CN2606262Y - A low-pollution waste incineration system - Google Patents
A low-pollution waste incineration system Download PDFInfo
- Publication number
- CN2606262Y CN2606262Y CN03223803.7U CN03223803U CN2606262Y CN 2606262 Y CN2606262 Y CN 2606262Y CN 03223803 U CN03223803 U CN 03223803U CN 2606262 Y CN2606262 Y CN 2606262Y
- Authority
- CN
- China
- Prior art keywords
- rotary kiln
- combustion chamber
- ash
- combustion
- housing
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 238000004056 waste incineration Methods 0.000 title description 13
- 238000002844 melting Methods 0.000 claims abstract description 17
- 230000008018 melting Effects 0.000 claims abstract description 17
- 239000010813 municipal solid waste Substances 0.000 claims description 20
- 239000002918 waste heat Substances 0.000 claims description 14
- 239000007789 gas Substances 0.000 claims description 6
- 229910001220 stainless steel Inorganic materials 0.000 claims description 3
- 239000010935 stainless steel Substances 0.000 claims description 3
- 238000007789 sealing Methods 0.000 claims description 2
- 230000009977 dual effect Effects 0.000 claims 6
- 238000010304 firing Methods 0.000 claims 6
- 239000003818 cinder Substances 0.000 claims 2
- 238000002485 combustion reaction Methods 0.000 abstract description 74
- 239000002956 ash Substances 0.000 abstract description 33
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 abstract description 19
- 239000003546 flue gas Substances 0.000 abstract description 19
- YLQBMQCUIZJEEH-UHFFFAOYSA-N Furan Chemical compound C=1C=COC=1 YLQBMQCUIZJEEH-UHFFFAOYSA-N 0.000 abstract description 16
- 239000000446 fuel Substances 0.000 abstract description 13
- 239000010881 fly ash Substances 0.000 abstract description 12
- 239000003344 environmental pollutant Substances 0.000 abstract description 11
- 231100000719 pollutant Toxicity 0.000 abstract description 11
- 239000002893 slag Substances 0.000 abstract description 9
- 239000002699 waste material Substances 0.000 abstract description 6
- 230000000694 effects Effects 0.000 abstract description 5
- 230000007613 environmental effect Effects 0.000 abstract description 2
- 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 2
- 239000000779 smoke Substances 0.000 description 8
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 6
- 238000000034 method Methods 0.000 description 6
- 150000002013 dioxins Chemical class 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 5
- 150000002240 furans Chemical class 0.000 description 5
- 238000012545 processing Methods 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 4
- 239000003921 oil Substances 0.000 description 4
- 239000010782 bulky waste Substances 0.000 description 3
- 238000009826 distribution Methods 0.000 description 3
- 238000012423 maintenance Methods 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 238000002679 ablation Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 230000007797 corrosion Effects 0.000 description 2
- 238000005260 corrosion Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000013461 design Methods 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 239000004744 fabric Substances 0.000 description 2
- 150000002894 organic compounds Chemical class 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000000123 paper Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000004033 plastic Substances 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 241000255925 Diptera Species 0.000 description 1
- 241000699670 Mus sp. Species 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 239000004035 construction material Substances 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 150000004826 dibenzofurans Chemical class 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000010794 food waste Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 239000002828 fuel tank Substances 0.000 description 1
- 238000002309 gasification Methods 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000010806 kitchen waste Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 239000000155 melt Substances 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000008520 organization Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 244000052769 pathogen Species 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 239000003473 refuse derived fuel Substances 0.000 description 1
- 239000005060 rubber Substances 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- -1 vegetation Substances 0.000 description 1
- 238000004017 vitrification Methods 0.000 description 1
Images
Classifications
-
- 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
Landscapes
- Gasification And Melting Of Waste (AREA)
Abstract
Description
技术领域Technical field
本实用新型涉及垃圾处理技术,特别涉及一种低污染垃圾焚烧系统。The utility model relates to garbage treatment technology, in particular to a low-pollution garbage incineration system.
背景技术 Background technique
城市垃圾堆放,有以下明显的危害:污染水源,污染农田、土壤,污染大气,成为蚊蝇、老鼠、病原体的滋生源,侵占土地等。城市生活垃圾中通常含有:纸、布、塑料、橡胶、厨余、草木、砖瓦、沙土、金属、玻璃等。但各组分的含量随各地区的生活习惯、经济发展水平、气候状况等的不同而异。在发达国家,城市生活垃圾的产量大,其中食品废物、纸、布、塑料等有机物占很大比重,可燃物含量很高,热值也很高。我国垃圾总体上来讲无机物的含量相对较高,但近年来,随着生活水平的提高,城市煤气的普及,垃圾中的有机成分也在逐渐增多,容重减小、热值增大。同时,垃圾的产量也逐年增大。国内外垃圾的这些特点表明:传统的填埋和堆肥处理已不能适应需要,因为这两种方法减容、减量效果差,而焚烧法则由于它的优点得到了迅速发展。The dumping of urban garbage has the following obvious hazards: polluting water sources, polluting farmland and soil, polluting the atmosphere, becoming a breeding source for mosquitoes, mice, and pathogens, and occupying land. Municipal solid waste usually contains: paper, cloth, plastic, rubber, kitchen waste, vegetation, bricks, sand, metal, glass, etc. However, the content of each component varies with the living habits, economic development level, and climate conditions of each region. In developed countries, the output of municipal solid waste is large, of which food waste, paper, cloth, plastic and other organic matter account for a large proportion, with high combustible content and high calorific value. Generally speaking, the content of inorganic substances in garbage in our country is relatively high, but in recent years, with the improvement of living standards and the popularization of city gas, the organic components in garbage are also gradually increasing, with a decrease in bulk density and an increase in calorific value. At the same time, the output of garbage is also increasing year by year. These characteristics of garbage at home and abroad show that the traditional landfill and composting treatment can no longer meet the needs, because the two methods have poor volume reduction and volume reduction effects, while the incineration method has been developed rapidly due to its advantages.
国外开发出的适合于固体废弃物焚烧的炉型主要有:马丁炉(MartinFurnace)、两段炉(two-stage furnace)、两室炉(two-chamber furnace)、回转窑(rotary kiln)、流化床(fluidized bed)、垃圾衍生燃料(refuse derived fuel)、控制氧量燃烧(controlled air oxidation)、直流电弧炉(direct-current arc melter)、等离子体焚烧炉(thermal plasma arc vitrification)及高温或低温裂解(high/lowtemperature decomposition)等。几种常见的垃圾焚烧炉型的比较如下:The furnace types suitable for solid waste incineration developed abroad mainly include: Martin Furnace, two-stage furnace, two-chamber furnace, rotary kiln, fluidized bed, refuse derived fuel, controlled air oxidation, direct-current arc melter, thermal plasma arc vitrification and high temperature or Low temperature cracking (high/low temperature decomposition), etc. A comparison of several common waste incinerator types is as follows:
(1)机械炉排式:主要应用于欧洲、美国、日本,处理能力在200t/d以上,设计、制造及操作维修技术已成熟,除大件垃圾外不分类破碎。其优点是:适用大容量,公害易处理,燃烧可靠;缺点是:造价高,运行、维修费高,应连续运转,操作运转技术要求高。(1) Mechanical grate type: It is mainly used in Europe, the United States, and Japan. The processing capacity is above 200t/d. The design, manufacturing, operation and maintenance technologies are mature. Except for bulky waste, it is not classified and shredded. Its advantages are: suitable for large capacity, easy to handle pollution, and reliable combustion; disadvantages are: high cost, high operation and maintenance costs, continuous operation, and high technical requirements for operation and operation.
(2)模组式:主要应用于美国、日本,处理能力在200t/d以下,设计、制造及操作维修技术已成熟,无法处理大件垃圾。其优点是:适用小容量,构造简单,装置可移动、机动性大;缺点是:燃烧不完全,燃烧效率低,使用年限短,平均建造成本较高。(2) Modular type: mainly used in the United States and Japan, the processing capacity is below 200t/d, and the design, manufacturing, operation and maintenance technology is mature, so it cannot handle bulky waste. Its advantages are: suitable for small capacity, simple structure, movable device and high mobility; disadvantages are: incomplete combustion, low combustion efficiency, short service life, and high average construction cost.
