CN203227404U - Novel sectional type cross flow smoke purifying and absorbing tower - Google Patents
Novel sectional type cross flow smoke purifying and absorbing tower Download PDFInfo
- Publication number
- CN203227404U CN203227404U CN2013202058722U CN201320205872U CN203227404U CN 203227404 U CN203227404 U CN 203227404U CN 2013202058722 U CN2013202058722 U CN 2013202058722U CN 201320205872 U CN201320205872 U CN 201320205872U CN 203227404 U CN203227404 U CN 203227404U
- Authority
- CN
- China
- Prior art keywords
- flue gas
- active coke
- coke bed
- adsorption tower
- collection chamber
- 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
Links
- 239000000779 smoke Substances 0.000 title description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 94
- 239000003546 flue gas Substances 0.000 claims abstract description 94
- 239000000571 coke Substances 0.000 claims abstract description 70
- 238000001179 sorption measurement Methods 0.000 claims abstract description 30
- 238000000746 purification Methods 0.000 claims abstract description 18
- 238000005192 partition Methods 0.000 claims abstract description 17
- 239000003344 environmental pollutant Substances 0.000 abstract description 5
- 239000000428 dust Substances 0.000 abstract description 4
- 231100000719 pollutant Toxicity 0.000 abstract description 4
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 2
- 238000006477 desulfuration reaction Methods 0.000 description 13
- 230000023556 desulfurization Effects 0.000 description 13
- 238000000034 method Methods 0.000 description 11
- 239000010440 gypsum Substances 0.000 description 9
- 229910052602 gypsum Inorganic materials 0.000 description 9
- 239000003245 coal Substances 0.000 description 4
- 230000007613 environmental effect Effects 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 235000019738 Limestone Nutrition 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 239000006028 limestone Substances 0.000 description 3
- 238000005065 mining Methods 0.000 description 3
- 229920006395 saturated elastomer Polymers 0.000 description 3
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 238000005245 sintering Methods 0.000 description 2
- 229910052717 sulfur Inorganic materials 0.000 description 2
- 239000011593 sulfur Substances 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- 229910000831 Steel Inorganic materials 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000003009 desulfurizing effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-N sulfuric acid Substances OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
Images
Landscapes
- Treating Waste Gases (AREA)
Abstract
一种新型分段式错流烟气净化吸附塔,从上到下包括依次连通的给料斗、布料器、活性焦床层以及卸料斗,活性焦床层内部为中间烟气集气室,外部被双层环形隔板分隔为上部的净烟气集气室和下部的原烟气布气室,净烟气集气室上部设置有出口烟道,原烟气布气室下部设置有和其连通的原烟气入口烟道,活性焦床层、原烟气布气室、净烟气集气室以及整个塔体的横截面均为圆环形;采用本实用新型吸附塔,烟气中污染物脱除效率高,SO2脱除效率大于96%,SO3,HCl、HF的脱除效率大于98%,重金属Hg的脱除效率大于90%,除尘效率大于80%;同时,本实用新型还有给料方便均匀、落料流畅、活性焦利用率高、易于大型化等优点。
A new segmented cross-flow flue gas purification adsorption tower, which includes a feeding hopper, a distributor, an active coke bed and a discharge hopper connected in sequence from top to bottom. The inside of the active coke bed is the middle flue gas collection chamber, and the It is divided into the upper clean flue gas collection chamber and the lower raw flue gas distribution chamber by the double-layer annular partition. The connected raw flue gas inlet flue, the active coke bed, the raw flue gas distribution chamber, the clean flue gas collection chamber and the cross-section of the entire tower body are circular; with the adsorption tower of the utility model, the flue gas High pollutant removal efficiency, SO 2 removal efficiency is greater than 96%, SO 3 , HCl, HF removal efficiency is greater than 98%, heavy metal Hg removal efficiency is greater than 90%, dust removal efficiency is greater than 80%; at the same time, this practical The new type also has the advantages of convenient and uniform feeding, smooth blanking, high utilization of active coke, and easy large-scale operation.
