inlet of the desulfurizer bin 7 is connected to the compressed air tank 6. connect.
所述脱硫浆液箱11通过脱硫剂输送泵12与脱硫雾化喷嘴13相连接;所述工艺水箱16通过给水泵15与脱硫雾化喷嘴13相连接。The desulfurization slurry tank 11 is connected to the desulfurization atomization nozzle 13 through the desulfurization agent delivery pump 12 ; the process water tank 16 is connected to the desulfurization atomization nozzle 13 through the feed water pump 15 .
本发明还提供了一种炉排式生物质电站锅炉烟气净化排放方法,包括:The present invention also provides a method for purifying and discharging flue gas from a grate type biomass power plant boiler, comprising:
1)、生物质锅炉32内进行SNCR脱硝处理后,采用EAS-FGR处理工艺,将排放气体经过脱硫塔14进行脱硫处理;1), after the SNCR denitration treatment is carried out in the biomass boiler 32, the EAS-FGR treatment process is adopted, and the exhaust gas is desulfurized through the desulfurization tower 14;
2)、脱硫塔14脱硫处理后的气体通过布袋除尘器23除尘后,脱硫脱硝处理后的净烟气一部分通过烟囱31排出,另一部分通过再循环风机25送入二次风口1进入炉膛二次燃烧;2) After the gas desulfurized by the desulfurization tower 14 is dedusted by the bag filter 23, part of the desulfurized and denitrified clean flue gas is discharged through the chimney 31, and the other part is sent into the secondary tuyere 1 through the recirculation fan 25 and enters the furnace for a second time. combustion;
3)、臭氧发生器28产生的臭氧送至氧化混合装置27与烟气进行湍流混合,臭氧与烟气中的NO发生氧化还原反应,NO被转化为易吸收脱除的NO2;反应后的烟气与再循环风机25的出口排出的脱硫脱硝处理后的净烟气混合,保证低负荷下流化床稳定运行、不塌床。3), the ozone produced by the ozone generator 28 is sent to the oxidation mixing device 27 for turbulent mixing with the flue gas, the ozone and the NO in the flue gas undergo a redox reaction, and the NO is converted into NO2 which is easy to absorb and remove; the flue gas after the reaction The gas is mixed with the desulfurized and denitrified net flue gas discharged from the outlet of the recirculation fan 25 to ensure the stable operation of the fluidized bed under low load and not to collapse the bed.
具体的,生物质锅炉32低氮采用EAS-FGR处理工艺,约15~40%经过脱硫脱硝处理后的净烟气通过再循环风机25送入二次风口1进入炉膛二次燃烧,处理后的烟气NOx浓度≤180mg/Nm3;脱硝采用炉内SNCR工艺,在脱硝剂箱5储存的脱硝剂由脱硝剂泵4泵入计量分配装置3稀释计量后送至脱硝雾化喷嘴2雾化成雾滴后进入锅炉炉膛与高温烟气进行氧化还原反应,脱硝效率不低于45%;两种工艺的协同处理后的NOx浓度≤100mg/Nm3,可根据锅炉负荷灵活操作。Specifically, the biomass boiler 32 adopts the EAS-FGR treatment process for low nitrogen, and about 15-40% of the net flue gas after desulfurization and denitration treatment is sent to the secondary tuyere 1 through the recirculation fan 25 and enters the furnace for secondary combustion. Flue gas NOx concentration ≤ 180mg/Nm3; denitrification adopts SNCR process in the furnace, and the denitrification agent stored in the denitrification agent box 5 is pumped into the metering distribution device 3 by the denitrification agent pump 4 and then sent to the denitrification atomizing nozzle 2 to be atomized into droplets Then it enters the boiler furnace and undergoes oxidation-reduction reaction with high-temperature flue gas, and the denitrification efficiency is not less than 45%. The NOx concentration after the synergistic treatment of the two processes is ≤100mg/Nm3, which can be flexibly operated according to the boiler load.
再循环风机25的出口排出的脱硫脱硝处理后的净烟还通过与臭氧发生器28产生的臭氧送至氧化混合装置27与经EAS-FGR和SNCR处理后的烟气进行湍流混合氧化,脱硫雾化喷嘴13喷出的碱性浆液与送入脱硫塔14烟气进一步反应,去除大部分NOx的烟气经过旋风除尘器17和布袋除尘器23进一步除尘后进入烟囱30达标排放。臭氧脱硝效率可到80%以上,保证处理后烟气中NOx浓度≤50mg/Nm3。The desulfurized and denitrified clean smoke discharged from the outlet of the recirculation fan 25 is also sent to the oxidation mixing device 27 through the ozone generated by the ozone generator 28 for turbulent mixed oxidation with the flue gas treated by EAS-FGR and SNCR, desulfurization mist The alkaline slurry ejected from the chemical nozzle 13 further reacts with the flue gas sent to the desulfurization tower 14, and the flue gas from which most of the NOx is removed is further dedusted by the cyclone dust collector 17 and the bag filter 23, and then enters the chimney 30 and is discharged up to the standard. The ozone denitrification efficiency can reach more than 80%, and the NOx concentration in the treated flue gas is guaranteed to be ≤50mg/Nm3.
脱硫剂仓7的外购的脱硫剂经螺旋给料机8下料给称重计量装置9计量后送入消化器10处理后的浆液送入脱硫浆液箱11进一步配制成10~15%脱硫浆液,通过脱硫剂输送泵12至脱硫雾化喷嘴13,雾化后的脱硫浆液在脱硫塔14与烟气污染物反应后再经去除旋风除尘器17和布袋除尘器23进一步除尘后进入烟囱30达标排放;处理后烟气中SO2浓度≤35mg/Nm3,脱硫效率不低于90%;The purchased desulfurizing agent in the desulfurizing agent warehouse 7 is fed into the weighing and metering device 9 through the screw feeder 8, and then sent to the digester 10. The treated slurry is sent to the desulfurizing slurry tank 11 for further preparation into 10-15% desulfurizing slurry , through the desulfurization agent delivery pump 12 to the desulfurization atomizing nozzle 13, the atomized desulfurization slurry reacts with the flue gas pollutants in the desulfurization tower 14, and then is further dedusted by the cyclone dust collector 17 and bag filter 23, and then enters the chimney 30 to reach the standard Emission; SO2 concentration in flue gas after treatment is ≤35mg/Nm3, desulfurization efficiency is not less than 90%;
需要说明的是,根据生物质锅炉烟气的特性,在脱硫塔14、旋风除尘器17和布袋除尘器23的收集灰,可以用作肥料;It should be noted that, according to the characteristics of the biomass boiler flue gas, the ash collected in the desulfurization tower 14, the cyclone dust collector 17 and the bag filter 23 can be used as fertilizer;
本发明可用于生物质锅炉烟气净化,通过对脱硫、脱硝、除尘尤其是脱硝工艺的优化设计,可实现生物质锅炉烟气二氧化硫、氮氧化物和粉尘等污染物超低排放。本发明对锅炉影响较小,既可根据负荷和实际污染物情况灵活运行,也可进行各分系统协同处理,方便整个生物质电厂系统的运行管理。The invention can be used for flue gas purification of biomass boilers, and can realize ultra-low emission of pollutants such as sulfur dioxide, nitrogen oxides and dust in flue gas of biomass boilers through optimized design of desulfurization, denitrification, dust removal, especially denitrification processes. The invention has little influence on the boiler, can operate flexibly according to the load and actual pollutant conditions, and can also carry out coordinated processing of various sub-systems, so as to facilitate the operation and management of the whole biomass power plant system.
(1)脱硫脱硝系统协同处理,操作灵活,便于维护,节水、节约运行成本;(1) Desulfurization and denitrification system coordinated processing, flexible operation, easy maintenance, water saving and operating cost saving;
(2)根据生物质锅炉的烟气特点,采用源头NOx控制、SNCR脱硝、氧化强化脱硝和半干法脱硫脱硝协同NOx控制技术,解决了采用SCR脱硝工艺投资成本高、容易堵塞、运行维护困难等问题;(2) According to the flue gas characteristics of the biomass boiler, the NOx control technology of source NOx control, SNCR denitrification, oxidation enhanced denitrification and semi-dry desulfurization and denitrification is adopted to solve the high investment cost, easy blockage and difficult operation and maintenance of the SCR denitrification process And other issues;
(3)脱硫脱硝产物可作为生物质灰的Ca、S、N元素的有益补充,用作复合肥料,无二次污染。(3) The desulfurization and denitrification products can be used as beneficial supplements of Ca, S, and N elements in biomass ash, and can be used as compound fertilizers without secondary pollution.
本发明性能可靠,操作灵活,便于维护,具有很好的经济效益和环境效益。The invention has reliable performance, flexible operation, convenient maintenance and good economic and environmental benefits.