(3)回转窑式:主要应用于美国、丹麦,处理能力在200t/d以上,供应商有限,除大件垃圾外不需分类破碎。其优点是:垃圾搅拌及干燥性佳,可适用中、大容量,可高温燃烧,残灰颗粒小。缺点是:连接传动装置复杂,炉内的耐火材料易损坏。(3) Rotary kiln type: mainly used in the United States and Denmark, with a processing capacity of more than 200t/d, limited suppliers, and no need for classification and crushing except for bulky waste. Its advantages are: good garbage mixing and drying, suitable for medium and large capacity, high temperature combustion, and small residual ash particles. The disadvantages are: the connection transmission device is complicated, and the refractory material in the furnace is easily damaged.
(4)流化床式:主要应用于日本,处理能力在150t/d以下,供应商有限,需分类破碎至5cm以下。其优点是:适用中容量,燃烧温度较低,热传导性佳,公害低,燃烧效率较佳。缺点是:操作运转技术高,燃料的种类受到限制,需添加流动媒介,进料颗粒较小,单位处理量所需动力高,炉床材料易冲蚀损坏。(4) Fluidized bed type: mainly used in Japan, the processing capacity is below 150t/d, the suppliers are limited, and it needs to be classified and crushed to below 5cm. Its advantages are: suitable for medium capacity, low combustion temperature, good thermal conductivity, low pollution, and good combustion efficiency. The disadvantages are: high operating technology, limited fuel types, need to add flow media, small feed particles, high power required per unit of processing capacity, and hearth materials are easily eroded and damaged.
在实践中人们逐渐认识到,直接焚烧处理具有以下不足之处:In practice, people have gradually realized that direct incineration has the following disadvantages:
(1)垃圾水分高,难以稳定、完全燃烧;(1) Garbage has high moisture content and is difficult to burn stably and completely;
(2)排放氯化二苯并二噁咽和氯化二苯并呋喃;(2) Emission of chlorinated dibenzodioxins and chlorinated dibenzofurans;
(3)国内制造炉排的技术不成熟,进口炉排昂贵;(3) The technology of domestic grate manufacturing is immature, and the imported grate is expensive;
(4)余热锅炉设备高温腐蚀。(4) High temperature corrosion of waste heat boiler equipment.
因此,能否在不投油或少投油的条件下稳定燃烧、完全燃烧;能否有效地控制腐蚀和二噁咽、呋喃等污染物的生成;能否降低投资和运行成本,成为垃圾焚烧技术发展的关键。Therefore, whether it can burn stably and completely under the condition of no or less oil input; can it effectively control corrosion and the formation of pollutants such as dioxins and furans; key to technological development.
发明内容Contents of Invention
本实用新型的目的在于克服现有技术的缺点及不足,提供一种有效地提高燃烧效率,减少辅助燃料的用量,减少烟气中二噁咽、呋喃等污染物的排放,减少对环境污染的低污染垃圾焚烧系统。The purpose of the utility model is to overcome the disadvantages and deficiencies of the prior art, to provide a fuel tank that can effectively improve combustion efficiency, reduce the amount of auxiliary fuel, reduce the discharge of pollutants such as dioxin and furan in the flue gas, and reduce the impact on environmental pollution. Low pollution waste incineration system.
本实用新型的目的通过下述技术方案实现:本低污染垃圾焚烧系统包括回转窑、二燃室、高温空气燃烧装置、灰渣熔融处理装置,回转窑一端与二燃室相连接,另一端与灰渣熔融处理装置相连接,高温空气燃烧装置分别与回转窑和二燃室相连接。The purpose of this utility model is achieved through the following technical solutions: the low-pollution waste incineration system includes a rotary kiln, a second combustion chamber, a high-temperature air combustion device, and ash melting treatment device. One end of the rotary kiln is connected with the second combustion chamber, and the other end is connected with the second combustion chamber. The ash melting treatment device is connected, and the high-temperature air combustion device is respectively connected with the rotary kiln and the second combustion chamber.
