[go: up one dir, main page]

CN1137759C - Method and device for comprehensive purification of waste incineration tail gas - Google Patents

Method and device for comprehensive purification of waste incineration tail gas Download PDF

Info

Publication number
CN1137759C
CN1137759C CNB001098748A CN00109874A CN1137759C CN 1137759 C CN1137759 C CN 1137759C CN B001098748 A CNB001098748 A CN B001098748A CN 00109874 A CN00109874 A CN 00109874A CN 1137759 C CN1137759 C CN 1137759C
Authority
CN
China
Prior art keywords
tail gas
gas
bed
garbage incinerating
solid
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 - Lifetime
Application number
CNB001098748A
Other languages
Chinese (zh)
Other versions
CN1332334A (en
Inventor
强 姚
姚强
项光明
廖洪强
张金成
刘惠永
郑跃红
孙俊民
李定凯
徐旭常
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.)
TONGFANG ENVIRONMENT CO Ltd
Tsinghua University
Original Assignee
Tsinghua University
Qinghua Tongfang 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 Tsinghua University, Qinghua Tongfang Co Ltd filed Critical Tsinghua University
Priority to CNB001098748A priority Critical patent/CN1137759C/en
Publication of CN1332334A publication Critical patent/CN1332334A/en
Application granted granted Critical
Publication of CN1137759C publication Critical patent/CN1137759C/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Landscapes

  • Treating Waste Gases (AREA)

Abstract

The present invention discloses a method and a device for comprehensively purifying tail gas produced in refuse incineration. After accelerated by an expansion jet-pipe, tail gas produced in refuse incineration is sprayed into a circulating fluid bed purifier taking calcium-based eliminating agents and adsorbing agents as the bed material, and the bed material is driven together for fluidization; gas, solution and solid are intensively mixed, and both heat transfer and mass transfer are sufficiently carried out, so that acid gas and ultra-fine particles, such as heavy metal, dioxin, etc., in the tail gas are neutrally reacted in the process of mass transfer and absorbed by the absorbing agents. As compared with the prior art, the present invention has the advantages of simple processing steps, easy realization, obvious purifying effect, compact device structure, small occupation area, and low investment and running cost.

Description

一种垃圾焚烧尾气全面净化的方法及其装置Method and device for comprehensive purification of waste incineration tail gas

本发明涉及燃烧炉尾气净化和除尘技术领域,尤其涉及垃圾焚烧尾气的干法脱硫、脱氯以及细颗粒、重金属、二恶英等的吸附脱除方法及其装置。The invention relates to the technical field of combustion furnace tail gas purification and dust removal, in particular to a method and device for dry desulfurization and dechlorination of waste incineration tail gas and adsorption and removal of fine particles, heavy metals, dioxins, etc.

大气污染一直是世界许多国家环境保护的工作重点,各国先后开发的烟气脱硫技术已达200多种。但是,能够工业应用的只有十多种。对于垃圾焚烧产生的尾气,除含有常规燃煤烟气污染物如氮氧化物、硫氧化物、细颗粒和重金属外,还含有更大量的单质氯、氯化氢、二恶英等有害物质,常规的脱硫除尘技术不能满足垃圾焚烧尾气严格净化要求。现有国外垃圾焚烧尾气净化技术大都采用湿法,如美国专利US4789532是采用常规喷石灰浆液吸收尾气中的酸性气体,如二氧化硫、氯化氢、单质氯等,然后在反应器后接袋式除尘器除尘。上述方法虽然可去除尾气中的酸性气体和飞灰,但存在着设备投资及运行费用高、占地面积大、不能有效去除垃圾焚烧产生的重金属和二恶英细颗粒的问题。Air pollution has always been the focus of environmental protection work in many countries in the world, and more than 200 flue gas desulfurization technologies have been developed successively by various countries. However, there are only a dozen kinds that can be applied industrially. For the tail gas produced by waste incineration, in addition to conventional coal-fired flue gas pollutants such as nitrogen oxides, sulfur oxides, fine particles and heavy metals, it also contains a larger amount of harmful substances such as elemental chlorine, hydrogen chloride, and dioxins. Desulfurization and dust removal technology cannot meet the strict purification requirements of waste incineration tail gas. Most of the existing foreign waste incineration tail gas purification technologies use wet methods. For example, US Patent No. 4,789,532 uses conventional lime spray slurry to absorb acid gases in the tail gas, such as sulfur dioxide, hydrogen chloride, and elemental chlorine, and then connects a bag filter after the reactor to remove dust. . Although the above method can remove acid gas and fly ash in the tail gas, it has the problems of high equipment investment and operating costs, large floor area, and inability to effectively remove heavy metals and dioxin fine particles produced by waste incineration.