Description
技术领域technical field
本实用新型涉及一种为电厂锅炉、冶金、垃圾焚烧以及化工行业废气进行脱硫的活性焦干法吸附塔,具体涉及一种新型分段式错流烟气净化吸附塔。The utility model relates to an active coke dry method adsorption tower for desulfurizing waste gas from power plant boilers, metallurgy, garbage incineration and chemical industries, in particular to a novel sectioned cross-flow flue gas purification adsorption tower.
背景技术Background technique
在燃煤电站烟气脱硫领域,目前90%以上采用的都是石灰石—石膏湿法烟气脱硫工艺,该工艺虽然技术成熟,应用广泛,但在应用过程中其缺点也逐渐显现出来:1)水耗高:对于不设烟气换热器GGH的电站锅炉烟气脱硫装置,折合每百万千瓦机组的耗水量高达220~250m3/h;2)烟囱防腐和“石膏雨”问题:湿法脱硫装置的出口烟气为饱和湿烟气,必须对烟囱进行高等级防腐,还可能出现烟囱“石膏雨”问题,对周边环境造成二次污染;3)净烟气液滴携带问题:净烟气中携带的液滴为20%左右浓度的石膏浆液,其中含有一定的固体颗粒,排入大气中即为粉尘污染;4)石灰石大量开采和石膏堆积问题:由于广泛采用石灰石—石膏湿法烟气脱硫工艺,导致大量石灰石山被开采,还造成部分地区的脱硫石膏堆积。In the field of flue gas desulfurization of coal-fired power stations, more than 90% of them currently use the limestone-gypsum wet flue gas desulfurization process. Although this process is mature and widely used, its shortcomings have gradually emerged during the application process: 1) High water consumption: For power plant boiler flue gas desulfurization devices without flue gas heat exchanger GGH, the water consumption per million kilowatt units is as high as 220-250m 3 /h; 2) Chimney anticorrosion and "gypsum rain" problems: wet The flue gas at the outlet of the desulfurization device using the desulfurization method is saturated wet flue gas, and high-grade anticorrosion must be carried out on the chimney, and the problem of "gypsum rain" in the chimney may also occur, causing secondary pollution to the surrounding environment; The liquid droplets carried in the flue gas are gypsum slurry with a concentration of about 20%, which contains certain solid particles, which is dust pollution when discharged into the atmosphere; 4) The problem of massive limestone mining and gypsum accumulation: due to the widespread use of limestone-gypsum wet method The flue gas desulfurization process has led to the mining of a large number of limestone mountains, and also caused the accumulation of desulfurized gypsum in some areas.
根据我国煤电发展规划,未来将重点建设大型煤电基地,我国富煤地区主要位于北方,也正是缺水地区。活性焦干法烟气净化工艺耗水量小,较传统湿法脱硫节水90%以上,而且吸附剂活性焦由煤炭制取,副产物为浓硫酸可资源化利用,不会造成大量石灰石开采和石膏堆积问题。另外,在环境保护重点地区,环境容量小,环保标准严格,活性焦烟气净化工艺可以对SO2、SO3、NOx、HCl、HF、Hg、细微粉尘等进行同时高效脱除,而且没有传统湿法脱硫的“石膏雨”、净烟气液滴携带等问题,可以满足十分严格的环保标准,适用于环境敏感地区的烟气净化。According to my country's coal power development plan, the future will focus on building large-scale coal power bases. my country's coal-rich areas are mainly located in the north, which is also a water-scarce area. The activated coke dry flue gas purification process consumes less water, saving more than 90% of water compared with the traditional wet desulfurization, and the adsorbent activated coke is made of coal, and the by-product is concentrated sulfuric acid, which can be recycled and utilized, without causing a large amount of limestone mining and Gypsum buildup problem. In addition, in the key areas of environmental protection, the environmental capacity is small and the environmental protection standards are strict. The activated coke flue gas purification process can simultaneously and efficiently remove SO 2 , SO 3 , NOx, HCl, HF, Hg, fine dust, etc., and there is no traditional The "gypsum rain" of wet desulfurization and the carryover of clean flue gas droplets can meet very strict environmental protection standards and are suitable for flue gas purification in environmentally sensitive areas.
此外,对于钢铁烧结烟气、垃圾焚烧烟气的净化处理,活性焦可以同时吸附其中的二噁英污染物,而传统的湿法脱硫工艺无法对二噁英进行有效脱除。因此,活性焦适用于对烧结烟气和垃圾焚烧烟气中的多污染物脱除和深度净化。In addition, for the purification of steel sintering flue gas and waste incineration flue gas, activated coke can simultaneously adsorb dioxin pollutants, while the traditional wet desulfurization process cannot effectively remove dioxin. Therefore, activated coke is suitable for multi-pollutant removal and deep purification of sintering flue gas and waste incineration flue gas.
吸附塔是活性焦烟气脱硫工艺的核心设备,但该工艺在我国的应用刚处于起步阶段,尤其是电厂规模的应用在我国尚无业绩,因此我国亟需开发具有自主知识产权的新型吸附塔结构。The adsorption tower is the core equipment of the activated coke flue gas desulfurization process, but the application of this process in my country is just in its infancy, especially the power plant scale application has no performance in my country, so my country urgently needs to develop a new type of adsorption tower with independent intellectual property rights structure.
实用新型内容Utility model content
为了解决上述现有技术存在的问题,本实用新型的目的在于提供一种新型分段式错流烟气净化吸附塔,具有污染物脱除效率高,系统阻力小,活性焦利用率高、循环量小、破损率低,布料均匀,卸料顺畅装置运行稳定的特点。In order to solve the problems existing in the above-mentioned prior art, the purpose of this utility model is to provide a novel sectioned cross-flow flue gas purification adsorption tower, which has the advantages of high pollutant removal efficiency, small system resistance, high utilization rate of active coke, and circulation Small quantity, low breakage rate, uniform cloth distribution, smooth unloading and stable operation of the device.
为达到以上目的,本实用新型采用如下技术方案:In order to achieve the above object, the utility model adopts the following technical solutions:
一种新型分段式错流烟气净化吸附塔,包括给料斗1,给料斗1下部设置布料器2,布料器2下部设置有横截面为环形的活性焦床层9,活性焦床层9内部为中间烟气集气室6,外部被双层环形隔板8分隔为上部的净烟气集气室4和下部的原烟气布气室10,所述活性焦床层9与中间烟气集气室(6)间通过中间烟气集气室栅格7连通,活性焦床层9与净烟气集气室4间通过净烟气集气栅格5连通,活性焦床层9与原烟气布气室10间通过原烟气进气栅格11连通,所述净烟气集气室4上部设置有和其连通的出口烟道3,所述原烟气布气室10下部设置有和其连通的原烟气入口烟道12,所述活性焦床层9下部设置有卸料斗14,卸料斗14下部设置有卸料阀15,所述中间烟气集气室6下部设置有灰斗16,灰斗16下部设置有卸灰阀17;所述活性焦床层9、原烟气布气室10、净烟气集气室4以及整个塔体的横截面均为圆环形。A new segmented cross-flow flue gas purification adsorption tower, including a
所述布料器2的形状为锥体。The shape of the distributor 2 is a cone.
所述锥体的圆锥母线与水平面之间的夹角α大于40°。The angle α between the generatrix of the cone and the horizontal plane is larger than 40°.
所述双层环形隔板8两层之间的距离大于活性焦床层9平均厚度的2倍。The distance between the two layers of the double-layer annular partition 8 is greater than twice the average thickness of the active coke bed 9 .
所述活性焦床层9的平均厚度D为0.8~2.5m。The average thickness D of the active coke bed 9 is 0.8-2.5m.
所述卸料斗14的中心线布置在活性焦床层9中心线的外侧。The centerline of the discharge hopper 14 is arranged outside the centerline of the active coke bed 9 .
所述卸料斗14内设置有1~5块导流板13,所述导流板13与水平夹角自内而外依次增大。The discharge hopper 14 is provided with 1 to 5 deflectors 13, and the angle between the deflectors 13 and the horizontal increases sequentially from the inside to the outside.
所述卸料斗14采用分区布置,分区数目为1、2、3、4、6、9、12个。The discharge hopper 14 is arranged in partitions, and the number of partitions is 1, 2, 3, 4, 6, 9, 12.
本实用新型和现有技术相比,具有如下优点:Compared with the prior art, the utility model has the following advantages:
1、本实用新型吸附塔整体呈圆环形,与方形塔相比,具有结构简单,节省材料,易于大型化,卸料流畅,不易出现死点,且可以避免应力集中。同时,由于整个塔体呈圆环形,内部设置锥形布料器,上部单点给料就可以实现整个系统的均匀给料,降低了对输送系统的要求。1. The adsorption tower of this utility model has a circular ring shape as a whole. Compared with the square tower, it has a simple structure, saves materials, is easy to enlarge, discharges smoothly, is not prone to dead spots, and can avoid stress concentration. At the same time, since the entire tower body is in the shape of a ring, with a conical distributor inside, the single-point feeding on the upper part can realize the uniform feeding of the whole system, which reduces the requirements on the conveying system.
2、本实用新型吸附塔被双层环向隔板分成两段,活性焦依靠重力自上而下流动,下部饱和度较高的活性焦首先与原烟气接触,使活性焦饱和度进一步增加,部分脱硫的烟气经中间烟气集气室再与上部新鲜活性焦接触,从而保证较高的脱硫效率。相比现有的单段错流技术,本实用新型出口活性焦饱和度高,整体吸附硫容大,脱硫效率高,从而活性焦装填量和循环量减少,吸附塔体积减小,破损率降低,建造和运行成本降低。2. The adsorption tower of this utility model is divided into two sections by double-layer annular partitions. The active coke flows from top to bottom relying on gravity, and the active coke with a higher saturation in the lower part first contacts with the original flue gas to further increase the saturation of the active coke. , Part of the desulfurized flue gas passes through the middle flue gas collection chamber and then contacts with the upper fresh activated coke, so as to ensure a high desulfurization efficiency. Compared with the existing single-stage cross-flow technology, the utility model has high outlet active coke saturation, large overall adsorption sulfur capacity, and high desulfurization efficiency, thereby reducing the loading and circulation of active coke, reducing the volume of the adsorption tower, and reducing the breakage rate , construction and operating costs are reduced.
3、本实用新型吸附塔被双层环向隔板分成两段,上半段高SO2浓度烟气首先与床层内侧活性焦接触,使内侧活性焦饱和度高于外侧活性焦,活性焦进入下半段后,高浓度SO2烟气首先与床层外侧活性焦接触,使出口活性焦饱和度趋于均匀。3. The adsorption tower of this utility model is divided into two sections by double-layer annular partitions. The flue gas with high SO2 concentration in the upper half section first contacts with the active coke inside the bed, so that the saturation of the active coke inside is higher than that of the outside active coke. After entering the second half, the high-concentration SO 2 flue gas first contacts with the active coke outside the bed, so that the outlet active coke saturation tends to be uniform.
4、本实用新型卸料斗靠活性焦层外侧布置,同时内部设置导流板,从而保证活性焦层外侧活性焦移动速度大于内侧活性焦移动速度,出口活性焦平均饱和度增加。4. The discharge hopper of the utility model is arranged on the outside of the active coke layer, and at the same time, a deflector is installed inside, so as to ensure that the moving speed of the active coke outside the active coke layer is greater than that of the inner active coke, and the average saturation of the outlet active coke increases.
附图说明Description of drawings
图1为本实用新型吸附塔主视图。Fig. 1 is the front view of the adsorption tower of the present utility model.
图2为本实用新型吸附塔俯视图。Figure 2 is a top view of the adsorption tower of the present invention.
图3为布料器倾角的示意图。Figure 3 is a schematic diagram of the inclination angle of the distributor.