所述回转窑分为四段,各段间采用不锈钢辊轮连接和密封。其中,第一、三段较短,为固定的进料段和进风段,用于进料和供风;第二、四段为转动段,由齿轮或辊轮带动,齿轮或辊轮则由电机带动,电机转速无级可调,实际运行时控制在3~5转/分钟。回转窑炉体倾斜角为2°,回转窑端部连接高温空气燃烧装置,中部的进风段连接鼓风机进行供风,鼓风机由电机带动,电机可根据需要进行调速,从而调节给风量。The rotary kiln is divided into four sections, and stainless steel rollers are used to connect and seal the sections. Among them, the first and third sections are relatively short, which are fixed feeding section and air inlet section, which are used for feeding and supplying air; the second and fourth sections are rotating sections, driven by gears or rollers, and the gears or rollers are Driven by a motor, the speed of the motor is steplessly adjustable, and the actual operation is controlled at 3 to 5 rpm. The inclination angle of the rotary kiln body is 2°. The end of the rotary kiln is connected to a high-temperature air combustion device, and the air inlet section in the middle is connected to a blower for air supply. The blower is driven by a motor, and the speed of the motor can be adjusted according to needs to adjust the air supply volume.
目前,现有回转窑采用一端送风焚烧,而且大多是顺流布置,使回转窑内温度偏低,燃烧不稳定;在本技术方案中,由于回转窑内垃圾前期处于加热、干燥阶段,所需空气量不大,但需要较高气体温度,以便于迅速加热干燥,故在一燃室中,空气、烟气流动与固体前进方向相反,采用逆流布置;由于中间反应较强烈,所以另外配风,补充氧气;本分级配风的回转窑可以克服传统回转窑配风和组织一燃室燃烧工况方面的不足之处,根据回转窑内的燃烧特性优化送风温度和送风量,有利于改善回转窑内温度分布及垃圾焚烧条件,从而达到垃圾稳定、完全燃烧的效果。At present, the existing rotary kiln is incinerated by air supply at one end, and most of them are arranged downstream, so that the temperature in the rotary kiln is low and the combustion is unstable; The amount of air required is not large, but a higher gas temperature is required to facilitate rapid heating and drying. Therefore, in the first combustion chamber, the flow of air and flue gas is opposite to the forward direction of the solid, and a countercurrent arrangement is adopted; due to the strong intermediate reaction, an additional configuration Wind, supplementary oxygen; the rotary kiln with graded air distribution can overcome the shortcomings of traditional rotary kiln air distribution and the organization of combustion conditions in the first combustion chamber, and optimize the air supply temperature and air supply volume according to the combustion characteristics in the rotary kiln. It is beneficial to improve the temperature distribution and waste incineration conditions in the rotary kiln, so as to achieve the effect of stable and complete combustion of waste.
所述二燃室的烟气进口与二燃室的壳体相切;亦即在二燃室采用切向进气方式,在二燃室组织起旋流燃烧工况。The flue gas inlet of the second combustion chamber is tangent to the casing of the second combustion chamber; that is, the second combustion chamber adopts a tangential air intake method, and a swirl combustion working condition is organized in the second combustion chamber.
现有的热解、气化炉中,如控制氧量燃烧的CAO系统的二燃室,都是采用轴向或径向进气,二燃室中无旋流流动,使得二燃室的供风与可燃气混合不好,并存在燃烧死角和部分低温区,不利于燃烧,同时可燃物在二燃室内的停留时间不够,若加大二燃室长度,则使得炉体庞大,投资增大;本技术方案中二燃室采用切向进气方式,在二燃室组织起旋流燃烧工况,加强炉内搅拌、混合,延长可燃物在炉内的停留时间,使烟气的可燃成分得到充分的燃烧,并有利于二噁咽、呋喃等污染物的分解。In existing pyrolysis and gasification furnaces, such as the secondary combustion chamber of the CAO system with controlled oxygen combustion, axial or radial air intake is adopted, and there is no swirling flow in the secondary combustion chamber, so that the supply of the secondary combustion chamber The mixture of wind and combustible gas is not good, and there are combustion dead angles and some low-temperature areas, which are not conducive to combustion. At the same time, the residence time of combustibles in the secondary combustion chamber is not enough. If the length of the secondary combustion chamber is increased, the furnace body will be huge and the investment will increase. ; In this technical solution, the second combustion chamber adopts a tangential air intake method, and the swirl combustion working condition is organized in the second combustion chamber to strengthen the stirring and mixing in the furnace, prolong the residence time of combustibles in the furnace, and make the combustible components of the flue gas It can be fully burned and is conducive to the decomposition of pollutants such as dioxins and furans.