对于本领域技术人员而言,显然能了解到上述具体事实例只是本发明的优选方案,因此本领域的技术人员对本发明中的某些部分所可能作出的改进、变动,体现的仍是本发明的原理,实现的仍是本发明的目的,均属于本发明所保护的范围。For those skilled in the art, it is obvious that the above-mentioned specific examples are only preferred solutions of the present invention, so those skilled in the art may make improvements and changes to some parts of the present invention, which still reflect the present invention. The principle of the present invention is still the object of the present invention, and all belong to the protection scope of the present invention.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810177320.2A CN108201784A (en) | 2018-03-02 | 2018-03-02 | A kind of grate-type biomass power plant boiler flue gas purification tapping equipment and its method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810177320.2A CN108201784A (en) | 2018-03-02 | 2018-03-02 | A kind of grate-type biomass power plant boiler flue gas purification tapping equipment and its method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108201784A true CN108201784A (en) | 2018-06-26 |
Family
ID=62605708
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810177320.2A Pending CN108201784A (en) | 2018-03-02 | 2018-03-02 | A kind of grate-type biomass power plant boiler flue gas purification tapping equipment and its method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108201784A (en) |
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108905568A (en) * | 2018-08-20 | 2018-11-30 | 山东省建设高压容器有限公司 | A kind of circulating fluidized bed boiler flue gas desulfuration and denitrification system and its remodeling method |
| CN108954298A (en) * | 2018-08-20 | 2018-12-07 | 山东省建设高压容器有限公司 | A kind of circulating fluidized bed boiler low nitrogen burning exhaust system and its remodeling method |
| CN110081454A (en) * | 2019-06-03 | 2019-08-02 | 安徽国祯生态科技有限公司 | Biomass boiler flue gas combined purification device and method |
| CN110624392A (en) * | 2019-10-29 | 2019-12-31 | 辽宁绿源能源环保科技集团有限责任公司 | Boiler structure and in-boiler desulfurization method |
| CN110711470A (en) * | 2019-09-23 | 2020-01-21 | 浙江大维高新技术股份有限公司 | Biomass boiler incineration flue gas desulfurization and denitrification purification process |
| CN111318105A (en) * | 2020-04-01 | 2020-06-23 | 中蓝长化工程科技有限公司 | A device for dust removal and denitrification of bagasse boiler flue gas |
| CN112197286A (en) * | 2020-11-11 | 2021-01-08 | 西安热工研究院有限公司 | A multi-pollutant coordinated ultra-low emission control system for biomass boiler flue gas |
| CN112717655A (en) * | 2019-10-14 | 2021-04-30 | 大唐环境产业集团股份有限公司 | Denitration, desulfurization and dust removal system and method for biomass boiler |
| CN114130174A (en) * | 2021-11-30 | 2022-03-04 | 北京华能长江环保科技研究院有限公司 | Full-load denitration device and denitration method for circulating fluidized bed boiler |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101259369A (en) * | 2008-04-29 | 2008-09-10 | 北京中科创丰科技有限公司 | Flue gas desulfurization denitration dust removing integrated technique |
| CN203447967U (en) * | 2013-08-05 | 2014-02-26 | 河北环科力创环境工程有限公司 | Combined smoke desulfuration, denitration and demercuration device of industrial boiler |
| CN104888591A (en) * | 2015-06-04 | 2015-09-09 | 南京龙源环保有限公司 | Boiler flue gas denitration purification system and boiler flue gas denitration purification method |
| CN106524205A (en) * | 2016-09-14 | 2017-03-22 | 科林环保技术有限责任公司 | Smoke ultra-low emission purification equipment of coal-fired industrial boiler |
| CN107213771A (en) * | 2017-07-14 | 2017-09-29 | 光大环境科技(中国)有限公司 | The biomass direct-fired device that flue gas recirculation and SNCR are combined |
| CN206846694U (en) * | 2017-05-18 | 2018-01-05 | 邵亚锋 | A kind of mixed by flue gas recirculation burns the device for reducing biomass bagasse boiler NOx emission |
| CN208145741U (en) * | 2018-03-02 | 2018-11-27 | 陕西大秦环境科技有限公司 | A kind of grate-type biomass power plant boiler flue gas purification tapping equipment |
-
2018
- 2018-03-02 CN CN201810177320.2A patent/CN108201784A/en active Pending
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101259369A (en) * | 2008-04-29 | 2008-09-10 | 北京中科创丰科技有限公司 | Flue gas desulfurization denitration dust removing integrated technique |
| CN203447967U (en) * | 2013-08-05 | 2014-02-26 | 河北环科力创环境工程有限公司 | Combined smoke desulfuration, denitration and demercuration device of industrial boiler |
| CN104888591A (en) * | 2015-06-04 | 2015-09-09 | 南京龙源环保有限公司 | Boiler flue gas denitration purification system and boiler flue gas denitration purification method |
| CN106524205A (en) * | 2016-09-14 | 2017-03-22 | 科林环保技术有限责任公司 | Smoke ultra-low emission purification equipment of coal-fired industrial boiler |
