CN111895799A - A multi-pollutant collaborative treatment system for heating furnace exhaust gas - Google Patents
A multi-pollutant collaborative treatment system for heating furnace exhaust gas Download PDFInfo
- Publication number
- CN111895799A CN111895799A CN202010863751.1A CN202010863751A CN111895799A CN 111895799 A CN111895799 A CN 111895799A CN 202010863751 A CN202010863751 A CN 202010863751A CN 111895799 A CN111895799 A CN 111895799A
- Authority
- CN
- China
- Prior art keywords
- soot
- air
- heat exchanger
- purification system
- heating furnace
- 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
Images
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F27—FURNACES; KILNS; OVENS; RETORTS
- F27D—DETAILS OR ACCESSORIES OF FURNACES, KILNS, OVENS OR RETORTS, IN SO FAR AS THEY ARE OF KINDS OCCURRING IN MORE THAN ONE KIND OF FURNACE
- F27D17/00—Arrangements for using waste heat; Arrangements for using, or disposing of, waste gases
- F27D17/20—Arrangements for treatment or cleaning of waste gases
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/02—Particle separators, e.g. dust precipitators, having hollow filters made of flexible material
-
- 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
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/501—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
- B01D53/504—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound characterised by a specific device
-
- 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
- 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
- B01D53/86—Catalytic processes
- B01D53/8621—Removing nitrogen compounds
- B01D53/8625—Nitrogen oxides
- B01D53/8631—Processes characterised by a specific device
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F27—FURNACES; KILNS; OVENS; RETORTS
- F27D—DETAILS OR ACCESSORIES OF FURNACES, KILNS, OVENS OR RETORTS, IN SO FAR AS THEY ARE OF KINDS OCCURRING IN MORE THAN ONE KIND OF FURNACE
- F27D17/00—Arrangements for using waste heat; Arrangements for using, or disposing of, waste gases
- F27D17/10—Arrangements for using waste heat
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/206—Ammonium compounds
- B01D2251/2062—Ammonia
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
- Y02A50/2351—Atmospheric particulate matter [PM], e.g. carbon smoke microparticles, smog, aerosol particles, dust
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/25—Process efficiency
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Biomedical Technology (AREA)
- Health & Medical Sciences (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- General Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Treating Waste Gases (AREA)
- Chimneys And Flues (AREA)
Abstract
本发明公开了一种加热炉废气多污染物协同治理系统。包括煤烟净化系统、空烟净化系统,所述煤烟净化系统,空烟净化系统分别包括SCR脱硝反应器、脱硫反应塔、袋式除尘器;所述煤烟净化系统中的SCR脱硝反应器的烟气入口前端通过管道连接煤烟一级换热器、煤烟二级换热器,所述煤烟二级换热器连接风热炉;所述空烟净化系统中的SCR脱硝反应器的烟气入口前端通过管道连接空烟一级换热器、混风装置,所述混风装置连接煤烟二级换热器。本系统可有效实现加热炉废气净化、余热回收和联合升温同步进行;本系统净化效率高,能同时有效脱除废气中的二氧化硫、氮氧化物和颗粒物,完全可满足新标准排放限值要求或超低排放指标。
The invention discloses a multi-pollutant cooperative treatment system for heating furnace exhaust gas. Including a soot purification system and an air and smoke purification system, the soot purification system and the air and smoke purification system respectively include an SCR denitration reactor, a desulfurization reaction tower, and a bag filter; the SCR denitration reactor in the soot purification system The front end of the flue gas inlet is connected to the soot primary heat exchanger and the soot secondary heat exchanger through pipes, and the soot secondary heat exchanger is connected to the air-heated furnace; the SCR denitration reactor in the air and smoke purification system The front end of the flue gas inlet is connected to the air-smoke primary heat exchanger and the air mixing device through a pipeline, and the air mixing device is connected to the soot secondary heat exchanger. This system can effectively realize the synchronous operation of heating furnace exhaust gas purification, waste heat recovery and joint temperature rise; the system has high purification efficiency, and can effectively remove sulfur dioxide, nitrogen oxides and particulate matter in the exhaust gas at the same time, which can fully meet the emission limit requirements of the new standard or Ultra-low emission targets.
Description
技术领域technical field
本发明属于工业烟气污染防治技术领域,涉及一种加热炉废气多污染物协同治理系统,特别涉及轧钢加热炉废气净化系统。The invention belongs to the technical field of industrial flue gas pollution prevention and control, and relates to a multi-pollutant coordinated treatment system for heating furnace waste gas, in particular to a steel rolling heating furnace waste gas purification system.
背景技术Background technique
加热炉是将物料或工件加热的进行再处理加工设备,也是给物料或是工件加热升温的设备。The heating furnace is a reprocessing equipment that heats materials or workpieces, and is also a device that heats materials or workpieces.
加热炉煤气燃烧后产生的废气主要有SO2、NOx、烟尘等,污染物呈有组织高架点源连续性排放,因其废气排放量较大而对大气环境造成的污染已不可忽视。The waste gas produced by the combustion of the heating furnace gas mainly includes SO2, NOx, soot, etc. The pollutants are continuously discharged from the organized elevated point source, and the pollution to the atmospheric environment caused by the large amount of waste gas emissions cannot be ignored.
2019年4月生态环境部、发改委等部门联合发布《关于推进实施钢铁行业超低排放的意见》,要求加热炉产生的烟气污染物排放指标:在基准含氧量8%,颗粒物、二氧化硫、氮氧化物小时均值排放浓度分别不高于10,50,200毫克/立方米。In April 2019, the Ministry of Ecology and Environment, the National Development and Reform Commission and other departments jointly issued the "Opinions on Promoting the Implementation of Ultra-Low Emissions in the Iron and Steel Industry", which requires the emission indicators of flue gas pollutants generated by heating furnaces: at the benchmark oxygen content of 8%, particulate matter, sulfur dioxide, The hourly mean emission concentration of nitrogen oxides shall not be higher than 10, 50 and 200 mg/m3 respectively.
如前所述,轧钢加热炉产生的烟气温度80-110℃、颗粒物浓度<100mg/m3、SO2浓度>300mg/m3、NOx浓度>500mg/m3,加热炉烟气通过煤烟烟囱和空烟烟囱分别排放,其中煤烟中含有CO爆炸性气体。As mentioned above, the temperature of the flue gas produced by the steel rolling heating furnace is 80-110 °C, the concentration of particulate matter is less than 100 mg/m 3 , the concentration of SO 2 is greater than 300 mg/m 3 and the concentration of NOx is greater than 500 mg/m 3 . The flue gas of the heating furnace passes through the soot. The chimney and the empty chimney are discharged separately, in which the soot contains CO explosive gas.
文献查阅显示,目前国内加热炉NOx采用循环烟气低氮燃烧技术,但NOx仍无法满足国家环保排放要求,缺乏针对颗粒物和二氧化硫治理工艺技术。Literature review shows that the current domestic heating furnace NOx adopts circulating flue gas low-nitrogen combustion technology, but NOx still cannot meet the national environmental protection emission requirements, and lacks the treatment technology for particulate matter and sulfur dioxide.
发明内容SUMMARY OF THE INVENTION
本发明的目的在于提供一种加热炉废气多污染物协同治理系统,针对轧钢加热炉烟气特性提出一种联合升温方式,即将煤烟侧烟气先进行升温,同时利用加热过煤烟侧烟气的热风对空烟侧烟气进行混合升温方式,以满足新的环保标准要求或超低排放要求。The purpose of the present invention is to provide a multi-pollutant cooperative treatment system for heating furnace exhaust gas, and propose a joint heating method according to the characteristics of the flue gas of the steel rolling heating furnace, that is, the soot side flue gas is heated first, and the heated soot side smoke is used at the same time. The hot air of the air is mixed to heat up the flue gas on the air smoke side to meet the requirements of new environmental protection standards or ultra-low emission requirements.
本发明的技术解决方案是:一种加热炉废气多污染物协同治理系统,包括煤烟净化系统、空烟净化系统,空烟净化系统分别包括SCR脱硝反应器、脱硫反应塔、袋式除尘器;所述煤烟净化系统中的SCR脱硝反应器的烟气入口前端通过管道连接煤烟一级换热器、煤烟二级换热器,所述煤烟二级换热器连接风热炉;所述空烟净化系统中的SCR脱硝反应器的烟气入口前端通过管道连接空烟一级换热器、混风装置,所述混风装置连接煤烟二级换热器;所述的热风炉主要是为煤烟和空烟烟气进行升温,满足SCR脱硝温度;热风炉产生的高温空气先对煤烟间接换热后,再与空烟在混合装置直接混合升温; 所述的煤烟净化系统和空烟净化系统,两套净化系统同时运行,互不干涉,确保安全。The technical solution of the present invention is: a multi-pollutant collaborative treatment system for heating furnace exhaust gas, including a soot purification system and an air and smoke purification system, and the air and smoke purification system respectively includes an SCR denitration reactor, a desulfurization reaction tower, and a bag filter. ; The front end of the flue gas inlet of the SCR denitration reactor in the soot purification system is connected to a soot primary heat exchanger and a soot secondary heat exchanger through a pipeline, and the soot secondary heat exchanger is connected to an air-heated furnace ; The front end of the flue gas inlet of the SCR denitration reactor in the air and smoke purification system is connected to the air and smoke primary heat exchanger and the air mixing device through a pipeline, and the air mixing device is connected to the soot secondary heat exchanger; the The hot blast stove is mainly to heat up the soot and air smoke to meet the SCR denitration temperature; the high temperature air generated by the hot blast stove first heats the soot indirectly, and then directly mixes with the air smoke in the mixing device to heat up; Smoke purification system and air smoke purification system, the two sets of purification systems run at the same time without interfering with each other to ensure safety.
根据本发明实施例,所述袋式除尘器的净烟气出口连接引风机、烟囱;所述的引风机为废气净化系统提供动力,风机控制可依需采用常规控制或变频控制。According to the embodiment of the present invention, the net flue gas outlet of the bag filter is connected to an induced draft fan and a chimney; the induced draft fan provides power for the exhaust gas purification system, and the fan control can be conventional control or frequency conversion control as required.
根据本发明实施例,所述SCR脱硝反应器包括催化反应器、喷氨格栅、静态混合器,SCR脱硝反应器用于对废气中的NOx进行脱除。According to an embodiment of the present invention, the SCR denitration reactor includes a catalytic reactor, an ammonia injection grid, and a static mixer, and the SCR denitration reactor is used for removing NOx in the exhaust gas.
根据本发明实施例,所述袋式除尘器是直通式袋式除尘器、预荷电袋滤器或电袋复合袋式除尘器;所述的袋式除尘器主要由滤袋袋笼、喷吹装置、箱体、灰斗等组成,用于对颗粒物进行高效脱除,保证颗粒物低浓度排放,满足环保要求。According to the embodiment of the present invention, the bag filter is a straight-through bag filter, a pre-charged bag filter or an electric bag compound bag filter; the bag filter is mainly composed of a filter bag cage, an injection bag filter It is composed of a device, a box, an ash hopper, etc., which are used to efficiently remove particulate matter, ensure low-concentration emission of particulate matter, and meet environmental protection requirements.
根据本发明实施例,所述煤烟一级换热器、煤烟二级换热器、空烟一级换热器是气气间接换热方式,换热器型式采用板式、热管或列管式,换热器具有废热回收的功用。According to the embodiment of the present invention, the soot primary heat exchanger, the soot secondary heat exchanger, and the air-smoke primary heat exchanger are gas-gas indirect heat exchangers, and the heat exchangers are of plate type, heat pipe or column-and-tube type. The heat exchanger has the function of waste heat recovery.
所述的脱硫反应塔是在反应塔中喷射脱硫剂对SO2进行高效脱除,保证二氧化硫低浓度排放,满足环保要求;可根据不同的工况条件采用不同的干法或半干法脱硫工艺(包括但不限于钙法、钠碱法等)。The desulfurization reaction tower is to spray desulfurization agent in the reaction tower to remove SO 2 efficiently, to ensure low concentration of sulfur dioxide emission, and to meet environmental protection requirements; different dry or semi-dry desulfurization processes can be used according to different working conditions. (including but not limited to calcium method, sodium-alkali method, etc.).
本发明的技术路线是:由于加热炉烟气的特点,采用煤烟净化系统和空烟净化系统,每套系统均采用SCR脱硝+干法(或半干法)脱硫对废气进行氮氧化物、二氧化硫和颗粒物的高效脱除,净化废气并达标排放;采用换热器进行降温及热能回收与利用;对煤烟和空烟采用联合升温,即热风炉产生的高温空气先对煤烟间接升温后,再与空烟直接混合升温。The technical route of the invention is: due to the characteristics of the flue gas of the heating furnace, a soot purification system and an air smoke purification system are used, and each system adopts SCR denitration + dry (or semi-dry) desulfurization to remove nitrogen oxides, Efficient removal of sulfur dioxide and particulate matter, purifying exhaust gas and discharging up to standard; using heat exchanger for cooling and heat energy recovery and utilization; using joint heating for soot and air smoke, that is, the high-temperature air generated by the hot blast stove first heats the soot indirectly , and then directly mixed with air smoke to heat up.
本发明系统显著的特征是包含废气净化、余热回收和联合升温三个回路。The remarkable feature of the system of the present invention is that it includes three circuits of exhaust gas purification, waste heat recovery and combined temperature rise.
本发明净化系统是:加热炉燃烧废气分为煤烟和空烟,因煤烟中含有CO爆炸性气体,煤烟和空烟各设1套净化系统,即煤烟净化系统和空烟净化系统。The purification system of the invention is as follows: the combustion exhaust gas of the heating furnace is divided into soot and air smoke. Because the soot contains CO explosive gas, the soot and the air smoke are each provided with a set of purification systems, namely the soot purification system and the air smoke purification system.
煤烟净化系统:煤烟先进入一级换热器和二级换热器,烟气先进入SCR脱硝装置对废气中的NOx进行脱除,再经干法(或半干法)脱硫进行SO2脱除,再经袋式除尘器对废气中的颗粒物进行脱除,净烟气由引风机进入烟囱高空排放。Soot purification system: the soot first enters the primary heat exchanger and the secondary heat exchanger, and the flue gas first enters the SCR denitrification device to remove NOx in the exhaust gas, and then undergoes dry (or semi-dry) desulfurization. SO 2 is removed, and then the particulate matter in the exhaust gas is removed by the bag filter, and the clean flue gas is discharged into the chimney at high altitude by the induced draft fan.
空烟净化系统:空烟先进入一级换热器和混合升温,再进入SCR脱硝装置对废气中的NOx进行脱除,再经干法(或半干法)脱硫进行SO2脱除,再经袋式除尘器对废气中的颗粒物进行脱除,净烟气由引风机进入烟囱高空排放。Air and smoke purification system: the air smoke first enters the primary heat exchanger and mixes to heat up, and then enters the SCR denitration device to remove NOx from the exhaust gas, and then dry (or semi - dry) desulfurization for SO2 removal. Then, the particulate matter in the exhaust gas is removed by the bag filter, and the clean flue gas is discharged into the chimney at high altitude by the induced draft fan.
本发明净化系统特征是:采用联合升温工艺。由于加热炉烟气的特点,煤烟侧烟气中CO浓度约为30000ppm,最高时可达70000ppm,因此不能利用热空气与烟气直接混合加热,仅能采用间接换热升温方式,利用换热器对烟气进行升温;而对煤烟侧烟气升温后的热风,再与空烟侧烟气直接混合,达到煤烟、空烟综合利用热能的目的。The purification system of the present invention is characterized in that: a combined heating process is adopted. Due to the characteristics of the flue gas of the heating furnace, the CO concentration in the flue gas on the soot side is about 30,000 ppm, and the highest can reach 70,000 ppm. Therefore, it is not possible to use hot air and flue gas to directly mix and heat, and only indirect heat exchange can be used. The flue gas is heated by the device; the hot air after heating the soot side flue gas is directly mixed with the air smoke side flue gas, so as to achieve the purpose of comprehensive utilization of thermal energy between soot and air smoke.
本发明有益的效果在于:本系统可有效实现加热炉废气净化、余热回收和联合升温同步进行;本系统净化效率高,能同时有效脱除废气中的二氧化硫、氮氧化物和颗粒物,使排放的SO2浓度低于30mg/m3,NOx浓度低于50mg/m3,颗粒物低于10mg/m3,完全可满足新标准排放限值要求或超低排放指标;本系统具有余热利用、节能降耗、运行成本低、安全可靠等显著特点,通过烟气换热,使废气温度降至130~150℃;本系统采用联合升温可有效满足煤烟和空烟的SCR脱硝温度,又能确保煤烟净化系统的安全可靠运行;所采用SCR脱硝方法,具有脱硝效率高、能耗省、占地小和运行成本低等优势;所采用干法(或半干法)脱硫方法,具有脱硫效率高、无废水、运行简单、阻力低、占地小等优势。The beneficial effects of the invention are as follows: the system can effectively realize the simultaneous purifying, waste heat recovery and joint temperature rise of the heating furnace; the purification efficiency of the system is high, and the sulfur dioxide, nitrogen oxides and particulate matter in the exhaust gas can be effectively removed at the same time, so that the discharged SO 2 concentration is lower than 30mg/m 3 , NO x concentration is lower than 50mg/m 3 , and particulate matter is lower than 10mg/m 3 , which can fully meet the new standard emission limit requirements or ultra-low emission targets; the system has the advantages of waste heat utilization and energy saving Consumption reduction, low operating cost, safety and reliability and other notable features, through flue gas heat exchange, the exhaust gas temperature can be reduced to 130~150 ℃; this system adopts combined heating, which can effectively meet the SCR denitration temperature of soot and air smoke, and can ensure Safe and reliable operation of the soot purification system; the adopted SCR denitration method has the advantages of high denitration efficiency, low energy consumption, small land occupation and low operating cost; the adopted dry (or semi-dry) desulfurization method has high desulfurization efficiency High, no waste water, simple operation, low resistance, small footprint and other advantages.
附图说明Description of drawings
图1是一种加热炉废气多污染物协同治理系统。Figure 1 is a multi-pollutant collaborative treatment system for heating furnace exhaust gas.
具体实施方式Detailed ways
下面结合附图对本发明进行进一步说明。The present invention will be further described below with reference to the accompanying drawings.
如图1,一种加热炉废气多污染物协同治理系统,包括煤烟净化系统、空烟净化系统,所述煤烟净化系统,空烟净化系统分别包括SCR脱硝反应器、脱硫反应塔、袋式除尘器;所述煤烟净化系统中的SCR脱硝反应器的烟气入口前端通过管道连接煤烟一级换热器、煤烟二级换热器,所述煤烟二级换热器连接风热炉;所述空烟净化系统中的SCR脱硝反应器的烟气入口前端通过管道连接空烟一级换热器、混风装置,所述混风装置连接煤烟二级换热器。As shown in Figure 1, a multi-pollutant collaborative treatment system for heating furnace exhaust gas includes a soot purification system and an air and smoke purification system. The soot purification system and the air and smoke purification system respectively include an SCR denitration reactor, a desulfurization reaction tower, a bag The front end of the flue gas inlet of the SCR denitration reactor in the soot purification system is connected to the soot primary heat exchanger and the soot secondary heat exchanger through pipes, and the soot secondary heat exchanger is connected to An air-heated furnace; the front end of the flue gas inlet of the SCR denitration reactor in the air-smoke purification system is connected to the air-smoke primary heat exchanger and the air mixing device through a pipeline, and the air mixing device is connected to the soot secondary heat exchanger.
如图1,所述的煤烟净化系统和空烟净化系统,两套净化系统同时运行,互不干涉,确保安全。As shown in Figure 1, the soot purification system and the air smoke purification system, the two sets of purification systems run at the same time without interfering with each other to ensure safety.
所述SCR脱硝反应器包括催化反应器、喷氨格栅、静态混合器,用于对废气中的NOx进行脱。The SCR denitration reactor includes a catalytic reactor, an ammonia injection grid, and a static mixer, and is used for removing NOx in the exhaust gas.
所述的脱硫反应塔是在反应塔中喷射脱硫剂对SO2进行高效脱除,保证二氧化硫低浓度排放,满足环保要求;可根据不同的工况条件采用不同的干法或半干法脱硫工艺(包括但不限于钙法、钠碱法等)。The desulfurization reaction tower is to spray desulfurization agent in the reaction tower to remove SO 2 efficiently, to ensure low concentration of sulfur dioxide emission, and to meet environmental protection requirements; different dry or semi-dry desulfurization processes can be used according to different working conditions. (including but not limited to calcium method, sodium-alkali method, etc.).
所述的袋式除尘器主要由滤袋袋笼、喷吹装置、箱体、灰斗等组成,用于对颗粒物进行高效脱除,保证颗粒物低浓度排放,满足环保要求;袋式除尘器包括但不限于直通式袋式除尘器、预荷电袋滤器、电袋复合袋式除尘器等。The bag filter is mainly composed of a filter bag cage, a blowing device, a box, an ash hopper, etc., which are used to efficiently remove particulate matter, ensure low-concentration emission of particulate matter, and meet environmental protection requirements; the bag filter includes: But not limited to straight-through bag filter, pre-charged bag filter, electric bag compound bag filter, etc.
所述煤烟一级换热器、煤烟二级换热器、空烟一级换热器是气气间接换热方式,换热器型式采用板式、热管或列管式;换热器具有废热回收的功用。The soot primary heat exchanger, soot secondary heat exchanger, and air-smoke primary heat exchanger are gas-gas indirect heat exchange, and the heat exchanger type adopts plate type, heat pipe or tube type; The function of waste heat recovery.
所述的引风机为废气净化系统提供动力,风机控制可依需采用常规控制或变频控制。The induced draft fan provides power for the exhaust gas purification system, and the fan control can be conventional control or frequency conversion control as required.
所述的热风炉主要是为煤烟和空烟烟气进行升温,满足SCR脱硝温度;热风炉产生的高温空气先对煤烟间接换热后,再与空烟在混合装置直接混合升温。The hot blast stove is mainly to heat up the soot and air smoke to meet the SCR denitration temperature; the high temperature air generated by the hot blast stove first heats the soot indirectly, and then directly mixes with the air smoke in the mixing device to heat up.
上述结合附图详细的实施方案描述仅为本发明的优选实施方案,但是,本发明并不限于上述方案中的具体细节,任何在本发明的思想和原则内所作的任何修改、替换;如干法或半干法脱硫工艺(包括但不限于钙法、钠碱法等),均在本发明的保护范围内。The above detailed description of the embodiments in conjunction with the accompanying drawings are only preferred embodiments of the present invention, but the present invention is not limited to the specific details in the above-mentioned solutions, and any modifications and substitutions made within the spirit and principles of the present invention; Desulfurization process (including but not limited to calcium method, sodium-alkali method, etc.) or semi-dry desulfurization process are all within the protection scope of the present invention.
Claims (5)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010863751.1A CN111895799A (en) | 2020-08-25 | 2020-08-25 | A multi-pollutant collaborative treatment system for heating furnace exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010863751.1A CN111895799A (en) | 2020-08-25 | 2020-08-25 | A multi-pollutant collaborative treatment system for heating furnace exhaust gas |
Publications (1)
Publication Number | Publication Date |
---|---|
CN111895799A true CN111895799A (en) | 2020-11-06 |
Family
ID=73225383
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202010863751.1A Pending CN111895799A (en) | 2020-08-25 | 2020-08-25 | A multi-pollutant collaborative treatment system for heating furnace exhaust gas |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN111895799A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113877419A (en) * | 2021-09-16 | 2022-01-04 | 上海嘉德环境能源科技有限公司 | Low-temperature flue gas desulfurization and denitrification system and method for heat accumulating type steel rolling heating furnace |
CN113959232A (en) * | 2021-11-19 | 2022-01-21 | 华北理工大学 | Heat accumulating type heating furnace flue gas multi-pollutant cooperative control system and method |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN209630986U (en) * | 2019-01-18 | 2019-11-15 | 浙江蓝天求是环保股份有限公司 | A kind of low-temperature flue gas mixing reheating denitration coordinated desulfurization system |
CN111495186A (en) * | 2020-06-02 | 2020-08-07 | 北京赛博宇科技发展有限公司 | A flue gas heat exchange, temperature rise, desulfurization and denitrification system for a hot-rolled steel regenerative heating furnace |
CN212431808U (en) * | 2020-08-25 | 2021-01-29 | 中钢集团天澄环保科技股份有限公司 | Heating furnace waste gas multi-pollutant cooperative treatment system |
-
2020
- 2020-08-25 CN CN202010863751.1A patent/CN111895799A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN209630986U (en) * | 2019-01-18 | 2019-11-15 | 浙江蓝天求是环保股份有限公司 | A kind of low-temperature flue gas mixing reheating denitration coordinated desulfurization system |
CN111495186A (en) * | 2020-06-02 | 2020-08-07 | 北京赛博宇科技发展有限公司 | A flue gas heat exchange, temperature rise, desulfurization and denitrification system for a hot-rolled steel regenerative heating furnace |
CN212431808U (en) * | 2020-08-25 | 2021-01-29 | 中钢集团天澄环保科技股份有限公司 | Heating furnace waste gas multi-pollutant cooperative treatment system |
Non-Patent Citations (1)
Title |
---|
顾璠等: "燃烧学基础", 31 August 2019, 东南大学出版社, pages: 284 - 285 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113877419A (en) * | 2021-09-16 | 2022-01-04 | 上海嘉德环境能源科技有限公司 | Low-temperature flue gas desulfurization and denitrification system and method for heat accumulating type steel rolling heating furnace |
CN113959232A (en) * | 2021-11-19 | 2022-01-21 | 华北理工大学 | Heat accumulating type heating furnace flue gas multi-pollutant cooperative control system and method |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN109794146B (en) | Grate-rotary kiln SNCR/SCR denitration and active coke desulfurization combined system and process | |
CN108176221B (en) | Sintering flue gas temperature rising denitration device and sintering flue gas temperature rising denitration method | |
CN204555717U (en) | Warm flue gas SCR denitration device in a kind of cement kiln end | |
CN106996702B (en) | A kind of agglomeration for iron mine flue gas segmentation enrichment and UTILIZATION OF VESIDUAL HEAT IN emission reduction SOxAnd NOxMethod | |
CN104190253A (en) | Coke oven flue gas SCR denitration system | |
CN104437082A (en) | Ultra-clean discharge system and method for fluidized bed boiler | |
CN101439260A (en) | System for removing nitrous oxides in low-temperature flue gas and technique thereof | |
CN203355611U (en) | Device for removing NOX and dioxins in sintering and pelletizing flue gas through SCR (Selective Catalytic Reduction) | |
CN209885578U (en) | Dust removal SOx/NOx control takes off white integration system | |
CN111495186A (en) | A flue gas heat exchange, temperature rise, desulfurization and denitrification system for a hot-rolled steel regenerative heating furnace | |
CN110833763A (en) | Production process and equipment for organic flue gas incineration, desulfurization, dust removal and denitrification | |
CN204619708U (en) | A kind of cement rotary kiln kiln gas combined denitration device | |
CN111895799A (en) | A multi-pollutant collaborative treatment system for heating furnace exhaust gas | |
CN111804138A (en) | Biomass boiler flue gas denitration system and application process thereof | |
CN110787620A (en) | Glass melting furnace flue gas is emission reduction coupling waste heat power generation system in coordination | |
CN212431808U (en) | Heating furnace waste gas multi-pollutant cooperative treatment system | |
CN210645862U (en) | Dry deacidification treatment system for flue gas of garbage incinerator | |
CN212841617U (en) | Ultralow discharging equipment of sludge drying incineration tail gas | |
CN208066118U (en) | A kind of coke oven flue gas desulphurization denitration dedusting comprehensive treatment device | |
CN112495160B (en) | Device and method for tail gas nitrogen oxide removal process of sulfur recovery device | |
CN213453647U (en) | Solid-gas waste efficient utilization and treatment system | |
CN211216127U (en) | A multi-effect COA system suitable for high temperature region | |
CN102658025A (en) | Low-temperature SCR (selective catalytic reduction) fixed bed fume denitration device for horizontal waste heat boiler | |
CN113842772A (en) | Grate-rotary kiln pellet flue gas SCR denitration method | |
CN216677683U (en) | Be used for steel rolling heating furnace flue gas to unite heat transfer intensification SOx/NOx control device |
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 |