所述高温空气燃烧装置包括空气预热器和余热锅炉,余热锅炉通过空气预热器与二燃室相连接。The high-temperature air combustion device includes an air preheater and a waste heat boiler, and the waste heat boiler is connected with the secondary combustion chamber through the air preheater.
现有的垃圾焚烧处理设备都是采用“焚烧炉-余热锅炉-空气预热器”的布置方式,或用蒸汽预热空气,空气预热温度低,有的甚至不预热空气,而垃圾含水率较高,这易造成炉温低、着火困难、燃烧不稳定、燃烧不完全的现象;另外燃烧温度较低,生成的痕量有机物二噁咽、呋喃等无法分解,由烟气排入大气,形成二次污染。本技术方案中采用“焚烧炉-空气预热器-余热锅炉”的布置方式,使焚烧垃圾产生的烟气余热,首先加热空气,这样可以大大提高供风的温度;然后,用高温空气来焚烧垃圾,提高反应温度,减少辅助燃料消耗量,减少烟气中二噁咽、呋喃等污染物的排放。The existing waste incineration treatment equipment adopts the arrangement of "incinerator-waste heat boiler-air preheater", or uses steam to preheat the air. The air preheating temperature is low, and some even do not preheat the air, and the waste contains water. The rate is high, which is easy to cause low furnace temperature, difficulty in ignition, unstable combustion, and incomplete combustion; in addition, the combustion temperature is low, and the trace organic compounds such as dioxin and furan cannot be decomposed, and are discharged into the atmosphere from the flue gas , forming secondary pollution. In this technical solution, the layout of "incinerator-air preheater-waste heat boiler" is adopted, so that the waste heat of flue gas generated by incineration of garbage can first heat the air, which can greatly increase the temperature of the air supply; then, use high-temperature air to incinerate Garbage, increase the reaction temperature, reduce the consumption of auxiliary fuel, and reduce the emission of pollutants such as dioxins and furans in the flue gas.
所述灰渣熔融处理装置包括壳体、灰斗、燃油烧嘴、排烟口、渣口,灰斗及燃油烧嘴穿过壳体上端面并与壳体固定连接,排烟口位于壳体上端面一侧,渣口位于壳体底端一侧。本灰渣熔融处理装置的原理是:灰渣和飞灰从灰斗落入壳体内的炉膛内,从燃油烧嘴中喷入燃油对灰渣和飞灰进行熔融处理,处理后的烟气从排烟口排出,废渣从渣口排出。The ash slag melting treatment device includes a shell, an ash hopper, a fuel burner, a smoke outlet, and a slag outlet. The ash hopper and the fuel burner pass through the upper surface of the shell and are fixedly connected with the shell. On the side of the upper end face, the slag port is located on the bottom side of the shell. The principle of this ash melting treatment device is: ash and fly ash fall from the ash hopper into the furnace in the casing, fuel oil is injected from the fuel burner to melt the ash and fly ash, and the processed flue gas is discharged from the The smoke is discharged from the exhaust port, and the waste residue is discharged from the slag port.
现有的一些垃圾焚烧炉,包括马丁炉、流化床、CAO、回转窑等,灰渣中可烧蚀量常高于5%,这说明燃烧不够充分,炉渣的可利用性也很低,另外灰渣和飞灰中的痕量有机物二噁咽、呋喃等也未得到有效控制,直接排向土壤、水源和大气,二次污染较严重。本技术方案中采用高温的灰渣熔融处理装置来处理灰渣和飞灰,对灰渣和飞灰进行熔融处理,消除灰渣、飞灰中的二噁咽、呋喃等污染物的排放;同时,熔融后的灰渣可以作为建筑和道路建设材料。In some existing waste incinerators, including Martin furnace, fluidized bed, CAO, rotary kiln, etc., the ablation amount in ash is usually higher than 5%, which means that the combustion is not sufficient and the availability of slag is also very low. In addition, trace amounts of organic compounds such as dioxins and furans in ash and fly ash have not been effectively controlled, and are directly discharged into soil, water sources and the atmosphere, causing serious secondary pollution. In this technical solution, a high-temperature ash melting treatment device is used to process ash and fly ash, and the ash and fly ash are melted to eliminate the discharge of pollutants such as dioxin and furan in the ash and fly ash; at the same time , the molten ash can be used as construction and road construction materials.
本实用新型相对于现有技术具有如下的优点及效果:本低污染垃圾焚烧系统采用分段进空气的回转窑作为一燃室,利用烟气余热加热空气,从而使该系统达到最佳的燃烧效率,并减少辅助燃料的用量;同时,提高燃烧温度,减少烟气中二噁咽、呋喃等污染物的排放;另外,对灰渣、飞灰进行熔融处理,有效地控制灰渣、飞灰二噁咽、呋喃等污染物的排放;因而具有处理效率高、环保效果好的优点,可广泛地使用于处理城市生活垃圾,应用前景较广。Compared with the prior art, the utility model has the following advantages and effects: the low-pollution garbage incineration system adopts a rotary kiln with segmental air intake as a combustion chamber, and uses the waste heat of the flue gas to heat the air, so that the system can achieve the best combustion efficiency and reduce the amount of auxiliary fuel; at the same time, increase the combustion temperature to reduce the emission of pollutants such as dioxin and furan in the flue gas; in addition, melt the ash and fly ash to effectively control the ash and fly ash Discharge of pollutants such as dioxin, furan, etc. Therefore, it has the advantages of high treatment efficiency and good environmental protection effect, and can be widely used in the treatment of urban domestic waste, with a wide application prospect.
附图说明Description of drawings
图1是本实用新型低污染垃圾焚烧系统的系统流程图。Fig. 1 is a system flow chart of the low-pollution waste incineration system of the present invention.
图2是图1所示低污染垃圾焚烧系统中回转窑的结构示意图。Fig. 2 is a schematic structural diagram of the rotary kiln in the low-pollution waste incineration system shown in Fig. 1 .
图3是图1所示低污染垃圾焚烧系统中二燃室的结构示意图。Fig. 3 is a schematic structural view of the secondary combustion chamber in the low-pollution waste incineration system shown in Fig. 1 .
图4是图1所示低污染垃圾焚烧系统中空气预热器的结构示意图。Fig. 4 is a schematic structural view of the air preheater in the low-pollution waste incineration system shown in Fig. 1 .
图5是图1所示低污染垃圾焚烧系统中灰渣熔融处理装置图Figure 5 is a diagram of the ash melting treatment device in the low-pollution waste incineration system shown in Figure 1
具体实施方式 Detailed ways
下面结合实施例及附图对本实用新型作进一步详细的描述,但本实用新型的实施方式不限于此。The utility model will be further described in detail below in conjunction with the embodiments and accompanying drawings, but the implementation of the utility model is not limited thereto.
实施例Example
图1~图5示出了本实用新型的具体结构,由图1可见,本垃圾焚烧系统包括回转窑(一燃室)2、二燃室7、空气预热器8、余热锅炉9、灰渣熔融处理装置1,回转窑2一端与二燃室7相连接,另一端与灰渣熔融处理装置1相连接,余热锅炉9通过空气预热器8与二燃室7相连接,空气预热器8同时与回转窑2一端相连接。此外,图1中3为鼓风机、4为进料机构、5为垃圾斗、6为燃油喷嘴、10为烟囱。Fig. 1~Fig. 5 has shown the specific structure of the present utility model, and by Fig. 1, this waste incineration system comprises rotary kiln (one combustion chamber) 2, two
所述回转窑2的结构如图2所示分为四段,各段间采用不锈钢辊轮连接及用密封罩密封;其中,第一、三段较短,为固定的进料段2-1和进风段2-3,用于进料和供风;第二、四段2-2、2-4为转动段,由齿轮或辊轮带动,齿轮或辊轮则由电机带动,电机转速无级可调,实际运行时控制在3~5转/分钟;回转窑2炉体倾斜角为2°,回转窑2端部连接的空气预热器8通入高温空气进行预热,中部的进风段2-3连接鼓风机3进行供风,鼓风机3由电机带动,电机可根据需要进行调速,从而调节给风量。The structure of the
所述二燃室7的结构如图3所示,包括壳体7-1、烟气进口7-2、烟气出口7-3、进油口7-4,壳体7-1由外壳7-1A及耐火层7-1B组成,烟气进口7-2位于与壳体7-1相切的位置,烟气出口7-3及进油口7-4分别位于壳体7-1的两端。The structure of the
所述空气预热器8的结构如图4所示,壳体8-1两端开有烟气进口8-2和烟气出口8-3,壳体8-1的一侧开有空气进口8-4和空气出口8-5;壳体8-1内设置有陶瓷换热管8-6,换热管8-6内为空气通道,换热管8-6外为烟气通道。The structure of the
所述灰渣熔融处理装置1如图5所示,包括壳体1-1、燃油烧嘴1-2、灰斗1-3、排烟口1-4、渣口1-5,灰斗1-3及燃油烧嘴1-2穿过壳体1-1上端面并与壳体1-1固定连接,排烟口1-4位于壳体1-1上端面一侧,渣口1-5位于壳体1-1底端一侧。The
本低污染垃圾焚烧系统的工作原理是:系统布置采用“焚烧炉-空气预热器-余热锅炉”的布置方式,在二燃室7和余热锅炉9间安装空气预热器8,回收部分烟气余热,充分利用高温烟气加热入炉空气,温度达到600℃以上,提高一燃室2反应温度到900℃以上,二燃室2反应温度到1000℃以上,从而减少烟气中二噁咽、呋喃等污染物的排放,同时使垃圾稳定、完全燃烧,减少辅助燃料消耗量。经过一燃室2处理后,机械不完全燃烧损失q4在3%以下;从一燃室2出来的可燃气和烟气,以切向流动的方式进入二燃室7,进气速度维持在6m/s以上,以保证有一定的旋流度;在二燃室7中通入600℃以上的高温空气,在高温空气环境下,可燃气可以在低于容积百分比10%以下的条件下着火并稳定燃烧,旋流工况则可以加强炉内混合,从而强化燃烧,并延长可燃物在二燃室7的停留时间,保证经过二燃室7后化学不完全燃烧损失q3在0.2%以下;从一燃室2出来的灰渣和从除尘器或烟囱底部收集的飞灰,进入灰渣熔融处理装置1,该室用油为燃料,在1500℃以上,对灰渣、飞灰进行熔融处理,完全消除灰渣、飞灰中的二噁咽、呋喃等污染物。经过灰渣熔融处理装置后,灰渣的烧蚀量在0.1%以下。The working principle of this low-pollution waste incineration system is: the system layout adopts the layout of "incinerator-air preheater-waste heat boiler", and an
Claims (5)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN03223803.7U CN2606262Y (en) | 2003-02-26 | 2003-02-26 | A low-pollution waste incineration system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN03223803.7U CN2606262Y (en) | 2003-02-26 | 2003-02-26 | A low-pollution waste incineration system |
Publications (1)
Publication Number | Publication Date |
---|---|
CN2606262Y true CN2606262Y (en) | 2004-03-10 |
Family
ID=34162995
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN03223803.7U Expired - Fee Related CN2606262Y (en) | 2003-02-26 | 2003-02-26 | A low-pollution waste incineration system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN2606262Y (en) |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101055081B (en) * | 2006-04-14 | 2010-10-27 | 林世平 | Method for burning garbage using water coal slurry and burning system |
CN104930520A (en) * | 2015-06-19 | 2015-09-23 | 中能世华(北京)节能科技有限公司 | Household rubbish burning waste heat utilization system |
CN106594741A (en) * | 2016-11-18 | 2017-04-26 | 四川九洲环保科技有限责任公司 | Combustion chamber |
CN106594751A (en) * | 2017-01-11 | 2017-04-26 | 北京生态岛科技有限责任公司 | Waste incineration system |
CN106678808A (en) * | 2016-11-18 | 2017-05-17 | 四川九洲环保科技有限责任公司 | Incineration system |
CN108592033A (en) * | 2018-05-07 | 2018-09-28 | 石力峰 | A kind of efficient incinerator of hazardous waste |
CN115298481A (en) * | 2020-03-18 | 2022-11-04 | 住友重机械工业株式会社 | Heat treatment system |
CN118463193A (en) * | 2024-06-04 | 2024-08-09 | 中国人民解放军军事科学院防化研究院 | A two-stage combustion plasma hazardous waste incinerator |