| CN206846694U (en) * | 2017-05-18 | 2018-01-05 | 邵亚锋 | A kind of mixed by flue gas recirculation burns the device for reducing biomass bagasse boiler NOx emission |
| CN107213771A (en) * | 2017-07-14 | 2017-09-29 | 光大环境科技(中国)有限公司 | The biomass direct-fired device that flue gas recirculation and SNCR are combined |
| CN208145741U (en) * | 2018-03-02 | 2018-11-27 | 陕西大秦环境科技有限公司 | A kind of grate-type biomass power plant boiler flue gas purification tapping equipment |
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108905568A (en) * | 2018-08-20 | 2018-11-30 | 山东省建设高压容器有限公司 | A kind of circulating fluidized bed boiler flue gas desulfuration and denitrification system and its remodeling method |
| CN108954298A (en) * | 2018-08-20 | 2018-12-07 | 山东省建设高压容器有限公司 | A kind of circulating fluidized bed boiler low nitrogen burning exhaust system and its remodeling method |
| CN110081454A (en) * | 2019-06-03 | 2019-08-02 | 安徽国祯生态科技有限公司 | Biomass boiler flue gas combined purification device and method |
| CN110711470A (en) * | 2019-09-23 | 2020-01-21 | 浙江大维高新技术股份有限公司 | Biomass boiler incineration flue gas desulfurization and denitrification purification process |
| CN112717655A (en) * | 2019-10-14 | 2021-04-30 | 大唐环境产业集团股份有限公司 | Denitration, desulfurization and dust removal system and method for biomass boiler |
| CN110624392A (en) * | 2019-10-29 | 2019-12-31 | 辽宁绿源能源环保科技集团有限责任公司 | Boiler structure and in-boiler desulfurization method |
| CN111318105A (en) * | 2020-04-01 | 2020-06-23 | 中蓝长化工程科技有限公司 | A device for dust removal and denitrification of bagasse boiler flue gas |
| CN112197286A (en) * | 2020-11-11 | 2021-01-08 | 西安热工研究院有限公司 | A multi-pollutant coordinated ultra-low emission control system for biomass boiler flue gas |
| CN114130174A (en) * | 2021-11-30 | 2022-03-04 | 北京华能长江环保科技研究院有限公司 | Full-load denitration device and denitration method for circulating fluidized bed boiler |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN108201784A (en) | A kind of grate-type biomass power plant boiler flue gas purification tapping equipment and its method | |
| CN202478804U (en) | Sintering machine flue gas desulphurization denitration device | |
| CN101915419A (en) | A method and system for reburning biomass gasification gas in a coal-fired fluidized bed | |
| CN205627573U (en) | System for ultralow emission of dust and NOx at high temperature | |
| CN112121614A (en) | Stable ultralow emission device and method for solid waste incineration flue gas | |
| CN102966945A (en) | Method for reducing nitrogen oxide discharge of biomass circulating fluid bed boiler | |
| CN103263828A (en) | Fume gas denitration system of coal-fired boiler based on SNCR (Selective Non-catalytic Reduction) and SCR (Selective Catalytic Reduction) combination method | |
| CN116651168B (en) | Dry-method multi-pollutant flue gas purification device and method | |
| CN113559692A (en) | Double-tower double-circulation semi-dry desulfurization device, process and application | |
| CN208177248U (en) | It is a kind of based on active carbon/coke coke oven flue gas system for desulfuration and denitration | |
| CN106861412B (en) | System and method for sharing and recycling high-calcium fly ash of multi-unit power station | |
| CN112426863A (en) | A dry-process double-bag flue gas purification integrated device for co-processing multiple pollutants | |
| CN102120139A (en) | Wet type combined desulfuration and denitration device and method for coal-fired boiler | |
| CN202823129U (en) | Flue gas cleaning device of spray drying method combined with hydrated lime powder spraying | |
| CN206549434U (en) | A kind of coke oven flue gas dry-type desulphurization device, the dust removal integrated system of coke oven flue gas dry type desulfurizing | |
| CN213348376U (en) | High-efficient SNCR deNOx systems of biomass boiler | |
| CN208145741U (en) | A kind of grate-type biomass power plant boiler flue gas purification tapping equipment | |
| CN118236835A (en) | A multifunctional dry denitrification method and device | |
| CN112197286A (en) | A multi-pollutant coordinated ultra-low emission control system for biomass boiler flue gas | |
| CN208465583U (en) | A kind of biomass flue gas dust-removal and desulfurizing denitrating system | |
| CN208244426U (en) | A kind of efficient NOx control device of biomass boiler | |
| CN111085092A (en) | Desulfurization and dust removal device and desulfurization and dust removal method for gas boiler | |
| CN207970687U (en) | Intermittent cyclic fluid bed and utilize its flue gas purification system | |
| CN207745708U (en) | Flue gas and desulfurizing and denitrifying integrated purification system | |
| CN212651555U (en) | Comprehensive treatment system for biomass boiler flue gas |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20180626 |