具体实施方式Detailed ways
以下结合附图及具体实施例,对本实用新型作进一步的详细描述。Below in conjunction with accompanying drawing and specific embodiment, the utility model is described in further detail.
如图1和图2所示,本实用新型一种新型分段式错流烟气净化吸附塔,包括给料斗1,给料斗1下部设置布料器2,布料器2下部设置有横截面为环形的活性焦床层9,活性焦床层9内部为中间烟气集气室6,外部被双层环形隔板8分隔为上部的净烟气集气室4和下部的原烟气布气室10,所述活性焦床层9与中间烟气集气室(6)间通过中间烟气集气室栅格7连通,活性焦床层9与净烟气集气室4间通过净烟气集气栅格5连通,活性焦床层9与原烟气布气室10间通过原烟气进气栅格11连通,所述净烟气集气室4上部设置有和其连通的出口烟道3,所述原烟气布气室10下部设置有和其连通的原烟气入口烟道12,所述活性焦床层9下部设置有卸料斗14,卸料斗14下部设置有卸料阀15,所述中间烟气集气室6下部设置有灰斗16,灰斗16下部设置有卸灰阀17;所述活性焦床层9、原烟气布气室10、净烟气集气室4以及整个塔体的横截面均为圆环形。As shown in Fig. 1 and Fig. 2, a new segmented cross-flow flue gas purification adsorption tower of the utility model includes a
作为本实用新型的优选实施方式,所述双层环形隔板8两层之间的距离大于活性焦床层9平均厚度的2倍。As a preferred embodiment of the present invention, the distance between the two layers of the double-layer annular partition 8 is greater than twice the average thickness of the active coke bed 9 .
作为本实用新型的优选实施方式,所述活性焦床层9的平均厚度D为0.8~2.5m。As a preferred embodiment of the present invention, the average thickness D of the active coke bed layer 9 is 0.8-2.5m.
作为本实用新型的优选实施方式,所述卸料斗14的中心线布置在活性焦床层9中心线的外侧。As a preferred embodiment of the present invention, the centerline of the discharge hopper 14 is arranged outside the centerline of the active coke bed 9 .
作为本实用新型的优选实施方式,所述卸料斗14内设置有1~5块导流板13,所述导流板13与水平夹角自内而外依次增大。As a preferred embodiment of the present utility model, 1 to 5 deflectors 13 are arranged in the discharge hopper 14, and the included angles between the deflectors 13 and the horizontal gradually increase from inside to outside.
作为本实用新型的优选实施方式,所述卸料斗14采用分区布置,分区数目为1、2、3、4、6、9、12个。As a preferred embodiment of the present utility model, the discharge hopper 14 is arranged in partitions, and the number of partitions is 1, 2, 3, 4, 6, 9, 12.
如图3所示,作为本实用新型的优选实施方式,所述布料器2的形状为锥体,所述锥体的圆锥母线与水平面之间的夹角α大于40°。As shown in Fig. 3, as a preferred embodiment of the present invention, the shape of the distributor 2 is a cone, and the angle α between the generatrix of the cone of the cone and the horizontal plane is greater than 40°.
本实用新型的工作原理为:活性焦由给料斗1给入,通过锥形布料器2使活性焦在床层内均匀分布,锅炉烟气从原烟气入口烟道12进入吸附塔,气流速度下降,由于床层阻力较大,气流在原烟气布气室10圆周方向上均匀分布,穿过下半段活性焦层首先与半饱和的活性焦接触,使出口活性焦达到较高的饱和度,经过部分脱硫的烟气进入中间烟气集气室6后,气流上行,垂直穿过上半段活性焦床层9再与上半段新鲜的活性焦接触,经净烟气集气室4收集,从出口烟道3流出吸附塔。活性焦依靠重力下降,通过下部沿圆周方向布置的多个卸料阀流出吸附塔。The working principle of the utility model is: the active coke is fed from the
如图1和图2所示,本实用新型整个塔体结构采用圆柱状,内部设置锥形布料器,下部设置沿圆周方向设置多个卸料斗,这样不仅保证了卸料顺畅,不出现滞留区,而且通过单点就可以实现均匀给料,不用布置长轴辊式卸料器,降低了对输送系统的要求。As shown in Figure 1 and Figure 2, the entire tower structure of the utility model adopts a cylindrical shape, and a conical distributor is arranged inside, and a plurality of unloading hoppers are arranged along the circumferential direction at the lower part, which not only ensures smooth unloading, but also does not cause stagnation areas , and uniform feeding can be achieved through a single point, without the need to arrange a long-axis roller unloader, which reduces the requirements for the conveying system.
如图1所示,本实用新型通过在外层圆环内设置双层环向隔板,两层隔板间的距离略大于活性焦床层厚度的两倍,从而合理组织烟气流向,实现分段,原烟气从吸附塔下部进入,高浓度SO2气体首先与半饱和的活性焦接触,使出口活性焦达到较高的饱和度,经过部分脱硫的烟气上行,再与上半段新鲜的活性焦接触,从而达到较高的脱硫效率。这样活性焦在塔内的停留时间和吸附硫容大幅度增加,降低了活性焦的装填量和循环量,使系统投资和运行成本均大幅度提高。采用本实用新型吸附塔,烟气中污染物脱除效率高,SO2脱除效率大于96%,SO3、HCl、HF的脱除效率大于98%,重金属Hg的脱除效率大于90%,除尘效率大于80%。As shown in Figure 1, the utility model arranges a double-layer annular partition in the outer ring, and the distance between the two partitions is slightly greater than twice the thickness of the active coke bed, so as to reasonably organize the flow direction of the flue gas and realize the separation section, the original flue gas enters from the lower part of the adsorption tower, and the high-concentration SO 2 gas first contacts with the semi-saturated activated coke, so that the outlet activated coke reaches a higher saturation degree, and the partially desulfurized flue gas goes up, and then with the upper half of the fresh Active coke contact, so as to achieve a higher desulfurization efficiency. In this way, the residence time of active coke in the tower and the adsorption capacity of sulfur are greatly increased, the loading and circulation of active coke are reduced, and the system investment and operating costs are greatly increased. Adopting the adsorption tower of the utility model, the removal efficiency of pollutants in the flue gas is high, the removal efficiency of SO 2 is greater than 96%, the removal efficiency of SO 3 , HCl, and HF is greater than 98%, and the removal efficiency of heavy metal Hg is greater than 90%. The dust removal efficiency is greater than 80%.
Claims (8)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2013202058722U CN203227404U (en) | 2013-04-22 | 2013-04-22 | Novel sectional type cross flow smoke purifying and absorbing tower |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2013202058722U CN203227404U (en) | 2013-04-22 | 2013-04-22 | Novel sectional type cross flow smoke purifying and absorbing tower |
Publications (1)
Publication Number | Publication Date |
---|---|
CN203227404U true CN203227404U (en) | 2013-10-09 |
Family
ID=49283554
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN2013202058722U Expired - Lifetime CN203227404U (en) | 2013-04-22 | 2013-04-22 | Novel sectional type cross flow smoke purifying and absorbing tower |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN203227404U (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103230723A (en) * | 2013-04-22 | 2013-08-07 | 西安热工研究院有限公司 | Annular sectional cross-flow fume cleaning adsorption tower |
CN108217606A (en) * | 2017-12-29 | 2018-06-29 | 山东大学 | Utilize the cross-flow moving bed device of carbon-based material reduction and desulfurization resolution gas Recovered sulphur |
CN110090511A (en) * | 2019-06-12 | 2019-08-06 | 中冶北方(大连)工程技术有限公司 | Online ash removal system for activated coke gas cleaning absorbing unit |
CN110898608A (en) * | 2018-09-18 | 2020-03-24 | 中国石化工程建设有限公司 | System and method for adsorbing and purifying flue gas by using active coke |
CN111298593A (en) * | 2018-12-12 | 2020-06-19 | 中国石化工程建设有限公司 | Active coke adsorption tower and method for adsorbing and purifying flue gas by using active coke |
-
2013
- 2013-04-22 CN CN2013202058722U patent/CN203227404U/en not_active Expired - Lifetime
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103230723A (en) * | 2013-04-22 | 2013-08-07 | 西安热工研究院有限公司 | Annular sectional cross-flow fume cleaning adsorption tower |
CN108217606A (en) * | 2017-12-29 | 2018-06-29 | 山东大学 | Utilize the cross-flow moving bed device of carbon-based material reduction and desulfurization resolution gas Recovered sulphur |
CN110898608A (en) * | 2018-09-18 | 2020-03-24 | 中国石化工程建设有限公司 | System and method for adsorbing and purifying flue gas by using active coke |
CN110898608B (en) * | 2018-09-18 | 2022-02-08 | 中国石化工程建设有限公司 | System and method for adsorbing and purifying flue gas by using active coke |
CN111298593A (en) * | 2018-12-12 | 2020-06-19 | 中国石化工程建设有限公司 | Active coke adsorption tower and method for adsorbing and purifying flue gas by using active coke |
CN111298593B (en) * | 2018-12-12 | 2022-03-29 | 中国石化工程建设有限公司 | Active coke adsorption tower and method for adsorbing and purifying flue gas by using active coke |
CN110090511A (en) * | 2019-06-12 | 2019-08-06 | 中冶北方(大连)工程技术有限公司 | Online ash removal system for activated coke gas cleaning absorbing unit |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103230723B (en) | Annular sectional cross-flow fume cleaning adsorption tower | |
CN103230724B (en) | New cross-convective flue gas purification absorption tower | |
CN102908869B (en) | Multi-layer type purifying absorption column for active coke smoke | |
CN203227404U (en) | Novel sectional type cross flow smoke purifying and absorbing tower | |
CN202410505U (en) | Desulfurization, denitration and demercuration integral device | |
CN101406805B (en) | Pneumatic desulfuration unit | |
CN102824846A (en) | Axial and radial cross flow moving bed reactor and activated coke flue gas desulfurization and denitration technology thereof | |
CN102716643B (en) | Device and method for removing acid gases in garbage incineration smoke at high temperature | |
CN105617851B (en) | A kind of method and its device of efficient double tower semi-dry desulphurization | |
CN104587756A (en) | Efficient multi-pipe spiral mist removing and dust removing system | |
CN104437069A (en) | Desulfurization and dust-removal device and desulfurization and dust-removal method of membrane separation circulating fluidized bed | |
CN102908867A (en) | Active coke smoke purifying device for optimizing air-flow distribution | |
CN203264529U (en) | Cross flow-convection flue gas purification and adsorption tower | |
CN104190244A (en) | Multi-stage suspension type flue gas desulfurization device for granular active coke and flue gas desulfurization method thereof | |
CN204469531U (en) | Membrane separation circulating fluid bed desulfation dust-extraction device | |
CN205796927U (en) | Reverse-flow integration activated coke smoke eliminator | |
CN203725021U (en) | Efficient integrated desulfurizing, dedusting and demisting device | |
CN204637975U (en) | Flue gas desulfurization enhancing device | |
CN203235395U (en) | Flue gas desulfurization equipment | |
CN107126811A (en) | Desulfurization system based on phase change active coke dry method | |
CN202343093U (en) | Device for removing sulfur dioxide and dioxin from sintering flue gas | |
CN202973137U (en) | Flow-folding type flue gas pollutant removal device | |
CN103463961B (en) | Airflow uniform distribution type wet-method smoke desulfurization and absorption tower | |
CN206730794U (en) | Activated coke integrated purifying desulfurizer | |
CN103657323A (en) | Wet electrostatic reinforced apparatus and method for simultaneous removal of PM2.5, SO2 and Hg |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
AV01 | Patent right actively abandoned |
Granted publication date: 20131009 Effective date of abandoning: 20150107 |
|
RGAV | Abandon patent right to avoid regrant |