CN105333440A - Flue gas recirculation type garbage pyrolysis gasification oxygen-rich incinerator - Google Patents
Flue gas recirculation type garbage pyrolysis gasification oxygen-rich incinerator Download PDFInfo
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- CN105333440A CN105333440A CN201510900753.2A CN201510900753A CN105333440A CN 105333440 A CN105333440 A CN 105333440A CN 201510900753 A CN201510900753 A CN 201510900753A CN 105333440 A CN105333440 A CN 105333440A
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- 239000003546 flue gas Substances 0.000 title claims abstract description 166
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 163
- 239000001301 oxygen Substances 0.000 title claims abstract description 108
- 229910052760 oxygen Inorganic materials 0.000 title claims abstract description 108
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 title claims abstract description 105
- 238000002309 gasification Methods 0.000 title claims abstract description 40
- 238000000197 pyrolysis Methods 0.000 title claims abstract description 39
- 238000002485 combustion reaction Methods 0.000 claims abstract description 76
- 239000003344 environmental pollutant Substances 0.000 claims abstract description 21
- 231100000719 pollutant Toxicity 0.000 claims abstract description 21
- 239000002918 waste heat Substances 0.000 claims abstract description 14
- 239000000446 fuel Substances 0.000 claims abstract description 12
- 239000007789 gas Substances 0.000 claims description 19
- 239000000779 smoke Substances 0.000 claims description 12
- 239000002826 coolant Substances 0.000 claims description 11
- 239000002245 particle Substances 0.000 claims description 5
- 238000001816 cooling Methods 0.000 claims description 2
- 238000010304 firing Methods 0.000 claims 14
- 230000009977 dual effect Effects 0.000 claims 13
- 238000005422 blasting Methods 0.000 claims 2
- 239000002737 fuel gas Substances 0.000 claims 2
- 239000003517 fume Substances 0.000 claims 2
- 238000005507 spraying Methods 0.000 claims 2
- 239000003595 mist Substances 0.000 claims 1
- 230000002194 synthesizing effect Effects 0.000 claims 1
- 239000002699 waste material Substances 0.000 abstract description 17
- 238000000746 purification Methods 0.000 abstract description 13
- 238000001914 filtration Methods 0.000 abstract description 10
- 239000002243 precursor Substances 0.000 abstract description 5
- 239000000126 substance Substances 0.000 abstract description 4
- 238000004056 waste incineration Methods 0.000 abstract description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 3
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 abstract 1
- 150000002013 dioxins Chemical class 0.000 description 9
- 230000000694 effects Effects 0.000 description 8
- 238000000034 method Methods 0.000 description 8
- 238000002347 injection Methods 0.000 description 7
- 239000007924 injection Substances 0.000 description 7
- 239000010881 fly ash Substances 0.000 description 6
- 230000001105 regulatory effect Effects 0.000 description 5
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 4
- 230000002378 acidificating effect Effects 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 230000009286 beneficial effect Effects 0.000 description 3
- 238000007036 catalytic synthesis reaction Methods 0.000 description 3
- 239000002956 ash Substances 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 238000001514 detection method Methods 0.000 description 2
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 239000012528 membrane Substances 0.000 description 2
- 239000013618 particulate matter Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 239000012298 atmosphere Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- MCJGNVYPOGVAJF-UHFFFAOYSA-N quinolin-8-ol Chemical compound C1=CN=C2C(O)=CC=CC2=C1 MCJGNVYPOGVAJF-UHFFFAOYSA-N 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/027—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
- F23G5/0276—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using direct heating
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
- F23G5/14—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
- F23G5/16—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion in a separate combustion chamber
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2202/00—Combustion
- F23G2202/10—Combustion in two or more stages
- F23G2202/106—Combustion in two or more stages with recirculation of unburned solid or gaseous matter into combustion chamber
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/34—Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Incineration Of Waste (AREA)
Abstract
本发明公开了一种烟气循环式的垃圾热解气化富氧焚烧炉,包括焚烧炉主体、烟气循环送风系统、烟气过滤装置、富氧送风系统、烟气余热换热器、烟气净化装置;其中焚烧炉主体包括一燃室和二燃室,分别用于垃圾热解气化和可燃物质的焚烧;循环的烟气通过烟气循环送风系统注入焚烧炉内,提高炉内湍流度,强化垃圾焚烧,减少未完全燃烧污染物如二噁英前驱体的生成,降低污染物排放。富氧送风系统能提高焚烧温度、减少辅助燃料消耗,烟气过滤装置、烟气净化装置可进一步减少污染物排放,烟气余热换热器可以回收烟气余热。本发明能有效解决垃圾热值低、含水量高、空气中含氧量低所带来的焚烧温度低、燃烧效率差、辅助燃料消耗多,污染物排放不达标等问题。
The invention discloses a flue gas circulation type garbage pyrolysis gasification oxygen-enriched incinerator, comprising an incinerator body, a flue gas circulation air supply system, a flue gas filtering device, an oxygen-enriched air supply system, and a flue gas waste heat heat exchanger , flue gas purification device; the main body of the incinerator includes a combustion chamber and a second combustion chamber, which are respectively used for pyrolysis gasification of waste and incineration of combustible substances; the circulating flue gas is injected into the incinerator through the flue gas circulation air supply system, improving The degree of turbulence in the furnace strengthens waste incineration, reduces the generation of incompletely burned pollutants such as dioxin precursors, and reduces pollutant emissions. The oxygen-enriched air supply system can increase the incineration temperature and reduce the consumption of auxiliary fuel. The flue gas filtering device and the flue gas purification device can further reduce pollutant emissions, and the flue gas waste heat heat exchanger can recover the waste heat of the flue gas. The invention can effectively solve the problems of low incineration temperature, poor combustion efficiency, high consumption of auxiliary fuel and substandard discharge of pollutants caused by low calorific value, high water content and low oxygen content in the air.
Description
技术领域technical field
本发明属于焚烧炉领域,更具体地,涉及一种采用烟气循环方式的垃圾热解气化富氧焚烧炉。The invention belongs to the field of incinerators, and more specifically relates to a garbage pyrolysis gasification oxygen-enriched incinerator adopting a flue gas circulation mode.
背景技术Background technique
随着经济的发展,人民物质生活水平得到极大的提高,伴随着产生了大量的垃圾,垃圾对大气、土壤、水源等造成严重污染,对我们的生存环境造成了巨大危害,解决垃圾问题刻不容缓。焚烧处理是目前公认的较好的垃圾减容、减量化的处理手段,除了产生的灰渣以外,可燃物质完全燃尽,一般认为能够减容85-90%。目前在发达国家,焚烧处理是主流的垃圾终端处理技术。近些年来,我国垃圾焚烧行业也获得了快速的发展,但垃圾焚烧水平与发达国家还有较大差距,先进焚烧设备尤其是处理较为分散的垃圾的小型紧凑焚烧设备缺口巨大。随着最新《生活垃圾焚烧污染控制标准》GB18485-2014的出台,污染物排放限值大幅下降,对焚烧水平提出了更高要求,因此急需开发出新型高效的焚烧设备。With the development of the economy, people's material living standards have been greatly improved, accompanied by a large amount of garbage, which has caused serious pollution to the atmosphere, soil, water sources, etc., and has caused great harm to our living environment. It is urgent to solve the garbage problem. . Incineration treatment is currently recognized as a better treatment method for volume reduction and volume reduction. Except for the ash generated, the combustible substances are completely burned, and it is generally believed that it can reduce volume by 85-90%. Currently in developed countries, incineration is the mainstream waste terminal treatment technology. In recent years, my country's waste incineration industry has also achieved rapid development, but there is still a large gap between the level of waste incineration and developed countries, and there is a huge gap in advanced incineration equipment, especially small and compact incineration equipment that handles scattered waste. With the introduction of the latest "Pollution Control Standards for Domestic Garbage Incineration" GB18485-2014, the pollutant discharge limits have dropped significantly, and higher requirements have been placed on the incineration level. Therefore, it is urgent to develop new and efficient incineration equipment.
垃圾焚烧效果主要取决于“3T”原则,“3T”即是指温度、湍流度、停留时间。焚烧温度越高、炉内湍流度越大、烟气炉内停留时间越长,焚烧效果越好,污染物如二噁英等分解更完全。根据环保部规定,我国生活垃圾二燃室焚烧温度需达到850℃以上,危险废弃物需达到1100℃以上,烟气二燃室停留时间需达到2S以上。由于我国垃圾成分复杂,含水量较高且热值较低,焚烧过程中存在以下难题:The effect of waste incineration mainly depends on the "3T" principle, "3T" refers to temperature, turbulence, and residence time. The higher the incineration temperature, the greater the turbulence in the furnace, and the longer the residence time of the flue gas in the furnace, the better the incineration effect and the more complete decomposition of pollutants such as dioxins. According to the regulations of the Ministry of Environmental Protection, the incineration temperature of domestic waste in the secondary combustion chamber in my country must be above 850 °C, hazardous waste must be above 1100 °C, and the residence time of flue gas in the secondary combustion chamber must be above 2S. Due to the complex composition of waste in my country, high water content and low calorific value, the following problems exist in the incineration process:
①难以实现稳定焚烧及达到规定的焚烧温度。为了达到要求,必须投入大量辅助燃料,增加了二噁英等污染物排放及运行成本。① It is difficult to achieve stable incineration and reach the specified incineration temperature. In order to meet the requirements, a large amount of auxiliary fuel must be invested, which increases the emission of pollutants such as dioxins and operating costs.
②为达到停留时间2S的规定,炉内烟气行程较长或烟气流速过低,容易造成炉内湍流度不足,影响焚烧效果,增加了二噁英等污染物的排放。② In order to meet the residence time requirement of 2S, the flue gas travel in the furnace is long or the flue gas flow rate is too low, which may easily cause insufficient turbulence in the furnace, affect the incineration effect, and increase the emission of pollutants such as dioxins.
③高原地区运行时由于缺氧,上述问题会更加严重。为保证燃烧,高原地区焚烧时需鼓入相比于平原地区更多的空气,使得焚烧温度大大降低,并且烟气流速增加,减少了炉内停留时间,二噁英等污染物的排放明显上升。③Due to lack of oxygen during operation in plateau areas, the above problems will be more serious. In order to ensure combustion, more air needs to be blown into the plateau area than in the plain area, so that the incineration temperature is greatly reduced, and the flue gas flow rate is increased, which reduces the residence time in the furnace and significantly increases the emission of pollutants such as dioxins. .
发明内容Contents of the invention
针对以上问题,本发明提供了一种采用烟气循环方式的垃圾热解气化富氧焚烧炉,该炉型在垃圾热解气化富氧焚烧炉的基础上,增加了烟气循环模式,可提高焚烧效果和焚烧炉热利用效率,减少污染物如二噁英的生成,并且设备体积较小,可制造为小型移动式的设备,方便处理比较分散的垃圾。本发明提出一种采用烟气循环方式的垃圾热解气化富氧焚烧炉,包括焚烧炉主体、烟气循环送风系统:In view of the above problems, the present invention provides a waste pyrolysis gasification oxygen-enriched incinerator adopting the flue gas circulation mode. It can improve the incineration effect and the heat utilization efficiency of the incinerator, reduce the generation of pollutants such as dioxin, and the equipment is small in size, and can be manufactured as a small mobile equipment to facilitate the treatment of scattered garbage. The present invention proposes a garbage pyrolysis gasification oxygen-enriched incinerator adopting the flue gas circulation mode, including the main body of the incinerator and the flue gas circulation air supply system:
所述焚烧炉主体包括一燃室2和二燃室3,一燃室2用于垃圾热解气化,产生的可燃气体送至二燃室3;一燃室2装有至少一个第一燃烧器1,用于一燃室2的送风及辅助燃料的喷入,实现一燃室2内垃圾的热解气化;二燃室3用于对一燃室2产生的可燃气体进行焚烧,其装有第二燃烧器4,用于二燃室3的送风及辅助燃料的喷入;The main body of the incinerator includes a combustion chamber 2 and a second combustion chamber 3. The first combustion chamber 2 is used for pyrolysis and gasification of garbage, and the combustible gas produced is sent to the second combustion chamber 3; the first combustion chamber 2 is equipped with at least one first combustion chamber. The device 1 is used for the air supply of the first combustion chamber 2 and the injection of auxiliary fuel to realize the pyrolysis and gasification of the garbage in the first combustion chamber 2; the second combustion chamber 3 is used to incinerate the combustible gas generated by the first combustion chamber 2, It is equipped with a second burner 4 for the air supply of the second combustion chamber 3 and the injection of auxiliary fuel;
所述烟气循环送风系统包括换热器13、烟气增压风机103和烟气回送管线81;二燃室3烟气出口通过烟气管线总线8与换热器13相连,换热器13经烟气回送管线81连接到焚烧炉;所述烟气增压风机103安装在烟气回送管线81上;The flue gas circulation air supply system includes a heat exchanger 13, a flue gas booster fan 103 and a flue gas return pipeline 81; the flue gas outlet of the second combustion chamber 3 is connected to the heat exchanger 13 through the flue gas pipeline bus 8, and the heat exchanger 13 is connected to the incinerator through the flue gas return pipeline 81; the flue gas booster fan 103 is installed on the flue gas return pipeline 81;
工作中,二燃室3产生的烟气经烟气管线总线8送到换热器13换热后,一路经烟气外排管线82排出系统外,另一路经烟气增压风机103加压,经烟气回送管线81回送至二燃室3。During operation, the flue gas generated in the second combustion chamber 3 is sent to the heat exchanger 13 through the flue gas pipeline bus 8 for heat exchange, and one way is discharged out of the system through the flue gas discharge pipeline 82, and the other way is pressurized by the flue gas booster fan 103 , and return to the secondary combustion chamber 3 through the flue gas return pipeline 81.
进一步的,所述的垃圾热解气化富氧焚烧炉的烟气增压风机103到二燃室3的烟气回送管线分两路连接到二燃室3,一路经第一烟气回送管线支线811连接至二燃室3的第二燃烧器4,一路经第二烟气回送管线支线812连接至二燃室循环烟气喷入口19;烟气回送的作用是提高二燃室内湍流度,增强焚烧效果,使得污染物如二噁英前驱体生成较少且分解完全,降低污染物排放。Further, the flue gas return pipeline from the flue gas booster fan 103 of the waste pyrolysis gasification oxygen-enriched incinerator to the second combustion chamber 3 is connected to the second combustion chamber 3 in two ways, and one path passes through the first flue gas return pipeline The branch line 811 is connected to the second burner 4 of the second combustion chamber 3, and one path is connected to the circulating flue gas injection port 19 of the second combustion chamber through the second flue gas return pipeline branch line 812; the function of the flue gas return is to increase the turbulence in the second combustion chamber, Enhance the incineration effect, so that pollutants such as dioxin precursors are less generated and completely decomposed, reducing pollutant emissions.
进一步的,所述垃圾热解气化富氧焚烧炉,包括烟气过滤装置14,烟气过滤装置14安装在换热器13出口和烟气回送管线81入口之间,用于将烟气中颗粒物捕集下来,减少对烟气增压风机103的磨损,并减少重金属排放。Further, the waste pyrolysis gasification oxygen-enriched incinerator includes a flue gas filtering device 14, which is installed between the outlet of the heat exchanger 13 and the inlet of the flue gas return pipeline 81, and is used to filter the flue gas The particles are captured to reduce wear on the flue gas booster fan 103 and reduce heavy metal emissions.
进一步的,所述的垃圾热解气化富氧焚烧炉,包括富氧送风系统,所述富氧送风系统包括富氧空气发生装置7和氧气增压风机101,两者相连后接通至换热器13;换热器13氧气出口端连接有热氧总管线9B,热氧总管线9B通过第二热氧管线支线92与二燃室3的第二燃烧器4连通;工作时,富氧空气发生装置7产生的富氧空气,经氧气增压风机101加压和换热器13预热,经热氧总管线9B,通过第二热氧管线支线92,送至二燃室3的第二燃烧器4。在此基础上,也可通过第一热氧管线支线91与一燃室2的第一燃烧器1连通;富氧送风系统,通过将富氧空气送至一燃室2,提高了一燃室2送风的温度和氧浓度,稳定一燃室2的垃圾的热解气化过程,并且产生的可燃气体热值较高,有利于二燃室3的焚烧,富氧送风系统还提高了送入二燃室3气体的温度和氧浓度,提高了二燃室3燃烧温度,减少污染物如二噁英前驱体的产生,富氧送风系统减少了辅助燃料消耗,提高焚烧炉的热利用效率。Further, the waste pyrolysis gasification oxygen-enriched incinerator includes an oxygen-enriched air supply system, and the oxygen-enriched air supply system includes an oxygen-enriched air generating device 7 and an oxygen booster fan 101, and the two are connected and then connected To the heat exchanger 13; the oxygen outlet end of the heat exchanger 13 is connected with a hot oxygen main pipeline 9B, and the hot oxygen main pipeline 9B communicates with the second burner 4 of the second combustion chamber 3 through the second hot oxygen pipeline branch line 92; during work, The oxygen-enriched air generated by the oxygen-enriched air generating device 7 is pressurized by the oxygen booster fan 101 and preheated by the heat exchanger 13, and then sent to the second combustion chamber 3 through the thermal oxygen main pipeline 9B and the second thermal oxygen pipeline branch line 92 The second burner 4. On this basis, it can also be communicated with the first burner 1 of the first combustion chamber 2 through the first hot oxygen branch line 91; The temperature and oxygen concentration of the air supply in chamber 2 stabilize the pyrolysis and gasification process of the garbage in the first combustion chamber 2, and the combustible gas produced has a higher calorific value, which is beneficial to the incineration of the second combustion chamber 3, and the oxygen-enriched air supply system also improves The temperature and oxygen concentration of the gas sent to the second combustion chamber 3 are improved, the combustion temperature of the second combustion chamber 3 is increased, and the generation of pollutants such as dioxin precursors is reduced. The oxygen-enriched air supply system reduces the consumption of auxiliary fuel and improves the efficiency of the incinerator. heat utilization efficiency.
进一步的,所述的垃圾热解气化富氧焚烧炉中,所述的烟气外排管线82是烟气过滤装置14出口连接到系统排烟出口的管线,包括烟气净化装置16和引风机102;外排烟气经烟气余热换热器15降温后,经烟气净化装置16进一步脱除烟气中的污染物后外排;所述引风机102安装在烟气外排管线82的排烟出口。Further, in the above-mentioned garbage pyrolysis gasification oxygen-enriched incinerator, the flue gas exhaust pipeline 82 is a pipeline connecting the outlet of the flue gas filtering device 14 to the exhaust outlet of the system, including the flue gas purification device 16 and the exhaust gas outlet. Fan 102; the exhausted flue gas is cooled by the flue gas waste heat exchanger 15, and the pollutants in the flue gas are further removed by the flue gas purification device 16, and then discharged; the induced draft fan 102 is installed on the flue gas discharge pipeline 82 smoke outlet.
进一步的,所述的垃圾热解气化富氧焚烧炉的烟气外排管线82中,还包括烟气余热换热器15和/或冷却介质管线17;所述烟气余热换热器15用于将外排的烟气降温,以便烟气后续净化处理;所述冷却介质管线17用于回收外排烟气余热,进一步提高系统能效。Further, the flue gas exhaust pipeline 82 of the waste pyrolysis gasification oxygen-enriched incinerator also includes a flue gas waste heat exchanger 15 and/or a cooling medium pipeline 17; the flue gas waste heat exchanger 15 It is used to cool down the exhausted flue gas for subsequent purification treatment of the flue gas; the cooling medium pipeline 17 is used to recover the waste heat of the exhausted flue gas to further improve the energy efficiency of the system.
进一步的,所述的垃圾热解气化富氧焚烧炉的中的烟气过滤装置14的运行温度优选为500-400℃,在此温度区间将飞灰等颗粒捕集下来可以避免飞灰与烟气中组分发生的200-400℃的从头合成异相催化反应(denovoheterogeneouslycatalysedreactions),减少烟气管道中二噁英的催化合成。Further, the operating temperature of the flue gas filtering device 14 in the oxygen-enriched pyrolysis gasification incinerator of waste is preferably 500-400°C, and trapping particles such as fly ash in this temperature range can avoid fly ash and Denovo heterogeneouslycatalysed reactions at 200-400°C for components in the flue gas reduce the catalytic synthesis of dioxins in the flue gas pipeline.
进一步的,所述的垃圾热解气化富氧焚烧炉的中的第一热氧管线支线91、第二热氧管线支线92、第一烟气回送管线支线811和第二烟气回送管线支线812上均设有计量表和调节阀。Further, the first thermal oxygen pipeline branch 91, the second thermal oxygen pipeline branch 92, the first flue gas return pipeline branch 811 and the second flue gas return pipeline branch in the waste pyrolysis gasification oxygen-enriched incinerator 812 is equipped with gauges and regulating valves.
进一步的,所述的垃圾热解气化富氧焚烧炉的中的富氧空气预热是通过换热器15实现的,所述换热器13加装有冷却介质管线17,用于回收烟气余热。Further, the preheating of the oxygen-enriched air in the waste pyrolysis gasification oxygen-enriched incinerator is realized through the heat exchanger 15, and the heat exchanger 13 is equipped with a cooling medium pipeline 17 for recovering smoke Air waste heat.
进一步的,所述的垃圾热解气化富氧焚烧炉的中的焚烧炉还包括空气供应管路,所述空气供应管路包括空气增压风机104、换热器13和空气管线18,空气增压风机104用于将空气加压送入换热器13换热后,经空气管线18送入一燃室2。一燃室2用空气代替富氧空气,可以降低运行成本。Further, the incinerator in the waste pyrolysis gasification oxygen-enriched incinerator also includes an air supply pipeline, and the air supply pipeline includes an air booster fan 104, a heat exchanger 13 and an air pipeline 18, and the air The booster fan 104 is used to pressurize the air into the heat exchanger 13 for heat exchange, and then send it into the combustion chamber 2 through the air pipeline 18 . The first combustion chamber 2 uses air instead of oxygen-enriched air, which can reduce operating costs.
进一步的,所述烟气外排管线82是烟气过滤装置14出口连接到系统排烟出口的管线,包括烟气净化装置16和引风机102;外排烟气经烟气余热换热器15降温后,经烟气净化装置16进一步脱除烟气中的污染物后外排;所述引风机102安装在烟气外排管线82的排烟出口;烟气净化装置16可对烟气中的酸性成分进行中和,使得烟气中的HCl、SO2等酸性物质得到脱除。Further, the flue gas exhaust pipeline 82 is a pipeline connecting the outlet of the flue gas filtering device 14 to the exhaust outlet of the system, including the flue gas purification device 16 and the induced draft fan 102; After cooling down, the pollutants in the flue gas are further removed by the flue gas purification device 16 and then discharged; the induced draft fan 102 is installed at the exhaust outlet of the flue gas discharge pipeline 82; The acidic components in the flue gas are neutralized, so that acidic substances such as HCl and SO 2 in the flue gas are removed.
进一步的,所述的垃圾热解气化富氧焚烧炉中,所述富氧空气发生装置7的型式包括气罐式或采用膜分离法、变压吸附法或深冷法的制氧装置。Further, in the above-mentioned waste pyrolysis gasification oxygen-enriched incinerator, the type of the oxygen-enriched air generating device 7 includes a gas tank type or an oxygen generating device using membrane separation method, pressure swing adsorption method or cryogenic method.
进一步的,所述的垃圾热解气化富氧焚烧炉中,所述富氧送风系统可取消送至一燃室2第一燃烧器1富氧空气的支路管线91,可由空气增压风机104通过空气管线18向一燃室2的第一燃烧器1送入经过换热器13预热的空气,节省运行成本。Further, in the above-mentioned waste pyrolysis gasification oxygen-enriched incinerator, the oxygen-enriched air supply system can cancel the branch line 91 of the oxygen-enriched air sent to the first burner 1 of the first combustion chamber 2, and can be pressurized by air The blower 104 sends the air preheated by the heat exchanger 13 to the first burner 1 of the first combustion chamber 2 through the air pipeline 18, so as to save operating costs.
进一步的,所述的垃圾热解气化富氧焚烧炉中,富氧空气也可经烟气余热换热器15预热;换热器13上也可装有冷却介质管线,用于回收烟气余热。Further, in the above-mentioned garbage pyrolysis gasification oxygen-enriched incinerator, the oxygen-enriched air can also be preheated through the flue gas waste heat heat exchanger 15; the heat exchanger 13 can also be equipped with a cooling medium pipeline for recovering smoke Air waste heat.
总体而言,通过本发明所构思的以上技术方案与现有技术相比,能够取得下列有益效果:Generally speaking, compared with the prior art, the above technical solutions conceived by the present invention can achieve the following beneficial effects:
1)回收了烟气中的显热,焚烧炉热利用效率提高,减少了辅助燃料的消耗。1) The sensible heat in the flue gas is recovered, the heat utilization efficiency of the incinerator is improved, and the consumption of auxiliary fuel is reduced.
2)焚烧炉的送风温度提高,稳定了热解气化焚烧过程,提高了热解气化产生的可燃气的热值,提高了焚烧的温度。2) The air supply temperature of the incinerator is increased, which stabilizes the pyrolysis gasification incineration process, increases the calorific value of the combustible gas produced by pyrolysis gasification, and increases the incineration temperature.
3)烟气循环提高了炉内湍流度,提高了焚烧效果,减少了污染物如二噁英的生成。3) The flue gas circulation improves the turbulence in the furnace, improves the incineration effect, and reduces the generation of pollutants such as dioxins.
4)烟气循环前采用烟气过滤装置将飞灰等颗粒捕集下来,减少了风机的磨损,降低了颗粒物及重金属的排放,并且避免了飞灰与烟气发生的200-400℃的从头合成异相催化反应,减少了烟道中的二噁英的催化合成,使得二噁英的生成量明显下降。4) The flue gas filter device is used to trap fly ash and other particles before the flue gas circulation, which reduces the wear of the fan, reduces the emission of particulate matter and heavy metals, and avoids the 200-400°C de novo generation of fly ash and flue gas Synthetic heterogeneous catalytic reaction reduces the catalytic synthesis of dioxins in the flue, making the generation of dioxins significantly reduced.
5)解决了高灰、高湿、低热值垃圾和高原地区垃圾清洁、高效的焚烧问题。5) Solve the problem of clean and efficient incineration of high ash, high humidity, low calorific value garbage and garbage in plateau areas.
总之,烟气循环式垃圾热解气化富氧焚烧炉能够实现较好的焚烧效果且具有节能意义,能够达到更严格的排放标准,具有很大的技术优势。In short, the flue gas circulation type waste pyrolysis gasification oxygen-enriched incinerator can achieve better incineration effect and has energy-saving significance, can meet stricter emission standards, and has great technical advantages.
附图说明Description of drawings
图1为本发明结构示意图;Fig. 1 is a structural representation of the present invention;
图中各个主要部件名称:1-第一燃烧器,2-一燃室,3-二燃室、4-第二燃烧器、51-调节阀、61-计量表、7-富氧空气发生装置、101-氧气增压风机、11-放散阀、12-开关阀、13-换热器、14-烟气过滤装置、103-烟气增压风机、15-烟气余热换热器、16-烟气净化装置、102-引风机、104-空气增压风机、19-循环烟气喷入口;Names of main components in the figure: 1-first burner, 2-first combustion chamber, 3-second combustion chamber, 4-second burner, 51-regulating valve, 61-meter, 7-oxygen-enriched air generator , 101-oxygen booster fan, 11-release valve, 12-on-off valve, 13-heat exchanger, 14-flue gas filter device, 103-flue gas booster fan, 15-flue gas waste heat exchanger, 16- Flue gas purification device, 102-induced fan, 104-air booster fan, 19-circulating flue gas injection inlet;
管线名称:9-氧气管线总线、9B-热氧管线总线、91-第一热氧管线支线、92-第二热氧管线支线、8-烟气管线总线、81-烟气回送管线、811-第一烟气回送管线支线、812-第二烟气回送管线支线、82-烟气外排管线、18-空气管线17-冷却介质管线。Pipeline name: 9-oxygen pipeline bus, 9B-thermal oxygen pipeline bus, 91-first thermal oxygen pipeline branch line, 92-second thermal oxygen pipeline branch line, 8-flue gas pipeline bus, 81-flue gas return pipeline, 811- The first flue gas return pipeline branch line, 812-the second flue gas return pipeline branch line, 82-the flue gas discharge pipeline, 18-air pipeline, 17-cooling medium pipeline.
具体实施方式detailed description
为了使本发明的目的、技术方案及优点更加清楚明白,以下结合附图及实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅仅用以解释本发明,并不用于限定本发明。此外,下面所描述的本发明各个实施方式中所涉及到的技术特征只要彼此之间未构成冲突就可以相互组合。In order to make the object, technical solution and advantages of the present invention clearer, the present invention will be further described in detail below in conjunction with the accompanying drawings and embodiments. It should be understood that the specific embodiments described here are only used to explain the present invention, not to limit the present invention. In addition, the technical features involved in the various embodiments of the present invention described below can be combined with each other as long as they do not constitute a conflict with each other.
参照图1,一种采用烟气循环方式的垃圾热解气化富氧焚烧炉,其特征在于,包括焚烧炉主体、烟气循环送风系统、烟气过滤装置、富氧送风系统、烟气余热换热器、烟气净化装置:Referring to Figure 1, a waste pyrolysis gasification oxygen-enriched incinerator adopting flue gas circulation is characterized in that it includes an incinerator main body, a flue gas circulation air supply system, a flue gas filtering device, an oxygen-enriched air supply system, a flue gas Gas waste heat exchanger, flue gas purification device:
所述焚烧炉主体包括一燃室2和二燃室3,一燃室2用于垃圾热解气化,产生的可燃气体送至二燃室3,一燃室装有至少一个第一燃烧器1,用于一燃室2的送风及辅助燃料的喷入,实现一燃室2内垃圾的热解气化;二燃室3对一燃室2产生的可燃气体进一步焚烧,其装有第二燃烧器4,用于二燃室3的送风及辅助燃料的喷入;The main body of the incinerator includes a combustion chamber 2 and a second combustion chamber 3. The first combustion chamber 2 is used for pyrolysis and gasification of garbage, and the combustible gas produced is sent to the second combustion chamber 3. The first combustion chamber is equipped with at least one first burner 1. It is used for the air supply of the first combustion chamber 2 and the injection of auxiliary fuel to realize the pyrolysis and gasification of the garbage in the first combustion chamber 2; the second combustion chamber 3 further incinerates the combustible gas produced by the first combustion chamber 2, which is equipped with The second burner 4 is used for the air supply of the second combustion chamber 3 and the injection of auxiliary fuel;
所述烟气循环送风系统包括烟气增压风机103、换热器13、和烟气回送管线81;其换热器13通过烟气管线总线与二燃室烟气出口连通;所述烟气过滤装置14安装在换热器13烟气出口,所述烟气回送管线是烟气过滤装置14出口连接到焚烧炉的管线;其中烟气增压风机103安装在烟气回送管线81上,位于烟气回送管线的始端;二燃室3产生的烟气经换热器13换热,再经烟气过滤装置14滤除颗料物后,一路经烟气外排管线82排出系统外,另一路经烟气增压风机103加压,经烟气回送管线82回送至二燃室3,烟气回送的作用是提高二燃室3内湍流度,增强焚烧效果,使得污染物如二噁英前驱体生成较少且分解完全,降低污染物排放;The flue gas circulation air supply system includes a flue gas booster fan 103, a heat exchanger 13, and a flue gas return pipeline 81; the heat exchanger 13 communicates with the flue gas outlet of the second combustion chamber through the flue gas pipeline bus; the flue gas The gas filter device 14 is installed at the flue gas outlet of the heat exchanger 13, and the flue gas return pipeline is a pipeline connected to the incinerator at the outlet of the flue gas filter device 14; wherein the flue gas booster fan 103 is installed on the flue gas return pipeline 81, Located at the beginning of the flue gas return pipeline; the flue gas generated by the second combustion chamber 3 is heat-exchanged by the heat exchanger 13, and then filtered by the flue gas filtering device 14 to remove particulate matter, and then discharged out of the system through the flue gas discharge pipeline 82 all the way. The other way is pressurized by the flue gas booster fan 103, and returned to the second combustion chamber 3 through the flue gas return pipeline 82. The function of the flue gas return is to increase the turbulence in the second combustion chamber 3, enhance the incineration effect, and make pollutants such as dioxin British precursors are less generated and completely decomposed, reducing pollutant emissions;
本实施例中,所述烟气增压风机103到二燃室3的烟气回送管线81分两路:一路811回送至二燃室第二燃烧器4,此管线811上有计量表63和调节阀53;一路812回送至二燃室循环烟气喷入口19,此管线812上有加量表64和调节阀54;In this embodiment, the flue gas return pipeline 81 from the flue gas booster blower 103 to the second combustion chamber 3 is divided into two routes: one route 811 is returned to the second burner 4 in the second combustion chamber, and the meter 63 and Regulating valve 53; one route 812 is sent back to the circulating flue gas injection inlet 19 of the second combustion chamber, and there is a meter 64 and a regulating valve 54 on this pipeline 812;
本实施例中,所述烟气外排管线82是烟气过滤装置14出口连接到系统排烟出口的管线,包括烟气净化装置16和引风机102;外排烟气经烟气余热换热器15降温后,经烟气净化装置16进一步脱除烟气中的污染物后外排;所述引风机102安装在烟气外排管线82的排烟出口;In this embodiment, the flue gas exhaust pipeline 82 is a pipeline connecting the outlet of the flue gas filtering device 14 to the exhaust outlet of the system, including the flue gas purification device 16 and the induced draft fan 102; After the device 15 cools down, the pollutants in the flue gas are further removed by the flue gas purification device 16 and then discharged; the induced draft fan 102 is installed at the smoke exhaust outlet of the flue gas discharge pipeline 82;
本实施例中,所述烟气余热换热器15位于烟气外排管线82上,位于烟气净化装置16之前,换热器15用于冷却介质管线17输送的冷却介质与烟气外排管线82输送的外排烟气换热,将外排的烟气降温,冷却介质获得的热量可以被系统外设施回收利用;In this embodiment, the flue gas waste heat heat exchanger 15 is located on the flue gas discharge pipeline 82 and before the flue gas purification device 16. The heat exchanger 15 is used for the cooling medium transported by the cooling medium pipeline 17 and the flue gas discharge. The heat exchange of the exhausted flue gas transported by the pipeline 82 cools the exhausted flue gas, and the heat obtained by the cooling medium can be recycled by facilities outside the system;
本实施例中,还包括富氧送风系统,所述富氧送风系统包括富氧空气发生装置7、氧气管线总线9上的氧气增压风机101、开关阀12、放散阀11;富氧空气发生装置7和氧气增压风机101相连后接通至换热器13,换热器13氧气出口端连接有热氧总管线9B,热氧总管线9B另一端分别分别通过第一热氧管线支线91与一燃室2的第一燃烧器1连通,通过第二热氧管线支线92与二燃室3的第二燃烧器4连通;富氧空气发生装置7产生的富氧空气,经氧气增压风机101加压和换热器13预热,一路91经计量表61和调节阀51的检测和调节,送至一燃室2的第一燃烧器1,另一路92经计量表62和调节阀52的检测和调节,送至二燃室3的第二燃烧器4,富氧送风系统,提高了向一燃室2和二燃室3送风中的氧浓度,能够稳定一燃室2的垃圾的热解气化过程,并且产生的可燃气体热值较高,有利于二燃室3的焚烧,富氧送风系统还提高了二燃室3燃烧温度,减少污染物如二噁英前驱体的产生,富氧送风系统减少了辅助燃料消耗,提高焚烧炉的热利用效率;In this embodiment, an oxygen-enriched air supply system is also included, and the oxygen-enriched air supply system includes an oxygen-enriched air generating device 7, an oxygen booster fan 101 on the oxygen pipeline bus 9, an on-off valve 12, and a release valve 11; The air generating device 7 is connected to the oxygen booster fan 101 and then connected to the heat exchanger 13. The oxygen outlet end of the heat exchanger 13 is connected to a thermal oxygen main pipeline 9B, and the other ends of the thermal oxygen main pipeline 9B pass through the first thermal oxygen pipeline respectively. The branch line 91 communicates with the first burner 1 of the first combustion chamber 2, and communicates with the second burner 4 of the second combustion chamber 3 through the second thermal oxygen pipeline branch line 92; the oxygen-enriched air produced by the oxygen-enriched air generating device 7 passes through oxygen The pressurized fan 101 is pressurized and the heat exchanger 13 is preheated, and one path 91 is sent to the first burner 1 of the first combustion chamber 2 through the detection and adjustment of the meter 61 and the regulating valve 51, and the other path 92 is passed through the meter 62 and The detection and adjustment of the regulating valve 52 is sent to the second burner 4 of the second combustion chamber 3, and the oxygen-enriched air supply system improves the oxygen concentration in the air supply to the first combustion chamber 2 and the second combustion chamber 3, which can stabilize the first combustion chamber. The pyrolysis gasification process of the garbage in the second combustion chamber, and the combustible gas produced has a higher calorific value, which is beneficial to the incineration of the second combustion chamber 3. The oxygen-enriched air supply system also improves the combustion temperature of the second combustion chamber 3 and reduces pollutants such as secondary combustion. The production of oxin precursors, the oxygen-enriched air supply system reduces the consumption of auxiliary fuel and improves the heat utilization efficiency of the incinerator;
本实施例中,所述烟气外排管线还包括烟气净化装置16,用于对烟气中的酸性成分进行中和,使得烟气中的HCl、SO2等酸性物质得到脱除;In this embodiment, the flue gas discharge pipeline also includes a flue gas purification device 16 , which is used to neutralize the acidic components in the flue gas, so that acidic substances such as HCl and SO in the flue gas are removed;
本实施例中,所述富氧空气发生装置7的型式为膜分离制氧装置;In this embodiment, the type of the oxygen-enriched air generator 7 is a membrane separation oxygen generator;
本实施例中,所述烟气过滤装置14的运行温度优选为400℃,在此温度将飞灰等颗粒捕集下来可以避免飞灰与烟气中组分发生的200-400℃的从头合成异相催化反应,减少烟气管道中二噁英的催化合成;In this embodiment, the operating temperature of the flue gas filtering device 14 is preferably 400°C. At this temperature, trapping fly ash and other particles can avoid the de novo synthesis of fly ash and components in the flue gas at 200-400°C. Heterogeneous catalytic reaction to reduce the catalytic synthesis of dioxins in the flue gas pipeline;
本领域的技术人员容易理解,以上所述仅为本发明的较佳实施例而已,并不用以限制本发明,凡在本发明的精神和原则之内所作的任何修改、简化、等同替换和改进等,均应包含在本发明的保护范围之内。Those skilled in the art can easily understand that the above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, simplifications, equivalent replacements and improvements made within the spirit and principles of the present invention etc., should be included within the protection scope of the present invention.
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