-
2003
- 2003-02-26 CN CN03223803.7U patent/CN2606262Y/en not_active Expired - Fee Related
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101055081B (en) * | 2006-04-14 | 2010-10-27 | 林世平 | Method for burning garbage using water coal slurry and burning system |
CN104930520A (en) * | 2015-06-19 | 2015-09-23 | 中能世华(北京)节能科技有限公司 | Household rubbish burning waste heat utilization system |
CN106594741A (en) * | 2016-11-18 | 2017-04-26 | 四川九洲环保科技有限责任公司 | Combustion chamber |
CN106678808A (en) * | 2016-11-18 | 2017-05-17 | 四川九洲环保科技有限责任公司 | Incineration system |
CN106678808B (en) * | 2016-11-18 | 2018-06-15 | 四川九洲环保科技有限责任公司 | A kind of incineration system |
CN106594751A (en) * | 2017-01-11 | 2017-04-26 | 北京生态岛科技有限责任公司 | Waste incineration system |
CN108592033A (en) * | 2018-05-07 | 2018-09-28 | 石力峰 | A kind of efficient incinerator of hazardous waste |
CN115298481A (en) * | 2020-03-18 | 2022-11-04 | 住友重机械工业株式会社 | Heat treatment system |
CN118463193A (en) * | 2024-06-04 | 2024-08-09 | 中国人民解放军军事科学院防化研究院 | A two-stage combustion plasma hazardous waste incinerator |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
WO2009015575A1 (en) | Double-loop double-pyrogenation incinerator for garbage harmless treatment and its usage method | |
CN101029727A (en) | High-temperature mixed-layer incinerating method and incinerator for fire gate | |
CN109812818B (en) | Waste incinerator fly ash heat treatment system | |
CN204648254U (en) | Residents in rural community CIU | |
CN101955804A (en) | Solid biomass gasification system and process thereof | |
CN105864782A (en) | Device and method for heating and melting rubbish under oxygen-rich condition | |
CN1566751A (en) | Multistage burning method and system for gasification of refuse and co-fusion of charcoal ash in rotary kiln | |
CN106524175A (en) | Waste fusing and curing treatment system and method | |
CN2606262Y (en) | A low-pollution waste incineration system | |
CN201688418U (en) | Oil sludge incinerator | |
CN100336751C (en) | City sludge fluidized bed combustion device and method | |
CN106524176B (en) | Waste gasification melt-combustion system | |
CN209688848U (en) | A waste incinerator fly ash heat treatment system | |
CN214619564U (en) | Thermal plasma waste incineration device | |
CN2425277Y (en) | Gasifying incinerator for municipal house refuse | |
CN201078701Y (en) | Petroleum sludge grate firing helix grate incineration furnace | |
CN106642138B (en) | waste gasification melting furnace | |
CN108467738A (en) | Solid waste medium temperature pyrocrack furnace | |
CN110160054B (en) | Heat exchange method for clean incineration of sludge | |
CN111288438A (en) | Fluidized bed combustion furnace and combustion method | |
CN111288458A (en) | Domestic garbage incinerator | |
CN2563442Y (en) | Waste Incineration Melting Furnace | |
CN2898620Y (en) | Vertical rotary pyrolytic gasification incinerator of domestic refuse | |
CN112050220B (en) | A treatment system and method for purifying stale garbage using plasma technology | |
CN112944353A (en) | Thermal plasma waste incineration device |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
C19 | Lapse of patent right due to non-payment of the annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |