CN110145749A - A system and method for safe incineration disposal of hyperaccumulator plants - Google Patents
A system and method for safe incineration disposal of hyperaccumulator plants Download PDFInfo
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- CN110145749A CN110145749A CN201910405789.1A CN201910405789A CN110145749A CN 110145749 A CN110145749 A CN 110145749A CN 201910405789 A CN201910405789 A CN 201910405789A CN 110145749 A CN110145749 A CN 110145749A
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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
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/10—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of field or garden waste or biomasses
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- 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
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- 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
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- 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
- F23J15/027—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 cyclone separators
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- 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
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- 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
- F23J15/06—Arrangements of devices for treating smoke or fumes of coolers
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23L—SUPPLYING AIR OR NON-COMBUSTIBLE LIQUIDS OR GASES TO COMBUSTION APPARATUS IN GENERAL ; VALVES OR DAMPERS SPECIALLY ADAPTED FOR CONTROLLING AIR SUPPLY OR DRAUGHT IN COMBUSTION APPARATUS; INDUCING DRAUGHT IN COMBUSTION APPARATUS; TOPS FOR CHIMNEYS OR VENTILATING SHAFTS; TERMINALS FOR FLUES
- F23L15/00—Heating of air supplied for combustion
- F23L15/04—Arrangements of recuperators
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- 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
- F23G2202/103—Combustion in two or more stages in separate chambers
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2204/00—Supplementary heating arrangements
- F23G2204/10—Supplementary heating arrangements using auxiliary fuel
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2209/00—Specific waste
- F23G2209/26—Biowaste
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2215/00—Preventing emissions
- F23J2215/20—Sulfur; Compounds thereof
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2215/00—Preventing emissions
- F23J2215/60—Heavy metals; Compounds thereof
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2217/00—Intercepting solids
- F23J2217/10—Intercepting solids by filters
- F23J2217/101—Baghouse type
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2217/00—Intercepting solids
- F23J2217/40—Intercepting solids by cyclones
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2219/00—Treatment devices
- F23J2219/40—Sorption with wet devices, e.g. scrubbers
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- 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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Abstract
本发明公开了一种超富集植物安全焚烧处置系统及方法,包括焚烧炉、二燃室、一次换热器、二次换热器、一次除尘器、二次除尘器、排风机和洗涤塔;所述焚烧炉的侧壁上设有燃烧器,所述焚烧炉的烟气出口通过管道顺次连接至所述二燃室、一次换热器、二次换热器、一次除尘器、二次除尘器、排风机和洗涤塔。本发明通过两次焚烧、双重降温、二次除尘、喷淋洗涤可以有效的处理尾气中的重金属元素和粉尘、硫化物等有害物质,实现富集植物的安全减量化。
The invention discloses a safe incineration disposal system and method for super-enriched plants, including an incinerator, a secondary combustion chamber, a primary heat exchanger, a secondary heat exchanger, a primary dust collector, a secondary dust collector, an exhaust fan and a washing tower The side wall of the incinerator is provided with a burner, and the flue gas outlet of the incinerator is connected to the second combustion chamber, the primary heat exchanger, the secondary heat exchanger, the primary dust collector, and the secondary combustion chamber in sequence through pipelines. Secondary dust collector, exhaust fan and scrubber. The present invention can effectively treat heavy metal elements, dust, sulfide and other harmful substances in the tail gas through double incineration, double cooling, secondary dust removal, and spray washing, so as to realize the safe reduction of enriched plants.
Description
技术领域technical field
本发明属于超富集植物处置技术领域,尤其涉及一种超富集植物安全焚烧处置系统及方法。The invention belongs to the technical field of hyperaccumulator plant disposal, and in particular relates to a system and method for safe incineration disposal of hyperaccumulator plants.
背景技术Background technique
植物修复技术作为生物修复技术的一种,除具有修复成本低、环境友好、无二次污染、对土壤结构不产生破坏等优点外,还能改善土壤生态、减少水土流失、增加碳固定。近年来广泛应用于重金属污染土壤修复,是一种绿色修复方法。As a kind of bioremediation technology, phytoremediation technology has the advantages of low repair cost, environmental friendliness, no secondary pollution, and no damage to soil structure, etc. It can also improve soil ecology, reduce soil erosion, and increase carbon fixation. In recent years, it has been widely used in the remediation of heavy metal-contaminated soil and is a green remediation method.
随着越来越多的超富集植物被发现,用于重金属污染土壤修复的富集植物生物量急剧增大,若不进行处理,会造成二次污染。处理超富集植物的方法有焚烧法、堆肥法、压缩填埋法、液相萃取法、高温分解法等。其中焚烧法是对富集植物进行减量处理最高效、最便捷的方法。但是焚烧过程中产生的尾气以及尾气中的重金属必须要进行合理治理。目前,在富集植物处理市场中仍未形成一套能广泛应用于焚烧处理富集植物的有效技术。As more and more hyperaccumulator plants are discovered, the biomass of enrichment plants used for remediation of heavy metal-contaminated soils increases sharply, which will cause secondary pollution if not treated. Methods for dealing with hyperaccumulators include incineration, composting, compressed landfill, liquid phase extraction, and pyrolysis. Among them, the incineration method is the most efficient and convenient method for reducing the amount of enriched plants. However, the tail gas produced during the incineration process and the heavy metals in the tail gas must be properly controlled. At present, a set of effective technologies that can be widely used in the incineration treatment of enriched plants has not been formed in the enriched plant treatment market.
发明内容Contents of the invention
本申请旨在至少解决现有技术中存在的技术问题之一。为此,本发明的目的之一在于提供一种超富集植物安全焚烧处置系统及方法,通过两次焚烧、双重降温、二次除尘、喷淋洗涤有效的处理尾气中的重金属元素和粉尘、硫化物等有害物质,实现富集植物的安全减量化。This application aims to solve at least one of the technical problems existing in the prior art. For this reason, one of the objects of the present invention is to provide a system and method for safe incineration of super-enriched plants, which can effectively treat heavy metal elements and dust in the tail gas through double burning, double cooling, secondary dust removal, and spray washing. Harmful substances such as sulfides can be safely reduced by enriching plants.
为解决上述技术问题,本申请采用如下技术方案:In order to solve the above technical problems, the application adopts the following technical solutions:
一种超富集植物安全焚烧处置系统,其特征在于:包括焚烧炉、二燃室、一次换热器、二次换热器、一次除尘器、二次除尘器、排风机和洗涤塔;所述焚烧炉的侧壁上设有燃烧器,所述焚烧炉的烟气出口通过管道顺次连接至所述二燃室、一次换热器、二次换热器、一次除尘器、二次除尘器、排风机和洗涤塔。A safe incineration disposal system for super-enriched plants, characterized in that it includes an incinerator, a secondary combustion chamber, a primary heat exchanger, a secondary heat exchanger, a primary dust collector, a secondary dust collector, an exhaust fan and a washing tower; The side wall of the incinerator is provided with a burner, and the flue gas outlet of the incinerator is connected to the second combustion chamber, the primary heat exchanger, the secondary heat exchanger, the primary dust collector, and the secondary dust collector in sequence through pipelines. devices, exhaust fans and scrubbers.
进一步的,所述焚烧炉上设有炉膛温度传感器和炉膛压力传感器,内部设有往复炉排。Further, the incinerator is provided with a furnace temperature sensor and a furnace pressure sensor, and a reciprocating fire grate is arranged inside.
进一步的,所述一次换热器采用水冷换热器,所述二次换热器采用空气换热器,所述空气换热器加热后的热空气由鼓风机引入所述焚烧炉和二燃室。Further, the primary heat exchanger adopts a water-cooled heat exchanger, and the secondary heat exchanger adopts an air heat exchanger, and the hot air heated by the air heat exchanger is introduced into the incinerator and the secondary combustion chamber by a blower. .
进一步的,所述二燃室采用旋风分离器式二燃室,其内设有二燃室温度传感器和二燃室压力传感器。Further, the secondary combustion chamber adopts a cyclone separator type secondary combustion chamber, and a secondary combustion chamber temperature sensor and a secondary combustion chamber pressure sensor are arranged in it.
进一步的,所述一次除尘器采用旋风除尘器,所述二次除尘器采用布袋除尘器。Further, the primary dust collector is a cyclone dust collector, and the secondary dust collector is a bag filter.
进一步的,连接所述一次除尘器和二次除尘器的管道上设有超温报警阀。Further, an over-temperature alarm valve is provided on the pipeline connecting the primary dust collector and the secondary dust collector.
进一步的,所述洗涤塔采用三层洗涤、两层除雾的多层结构。Further, the washing tower adopts a multi-layer structure with three layers of washing and two layers of demisting.
进一步的,所述洗涤塔后还连接有烟囱。Further, a chimney is connected after the washing tower.
一种超富集植物安全焚烧处置方法,包括如下步骤:A method for safe incineration disposal of hyperaccumulator plants, comprising the steps of:
将超富集植物破碎造粒;Crushing and granulating hyperaccumulator plants;
将破碎造粒后的超富集植物投入焚烧炉内高温热解燃烧,燃烧温度在800-1000℃左右;Put the crushed and granulated super-enriched plants into the incinerator for high-temperature pyrolysis and combustion, and the combustion temperature is about 800-1000 °C;
焚烧后的高温烟气进入二燃室,高温烟气中未完全分解的有机物质在富氧状态下进一步燃烧;The high-temperature flue gas after incineration enters the secondary combustion chamber, and the incompletely decomposed organic substances in the high-temperature flue gas are further burned in an oxygen-enriched state;
经二燃室出来的高温烟气经过水冷换热器和空气换热器进行双重降温,温度下降至200℃以下;The high-temperature flue gas from the second combustion chamber is double-cooled by the water-cooled heat exchanger and the air heat exchanger, and the temperature drops below 200°C;
降温后的烟气进入旋风除尘器和布袋除尘器,进行二次除尘;The cooled flue gas enters the cyclone dust collector and bag filter for secondary dust removal;
二次除尘后的烟气进入喷淋洗涤塔,通过喷淋洗涤塔去除惰性有害气体和小颗粒粉尘,最终通过烟囱达标排放。The flue gas after secondary dust removal enters the spray scrubber, removes inert harmful gases and small particle dust through the spray scrubber, and finally discharges through the chimney up to the standard.
进一步的,还包括如下步骤:新鲜空气经过空气换热器换热升温由鼓风机引入焚烧炉和二燃室。Further, the following steps are also included: the fresh air is introduced into the incinerator and the secondary combustion chamber by the blower through the air heat exchanger for heat exchange and temperature rise.
与现有技术相比,本发明具有的有益效果在于:Compared with the prior art, the present invention has the beneficial effects of:
1、通过两次焚烧、双重降温、二次除尘、喷淋洗涤可以有效的处理尾气中的重金属元素和粉尘、硫化物等有害物质,处置后尾气排放完全达到国家或地区标准。1. Heavy metal elements, dust, sulfide and other harmful substances in the tail gas can be effectively treated through double incineration, double cooling, double dust removal, and spray washing, and the tail gas emission after disposal can fully meet the national or regional standards.
2、采用干法除尘,工艺可靠,所需投资少。2. Dry dust removal is adopted, the process is reliable, and the required investment is small.
3、新鲜空气经过空气换热器换热升温由鼓风机引入焚烧炉和二燃室,能源再利用,运行成本低。3. The fresh air passes through the air heat exchanger for heat exchange and temperature rise, and is introduced into the incinerator and the secondary combustion chamber by the blower, and the energy is reused, and the operating cost is low.
4、设备模块化,安装拆卸方便,修复完一个地区后可运输至下一个地区使用。4. The equipment is modularized, easy to install and disassemble, and can be transported to the next area after repairing one area.
附图说明Description of drawings
图1为本发明的结构示意图;Fig. 1 is a structural representation of the present invention;
其中:1-提升进料机构;2-焚烧炉;3-点火器;4-二燃室;5-管路;6-水冷换热器;7-空气换热器;8-旋风除尘器;9-超温报警阀;10-布袋除尘器;11-排风机;12-洗涤塔;13-烟囱。Among them: 1-lifting feeding mechanism; 2-incinerator; 3-igniter; 4-second combustion chamber; 5-pipeline; 6-water-cooled heat exchanger; 7-air heat exchanger; 8-cyclone dust collector; 9-over-temperature alarm valve; 10-bag filter; 11-exhaust fan; 12-washing tower; 13-chimney.
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,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作出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, 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 creative efforts fall within the protection scope of the present invention.
参见图1,一种超富集植物安全焚烧处置系统,包括焚烧炉2、二燃室4、水冷换热器6、空气换热器7、旋风除尘器8、布袋除尘器10、排风机11、洗涤塔12、烟囱13以及鼓风机、控制系统等。在焚烧炉2的烟气出口通过管道5顺次连接至二燃室4、水冷换热器6、空气换热器7、旋风除尘器8、布袋除尘器10、排风机11、洗涤塔12和烟囱13,在焚烧炉2的侧壁上设有燃烧器3。Referring to Fig. 1, a safe incineration disposal system for super-enriched plants includes an incinerator 2, a secondary combustion chamber 4, a water-cooled heat exchanger 6, an air heat exchanger 7, a cyclone dust collector 8, a bag filter 10, and an exhaust fan 11 , scrubber 12, chimney 13, blower, control system, etc. The flue gas outlet of the incinerator 2 is connected to the second combustion chamber 4, water-cooled heat exchanger 6, air heat exchanger 7, cyclone dust collector 8, bag filter 10, exhaust fan 11, washing tower 12 and A chimney 13 is provided with a burner 3 on the side wall of the incinerator 2 .
本实施例中,旋风除尘,8用于粉尘预除尘,由旋风筒体、集灰斗、集风帽组成。布袋除尘器10采用高效过滤除尘器,过滤效果可达99.9%。主要由上箱体、中箱体、下箱体和钢支架与灰斗组成,滤袋采用耐高温的材质,除尘器内置脉冲反吹装置,可以自动清灰。In this embodiment, cyclone dust removal, 8 is used for dust pre-dedusting, and is composed of cyclone barrel, dust collecting hopper, and wind collecting cap. The bag filter 10 adopts a high-efficiency filter dust collector, and the filtering effect can reach 99.9%. It is mainly composed of upper box, middle box, lower box, steel bracket and ash hopper. The filter bag is made of high temperature resistant material. The dust collector has a built-in pulse blowback device, which can automatically clean dust.
在旋风除尘器8和布袋除尘器10之间有超温报警阀9,超温报警阀9可以实时监测管路系统该处的温度,避免温度过高时,烟气对布袋除尘器10造成损害。There is an over-temperature alarm valve 9 between the cyclone dust collector 8 and the bag filter 10. The over-temperature alarm valve 9 can monitor the temperature of the pipeline system in real time to avoid damage to the bag filter 10 caused by flue gas when the temperature is too high .
排风机11采用高压离心风机,由外壳、轴心、叶轮、轴承、马达、皮带等部件组成,使整个系统处于负压状态。烟囱13用于排放净化后的烟气,烟囱上有在线温度、压力、SOx、NOx、重金属元素的监测装置。Exhaust fan 11 adopts high-pressure centrifugal fan, which is composed of shell, shaft, impeller, bearing, motor, belt and other components, so that the whole system is in a negative pressure state. The chimney 13 is used to discharge purified flue gas, and there are monitoring devices for online temperature, pressure, SO x , NO x , and heavy metal elements on the chimney.
本实施例,通过两次焚烧、双重降温、二次除尘、喷淋洗涤可以有效的处理尾气中的重金属元素和粉尘、硫化物等有害物质,实现富集植物的安全减量化,处置后尾气排放完全达到国家或地区标准。In this embodiment, heavy metal elements, dust, sulfide and other harmful substances in the tail gas can be effectively treated through double incineration, double cooling, double dust removal, and spray washing, so as to realize the safe reduction of enriched plants, and the tail gas after disposal Emissions fully meet national or regional standards.
参见图1,在一实施例中,本实施例处置系统,焚烧炉2采用往复炉排炉结构,炉内结构为多回程,砌筑耐火砖炉墙,浇注硅酸铝耐高温材料,外部使用岩棉保温。焚烧炉以空气作为介质,配备自动点火装置,使物料在炉内充分焚烧,可以使炉内温度达到900℃。炉内有炉膛温度传感器和炉膛压力传感器(图中未标示),在线监控炉内温度和压力,燃烧器3共两个,分别用于焚烧炉2和二燃室4,为物料燃烧提供动力。二燃室4采用旋风分离器式二燃室,为竖直双回程结构,配备防爆口,用于将烟气进行二次焚烧,二燃室4内有二燃室温度传感器和二燃室压力传感器(图中未标示),在线监控二燃室内温度和压力。Referring to Fig. 1, in one embodiment, in the disposal system of this embodiment, the incinerator 2 adopts a reciprocating grate furnace structure, the furnace structure is multi-pass, the refractory brick furnace wall is built by masonry, and aluminum silicate high-temperature-resistant materials are poured for external use Rock wool insulation. The incinerator uses air as the medium and is equipped with an automatic ignition device to fully incinerate the material in the furnace, and the temperature in the furnace can reach 900°C. There are a furnace temperature sensor and a furnace pressure sensor (not shown in the figure) in the furnace to monitor the temperature and pressure in the furnace online. There are two burners 3, which are used in the incinerator 2 and the secondary combustion chamber 4 respectively to provide power for material combustion. The secondary combustion chamber 4 adopts a cyclone separator type secondary combustion chamber, which is a vertical double-return structure, and is equipped with an explosion-proof port for secondary combustion of the flue gas. The secondary combustion chamber 4 has a secondary combustion chamber temperature sensor and a secondary combustion chamber pressure. A sensor (not shown in the figure) monitors the temperature and pressure in the secondary combustion chamber online.
需要说明的是,在实际设计中,洗涤塔12采用三层洗涤、两层除雾的多层结构,可以充分洗涤烟气,实现烟气的净化。It should be noted that in actual design, the washing tower 12 adopts a multi-layer structure with three layers of washing and two layers of demisting, which can fully wash the flue gas and realize the purification of the flue gas.
参见图1,在另一实施例中,本实施例处置系统,水冷换热器6采用间接水冷方式,内置多根碳钢材质的水管,冷水在管内流动,高温烟气从管外经过,可以快速将烟气的温度降至300℃。空气换热器7内置多根碳钢材质的气管,烟气从气管外经过,管内为新鲜的冷空气,进一步将烟气进行降温,可降至200℃以下。新鲜冷空气受高温烟气影响,温度会上升到70℃,由鼓风机引入焚烧炉2和二燃室4,在为物料燃烧补充新鲜空气的同时,尽可能的避免焚烧炉2和二燃室4温度的降低,进而节约系统的能耗。二燃室温度传感器、二燃室压力传感器、炉膛温度传感器、炉膛压力传感器、排风机、超温报警阀和鼓风机电性连接至控制系统,至于控制系统的具体构成,均为电控领域常规设计,在此不再赘述。Referring to Fig. 1, in another embodiment, in the disposal system of this embodiment, the water-cooled heat exchanger 6 adopts an indirect water cooling method, and a plurality of carbon steel water pipes are built in. The cold water flows in the pipes, and the high-temperature flue gas passes outside the pipes, which can Rapidly lower the temperature of the flue gas to 300°C. The air heat exchanger 7 has built-in multiple air pipes made of carbon steel, the flue gas passes through the air pipes, and the fresh cold air inside the pipes further cools the flue gas down to below 200°C. The fresh cold air is affected by the high-temperature flue gas, and the temperature will rise to 70°C. It is introduced into the incinerator 2 and the second combustion chamber 4 by the blower. While supplementing fresh air for the material combustion, avoid the incinerator 2 and the second combustion chamber 4 as much as possible. The temperature is lowered, thereby saving the energy consumption of the system. The temperature sensor of the second combustion chamber, the pressure sensor of the second combustion chamber, the furnace temperature sensor, the furnace pressure sensor, the exhaust fan, the over-temperature alarm valve and the blower are electrically connected to the control system. As for the specific composition of the control system, they are all conventional designs in the field of electric control , which will not be repeated here.
下面将以重金属超富集植物如籽粒苋的安全焚烧处置为例说明使用本申请富集植物安全焚烧处置系统处理籽粒苋的具体过程:The following will take the safe incineration disposal of heavy metal hyperaccumulator plants such as grain amaranth as an example to illustrate the specific process of using the safe incineration disposal system for enriched plants of this application to process grain amaranth:
所需处置的植物堆密度大,不利于进料;占用炉膛体积大,燃烧特性差。因此需先将物料进行破碎,以便减少体积(破碎物料5~8mm),同时便于造粒、运输、储存等。之后进行造粒(颗粒大小为),造粒后可以改善物料燃烧特性、增加热值、增大燃料密度、便于上料、装袋储存。The bulk density of the plants to be disposed is high, which is not conducive to feeding; it occupies a large volume of the furnace and has poor combustion characteristics. Therefore, the material needs to be crushed first in order to reduce the volume (the crushed material is 5-8mm), and at the same time, it is convenient for granulation, transportation, storage, etc. Then granulate (particle size is ), after granulation, it can improve the combustion characteristics of the material, increase the calorific value, increase the fuel density, and facilitate feeding and bagging storage.
经造粒后的原料类似于生物质颗粒,其特殊之处在于含有重金属元素。因此需对尾气进行合理的治理。具体处理如下:The granulated raw material is similar to biomass granules, and its special feature is that it contains heavy metal elements. Therefore, it is necessary to carry out reasonable treatment of exhaust gas. The specific treatment is as follows:
(1)提升进料机构1通过料斗将废弃物投入焚烧炉2的燃烧室,废弃物在燃烧器3的助燃以及鼓风机所提供的空气扰动作用下,根据燃烧三T原则(温度、时间、涡流)在炉内高温热解燃烧,燃烧温度在800~1000℃左右,整个燃烧过程呈负压状态。焚烧后物料减量率在90%以上。(1) The lifting feeding mechanism 1 puts the waste into the combustion chamber of the incinerator 2 through the hopper. Under the combustion-supporting action of the burner 3 and the air disturbance provided by the blower, the waste is burned according to the three-T principle of combustion (temperature, time, swirl flow) ) is pyrolyzed and burned at high temperature in the furnace, the combustion temperature is about 800-1000°C, and the whole combustion process is in a negative pressure state. The material reduction rate after incineration is over 90%.
具体的,提升进料机构1包含料斗、电机、电动推杆、链条等元件,通过电动推杆带动链条升降,将料斗从底部提升之顶部,实现物料的自动进料,并具有自动称重功能。Specifically, the lifting and feeding mechanism 1 includes components such as a hopper, a motor, an electric push rod, and a chain. The electric push rod drives the chain up and down, and lifts the hopper from the bottom to the top to realize automatic feeding of materials and has an automatic weighing function. .
(2)焚烧后的高温烟气进入二燃室4,二燃室4是一个立式圆柱形的内壁衬有耐火材料的炉子。炉体采用旋风式结构,补氧空气采用切向补给,增强扰动保证有机物充分气化。炉体氧化区由于氧化空气的补充使得氧化区处于富氧状态,高温烟气中未完全分解的有机物质在富氧状态下进一步燃烧,并且保证较长的滞留时间,使得有机废物在此能够完全分解。(2) The high-temperature flue gas after incineration enters the second combustion chamber 4, and the second combustion chamber 4 is a furnace with a vertical cylindrical inner wall lined with refractory materials. The furnace body adopts a cyclone structure, and the oxygen supply air is supplied tangentially to enhance the disturbance to ensure the full gasification of organic matter. Due to the supplement of oxidizing air in the oxidation zone of the furnace body, the oxidation zone is in an oxygen-enriched state, and the incompletely decomposed organic substances in the high-temperature flue gas are further burned in an oxygen-enriched state, and a longer residence time is ensured, so that the organic waste can be completely discharged here. break down.
(3)经二燃室4出来的烟气温度高达1100℃,需进行烟气冷却,采用水冷跟风冷双重冷却,高温烟气经水冷换热器6跟空气换热器7进行降温后温度在200℃以下;新鲜空气进入空气换热器6后温度可升高至60~70℃,由鼓风机供焚烧炉2跟二燃室4使用,有效的节约了能耗。(3) The temperature of the flue gas coming out of the second combustion chamber 4 is as high as 1100°C, and the flue gas needs to be cooled by water cooling and air cooling. The high temperature flue gas is cooled by the water cooling heat exchanger 6 and the air heat exchanger 7. Below 200°C; after fresh air enters the air heat exchanger 6, the temperature can rise to 60-70°C, and the blower is used for the incinerator 2 and the second combustion chamber 4, which effectively saves energy consumption.
(4)降温后的烟气由旋风除尘器8除去大颗粒粉尘,有效的减轻了布袋除尘器10的工作负荷。在旋风除尘器8和布袋除尘器10之间有超温报警阀9,以防烟气温度过高对布袋除尘器的滤袋造成损害。之后烟气进入布袋除尘器10进行高效过滤。(4) The flue gas after cooling is removed by the cyclone dust collector 8 to remove large particles of dust, which effectively reduces the workload of the bag filter 10 . There is an over-temperature alarm valve 9 between the cyclone dust collector 8 and the bag dust collector 10 to prevent damage to the filter bag of the bag dust collector due to excessive flue gas temperature. After that, the flue gas enters the bag filter 10 for high-efficiency filtration.
(5)除尘后的烟气进入喷淋洗涤塔12,通过喷淋特定配备的溶液吸收去除性有害气体和小颗粒粉尘,达到无毒、无烟、无害、无臭效果,经除沫处理后的达标气体引进烟囱13排入大气层。(5) The flue gas after dust removal enters the spray scrubber 12, and absorbs and removes harmful gases and small particles of dust by spraying a specially equipped solution to achieve non-toxic, smoke-free, harmless, and odorless effects. After defoaming treatment After reaching the standard gas introduction chimney 13 is discharged into atmosphere.
(6)整套系统同时设有紧急排放系统,一旦焚烧炉系统出现故障,气动切换阀瞬间动作,烟气由紧急排放系统排空,保证系统安全操作。(6) The whole system is also equipped with an emergency discharge system. Once the incinerator system fails, the pneumatic switching valve will act instantly, and the flue gas will be emptied by the emergency discharge system to ensure the safe operation of the system.
(7)焚烧系统产生的灰渣,主要是金属的氧化物,属于危废类,统一收集后由危废厂家进行集中处理;焚烧系统产生的废水,主要为系统用冷却水和循环池的循环水,经沉降处理后定期进入污水管网系统处理;焚烧系统产生的废气经处理后完全可实现达标排放。(7) The ash and slag produced by the incineration system are mainly metal oxides, which belong to the hazardous waste category. After being collected in a unified manner, the hazardous waste manufacturers will conduct centralized treatment; the waste water produced by the incineration system is mainly the cooling water for the system and the circulation of the circulation pool Water, after sedimentation treatment, regularly enters the sewage pipe network system for treatment; the waste gas generated by the incineration system can fully achieve standard discharge after treatment.
上述实施例仅仅是清楚地说明本发明所作的举例,而非对实施方式的限定。对于所属领域的普通技术人员来说,在上述说明的基础上还可以做出其它不同形式的变化或变动。这里也无需也无法对所有的实施例予以穷举。而由此所引申出的显而易见的变化或变动仍处于本发明的保护范围之中。The above-mentioned embodiments are only examples for clearly illustrating the present invention, rather than limiting the implementation. For those of ordinary skill in the art, on the basis of the above description, other changes or changes in different forms can also be made. It is not necessary and impossible to exhaustively list all the embodiments here. However, the obvious changes or variations derived therefrom are still within the protection scope of the present invention.
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