针对上述现有技术中存在的问题,本发明的目的是提供一种垃圾焚烧尾气全面净化的方法及其装置。使用该方法,可使工艺步骤简单、不仅净化尾气中酸性气体和飞灰的效果显著,更为突出的是可有效去除垃圾焚烧产生的重金属和二恶英细颗粒。为实施该方法的装置,其结构紧凑、占地面积小、投资运行费用低。In view of the above-mentioned problems in the prior art, the object of the present invention is to provide a method and device for comprehensive purification of waste incineration tail gas. Using the method, the process steps are simple, and not only the effect of purifying acid gas and fly ash in the tail gas is remarkable, but more prominently, it can effectively remove heavy metals and dioxin fine particles produced by garbage incineration. The device for implementing the method has a compact structure, a small occupied area, and low investment and operation costs.

为了达到上述的发明目的,本发明的技术方案以如下方式实现:一种垃圾焚烧尾气全面净化的方法,其步骤为:①将燃烧设备排出的烟气经过缩放喷管加速后喷入以钙基脱除剂和吸附剂为床料的流化床净化器内并带动床料一起流化;②在尾气与床料共流化的过程中发生气、液、固强烈混合与充分的传热和传质,使尾气中的酸性气体如二氧化硫、三氧化硫、氯化氢、单质氯和氮氧化物等与钙基脱除剂床料发生中和反应,并使尾气中重金属和二恶英等超细颗粒在传质过程中被床料中吸附剂吸附;③反应和吸附后形成的物料留在脱除剂中以固体形式和未完全反应的床料一道随烟气进入气固分离器;④经气固分离器后,固体颗粒进入缓冲仓中,使90%以上的固体颗粒进入混合造粒器并与新鲜石灰粉、活性炭和少量水混合造粒,缓冲仓中多余的物料排出。净化后的洁净烟气通过引风机由烟囱达标排放;⑤混合造粒后的颗粒再进入流化床净化器中循环使用。In order to achieve the above-mentioned purpose of the invention, the technical solution of the present invention is realized in the following manner: a method for comprehensive purification of waste incineration tail gas, the steps of which are: ① spray the flue gas discharged from the combustion equipment into a calcium-based The removal agent and adsorbent are bed materials in the fluidized bed purifier and drive the bed materials to fluidize together; ② During the co-fluidization process of tail gas and bed materials, strong mixing of gas, liquid and solid and sufficient heat transfer and Mass transfer, so that the acid gases in the tail gas, such as sulfur dioxide, sulfur trioxide, hydrogen chloride, elemental chlorine and nitrogen oxides, etc., react with the calcium-based remover bed material, and make the heavy metals and dioxins in the tail gas ultra-fine The particles are adsorbed by the adsorbent in the bed material during the mass transfer process; ③The material formed after the reaction and adsorption remains in the remover in solid form and enters the gas-solid separator together with the incompletely reacted bed material along with the flue gas; ④After After the gas-solid separator, the solid particles enter the buffer bin, and more than 90% of the solid particles enter the mixing granulator and are mixed with fresh lime powder, activated carbon and a small amount of water for granulation, and the excess materials in the buffer bin are discharged. The purified flue gas is discharged up to the standard through the induced draft fan from the chimney; ⑤The mixed and granulated particles enter the fluidized bed purifier for recycling.

实现上述发明目的垃圾焚烧尾气全面净化方法的装置,它包括以钙基脱除剂和吸附剂为床料的流化床净化器,以高效旋风除尘器、静电除尘器、布袋除尘器或它们有机结合组成的气固分离器,带有给料与排料装置的缓冲仓和混合造粒器。其结构特点是:所述流化床净化器的入口端设有可使尾气加速的缩放喷管及床料入口。缩放喷管另一端与垃圾焚烧尾气入口相接。床料入口与混合造粒器的出口相接。混合造粒器置有多个配料入口并与给料机相接。给料机另一端与缓冲仓相接。缓冲仓上方及侧上方置有气固分离器及排料机。气固分离器上方及侧上方置有净化气出口及水平连接管。水平连接管另一端与流化床净化器的出口端相接。The device for realizing the comprehensive purification method of waste incineration tail gas for the purpose of the above invention, which includes a fluidized bed purifier with calcium-based removal agent and adsorbent as bed material, high-efficiency cyclone dust collector, electrostatic precipitator, bag filter or their organic Combined gas-solid separator, buffer bin with feeding and discharging device and mixing granulator. Its structural features are: the inlet end of the fluidized bed purifier is provided with a scaling nozzle and a bed material inlet that can accelerate the tail gas. The other end of the scaling nozzle is connected to the waste incineration tail gas inlet. The bed material inlet is connected with the outlet of the mixing granulator. The mixing granulator is equipped with multiple ingredient inlets and is connected with the feeder. The other end of the feeder is connected with the buffer bin. A gas-solid separator and a discharge machine are installed above and beside the buffer bin. There are purified gas outlets and horizontal connecting pipes on the top and side of the gas-solid separator. The other end of the horizontal connecting pipe is connected with the outlet end of the fluidized bed purifier.

按照上述的技术方案,所述混合造粒器的多个配料入口为给水口,活性炭给料口及石灰粉给料口;所述缩放喷管的形状呈中间细、两端粗的双曲线圆管。According to the above-mentioned technical scheme, the multiple batching inlets of the mixing granulator are water inlets, activated carbon feeding inlets and lime powder feeding inlets; the shape of the scaling nozzle is a hyperbolic circle with a thin middle and thick ends. Tube.

本发明与现有技术相比,具有以下优点和积极效果:Compared with the prior art, the present invention has the following advantages and positive effects:

(1)在传统干式循环流化床烟气净化技术基础上,根据垃圾焚烧尾气污染物的特点和净化要求,通过循环流化床净化器、气固分离器和混合造粒器有机结合为一体化,利用钙基脱除剂反应去除尾气中的酸性气体,同时添加飞灰和活性炭等吸附剂有效去除重金属和二恶英。不仅工艺简单,设备结构紧凑,节省投资和占地面积,而且尾气净化效果好,完全满足环保要求,实现垃圾焚烧尾气达标排放。(1) Based on the traditional dry circulating fluidized bed flue gas purification technology, according to the characteristics and purification requirements of waste incineration tail gas pollutants, through the organic combination of circulating fluidized bed purifier, gas-solid separator and mixing granulator Integrated, using calcium-based remover to remove acid gas in tail gas, and adding adsorbents such as fly ash and activated carbon to effectively remove heavy metals and dioxins. Not only is the process simple, the equipment structure is compact, saving investment and floor space, but also the exhaust gas purification effect is good, which fully meets the environmental protection requirements and achieves waste incineration exhaust emission standards.

(2)使用混合造粒器进行造粒,能根据尾气温度、污染物浓度和气流速度,来及时调节新鲜物料的加入量,加入速度,造粒大小等参数,形成具有丰富活性吸附位和孔隙结构的颗粒,有利于保证系统运行的最佳状态和最佳净化效率,同时提高添加剂的利用率,降低其运行成本。(2) Use a mixing granulator for granulation, which can timely adjust the addition of fresh materials, addition speed, granulation size and other parameters according to the exhaust gas temperature, pollutant concentration and airflow velocity, forming rich active adsorption sites and pores Structured particles are beneficial to ensure the best state of system operation and the best purification efficiency, while improving the utilization rate of additives and reducing their operating costs.

(3)在脱除污染物的过程中,床料保持相对干燥状态,有效避免了湿法净化系统中的管道腐蚀和堵塞问题。(3) During the process of removing pollutants, the bed material remains relatively dry, which effectively avoids the problems of pipeline corrosion and blockage in the wet purification system.

(4)由于采用干式循环流化床尾气净化技术,系统所需水分极少,而且产物为干态,减少了用水量,避免了湿法中的水污染问题,并降低了产物的处理成本。(4) Due to the use of dry circulating fluidized bed tail gas purification technology, the system requires very little water, and the product is in a dry state, which reduces water consumption, avoids the water pollution problem in the wet process, and reduces the processing cost of the product .

下面结合附图及具体的实施方式对本发明作进一步的详细说明。The present invention will be further described in detail below in conjunction with the accompanying drawings and specific embodiments.

附图是本发明方法步骤及其装置连接原理图。Accompanying drawing is the method step of the present invention and its device connection schematic diagram.

参看附图从燃烧设备出来的垃圾焚烧尾气,由尾气入口13,经过中间细、两端粗的双曲线圆管为缩放喷管1加速后,进入流化床净化器2。尾气在流化床净化器2中带动由钙基脱除剂和飞灰、活性炭吸附剂组成的床料一起流化,流化速度高达5-10米/秒,同时进行充分传热和传质。在此过程中,尾气中酸性气体如二氧化硫、三氧化硫、氯化氢、单质氯和氮氧化物等与钙基碱性化合物发生中和反应,生成固体钙盐。同时尾气中的重金属和二恶英等超细颗粒在与床料充分混合过程中被吸附剂飞灰和活性炭所吸附而去除。反应和吸附后的固体颗粒随气流经过水平过渡管3进入气固分离器4,在气固分离器4中用除尘器,该除尘器可以是布袋除尘器、旋风除尘器、静电除尘器或者是它们的有机组合体实现气体和固体颗粒的高效分离,除尘率高达99.9%,并进一步脱除烟气中的酸性气体、二恶英和重金属。本发明脱硫效率可达95%以上,脱氯效率大于97%,重金属及二恶英脱除率均大于90%。净化后的气体由净化气出口14经引风机排往烟囱。气固分离器4脱除下来的固体颗粒、已经完全反应的脱除剂颗粒以及还没有完全反应的脱除剂颗粒进入缓冲仓5。缓冲仓5中的固体物料90%以上通过给料机7进入混合造粒器8,其余不循环的物料由排料机6排出灰仓进一步处理。进入混合造粒器8中的循环物料与来自石灰粉给料口9的石灰粉、活性炭给料口10的活性炭以及给水口11的水充分混合造粒,粒度范围为200-300um,最大不超过500um。造粒后的混合物料作为循环流化床净化器2的床料,并通过混合造粒器8经由床料入口12进入流化床净化器2中循环使用。Referring to the accompanying drawings, the waste incineration exhaust gas coming out from the combustion equipment enters the fluidized bed purifier 2 after being accelerated by the zoom nozzle 1 through the thin hyperbolic circular pipe in the middle and thick at both ends by the exhaust gas inlet 13. The exhaust gas drives the bed material composed of calcium-based remover, fly ash and activated carbon adsorbent to fluidize together in the fluidized bed purifier 2. The fluidization speed is as high as 5-10 m/s, and the heat and mass transfer are fully carried out at the same time. . During this process, acid gases such as sulfur dioxide, sulfur trioxide, hydrogen chloride, elemental chlorine and nitrogen oxides in the tail gas undergo neutralization reactions with calcium-based basic compounds to form solid calcium salts. At the same time, ultrafine particles such as heavy metals and dioxins in the tail gas are adsorbed and removed by the adsorbent fly ash and activated carbon during the process of fully mixing with the bed material. The reacted and adsorbed solid particles enter the gas-solid separator 4 through the horizontal transition pipe 3 with the airflow, and a dust collector is used in the gas-solid separator 4. The dust collector can be a bag filter, a cyclone dust collector, an electrostatic precipitator or a Their organic combination achieves efficient separation of gas and solid particles, with a dust removal rate as high as 99.9%, and further removes acid gases, dioxins and heavy metals in the flue gas. The desulfurization efficiency of the invention can reach more than 95%, the dechlorination efficiency is greater than 97%, and the removal rates of heavy metals and dioxins are both greater than 90%. The purified gas is discharged to the chimney from the purified gas outlet 14 through the induced draft fan. The solid particles removed by the gas-solid separator 4 , the completely reacted remover particles and the incompletely reacted remover particles enter the buffer bin 5 . More than 90% of the solid materials in the buffer bin 5 enter the mixing granulator 8 through the feeder 7, and the rest of the non-circulating materials are discharged from the ash bin by the discharger 6 for further processing. The circulating material entering the mixing granulator 8 is fully mixed with the lime powder from the lime powder feed port 9, the activated carbon from the activated carbon feed port 10, and the water from the water feed port 11. The particle size range is 200-300um, and the maximum 500um. The granulated mixed material is used as the bed material of the circulating fluidized bed purifier 2, and enters the fluidized bed purifier 2 through the mixing granulator 8 through the bed material inlet 12 for recycling.

Claims (8)

1, a kind of method of comprehensive garbage incinerating tail gas purifying the steps include: 1) tail gas that combustion apparatus is discharged sprays into after quickening through de Laval noz(zle) to remove in the fluid bed clarifier that agent and adsorbent are the bed material and drive bed with the calcium base and expects fluidisation together; 2) in a tail gas and the process of material, take place to conduct heat and mass transfer strong mixing of gas, liquid, solid with sufficient in fluidisation, make sour gas such as sulfur dioxide, tri-chlorination sulphur, hydrogen chloride, simple substance chlorine and nitrogen oxide etc. in the tail gas remove agent bed material generation neutralization reaction with the calcium base, and make in the tail gas ultra-fine grain such as heavy metal and dioxin in mass transport process by adsorbents adsorb in the bed material; 3) material that forms with absorption back of reaction stay remove in the agent with solid form and not the bed of complete reaction expect to send into gas-solid separator with flue gas; 4) behind gas-solid separator, solid particle enters in the surge bunker, make solid particle more than 90% enter the mixing granulation device and with fresh pulverized limestone, active carbon and mixes with small amount of water granulation, object unnecessary in the surge bunker is discharged, the clean flue gas after the purification by air-introduced machine by the chimney qualified discharge; 5) particle behind the mixing granulation enters in the fluid bed clarifier again and recycles.
2, according to the method for the described comprehensive garbage incinerating tail gas purifying of claim 1, it is 5-10m/S with bed materials flow speed designs in the fluid bed clarifier that its feature is appointed in: the flue gas that described combustion apparatus is discharged.
3, according to the method for the described comprehensive garbage incinerating tail gas purifying of claim 2, it is characterized in that: described adsorbent is a porous mass, comprises flying dust, active carbon and coke.
4, according to the method for the described comprehensive garbage incinerating tail gas purifying of claim 3, it is characterized in that: described mixing granulation diameter range is 200um-500um.
5, a kind of device of realizing claim 1 or 4 described comprehensive garbage incinerating tail gas purifyings, it comprises with the calcium base and removes the sulfuration bed clarifier (2) that agent and adsorbent are the bed material, gas-solid separator (4), surge bunker (5) and mixing granulation device (8), the arrival end of described fluid bed clarifier (2) is provided with de Laval noz(zle) (1) and the bed material inlet (12) that tail gas is quickened, de Laval noz(zle) (1) other end and garbage incinerating tail gas inlet (13) join, it is characterized in that: bed material inlet (12) joins with the outlet of mixing granulation device (8), mixing granulation device (8) is equipped with a plurality of batching inlets and joins with batcher (7), batcher (7) other end and surge bunker (5) join, surge bunker (5) top and side top are equipped with gas-solid separator (4) and discharge machine (6), gas-solid separator (4) top and side top are equipped with clean gas outlet (14) and horizontal connection tube (3), and the outlet of horizontal connection tube (3) other end and fluid bed clarifier (2) is joined.
6, to come the 5 described devices that are used for comprehensive garbage incinerating tail gas purifying according to right, it is characterized in that: be provided with deduster between described horizontal connection tube (3) and gas-solid separator (4) junction, this deduster can be sack cleaner, cyclone dust collectors, electrostatic precipitator or their organic assembling body; Described clean gas outlet is provided with air-introduced machine in (14).
7, according to the described device that is used for comprehensive garbage incinerating tail gas purifying of claim 6, it is characterized in that: a plurality of batching inlets of described mixing granulation device (8) are admission port (11), active carbon material inlet (10) and pulverized limestone material inlet (9).
8, according to the described device that is used for comprehensive garbage incinerating tail gas purifying of claim 7, it is characterized in that: thin, the thick hyperbola pipe in two ends in the middle of the shape of described de Laval noz(zle) (1) is.
CNB001098748A 2000-07-10 2000-07-10 Method and device for comprehensive purification of waste incineration tail gas Expired - Lifetime CN1137759C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB001098748A CN1137759C (en) 2000-07-10 2000-07-10 Method and device for comprehensive purification of waste incineration tail gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB001098748A CN1137759C (en) 2000-07-10 2000-07-10 Method and device for comprehensive purification of waste incineration tail gas

Publications (2)

Publication Number Publication Date
CN1332334A CN1332334A (en) 2002-01-23
CN1137759C true CN1137759C (en) 2004-02-11

Family

ID=4579925

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB001098748A Expired - Lifetime CN1137759C (en) 2000-07-10 2000-07-10 Method and device for comprehensive purification of waste incineration tail gas

Country Status (1)

Country Link
CN (1) CN1137759C (en)

Families Citing this family (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100409924C (en) * 2006-06-13 2008-08-13 冯之军 Coal-fired smoke boiler purifier and purification
CN102641645B (en) * 2011-02-18 2015-06-17 宝山钢铁股份有限公司 Removing system for sintering fuel gas dioxin and method thereof
CN102674447B (en) * 2012-05-30 2014-11-05 成都易态科技有限公司 Method and equipment for purifying mixed gas containing chlorine
CN102674448B (en) * 2012-05-30 2014-12-10 成都易态科技有限公司 Titanium tetrachloride production method and equipment and titanium tetrachloride gas-state dust removal process
CN103272475B (en) * 2013-05-31 2016-02-03 神华集团有限责任公司 The desulphurization system of CFBB
CN107233793A (en) * 2016-03-29 2017-10-10 沈阳铝镁设计研究院有限公司 A kind of electrolytic aluminum smoke desulfurizer and sulfur method
CN105953236B (en) * 2016-05-28 2018-06-19 杨芳芳 A kind of igelite waste disposal method
CN108592065A (en) * 2018-03-16 2018-09-28 赵登强 A kind of environmental protection flue gas waste heat recovery apparatus
CN109173539A (en) * 2018-11-02 2019-01-11 成都芯飞环保智能设备有限公司 Based on the pretreated paint spray booth exhaust treatment system of pulverized limestone circulation absorption
CN109621636B (en) * 2018-11-15 2025-03-07 华中科技大学 A flue gas purification system for burning urban domestic waste
CN110052089A (en) * 2019-04-01 2019-07-26 浙江菲达环保科技股份有限公司 A kind of Hg, SO3The sack cleaner of cooperation-removal
CN110657434A (en) * 2019-10-21 2020-01-07 华南理工大学 A kind of garbage incinerator and method for dechlorination and heavy metal recovery in furnace
CN111203093A (en) * 2020-03-16 2020-05-29 重庆三峰环境集团股份有限公司 A kind of waste incineration flue gas dry processing mixer
CN112111304B (en) * 2020-09-24 2021-05-14 新奥科技发展有限公司 Fly ash circulating gasification system and recovery treatment method of fly ash in coal gas
CN113289441A (en) * 2021-06-04 2021-08-24 中国矿业大学 Device and method for purifying domestic garbage cracking gasification tail gas

Also Published As

Publication number Publication date
CN1332334A (en) 2002-01-23

Similar Documents

Publication Publication Date Title
CN1239235C (en) Dry smoke cleaning process for desulfurizing and denitrating simultaneously and its system
CN206652386U (en) A kind of minimum discharge purifier of burning city domestic garbage flue gas
CN102228788B (en) Device and method for removing sulfur dioxide and dioxin from sintering flue gas
CN1137759C (en) Method and device for comprehensive purification of waste incineration tail gas
CN100496676C (en) Wet ammonia flue gas cleaning technology simultaneously removing various pollutant and system thereof
CN101108303A (en) Wet-type ammonia process flue gas purifying technique for jointly removing multipollutant and system thereof
CN1962034A (en) Method and apparatus for removing sulfur, nitrate and mercury simultaneously from boiler flue gas
WO2016011681A1 (en) Equipment and method for circulating fluidized bed semidry simultaneous desulfurization and denitration of sintering flue gas
CN210814645U (en) A waste incineration flue gas ultra-low emission purification system
WO2016011682A1 (en) Equipment and method for circulating fluidized bed semidry simultaneous desulfurization, denitration, demercuration, and removal of dioxins of sintering flue gas
CN102380308A (en) Sintering flue gas desulfurization and purification method and equipment
CN103990375A (en) Integrated semi-dry purifying method for sintering flue gas
CN203436995U (en) Cooperative control device for multi-pollutant in sintering flue gas
CN101342459A (en) Waste gas desulfurization and reuse treatment method and device
CN101785969A (en) Method of flue gas purification and system thereof
CN204320062U (en) A kind of high effective flue gas cleaning system
CN103977702A (en) Flue gas desulfurization, denitration and demercuration integrated device with circulating fluidized bed and method
CN1172738C (en) Composite Desulfurization Process of Circulating Fluidized Bed Boiler
CN1231286C (en) A circulating fluidized bed process for cleaning fume by adding iron ash and its equipment
CN1896591A (en) Smoke purifier of domestic refuse incinerator
CN102366704A (en) Device and method for removing sulphur dioxide and dioxin from sintering flue gas
CN102266718A (en) Semi dry process flue gas desulfurization method of circulating fluidized bed based on circulation, and apparatus thereof
CN100402927C (en) An integrated device for circulating fluidized bed boiler incineration of garbage and purification of tail gas
CN203893210U (en) Novel smoke comprehensive treatment device
CN201791470U (en) Dry-method suspension bed type flue gas desulfurization system for small and medium sized coal burning boiler

Legal Events

Date Code Title Description
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C06 Publication
PB01 Publication
C14 Grant of patent or utility model
GR01 Patent grant
C56 Change in the name or address of the patentee

Owner name: QINGHUA UNIVERSITY; TONGFANG CO., LTD.

Free format text: FORMER NAME OR ADDRESS: QINGHUA UNIVERSITY; TSINGHUA TONGFANG CO., LTD.

CP03 Change of name, title or address

Address after: 100084 mailbox 2670, Beijing City

Co-patentee after: Tongfang Co., Ltd.

Patentee after: Tsinghua University

Address before: 100084 mailbox 2670, Beijing City

Co-patentee before: Qinghua Tongfang Co., Ltd.

Patentee before: Tsinghua University

ASS Succession or assignment of patent right

Owner name: QINGHUA UNIVERSITY; TONGFANG ENVIRONMENT CO.

Free format text: FORMER OWNER: QINGHUA UNIVERSITY; TONGFANG CO., LTD.

Effective date: 20080516

C41 Transfer of patent application or patent right or utility model
TR01 Transfer of patent right

Effective date of registration: 20080516

Address after: A, block 100083, Tongfang Plaza, Beijing, 2901

Co-patentee after: Tongfang Environment Co., Ltd.

Patentee after: Tsinghua University

Address before: Beijing 2670 mailbox: 100084

Co-patentee before: Tongfang Co., Ltd.

Patentee before: Tsinghua University

CX01 Expiry of patent term

Granted publication date: 20040211

CX01 Expiry of patent term