CN1113682C - Two-segment desulfurizing method for high-temp combustion - Google Patents
Two-segment desulfurizing method for high-temp combustion Download PDFInfo
- Publication number
- CN1113682C CN1113682C CN00101316A CN00101316A CN1113682C CN 1113682 C CN1113682 C CN 1113682C CN 00101316 A CN00101316 A CN 00101316A CN 00101316 A CN00101316 A CN 00101316A CN 1113682 C CN1113682 C CN 1113682C
- Authority
- CN
- China
- Prior art keywords
- desulfurization
- combustion
- space
- based additives
- calcium based
- 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.)
- Expired - Fee Related
Links
Abstract
本发明公开了一种高温燃烧两段脱硫方法。高温燃烧两段脱硫方法是利用风力将部分钙基添加剂粉末吹入炉膛空间,将层燃炉煤层中的燃烧脱硫反应部分转移到燃烧空间及整个烟气流程,以及时有效地捕捉从煤层释放到烟气中的SO2,实现床层和空间两段脱硫;并通过配风增强高温燃烧段的还原性气氛和后期燃烬段的氧化性气氛,在保证燃烧效率的前提下实现同时脱硫脱硝的效果。本发明能使层燃炉燃烧脱硫效率提高到70-80%。The invention discloses a high-temperature combustion two-stage desulfurization method. The high-temperature combustion two-stage desulfurization method is to use wind force to blow part of the calcium-based additive powder into the furnace space, and transfer the combustion desulfurization reaction part in the coal seam of the bed-fired furnace to the combustion space and the entire flue gas flow, so as to capture the release from the coal seam to SO 2 in the flue gas can achieve two-stage desulfurization in the bed and space; and through air distribution, the reducing atmosphere in the high-temperature combustion section and the oxidizing atmosphere in the post-combustion section can be enhanced to achieve simultaneous desulfurization and denitrification under the premise of ensuring combustion efficiency. Effect. The invention can increase the combustion desulfurization efficiency of the layer combustion furnace to 70-80%.
Description
本发明涉及燃烧生成物的清除,尤其涉及一种高温燃烧两段脱硫的方法。The invention relates to the removal of combustion products, in particular to a high-temperature combustion two-stage desulfurization method.
炉内燃烧脱硫技术,成本低廉,工艺简单,是解决我国量大面广的工业锅炉严重的污染排放问题的较为有效的途径之一。但钙基脱硫剂在层燃炉内的燃烧脱硫效率低是一个世界性难题,在Ca/S=2时,采用链条炉内直接喷钙的方式,燃烧脱硫率一般为30~50%;而采用与入炉散煤预混的方式,燃烧脱硫率一般在20~40%,长期以来一直没有重大突破。研究表明:造成层燃炉内钙基钙基添加剂高温燃烧脱硫率低的主要原因是层燃炉燃烧过程中床层的高温环境(1200℃左右)和固硫剂在床层中漫长的停留时间(1小时左右)使得固硫反应产物CaSO4难以大量生成或重新分解所致。因此,我们不仅应该考虑化学热力学和反应动力学的因素,重视脱硫剂配方及其微观物化特性的研究,更重要的是应在链条炉热工环境这个根本原因上寻找突破点,以大幅度改善钙基脱硫剂在层燃炉内燃烧脱硫率低的状况。In-furnace combustion desulfurization technology, with low cost and simple process, is one of the more effective ways to solve the serious pollution emission problem of industrial boilers with large quantities and wide areas in our country. However, the low combustion desulfurization efficiency of calcium-based desulfurizers in the layer-fired furnace is a worldwide problem. When Ca/S=2, the combustion desulfurization rate is generally 30-50% when Ca/S=2, using the method of directly spraying calcium in the chain furnace; Using the method of pre-mixing with the loose coal into the furnace, the combustion desulfurization rate is generally 20-40%, and there has been no major breakthrough for a long time. Studies have shown that the main reasons for the low desulfurization rate of calcium-based calcium-based additives in the bed-burning furnace are the high-temperature environment (about 1200°C) of the bed during the combustion process of the bed-burning furnace and the long residence time of the sulfur-fixing agent in the bed. (about 1 hour) makes it difficult for the sulfur-fixing reaction product CaSO 4 to be generated in large quantities or decomposed again. Therefore, we should not only consider the factors of chemical thermodynamics and reaction kinetics, pay attention to the research on the formula of desulfurizer and its microscopic physical and chemical properties, but more importantly, we should find a breakthrough point on the root cause of the thermal environment of the chain furnace to greatly improve Calcium-based desulfurizer combustion desulfurization rate is low in the layer combustion furnace.
本发明的目的是提供一种使层燃炉脱硫效率提高到70~80%的高温燃烧两段脱硫的方法。The object of the present invention is to provide a method for high-temperature combustion two-stage desulfurization, which can increase the desulfurization efficiency of a layered combustion furnace to 70-80%.
为了达到上述目的本发明采取下列措施:In order to achieve the above object the present invention takes the following measures:
高温燃烧两段脱硫方法是利用风力将部分钙基添加剂粉末吹入炉膛空间,将层燃炉煤层中的燃烧脱硫反应部分转移到燃烧空间及整个烟气流程,以及时有效地捕捉从煤层释放到烟气中的SO2,实现床层和空间两段脱硫;并通过配风增强高温燃烧段的还原性气氛和后期燃烬段的氧化性气氛,在保证燃烧效率的前提下实现同时脱硫脱硝的效果。The high-temperature combustion two-stage desulfurization method is to use wind force to blow part of the calcium-based additive powder into the furnace space, and transfer the combustion desulfurization reaction part in the coal seam of the bed-fired furnace to the combustion space and the entire flue gas flow, so as to capture the release from the coal seam to SO 2 in the flue gas can achieve two-stage desulfurization in the bed and space; and through air distribution, the reducing atmosphere in the high-temperature combustion section and the oxidizing atmosphere in the post-combustion section can be enhanced to achieve simultaneous desulfurization and denitrification under the premise of ensuring combustion efficiency. Effect.
本发明的优点:采用半预混半喷粉、预混鼓风分层和覆盖鼓风分层三种脱硫剂添加方法,实现层燃炉床层和空间两段脱硫,从时间和空间两个方面克服了简单与入炉散煤预混或炉内直接喷钙脱硫方式的根本缺陷,使层燃炉燃烧脱硫效率提高到70-80%;并且通过合理配风将高温燃烧段的部分风量后移到尾部燃烬段,在保证燃烧效率的前提下实现同时脱硫脱硝的效果。Advantages of the present invention: adopting three desulfurizing agent addition methods of semi-premixed and semi-powder spraying, premixed blast layering and covered blast layering to realize two-stage desulfurization of the bed and space of the layered furnace, from both time and space On the one hand, it overcomes the fundamental defect of simply premixing with loose coal into the furnace or directly spraying calcium into the furnace for desulfurization, so that the combustion desulfurization efficiency of the layer combustion furnace is increased to 70-80%; and through reasonable air distribution, part of the air volume in the high-temperature combustion section is Move to the tail burner section to achieve the effect of simultaneous desulfurization and denitrification under the premise of ensuring combustion efficiency.
下面结合实施例对本发明作详细说明:Below in conjunction with embodiment the present invention is described in detail:
所说的两段脱硫方法为半预混半喷粉、预混鼓风分层和覆盖鼓风分层三种脱硫剂添加方法;并通过配风将高温燃烧段的部分风量后移到尾部燃烬段。The two-stage desulfurization methods are three desulfurizer addition methods: semi-premixed and semi-powder spraying, premixed blast layering and covered blast layering; ember section.
所说的脱硫钙基添加剂的添加方法为:1)半预混半喷粉方法是将部分脱硫钙基添加剂在燃料入炉前与原煤掺混均匀,而将另一部分脱硫钙基添加剂直接喷入炉内燃烧空间,以实现层燃炉床层和空间两段脱硫;2)预混鼓风分层方法是将脱硫钙基添加剂在燃料入炉前与原煤掺混均匀,并且在层燃炉预热及燃烧段利用风力将煤层中的部分钙基添加剂吹散到烟气空间,以实现层燃炉床层和空间两段脱硫。3)覆盖鼓风分层方法是将脱硫钙基添加剂与原煤分层给料,将薄薄一层钙基添加剂粉末均匀覆盖在煤层表面送入炉内,并且在层燃炉预热及燃烧段利用风力将煤层中的部分钙基添加剂吹散到烟气空间,将平铺在煤层表面的钙基添加剂吹散到烟气空间,以实现层燃炉床层和空间两段脱硫。The method of adding the desulfurization calcium-based additives is as follows: 1) The semi-premixed semi-powdering method is to mix part of the desulfurization calcium-based additives with the raw coal evenly before the fuel is put into the furnace, and directly spray another part of the desulfurization calcium-based additives into the furnace. The combustion space in the furnace is used to achieve two-stage desulfurization of the bed and space of the layer-fired furnace; The heat and combustion section uses wind force to blow part of the calcium-based additives in the coal seam into the flue gas space, so as to realize two-stage desulfurization of the bed and space of the bed combustion furnace. 3) The method of covering and blasting layering is to feed desulfurization calcium-based additives and raw coal in layers, and evenly cover a thin layer of calcium-based additive powder on the surface of the coal seam and send it into the furnace, and in the preheating and combustion section of the layer combustion furnace Part of the calcium-based additive in the coal seam is blown into the flue gas space by wind force, and the calcium-based additive spread on the surface of the coal seam is blown into the flue gas space to realize two-stage desulfurization of the bed and space of the bed furnace.
所说的配风方法为:在保证总风量基本不变的情况下,通过配风使层燃炉在高温燃烧段配风量适当减少,而尾部燃烬段配风量相应增加。The air distribution method is as follows: under the condition that the total air volume is basically unchanged, the air distribution volume in the high-temperature combustion section of the bed furnace is appropriately reduced through air distribution, and the air distribution volume in the tail combustion section is correspondingly increased.
本发明的原理:钙基钙基添加剂在层燃炉内高温燃烧脱硫率低的主要原因是:①煤中有机硫在400℃左右即开始分解生成SO2,而石灰石作为最具有工业价值且应用也最为广泛的脱硫剂要在800℃左右才开始大量分解,故在层燃炉预热段煤中有机硫的析出速率远远大于CaCO3的分解速率,大量的SO2从煤层中逸出弥散到燃烧空间;②在层燃炉高温燃烧段,虽然已有大量CaCO3分解成CaO,但由于一次风速的影响,SO2在煤层中的停留时间仅为1秒左右,且SO2与混在煤层中的钙基添加剂存在严重的接触不良问题,故大量SO2来不及与CaO反应即逸散到燃烧空间中,在燃烧烟气中停留3~4秒后离开炉膛出口;③层燃炉燃烧过程中床层的高温环境(1200℃左右)和固硫剂在床层中漫长的停留时间(1小时左右)使得固硫反应产物CaSO4难以大量生成或生成后又重新分解。如果仅仅采用钙基添加剂与散煤预混或炉内直接喷钙脱硫的方法,脱硫率仅能达到20~50%。而采用高温燃烧两段脱硫技术,将脱硫钙基添加剂以半预混半喷粉、预混鼓风分层或覆盖鼓风分层等方法加入炉内,利用风力将部分钙基添加剂粉末吹入炉膛空间,将层燃炉煤层中的燃烧脱硫反应部分转移到燃烧空间及整个烟气流程,以及时有效地捕捉从煤层释放到烟气中的SO2,实现床层和空间两段脱硫,从时间和空间两个方面克服了钙基钙基添加剂在层燃炉内燃烧脱硫率低的困难,使脱硫率大幅度提高到70~80%;并且通过配风,使层燃炉在高温燃烧段配风量适当减少,而尾部燃烬段配风量相应增加,以增强高温燃烧段的还原性气氛和尾部燃烬段的氧化性气氛,使得煤中析出的硫分在燃烧段高温还原区生成更多热稳定性好的CaS,继而在燃烬段低温氧化段转化成更多的CaSO4,克服了CaSO4在高温氧化区热稳定性差的困难,从而大大提高燃烧脱硫率;再则通过配风将高温燃烧段的部分风量后移到尾部燃烬段,使得层燃炉燃烧段的高温分布曲线趋于均匀平缓,同时增强了燃烧段的还原性气氛,使得热力型NOx和燃料型NOx的生成量大为减少,在保证燃烧效率的前提下较好地实现了同时脱硫脱硝的效果。The principle of the present invention: the main reasons for the low desulfurization rate of calcium-based calcium-based additives in the high-temperature combustion in the bed furnace are: ① The organic sulfur in coal begins to decompose to generate SO 2 at about 400 ° C, and limestone is the most industrially valuable and widely used It is also the most widely used desulfurizer that begins to decompose in large quantities at around 800°C, so the precipitation rate of organic sulfur in the coal in the preheating section of the bed furnace is far greater than the decomposition rate of CaCO 3 , and a large amount of SO 2 escapes and disperses from the coal seam to the combustion space; ②In the high-temperature combustion section of the bed-burning furnace, although a large amount of CaCO 3 has been decomposed into CaO, due to the influence of primary wind speed, the residence time of SO 2 in the coal seam is only about 1 second, and SO 2 is mixed with the coal seam The calcium-based additives in the furnace have serious poor contact problems, so a large amount of SO 2 escapes into the combustion space before it can react with CaO, and leaves the furnace outlet after staying in the combustion flue gas for 3 to 4 seconds; ③ During the combustion process of the layer combustion furnace The high temperature environment of the bed (about 1200°C) and the long residence time of the sulfur-fixing agent in the bed (about 1 hour) make it difficult for the sulfur-fixing reaction product CaSO 4 to be generated in large quantities or re-decomposed after being generated. If only calcium-based additives are premixed with loose coal or directly sprayed with calcium in the furnace for desulfurization, the desulfurization rate can only reach 20-50%. The high-temperature combustion two-stage desulfurization technology is used to add desulfurized calcium-based additives into the furnace by half-premixed and half-sprayed powder, premixed blast layering or covered blast layering, and part of the calcium-based additive powder is blown into the furnace by wind force. The furnace space transfers the combustion desulfurization reaction part in the coal seam of the bed-fired furnace to the combustion space and the entire flue gas flow, so as to capture SO 2 released from the coal seam into the flue gas in a timely and effective manner, and realize two-stage desulfurization of the bed and space, from In terms of time and space, it overcomes the difficulty of low desulfurization rate of calcium-based calcium-based additives in the layer combustion furnace, so that the desulfurization rate is greatly increased to 70-80%; The air distribution volume is appropriately reduced, while the air distribution volume in the tail burnout section is increased accordingly to enhance the reducing atmosphere in the high-temperature combustion section and the oxidative atmosphere in the tail burnout section, so that more sulfur precipitated from coal can be generated in the high-temperature reduction zone of the combustion section. CaS with good thermal stability is then converted into more CaSO 4 in the low-temperature oxidation section of the burnout section, which overcomes the difficulty of poor thermal stability of CaSO 4 in the high-temperature oxidation zone, thereby greatly improving the combustion desulfurization rate; Part of the air volume in the high-temperature combustion section is moved to the tail combustion section, which makes the high-temperature distribution curve in the combustion section of the bed-burning furnace tend to be uniform and gentle, and at the same time enhances the reducing atmosphere in the combustion section, so that the thermal NOx and fuel-type NOx The amount of generation is greatly reduced, and the effect of simultaneous desulfurization and denitrification is better achieved under the premise of ensuring combustion efficiency.
实施例:杭州煤苑宾馆4T/H链条炉,由浙江省节能技术检测中心和浙江省环境检测中心站于1999年1月进行了热工测试和脱硫效果测试,在水膜除尘器前,用SYC系列烟气采样仪采样、吸收法捕集、碘量法分析烟气中SO2浓度;在水膜除尘器后用武汉天虹智能仪表厂HT-900型智能烟气分析仪测定烟气中SO2浓度,两段燃烧脱硫技术在4T/H链条炉上的应用效果如表1所示。Embodiment: Hangzhou Coal Garden Hotel 4T/H chain furnace, carried out thermal test and desulfurization effect test in January, 1999 by Zhejiang Provincial Energy Saving Technology Testing Center and Zhejiang Provincial Environmental Testing Center Station, before the water film dust collector, use SYC series flue gas sampler sampling, absorption method capture, and iodometric method to analyze the concentration of SO 2 in the flue gas; after the water film dust collector, use Wuhan Tianhong Intelligent Instrument Factory HT-900 intelligent flue gas analyzer to measure SO in the flue gas 2 concentration, the application effect of the two-stage combustion desulfurization technology on the 4T/H chain furnace is shown in Table 1.
表1两段燃烧脱硫技术在4T/H链条炉上的应用效果
Claims (5)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN00101316A CN1113682C (en) | 2000-01-05 | 2000-01-05 | Two-segment desulfurizing method for high-temp combustion |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN00101316A CN1113682C (en) | 2000-01-05 | 2000-01-05 | Two-segment desulfurizing method for high-temp combustion |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1302683A CN1302683A (en) | 2001-07-11 |
CN1113682C true CN1113682C (en) | 2003-07-09 |
Family
ID=4575876
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN00101316A Expired - Fee Related CN1113682C (en) | 2000-01-05 | 2000-01-05 | Two-segment desulfurizing method for high-temp combustion |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN1113682C (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1924029A (en) * | 2002-09-19 | 2007-03-07 | 李耀中 | Heat static state desulfurizer in molten metal and desulfurization method |
CN104266179A (en) * | 2014-10-11 | 2015-01-07 | 中国电力工程顾问集团西南电力设计院 | Limestone two-stage adding system for CFB (Circulating Fluid Bed) boiler |
CN106402912A (en) * | 2016-08-30 | 2017-02-15 | 上海交通大学 | Method for alleviating stains on flue heating surface of boiler and reducing acid dew point of flue gas |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5160708A (en) * | 1989-03-02 | 1992-11-03 | Kawasaki Jukogyo Kabushiki Kaisha | Dry type simultaneous desulfurization and dedusting apparatus and method of operation therefor |
US5304234A (en) * | 1991-08-30 | 1994-04-19 | Chiyoda Corporation | Gas separation process and unit therefor |
CN1112660A (en) * | 1995-02-15 | 1995-11-29 | 李耀中 | Energy-saving uniflow heat resistance type combined boiler |
US5500195A (en) * | 1992-11-13 | 1996-03-19 | Foster Wheeler Energy Corporation | Method for reducing gaseous emission of halogen compounds in a fluidized bed reactor |
CN1154263A (en) * | 1996-01-11 | 1997-07-16 | 彭斯干 | Method and equipment for desulfurizing flue gas by circulation and fluidization |
-
2000
- 2000-01-05 CN CN00101316A patent/CN1113682C/en not_active Expired - Fee Related
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5160708A (en) * | 1989-03-02 | 1992-11-03 | Kawasaki Jukogyo Kabushiki Kaisha | Dry type simultaneous desulfurization and dedusting apparatus and method of operation therefor |
US5304234A (en) * | 1991-08-30 | 1994-04-19 | Chiyoda Corporation | Gas separation process and unit therefor |
US5500195A (en) * | 1992-11-13 | 1996-03-19 | Foster Wheeler Energy Corporation | Method for reducing gaseous emission of halogen compounds in a fluidized bed reactor |
CN1112660A (en) * | 1995-02-15 | 1995-11-29 | 李耀中 | Energy-saving uniflow heat resistance type combined boiler |
CN1154263A (en) * | 1996-01-11 | 1997-07-16 | 彭斯干 | Method and equipment for desulfurizing flue gas by circulation and fluidization |
Also Published As
Publication number | Publication date |
---|---|
CN1302683A (en) | 2001-07-11 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN108554145A (en) | A kind of flue gas desulfurization denitration dust-removing takes off white device | |
CN106969641A (en) | One kind sintering flue gas decomposes bioxin desulphurization denitration recovery waste heat system and method from combustion-supporting | |
CN100387693C (en) | Formulation and preparation method of desulfurization agent for assisting combustion of fire coal | |
CN101078517A (en) | Method for simultaneously removing SO2, NOx from coal-fired furnace | |
CN109111132A (en) | Low NOx cleaning burning type lime production method, apparatus and its control method | |
CN102671541B (en) | SNCR denitration agent for high and medium-temperature flue gas and use method thereof | |
CN101735877A (en) | Fire coal additive and preparation method thereof | |
CN1113682C (en) | Two-segment desulfurizing method for high-temp combustion | |
CN107099336A (en) | Cement decomposing furnace high temperature tertiary air coal gasification fires NO_x Reduction by Effective system again | |
CN1259523C (en) | A dual-temperature twin-bed gasification and oxidation fluidized bed incinerator for treating high-concentration organic waste liquid | |
CN201363715Y (en) | Smoke purifying boiler | |
CN219161015U (en) | Ultralow emission system of cement kiln flue gas pollutant | |
CN109603544A (en) | A kind of equipment for denitrifying flue gas and method | |
CN114353527B (en) | Green calcining system and process for preparing aggregate by utilizing solid waste | |
WO2022205778A1 (en) | Biomass low-nitrogen combustion boiler based on local gasification technology | |
CN105299628A (en) | Method for applying biomass gasified gases to coal-fired boiler | |
CN213725710U (en) | Sintering flue gas coprocessing system | |
CN109354420A (en) | A kind of low NOx cleaning burning type lime production method, apparatus and its control method | |
CN101225343A (en) | Coal-saving combustion-supporting additive | |
CN114183748A (en) | Low-sulfur low-nitrogen circulating fluidized bed boiler with double ultralow emissions | |
CN212712775U (en) | System for preparing ammonia by pyrolyzing urea with blast furnace gas | |
CN102671532A (en) | Enhanced selective non-catalytic reduction flue gas denitrification method | |
CN107883779B (en) | A system and method for comprehensive treatment of sintering flue gas in a steel plant | |
CN202675299U (en) | Device for combusting nitrogen-containing organic wastes | |
CN113154365A (en) | Supercritical CO2Experimental system for coal-fired boiler ultralow emission research |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C06 | Publication | ||
PB01 | Publication | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
C19 | Lapse of patent right due to non-payment of the annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |