CN106705062B - Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace - Google Patents

Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace Download PDF

Info

Publication number
CN106705062B
CN106705062B CN201710044585.0A CN201710044585A CN106705062B CN 106705062 B CN106705062 B CN 106705062B CN 201710044585 A CN201710044585 A CN 201710044585A CN 106705062 B CN106705062 B CN 106705062B
Authority
CN
China
Prior art keywords
area
baffling
depositing dust
deep
deep combustion
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.)
Active
Application number
CN201710044585.0A
Other languages
Chinese (zh)
Other versions
CN106705062A (en
Inventor
宋海农
杨崎峰
林宏飞
陈国宁
王爱
周永信
张先铃
詹馥蔓
王光红
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Guangxi Boshike Environmental Technology Co ltd
Guangxi Bossco Environmental Protection Technology Co Ltd
Original Assignee
Guangxi Bossco Environmental Protection Technology Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Guangxi Bossco Environmental Protection Technology Co Ltd filed Critical Guangxi Bossco Environmental Protection Technology Co Ltd
Priority to CN201710044585.0A priority Critical patent/CN106705062B/en
Publication of CN106705062A publication Critical patent/CN106705062A/en
Application granted granted Critical
Publication of CN106705062B publication Critical patent/CN106705062B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage
    • F23G5/0276Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage using direct heating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D45/00Separating dispersed particles from gases or vapours by gravity, inertia, or centrifugal forces
    • B01D45/04Separating dispersed particles from gases or vapours by gravity, inertia, or centrifugal forces by utilising inertia
    • B01D45/08Separating dispersed particles from gases or vapours by gravity, inertia, or centrifugal forces by utilising inertia by impingement against baffle separators
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/08Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
    • F23G5/14Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
    • F23G5/16Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion in a separate combustion chamber
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/50Control or safety arrangements
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23LSUPPLYING 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
    • F23L9/00Passages or apertures for delivering secondary air for completing combustion of fuel 

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Incineration Of Waste (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Combustion & Propulsion (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)

Abstract

The invention discloses the dual firing chamber's treatment process and processing unit that are applied to domestic garbage pyrolysis furnace, which is: 1) entering in deep combustion area combustible pyrolysis's conductance that pyrolysis oven generates and be sufficiently mixed with Secondary Air, burn;2) high-temperature tail gas that the burning of deep combustion area generates is imported into baffling depositing dust area, and conveyed from lower to upper, high-temperature tail gas is discharged from baffling depositing dust area top after multistage depositing dust and baffling in baffling depositing dust area and is sent into exhaust gas purification system.The processing unit includes the deep combustion area and baffling depositing dust area that bottom is connected, and deep combustion area is equipped with air inlet, and baffling depositing dust area is equipped with annular escape pipe;The processing unit further includes flue-dust retainer and ash hole.The present invention has many advantages, such as that system operatio is easy, process control is strong, pyrolysis is high-efficient, second-time burning is abundant, baffling depositing dust is efficient, pollutant concentration is low, exhaust emissions amount is small, investment and operating cost save, and can be widely applied to application of city life garbage pyrolysis processing field.

Description

应用于生活垃圾热解炉的二燃室的处理工艺及处理装置Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace

技术领域technical field

本发明涉及生活垃圾热解气化燃烧处理领域,具体是一种应用于生活垃圾热解炉的二燃室处理工艺及处理装置。The invention relates to the field of domestic waste pyrolysis gasification combustion treatment, in particular to a secondary combustion chamber treatment process and a treatment device applied to a domestic waste pyrolysis furnace.

背景技术Background technique

近年来,随着环保意识的加强和日益严格的国家环保法规和政策的相继出台,生活垃圾处置的“无害化、减量化和资源化”已成为各国遵循的基本原则,垃圾热解技术作为实现这一原则的有效途径之一,已逐渐得到业界公认。垃圾热解技术的核心在于热解炉,其结构主要包括热解气化炉和二燃室。生活垃圾经热解气化炉产生低分子可燃气体,并通过合理的导气装置进入二燃室进行深度燃烧,以上两个工艺步骤既要严格区分、独立运行,又要互为帮辅、有机结合,最终实现热解气化和燃烧净化过程的一体化高度整合。In recent years, with the strengthening of environmental protection awareness and the successive introduction of increasingly strict national environmental protection regulations and policies, the "harmless, reduced and recycled" disposal of domestic waste has become the basic principle followed by all countries. Waste pyrolysis technology As one of the effective ways to realize this principle, it has gradually been recognized by the industry. The core of waste pyrolysis technology lies in the pyrolysis furnace, whose structure mainly includes a pyrolysis gasifier and a secondary combustion chamber. The domestic waste generates low-molecular-weight combustible gas through the pyrolysis gasifier, and enters the secondary combustion chamber through a reasonable gas guiding device for deep combustion. The above two process steps must be strictly distinguished and operated independently, and they must be mutually complementary and organic. Combined, the integration and high integration of pyrolysis gasification and combustion purification process are finally realized.

现有生活垃圾热解炉的结构主要分为两种类型,一类采用立式同轴套筒结构,即由立式热解气化炉膛和环绕其四周的环状二次燃烧室腔体组成,生活垃圾经热解气化炉膛热解产生的可燃气通过布置于炉膛壁上的导气通道进入二燃室腔体内,二燃室腔体上布设燃烧器和二次风供给系统,热解气在腔体内燃烧并最终经尾气处理系统净化后达标排放,该结构具有占地省、操作简便、燃烧热利用直接等优点,但是热解炉温会随着二燃室燃烧工况变化而波动,热解过程温度可控性差,且该结构比较复杂,维护检修困难;另一类采用立式或卧式分体结构,热解气化炉和二燃室分为两个独立的结构单元,二者通过导气管道连通,该结构具有结构简单、控温精确、维修方便等特点,但也存在占地较大、余热利用率较低等不足。此外,以上两类目前普遍使用的生活垃圾热解炉还存在以下共性问题:①热解气化炉结构设计不够合理,如进料布料不均、布风供氧不足、炉排易堵易卡和集气导气不均等,直接影响热解气化效率和后续深度燃烧效果;②二燃室内部结构有待优化,主要存在以下几点问题:一是燃烧区与折流降尘区混为一体,无法分别对燃烧过程和折流降尘过程进行精确控制,进而不能实现对二噁英和金属粉尘等有毒有害物质的有效控制;二是燃烧区设计不够合理,由于热解气经导气管道进入二燃室瞬间,燃烧区域突然过度放大,使得热解气浓度稀释过低,速度也迅速下降,造成热解气与助燃二次风混合不均,燃烧不够充分,为解决这一问题,目前一般采用加大二次风风量或补充燃料进行辅助燃烧,由此带来运行成本和尾气排放量的增大;三是集气导气系统和折流降尘结构简单,热解气的集气、导气位置和进气方向设置不当,使得热解气与二次风的混合不均,影响燃烧效率,同时,折流降尘区的结构过于简单,无法保证烟气的有效停留时间和降尘效果,抑制二噁英合成的效果较差,不能彻底解决二噁英和重金属等二次污染物的生成和排放问题。The structure of the existing domestic waste pyrolysis furnace is mainly divided into two types. The first type adopts a vertical coaxial sleeve structure, that is, it consists of a vertical pyrolysis gasification furnace and an annular secondary combustion chamber cavity surrounding it. , the combustible gas generated by the pyrolysis of the domestic garbage through the pyrolysis gasification furnace enters the secondary combustion chamber through the air guide channel arranged on the furnace wall. The gas is burned in the chamber and finally purified by the exhaust gas treatment system and then discharged up to the standard. This structure has the advantages of saving land, easy operation, and direct utilization of combustion heat. However, the temperature of the pyrolysis furnace will fluctuate with the change of the combustion conditions of the second combustion chamber. , the temperature controllability of the pyrolysis process is poor, and the structure is relatively complex and difficult to maintain and repair; the other type adopts a vertical or horizontal split structure, and the pyrolysis gasifier and the secondary combustion chamber are divided into two independent structural units. The two are connected through an air-conducting pipe. The structure has the characteristics of simple structure, accurate temperature control, and convenient maintenance. In addition, the above two types of domestic waste pyrolysis furnaces currently commonly used still have the following common problems: ① The structural design of the pyrolysis gasifier is not reasonable, such as uneven feed distribution, insufficient air distribution and oxygen supply, and the grate is easily blocked and easily jammed It is not equal to the gas collection and air conduction, which directly affects the pyrolysis gasification efficiency and the subsequent deep combustion effect; (2) The internal structure of the secondary combustion chamber needs to be optimized, and there are mainly the following problems: First, the combustion area and the baffled dust reduction area are mixed together. It is impossible to accurately control the combustion process and the baffled dust reduction process, and thus cannot achieve effective control of toxic and harmful substances such as dioxins and metal dust; second, the design of the combustion area is not reasonable, because the pyrolysis gas enters the secondary combustion through the gas guide pipe. At the moment of the chamber, the combustion area is suddenly enlarged too much, so that the concentration of the pyrolysis gas is too low, and the speed also drops rapidly, resulting in uneven mixing of the pyrolysis gas and the combustion-supporting secondary air, and insufficient combustion. Large secondary air volume or supplementary fuel is used for auxiliary combustion, which will increase operating costs and exhaust emissions; third, the air collection and air guide system and the baffle dust reduction structure are simple, and the gas collection and air guide positions of the pyrolysis gas Improper setting of the air intake direction and the air intake direction makes the mixing of the pyrolysis gas and the secondary air uneven, which affects the combustion efficiency. At the same time, the structure of the deflected dust reduction area is too simple, which cannot ensure the effective residence time of the flue gas and the dust reduction effect, and suppress the dioxin. The effect of British synthesis is poor, and it cannot completely solve the generation and discharge of secondary pollutants such as dioxins and heavy metals.

发明内容SUMMARY OF THE INVENTION

本发明所要解决的技术问题是提供一种应用于生活垃圾热解炉的二燃室处理工艺及处理装置,通过采用独立运行的深度燃烧区和折流降尘区,从根本上抑制二噁英的产生,有效控制二次污染物及尾气排放量,减轻尾气处理系统的负担,从而降低设备投资和运维成本,实现城镇生活垃圾的无害化和减量化处理。The technical problem to be solved by the present invention is to provide a two-combustion chamber treatment process and treatment device applied to a domestic waste pyrolysis furnace. By using an independently operated deep combustion zone and a baffled dust-reducing zone, the emission of dioxins can be fundamentally suppressed. It can effectively control the amount of secondary pollutants and tail gas emissions, reduce the burden on the tail gas treatment system, thereby reduce equipment investment and operation and maintenance costs, and realize the harmless and reduced treatment of urban domestic waste.

本发明以如下技术方案解决上述技术问题:The present invention solves the above-mentioned technical problems with the following technical solutions:

发明一,应用于生活垃圾热解炉的二燃室处理工艺,它包括如下操作步骤:Invention 1 is applied to a secondary combustion chamber treatment process of a domestic waste pyrolysis furnace, which includes the following operation steps:

1)将热解炉产生的可燃热解气导入设在二燃室中心部位的深度燃烧区上部,可燃热解气由上往下通过深度燃烧区,并与进入深度燃烧区的二次风充分混合、燃烧;1) The combustible pyrolysis gas generated by the pyrolysis furnace is introduced into the upper part of the deep combustion zone located in the center of the secondary combustion chamber. The combustible pyrolysis gas passes through the deep combustion zone from top to bottom, and is fully compatible with the secondary air entering the deep combustion zone. mixing, burning;

2)将深度燃烧区燃烧产生的高温尾气从深度燃烧区的底部出来导入设在深度燃烧区外面的折流降尘区,并由下往上输送,高温尾气在折流降尘区内经多级降尘和折流后从折流降尘区上部排出并送入尾气净化系统。2) The high-temperature exhaust gas generated by the combustion of the deep combustion zone is introduced from the bottom of the deep combustion zone into the baffled dust-reducing zone outside the deep-burning zone, and transported from bottom to top. After baffled, it is discharged from the upper part of the baffled dust-reducing area and sent to the exhaust gas purification system.

发明二,应用于生活垃圾热解炉的二燃室处理装置,该装置包括二燃室壳体,二燃室壳体内设有深度燃烧区与折流降尘区,深度燃烧区设置在二燃室壳体的中心部位,折流降尘区位于深度燃烧区的外面,深度燃烧区与折流降尘区的底部相连通;深度燃烧区的上部设有切向接入的进气口,折流降尘区的上部设有将尾气收集并导入尾气净化系统的环形出气管;二燃室壳体的下部设有位于深度燃烧区和折流降尘区下方的集灰斗,二燃室壳体的底部设有出灰口。The second invention is a secondary combustion chamber treatment device applied to a domestic waste pyrolysis furnace. The device includes a secondary combustion chamber shell, the secondary combustion chamber casing is provided with a deep combustion zone and a baffled dust reduction zone, and the deep combustion zone is arranged in the secondary combustion chamber. In the center of the shell, the baffled dust reduction area is located outside the deep combustion area, and the deep combustion area is connected with the bottom of the baffled dust reduction area; the upper part of the deep combustion area is provided with a tangentially connected air inlet, and the baffled dust reduction area The upper part is provided with an annular outlet pipe that collects and guides the exhaust gas into the exhaust gas purification system; the lower part of the secondary combustion chamber shell is provided with an ash collecting hopper located under the deep combustion area and the baffled dust reduction area, and the bottom of the secondary combustion chamber housing is provided with Ash outlet.

所述深度燃烧区为圆形直管形,其顶端封闭,热解炉产生的可燃热解气通过进气口导入深度燃烧区内,深度燃烧区设有多个二次风补给口以及多个燃烧器,深度燃烧区的底部设有喇叭状出气口。The deep combustion zone is in the shape of a circular straight tube, the top of which is closed, the combustible pyrolysis gas generated by the pyrolysis furnace is introduced into the deep combustion zone through the air inlet, and the deep combustion zone is provided with a plurality of secondary air supply ports and a plurality of The burner has a flared air outlet at the bottom of the deep combustion zone.

所述深度燃烧区上部的进气口设有热解气监测孔,热解气监测孔内安装有气体监测装置,进气口的口径小于深度燃烧区的内径。The air inlet at the upper part of the deep combustion zone is provided with a pyrolysis gas monitoring hole, a gas monitoring device is installed in the pyrolysis gas monitoring hole, and the diameter of the air inlet is smaller than the inner diameter of the deep combustion zone.

所述折流降尘区为深度燃烧区与二燃室壳体内壁之间的空腔区域,折流降尘区上部的环形出气口设有尾气监测孔,尾气监测孔内安装有气体监测装置,深度燃烧区的中下部设有折流导向台和降尘花孔板,折流导向台位于降尘花孔板上方,从深度燃烧区出来的高温尾气经降尘花孔板进入折流降尘区。The baffled dust reduction area is the cavity area between the deep combustion area and the inner wall of the second combustion chamber shell. The annular air outlet at the upper part of the baffled dust reduction area is provided with an exhaust gas monitoring hole, and a gas monitoring device is installed in the exhaust gas monitoring hole. The middle and lower part of the combustion zone is provided with a baffle guide table and a dust reduction orifice plate. The baffle guide table is located above the dust reduction orifice plate.

所述折流导向台设有多个,折流导向台为耐火耐磨材料制成的向下倾斜的环状斜台,其倾斜度≥45°。The baffle guide table is provided with a plurality of, and the baffle guide table is a downwardly inclined annular inclined table made of refractory and wear-resistant material, and its inclination is ≥45°.

所述二燃室壳体上安装有观察孔、燃烧气监测孔、压缩空气吹灰管和检修口。An observation hole, a combustion gas monitoring hole, a compressed air soot blowing pipe and an inspection port are installed on the casing of the second combustion chamber.

所述集灰斗的中部设有挡火格栅。The middle of the ash collecting hopper is provided with a fire blocking grille.

所述二次风补给口和燃烧器从上至下非等距地设置在深度燃烧区。The secondary air supply port and the burner are not equidistantly arranged in the deep combustion zone from top to bottom.

本发明与现有技术相比,具有如下有益效果:Compared with the prior art, the present invention has the following beneficial effects:

1、采用二燃室内深度燃烧区和折流降尘区的独立运行,优化集气导气系统、二燃室结构和整体热解燃烧工艺,实现深度燃烧与折流降尘过程的分步精确控制,从根本上抑制二噁英的产生;1. The independent operation of the deep combustion area and the deflected dust reduction area in the secondary combustion chamber is adopted to optimize the gas collection and air guiding system, the secondary combustion chamber structure and the overall pyrolysis combustion process, so as to realize the step-by-step precise control of the deep combustion and the deflected dust reduction process. Fundamentally inhibit the production of dioxins;

2、深度燃烧区采用切向进气口、非等距二次风补给口和喇叭形出气口的优化组合,结构设计合理、新颖,热解气彻底燃烧的同时,尽可能地减少二次风用量,有效控制污染物浓度及尾气排放量,减轻尾气处理系统的负担,降低设备投资和运维成本;2. The deep combustion area adopts the optimal combination of tangential air inlet, non-equidistant secondary air supply port and trumpet-shaped air outlet. The structure design is reasonable and novel. While the pyrolysis gas is completely burned, the secondary air is reduced as much as possible. It can effectively control the concentration of pollutants and exhaust emissions, reduce the burden on the exhaust gas treatment system, and reduce equipment investment and operation and maintenance costs;

3、折流降尘区通过设置挡火格栅、降尘花孔板和折流导向台的多级降尘和折流作用,高效去除高温尾气中的金属粉尘和其它尘粒,并保证高温尾气在二燃室内停留足够时间,从根本上破坏二噁英等有毒有害二次污染物的合成条件,实现城镇生活垃圾的无害化处理。3. The baffled and dust-reducing area efficiently removes metal dust and other dust particles in the high-temperature exhaust gas by setting the fire-blocking grille, the dust-reducing orifice plate and the baffled guide table for multi-stage dust reduction and baffle action, and ensures that the high-temperature exhaust gas is in the second stage. Staying in the combustion chamber for enough time will fundamentally destroy the synthesis conditions of toxic and harmful secondary pollutants such as dioxins, and realize the harmless treatment of urban domestic waste.

4、本发明具有系统操作简便、过程可控性强、热解效率高、二次燃烧充分、折流降尘高效、污染物浓度低、尾气排放量小、投资和运行成本省等优点,可广泛应用于城镇生活垃圾热解处理领域。4. The present invention has the advantages of simple system operation, strong process controllability, high pyrolysis efficiency, sufficient secondary combustion, high efficiency of deflecting and dust reduction, low pollutant concentration, small exhaust emission, low investment and operating cost, etc., and can be widely used. It is used in the field of urban domestic waste pyrolysis treatment.

附图说明Description of drawings

图1是本发明应用于生活垃圾热解炉的二燃室处理装置的主视示意图;1 is a schematic front view of a secondary combustion chamber treatment device of the present invention applied to a domestic waste pyrolysis furnace;

图2是图1中深度燃烧区的主视示意图;Figure 2 is a schematic front view of the deep combustion zone in Figure 1;

图3是图1中折流降尘区的主视示意图;Fig. 3 is the front view schematic diagram of the deflecting dust-reducing area in Fig. 1;

图4是图3中挡火格栅的俯视示意图;Fig. 4 is the top view schematic diagram of the fire-stop grill in Fig. 3;

图5是图3中降尘花孔板的俯视示意图;Fig. 5 is the top view schematic diagram of the dust-reducing flower orifice plate in Fig. 3;

图6是图3中降尘花孔板的主视示意图;Figure 6 is a schematic front view of the dust-reducing flower orifice plate in Figure 3;

图7是图3中折流导向台的俯视示意图;Fig. 7 is the top view schematic diagram of baffle guide table in Fig. 3;

图8是图3中折流导向台的主视示意图;Figure 8 is a schematic front view of the baffle guide table in Figure 3;

图9是图3中环形出气管的俯视示意图。FIG. 9 is a schematic top view of the annular air outlet pipe in FIG. 3 .

图中:1-深度燃烧区、1-1进气口、1-2燃烧段、1-3二次风补给口、1-4燃烧器、1-5出气口、1-6热解气监测孔、2-折流降尘区、2-1挡火格栅、2-2降尘花孔板、2-3折流导向台、2-4燃烧气监测孔、2-5观察孔、2-6尾气监测孔、2-7环形出气管、2-8压缩空气吹灰管、2-9检修口、2-10集灰斗、2-11出灰口,3-二燃室壳体。In the picture: 1-deep combustion zone, 1-1 air inlet, 1-2 combustion section, 1-3 secondary air supply port, 1-4 burner, 1-5 air outlet, 1-6 pyrolysis gas monitoring Holes, 2-baffle dust reduction area, 2-1 fire blocking grille, 2-2 dust reduction flower plate, 2-3 baffle guide table, 2-4 combustion gas monitoring hole, 2-5 observation hole, 2-6 Exhaust gas monitoring hole, 2-7 annular outlet pipe, 2-8 compressed air soot blowing pipe, 2-9 inspection port, 2-10 ash collecting hopper, 2-11 ash outlet, 3- secondary combustion chamber shell.

具体实施方式Detailed ways

下面对本发明技术方案作进一步描述:The technical scheme of the present invention is further described below:

本发明应用于生活垃圾热解炉的二燃室处理工艺,具体包括如下操作步骤:The invention is applied to the secondary combustion chamber treatment process of the domestic waste pyrolysis furnace, and specifically includes the following operation steps:

1)将热解炉产生的可燃热解气导入设在二燃室中心部位的深度燃烧区上部,可燃热解气由上往下通过深度燃烧区,并与进入深度燃烧区的二次风充分混合、燃烧;1) The combustible pyrolysis gas generated by the pyrolysis furnace is introduced into the upper part of the deep combustion zone located in the center of the secondary combustion chamber. The combustible pyrolysis gas passes through the deep combustion zone from top to bottom, and is fully compatible with the secondary air entering the deep combustion zone. mixing, burning;

2)将深度燃烧区燃烧产生的高温尾气从深度燃烧区的底部出来导入设在深度燃烧区外面的折流降尘区,并由下往上输送,高温尾气在折流降尘区内经多级降尘和折流后从折流降尘区上部排出并送入尾气净化系统。2) The high-temperature exhaust gas generated by the combustion of the deep combustion zone is introduced from the bottom of the deep combustion zone into the baffled dust-reducing zone outside the deep-burning zone, and transported from bottom to top. After baffled, it is discharged from the upper part of the baffled dust-reducing area and sent to the exhaust gas purification system.

实施上述处理工艺所采用的处理装置见图1—图9所示,为使附图简洁,图中仅示意性的表示出与本发明相关的部分,而且图中具有相同结构或功能的部件,仅示意性地标示出了其中的一个。The processing device used to implement the above-mentioned treatment process is shown in Figures 1-9. In order to make the accompanying drawings concise, only the parts relevant to the present invention are schematically shown in the figures, and the parts in the figures have the same structure or function, Only one of them is indicated schematically.

如图1—图3所示,本发明应用于生活垃圾热解炉的二燃室处理装置包括圆筒状的二燃室壳体3,二燃室壳体3内设有深度燃烧区1与折流降尘区2,深度燃烧区1与折流降尘区2互为独立单元,实行分区运行。深度燃烧区1设置在二燃室壳体3的中心部位,折流降尘区2位于深度燃烧区的外面,深度燃烧区1与折流降尘区2的底部相通;深度燃烧区1的上部设有切向接入的进气口1-1,折流降尘区2的上部设有将尾气收集并导入尾气净化系统的环形出气管2-7;二燃室壳体的下部设有位于深度燃烧区和折流降尘区下方的集灰斗2-10,二燃室壳体3的底部设有出灰口2-11。As shown in Figure 1-Figure 3, the present invention is applied to the two-combustion chamber treatment device of the domestic waste pyrolysis furnace and comprises a cylindrical two-combustion chamber casing 3, and the two-combustion chamber casing 3 is provided with a deep combustion zone 1 and a Baffled dust reduction area 2, deep combustion area 1 and baffled dust reduction area 2 are independent units of each other, and implement partitioned operation. The deep combustion zone 1 is arranged in the center of the secondary combustion chamber shell 3, the baffled dust reduction zone 2 is located outside the deep combustion zone, and the deep combustion zone 1 communicates with the bottom of the baffled dust reduction zone 2; the upper part of the deep combustion zone 1 is provided with The air inlet 1-1 connected tangentially, the upper part of the deflected dust reduction zone 2 is provided with an annular outlet pipe 2-7 that collects and guides the exhaust gas into the exhaust gas purification system; And the ash collecting hopper 2-10 below the baffled dust-reducing area, and the bottom of the secondary combustion chamber shell 3 is provided with an ash outlet 2-11.

如图2所示,所述深度燃烧区1呈圆形直管形结构,其顶端封闭,深度燃烧区1设有进气口1-1、燃烧段1-2和出气口1-5,进气口1-1和出气口1-5分别位于燃烧段1-2的上部和底部,由热解炉产生的可燃热解气通过进气口1-1导入燃烧段1-2内,进气口1-1的口径小于深度燃烧区的内径;燃烧段1-2设有多个二次风补给口1-3以及多个燃烧器1-4,从上到下非等距地设置;出气口1-5为喇叭状出气口,高温尾气经喇叭口瞬间扩管减速,可提升降尘效果并增加尾气在高温段停留时间。As shown in FIG. 2 , the deep combustion zone 1 has a circular straight tubular structure with a closed top end. The deep combustion zone 1 is provided with an air inlet 1-1, a combustion section 1-2 and an air outlet 1-5. The gas port 1-1 and the gas outlet 1-5 are located at the top and bottom of the combustion section 1-2, respectively. The combustible pyrolysis gas generated by the pyrolysis furnace is introduced into the combustion section 1-2 through the air inlet 1-1, and the air intake The diameter of the port 1-1 is smaller than the inner diameter of the deep combustion zone; the combustion section 1-2 is provided with multiple secondary air supply ports 1-3 and multiple burners 1-4, which are arranged non-equidistantly from top to bottom; The air ports 1-5 are horn-shaped air outlets. The high-temperature exhaust gas is instantly expanded and decelerated through the bell mouth, which can improve the dust reduction effect and increase the residence time of the exhaust gas in the high temperature section.

如图2所示,所述进气口1-1采用切向进气方式,进气口1-1的一端与收集热解气化炉产生的可燃热解气的环形集气管相连通,另一端切向旋入深度燃烧区1内,进气口1-1设有热解气监测孔1-6,热解气监测孔1-6内安装有气体监测装置,监测数据包括热解气的流量、压力、温度和浓度,以上工艺参数分别通过传输线与自动控制系统连接;进气口1-1的口径小于燃烧段1-2段的内径。As shown in Fig. 2, the air inlet 1-1 adopts a tangential air inlet mode, one end of the air inlet 1-1 is connected with the annular gas collecting pipe for collecting the combustible pyrolysis gas generated by the pyrolysis gasifier, and the other One end is tangentially screwed into the deep combustion zone 1, the air inlet 1-1 is provided with a pyrolysis gas monitoring hole 1-6, and a gas monitoring device is installed in the pyrolysis gas monitoring hole 1-6, and the monitoring data includes the pyrolysis gas. Flow, pressure, temperature and concentration, the above process parameters are respectively connected with the automatic control system through the transmission line; the diameter of the air inlet 1-1 is smaller than the inner diameter of the combustion section 1-2.

如图3所示,所述折流沉降区2为深度燃烧区1与二燃室壳体3内壁之间的空腔区域,折流降尘区2上部的环形出气口2-7设有尾气监测孔2-6,尾气监测孔2-6内安装有气体监测装置,监测数据包括热解气的流量、压力、温度和浓度,以上工艺参数分别通过传输线与自动控制系统连接;深度燃烧区2的中下部设有折流导向台2-3和降尘花孔板2-2,折流导向台2-3位于降尘花孔板2-2上方,从深度燃烧区1出来的高温尾气经降尘花孔板2-2进入折流降尘区2。As shown in FIG. 3 , the baffle sedimentation zone 2 is a cavity area between the deep combustion zone 1 and the inner wall of the secondary combustion chamber shell 3 , and the annular gas outlet 2-7 on the upper part of the baffled dust reduction zone 2 is provided with exhaust gas monitoring Holes 2-6 and exhaust gas monitoring holes 2-6 are equipped with gas monitoring devices. The monitoring data includes the flow rate, pressure, temperature and concentration of pyrolysis gas. The above process parameters are respectively connected with the automatic control system through transmission lines; The middle and lower part are provided with a baffle guide table 2-3 and a dust reduction flower hole plate 2-2. The baffle guide table 2-3 is located above the dust reduction flower hole plate 2-2. The high temperature exhaust gas from the deep combustion zone 1 passes through the dust reduction flower hole. The plate 2-2 enters the baffled dust-reducing area 2.

所述折流导向台2-3设有多个,折流导向台为耐火耐磨材料制成的向下倾斜的环状斜台,其倾斜度≥45°。There are a plurality of the baffle guide platforms 2-3, and the baffle guide platforms are downwardly inclined annular inclined platforms made of refractory and wear-resistant materials, and the inclination is greater than or equal to 45°.

所述二燃室壳体3上安装有观察孔2-5、燃烧气监测孔2-4、压缩空气吹灰管2-8和检修口2-9,压缩空气吹灰管2-8设置在折流导向台2-3和降尘花孔板2-2的上方位置,可定期对其表面进行吹扫,预防积灰和堵塞发生;检修口2-9设置在集灰斗2-10的中部和降尘花孔板2-2的下方位置。The second combustion chamber shell 3 is provided with an observation hole 2-5, a combustion gas monitoring hole 2-4, a compressed air soot blowing pipe 2-8 and an inspection port 2-9, and the compressed air soot blowing pipe 2-8 is arranged in the The upper position of the baffle guide table 2-3 and the dust reduction flower orifice plate 2-2 can be regularly purged to prevent the occurrence of ash accumulation and blockage; the inspection port 2-9 is set in the middle of the ash collecting hopper 2-10 and the lower position of the dust suppression flower orifice plate 2-2.

如图3和图4所示,所述集灰斗2-10的中部设有挡火格栅2-1,挡火格栅2-1为圆孔或方孔状高温耐火耐磨格栅,位于深度燃烧区1和折流降尘区2的下部,挡火格栅2-1上的圆孔或方孔直径可根据实际情况进行设计和调整。As shown in Figures 3 and 4, the middle of the ash collecting hopper 2-10 is provided with a fire blocking grille 2-1. Located in the lower part of the deep combustion zone 1 and the baffled dust reduction zone 2, the diameter of the round or square holes on the fire-blocking grille 2-1 can be designed and adjusted according to the actual situation.

如图3、图5和图6所示,所述降尘花孔板2-2为环形耐热冲孔钢板,固定安装于出气口1-5与二燃室壳体3内壁之间,降尘花孔板2-2厚度和冲孔的孔径大小可根据实际情况进行设计和调整。As shown in Figure 3, Figure 5 and Figure 6, the dust suppression flower orifice plate 2-2 is an annular heat-resistant punched steel plate, which is fixedly installed between the air outlet 1-5 and the inner wall of the second combustion chamber shell 3. The thickness of the orifice plate 2-2 and the aperture size of the punching holes can be designed and adjusted according to the actual situation.

如图3、图7和图8所示,所述折流导向台2-3为耐火耐磨材料制成的向下倾斜(倾斜度≥45°)的环状斜台,固定安装于二燃室壳体3内壁上,起折流导向和降尘作用。As shown in Fig. 3, Fig. 7 and Fig. 8, the baffle guide table 2-3 is an annular inclined table made of refractory and wear-resistant material that slopes downward (inclination ≥ 45°), and is fixedly installed on the secondary combustion chamber. On the inner wall of the chamber shell 3, it plays the role of deflecting and guiding and reducing dust.

如图3和图9所示,所述环形出气管2-7环绕于二燃室壳体3上部外壳,通过环形集气和导气结构,将经过折流降尘后的高温尾气集中收集,并导入尾气净化系统。As shown in Figure 3 and Figure 9 , the annular gas outlet pipe 2-7 surrounds the upper shell of the secondary combustion chamber shell 3, and the high temperature exhaust gas after deflecting and dust reduction is collected through the annular gas collecting and air guiding structure, and the Introduce the exhaust gas purification system.

本发明应用于生活垃圾热解炉的二燃室处理装置工作原理如下:The working principle of the second combustion chamber treatment device of the present invention applied to the domestic waste pyrolysis furnace is as follows:

运行时,由热解气化炉经热解气化产生的可燃热解气首先通过环形集气管收集后再经过进气口1-1导入深度燃烧区1内的燃烧段1-2,并以切向旋流方式进入燃烧段1-2,以增加热解气湍流度,促进热解气与二次风的均匀混合。进入燃烧段1-2的热解气与二次风混合,由于燃烧段1-2的内径稍大于进气口1-1的管径,且二次风补给口1-3在燃烧段1-2内从上到下采用非等距的布置方式,越靠近进气口一端布置得越密,此种进气和布风方式既能避免热解气浓度被二次风过度稀释,又能保证热解气在燃烧段1-2的上半部即被少量的二次风均匀混合并充分燃烧,尽可能地减少尾气排放量,同时,为防止热解气未经彻底燃烧便排入折流降尘区,燃烧段1-2下半部也设置少量二次风补给口1-3和燃烧器1-4,热解气经彻底燃烧产生的高温尾气通过出气口1-5进入折流降尘区2,高温尾气经喇叭口出气口1-5瞬间扩管减速,可提升降尘效果并增加尾气在高温段停留时间。高温尾气在折流降尘区2内通过挡火格栅2-1、降尘花孔板2-2和折流导向台2-3的多级降尘和折流作用,有效去除其中的金属粉尘和其它尘粒,并保证高温尾气在二燃室内停留足够时间,从根本上抑制二噁英等有毒有害二次污染物的生成,经折流降尘后的高温尾气通过二燃室壳体上部的环形出气管2-7集中收集,并导入尾气净化系统。During operation, the combustible pyrolysis gas produced by the pyrolysis gasifier through pyrolysis gasification is first collected through the annular gas header and then introduced into the combustion section 1-2 in the deep combustion zone 1 through the air inlet 1-1, The tangential swirl method enters the combustion section 1-2 to increase the turbulence of the pyrolysis gas and promote the uniform mixing of the pyrolysis gas and the secondary air. The pyrolysis gas entering the combustion section 1-2 is mixed with the secondary air, because the inner diameter of the combustion section 1-2 is slightly larger than the pipe diameter of the air inlet 1-1, and the secondary air supply port 1-3 is located in the combustion section 1-2. 2. The non-equidistant arrangement is adopted from top to bottom. The closer to the air inlet, the denser the arrangement is. This air intake and air distribution method can not only avoid the excessive dilution of the pyrolysis gas concentration by the secondary air, but also ensure that the heat The pyrolysis gas is uniformly mixed with a small amount of secondary air in the upper half of the combustion section 1-2 and fully combusted to reduce exhaust emissions as much as possible. In the lower half of the combustion section 1-2, a small amount of secondary air supply ports 1-3 and burners 1-4 are also set, and the high-temperature exhaust gas generated by the thorough combustion of the pyrolysis gas enters the baffled dust reduction zone 2 through the gas outlet 1-5. , the high-temperature exhaust gas is instantly expanded and decelerated through the bell mouth outlet 1-5, which can improve the dust reduction effect and increase the residence time of the exhaust gas in the high temperature section. The high-temperature exhaust gas passes through the multi-stage dust reduction and baffle action of the fire blocking grille 2-1, the dust reduction flower orifice 2-2 and the baffle guide table 2-3 in the baffled dust reduction zone 2, effectively removing the metal dust and other Dust particles, and ensure that the high-temperature exhaust gas stays in the secondary combustion chamber for a sufficient time to fundamentally inhibit the formation of toxic and harmful secondary pollutants such as dioxins. The trachea 2-7 are collected centrally and introduced into the exhaust gas purification system.

本发明二燃室处理装置运行期间,自动控制系统通过热解气和高温尾气的流量、压力、温度和污染物浓度等数据分析进行自动调控,以达到最优运行工况,将二燃室的深度燃烧和折流降尘过程与热解炉的热解气化过程有机结合,实现对各过程的精确控制;例如,当热解气流量小、浓度低时,可关闭燃烧段1-2下半部的二次风补给口和燃烧器,只开启燃烧段1-2上半部的二次风供给和燃烧器,系统灵活性高,有效控制燃烧工况和尾气排放量,减轻尾气净化系统的处理负荷,节省运行成本。During the operation of the secondary combustion chamber treatment device of the present invention, the automatic control system performs automatic regulation through data analysis such as the flow rate, pressure, temperature and pollutant concentration of the pyrolysis gas and high-temperature exhaust gas, so as to achieve the optimal operating condition, and the secondary combustion chamber The deep combustion and baffled dust reduction process is organically combined with the pyrolysis gasification process of the pyrolysis furnace to achieve precise control of each process; for example, when the pyrolysis gas flow rate is small and the concentration is low, the lower half of the combustion section 1-2 can be closed The secondary air supply port and burner in the upper part of the system only open the secondary air supply and burner in the upper half of the combustion section 1-2. The system has high flexibility, effectively controls the combustion conditions and exhaust emissions, and reduces the exhaust gas purification system. Handling load and saving operating costs.

本发明与现有技术相比,具有系统操作简便、过程可控性强、热解效率高、二次燃烧充分、折流降尘高效、污染物浓度低、尾气排放量小、投运成本低等优点,可广泛应用于城镇生活垃圾热解处理领域。Compared with the prior art, the invention has the advantages of simple and convenient system operation, strong process controllability, high pyrolysis efficiency, sufficient secondary combustion, high efficiency of deflecting and dust reduction, low pollutant concentration, small exhaust gas emission, low operation cost, etc. Advantages, it can be widely used in the field of urban domestic waste pyrolysis treatment.

以上所述之例仅为本发明的较佳实施方式而已,并非用来限制本发明的实施范围。应当指出,由于文字表达的有限性,而客观上存在无限的具体结构,对于本发明所属技术领域的普通技术人员来说,在不脱离本发明主要构思的前提下,还可以做出若干简单推演或替换,均应视为属于本发明的保护范围。The above-mentioned examples are only preferred embodiments of the present invention, and are not intended to limit the scope of implementation of the present invention. It should be pointed out that due to the limitation of written expression, and objectively there are infinite specific structures, for those of ordinary skill in the technical field to which the present invention belongs, without departing from the main idea of the present invention, some simple deductions can also be made Or replacement, should be regarded as belonging to the protection scope of the present invention.

Claims (9)

1. being applied to dual firing chamber's treatment process of domestic garbage pyrolysis furnace, which is characterized in that the treatment process includes following operation Step:
1) combustible pyrolysis's conductance that pyrolysis oven generates is entered to be located at the deep combustion area top in dual firing chamber centre, combustible pyrolysis Gas passes through deep combustion area from top to bottom, and enters deep combustion Qu Houyu Secondary Air in a manner of tangential swirl and be sufficiently mixed, fire It burns;
2) high-temperature tail gas that the burning of deep combustion area generates is come out to import from the bottom in deep combustion area and is located at deep combustion area The baffling depositing dust area of outside, and convey from lower to upper, separate unit, implementation subregion are transported each other for deep combustion area and baffling depositing dust area Row;High-temperature tail gas is discharged from baffling depositing dust area top after multistage depositing dust and baffling in baffling depositing dust area and is sent into tail gas clean-up System.
2. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace, which is characterized in that the device includes dual firing chamber's shell, and two It fires and is equipped with deep combustion area and baffling depositing dust area in room housing, the centre of dual firing chamber's shell is arranged in deep combustion area, rolls over Stream depositing dust area is located at the outside in deep combustion area, and deep combustion area is connected with the bottom in baffling depositing dust area;Deep combustion area Top is equipped with the air inlet tangentially accessed, and the top in baffling depositing dust area is equipped with exhaust collection and imports the ring of exhaust gas purification system Shape escape pipe;The lower part of dual firing chamber's shell is equipped with the flue-dust retainer below deep combustion area and baffling depositing dust area, dual firing chamber's shell The bottom of body is equipped with ash hole.
3. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace according to claim 2, which is characterized in that the depth Degree combustion zone is circular straighttube shape, and combustible pyrolysis's gas of top closure, pyrolysis oven generation imports deep combustion by air inlet In area, deep combustion area is equipped with multiple Secondary Airs supply mouth and multiple burners, and the bottom in deep combustion area is equipped with horn-like Gas outlet.
4. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace according to Claims 2 or 3, which is characterized in that institute The air inlet for stating deep combustion area top is equipped with pyrolysis gas monitoring holes, is equipped with gas controlling device in pyrolysis gas monitoring holes, into The bore of port is less than the internal diameter in deep combustion area.
5. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace according to Claims 2 or 3, which is characterized in that institute Cavity area of the baffling depositing dust area between deep combustion area and dual firing chamber's inner walls is stated, the annular on baffling depositing dust area top goes out Port is equipped with tail gas monitoring holes, and gas controlling device is equipped in tail gas monitoring holes, and the middle and lower part in deep combustion area is equipped with baffling Guide table and depositing dust flower orifice plate, baffling guide table are located above depositing dust flower orifice plate, the high-temperature tail gas warp come out from deep combustion area Depositing dust flower orifice plate enters baffling depositing dust area.
6. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace according to claim 5, which is characterized in that the folding It flowing guide table and is equipped with multiple, baffling guide table is the cyclic annular sloping platform that tilts down made of Fire and abrasion resistant material, gradient >= 45°。
7. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace according to Claims 2 or 3, which is characterized in that institute It states and peep hole, combustion gas monitoring holes, compressed air soot-blowing pipe and access hole is installed on dual firing chamber's shell.
8. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace according to claim 2, which is characterized in that the collection The middle part of ash bucket, which is equipped with, keeps off fiery grid.
9. being applied to dual firing chamber's processing unit of domestic garbage pyrolysis furnace according to claim 3, which is characterized in that described two Deep combustion area is arranged in non-equidistant in secondary wind supply mouth and burner from top to bottom.
CN201710044585.0A 2017-01-19 2017-01-19 Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace Active CN106705062B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710044585.0A CN106705062B (en) 2017-01-19 2017-01-19 Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710044585.0A CN106705062B (en) 2017-01-19 2017-01-19 Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace

Publications (2)

Publication Number Publication Date
CN106705062A CN106705062A (en) 2017-05-24
CN106705062B true CN106705062B (en) 2019-06-25

Family

ID=58909302

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710044585.0A Active CN106705062B (en) 2017-01-19 2017-01-19 Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace

Country Status (1)

Country Link
CN (1) CN106705062B (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109724088A (en) * 2017-10-31 2019-05-07 云南蓝澈科技有限公司 A kind of multistage gasification flash burning furnace
CN110081435B (en) * 2019-05-23 2023-12-26 江苏利百川环保科技有限公司 Two-combustion-chamber structure of pyrolysis furnace
CN113375165A (en) * 2021-06-04 2021-09-10 北京基亚特环保科技有限公司 Vertical secondary combustion chamber device
CN114001357B (en) * 2021-09-24 2023-10-31 中国科学院广州能源研究所 A mobile medical waste cleaning and heat treatment device
DE102021005290A1 (en) 2021-10-23 2023-04-27 Dimitrios Fotakis Device for dust reduction when hot gas is extracted from furnaces or gasifications.

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2581822Y (en) * 2002-09-12 2003-10-22 广州贝龙环保热力设备股份有限公司 Refuse pyrolising incinerator
JP2004169931A (en) * 2002-11-15 2004-06-17 Jfe Engineering Kk Waste treatment equipment
CN2653308Y (en) * 2003-10-10 2004-11-03 清华紫光环保有限公司 Homogenizing pyrogenic medical garbage incinerator
JP4474429B2 (en) * 2007-03-13 2010-06-02 メタウォーター株式会社 Waste incinerator and incineration method
CN102012032A (en) * 2010-12-29 2011-04-13 中国科学院广州能源研究所 Medical waste complete incineration device
CN104456575A (en) * 2014-11-10 2015-03-25 宜昌市九天环保科技有限公司 Household garbage pyrolysis combustion furnace and operation process thereof
CN206439838U (en) * 2017-01-19 2017-08-25 广西博世科环保科技股份有限公司 Dual firing chamber's processing unit applied to domestic garbage pyrolysis stove

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2581822Y (en) * 2002-09-12 2003-10-22 广州贝龙环保热力设备股份有限公司 Refuse pyrolising incinerator
JP2004169931A (en) * 2002-11-15 2004-06-17 Jfe Engineering Kk Waste treatment equipment
CN2653308Y (en) * 2003-10-10 2004-11-03 清华紫光环保有限公司 Homogenizing pyrogenic medical garbage incinerator
JP4474429B2 (en) * 2007-03-13 2010-06-02 メタウォーター株式会社 Waste incinerator and incineration method
CN102012032A (en) * 2010-12-29 2011-04-13 中国科学院广州能源研究所 Medical waste complete incineration device
CN104456575A (en) * 2014-11-10 2015-03-25 宜昌市九天环保科技有限公司 Household garbage pyrolysis combustion furnace and operation process thereof
CN206439838U (en) * 2017-01-19 2017-08-25 广西博世科环保科技股份有限公司 Dual firing chamber's processing unit applied to domestic garbage pyrolysis stove

Also Published As

Publication number Publication date
CN106705062A (en) 2017-05-24

Similar Documents

Publication Publication Date Title
CN106705062B (en) Treatment process and treatment device applied to the secondary combustion chamber of domestic waste pyrolysis furnace
CN107461746B (en) A kind of small-sized domestic garbage pyrolysis gasification oven and purification system
CN102628589B (en) Combustion method and device for pulverized coal at high temperature and low NOx
CN108870398A (en) Small-sized living garbage incinerator
CN106352343A (en) Gasifying incinerator applicable to household garbage with high heat value
CN105698182B (en) CIU for handling rubbish
CN201387005Y (en) Dust-removing fluidized-bed furnace
CN201666566U (en) An industrial boiler system using pulverized coal
CN105698183B (en) Incinerator for handling rubbish
CN112944352B (en) A domestic waste incinerator
CN208090687U (en) A kind of dual firing chamber's air inlet system
CN108686839B (en) High-efficient cyclone that purifies
CN204730212U (en) A kind of living beings class solid waste and the useless burning of danger vapour system processed
CN208907617U (en) Burner, combustion system and bituminous mixing plant
CN211450954U (en) Waste incineration equipment based on energy-saving and environment-friendly technology
CN206439838U (en) Dual firing chamber's processing unit applied to domestic garbage pyrolysis stove
CN2198506Y (en) Vertical rear trap slag tube bundle whirlwind boiler with ring room
CN209084790U (en) It is a kind of to adjust than rubbish tail gas incinerator greatly
CN210004388U (en) kinds of low-nitrogen burner
CN206037061U (en) Multistage burning remains sacrificial offerings burn burning furnace
CN223323346U (en) A fully burning incinerator
CN223855671U (en) A ventilation system device for an incineration equipment
CN119755622B (en) Biomass coupling blending combustion power generation device
CN212204542U (en) Waste heat recovery incinerator for pharmaceutical solid waste
CN218237476U (en) Garbage incinerator with air inlet after complete preheating

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CP03 Change of name, title or address
CP03 Change of name, title or address

Address after: Intersection of Dongcheng Avenue and Dongcheng Road in Heli Park, Ningguo Economic and Technological Development Zone, Ningguo City, Xuancheng City, Anhui Province

Patentee after: Anhui Boshike Environmental Protection Technology Co.,Ltd.

Country or region after: China

Address before: 530007 12 Kexing Road, hi tech Zone, Nanning, the Guangxi Zhuang Autonomous Region

Patentee before: GUANGXI BOSSCO ENVIRONMENTAL PROTECTION TECHNOLOGY Co.,Ltd.

Country or region before: China

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20240510

Address after: 530000 No. 101, Gao'an Road, high tech Zone, Nanning, Guangxi Zhuang Autonomous Region

Patentee after: Guangxi Boshike Environmental Technology Co.,Ltd.

Country or region after: China

Patentee after: Anhui Boshike Environmental Protection Technology Co.,Ltd.

Address before: Intersection of Dongcheng Avenue and Dongcheng Road in Heli Park, Ningguo Economic and Technological Development Zone, Ningguo City, Xuancheng City, Anhui Province

Patentee before: Anhui Boshike Environmental Protection Technology Co.,Ltd.

Country or region before: China

CP03 Change of name, title or address
CP03 Change of name, title or address

Address after: 530000 No. 101, Gao'an Road, high tech Zone, Nanning, Guangxi Zhuang Autonomous Region

Patentee after: Guangxi Boshike Environmental Technology Co.,Ltd.

Country or region after: China

Patentee after: GUANGXI BOSSCO ENVIRONMENTAL PROTECTION TECHNOLOGY Co.,Ltd.

Address before: 530000 No. 101, Gao'an Road, high tech Zone, Nanning, Guangxi Zhuang Autonomous Region

Patentee before: Guangxi Boshike Environmental Technology Co.,Ltd.

Country or region before: China

Patentee before: Anhui Boshike Environmental Protection Technology Co.,Ltd.