CN106693592A - Double-jet type streamlined ultra-fine particle coagulation box - Google Patents
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- 230000015271 coagulation Effects 0.000 title abstract description 47
- 238000005345 coagulation Methods 0.000 title abstract description 47
- 239000011882 ultra-fine particle Substances 0.000 title abstract description 12
- 239000000428 dust Substances 0.000 claims abstract description 32
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 20
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000003546 flue gas Substances 0.000 claims abstract description 19
- 239000003463 adsorbent Substances 0.000 claims abstract description 16
- 239000007789 gas Substances 0.000 claims abstract description 5
- 239000007921 spray Substances 0.000 claims abstract description 5
- 238000004581 coalescence Methods 0.000 claims description 22
- 239000007788 liquid Substances 0.000 claims description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 4
- 239000003595 mist Substances 0.000 claims description 3
- 238000001556 precipitation Methods 0.000 claims description 2
- 238000000889 atomisation Methods 0.000 claims 1
- 238000009833 condensation Methods 0.000 abstract description 35
- 230000005494 condensation Effects 0.000 abstract description 35
- 239000012717 electrostatic precipitator Substances 0.000 abstract description 10
- 238000009434 installation Methods 0.000 abstract description 3
- 239000002245 particle Substances 0.000 description 21
- 239000002956 ash Substances 0.000 description 10
- 238000000034 method Methods 0.000 description 10
- 239000010419 fine particle Substances 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- 239000002131 composite material Substances 0.000 description 5
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 5
- 229910052753 mercury Inorganic materials 0.000 description 5
- 239000000243 solution Substances 0.000 description 5
- 230000000694 effects Effects 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 238000000746 purification Methods 0.000 description 4
- 230000009471 action Effects 0.000 description 3
- 239000011362 coarse particle Substances 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- 239000010881 fly ash Substances 0.000 description 3
- 239000003517 fume Substances 0.000 description 3
- 230000006870 function Effects 0.000 description 3
- 238000002347 injection Methods 0.000 description 3
- 239000007924 injection Substances 0.000 description 3
- 230000007246 mechanism Effects 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- 239000000779 smoke Substances 0.000 description 3
- 239000002594 sorbent Substances 0.000 description 3
- 238000005507 spraying Methods 0.000 description 3
- 230000007704 transition Effects 0.000 description 3
- 229910052799 carbon Inorganic materials 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000009826 distribution Methods 0.000 description 2
- 230000005684 electric field Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 230000003213 activating effect Effects 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000005457 optimization Methods 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000004071 soot Substances 0.000 description 1
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- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D51/00—Auxiliary pretreatment of gases or vapours to be cleaned
- B01D51/02—Amassing the particles, e.g. by flocculation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D51/00—Auxiliary pretreatment of gases or vapours to be cleaned
- B01D51/02—Amassing the particles, e.g. by flocculation
- B01D51/04—Amassing the particles, e.g. by flocculation by seeding, e.g. by adding particles
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Abstract
双喷式流线型超细颗粒凝并箱,整个凝并箱呈箱式,适于安装在电—袋除尘器之间;凝并箱由进气口、出气口、凝并区和灰斗组成;进气口为电除尘器之后的通道,烟气由电除尘器而来;凝并区中设置有2~4组横条,横条横置于凝并区中,横条的断面形状为流线型的导弹头状;出气口位于凝并区下部,灰斗上方,设置成过流通道;可将活性炭等吸附剂,凝并促进剂分别通过引导管经喷嘴喷入凝并区,经凝并之后的烟气进入袋式除尘器进行处理。本发明针对性强、适应面广、构造优化、可靠性好。
Double-spray streamline ultra-fine particle coagulation box, the whole coagulation box is box-shaped, suitable for installation between electrostatic-bag dust collectors; the coagulation box is composed of an air inlet, an air outlet, a coagulation area and an ash hopper; The air inlet is the channel behind the electrostatic precipitator, and the flue gas comes from the electrostatic precipitator; there are 2~4 sets of horizontal bars in the condensation area, and the horizontal bars are placed horizontally in the condensation area, and the cross-sectional shape of the horizontal bars is streamlined. The missile head shape; the gas outlet is located at the lower part of the condensation area and above the ash hopper, and is set as a flow passage; the activated carbon and other adsorbents and condensation accelerators can be sprayed into the condensation area through the nozzle through the guide pipe respectively, and after condensation The flue gas enters the bag filter for treatment. The invention has strong pertinence, wide adaptability, optimized structure and good reliability.
Description
技术领域technical field
本发明属于烟气除尘处理领域,涉及双喷式流线型超细颗粒凝并箱。The invention belongs to the field of flue gas dust removal treatment, and relates to a double-spray streamlined superfine particle coagulation box.
背景技术Background technique
近年来,我国大中城市雾霾天气越来越多,严重影响了城市居民的健康工作和生活,其中城市环境中PM2.5(主要为PM0.4-1.0)含量过高是导致雾霾天气的主要原因。因此,如何控制PM2.5产生,并减少其存在,成为亟待解决的问题。In recent years, there have been more and more smog weather in large and medium-sized cities in China, which has seriously affected the healthy work and life of urban residents. Among them, the high content of PM 2.5 (mainly PM 0.4-1.0 ) in the urban environment is the main cause of smog weather. reason. Therefore, how to control the production of PM 2.5 and reduce its existence has become an urgent problem to be solved.
中国专利CN101664623A公开了涉及用于工业烟尘治理的微细粒子除尘器。具体是通过对现有二级过滤方式的电袋复合除尘器改进,在滤袋除尘机构的出口与引风机的进口之间设有湍流涡旋机构,该湍流涡旋机构包括湍流涡旋室、烟尘入口管和烟尘出口管。湍流涡旋室为横截面为倒等腰梯形的斗状,其底部连接着灰斗室。经过第二级处理的含有较细颗粒物的烟尘进入烟尘入口管,经过导风板,使气流发生向下偏转,进入湍流涡旋室,较细颗粒物与湍流涡旋室内壁产生扩散和碰撞促使微细粒子沉淀,使微细颗粒物从烟尘中分离出来。但该处理工艺中单独用湍流涡旋室进行细颗粒物的物化凝并,凝并效率并不高。Chinese patent CN101664623A discloses a fine particle dust collector for industrial smoke control. Specifically, a turbulent vortex mechanism is provided between the outlet of the filter bag dust removal mechanism and the inlet of the induced draft fan through the improvement of the electric bag composite dust collector of the existing two-stage filtration method. The turbulent vortex mechanism includes a turbulent vortex chamber, Fume inlet pipe and fume outlet pipe. The turbulent vortex chamber is in the shape of a bucket with an inverted isosceles trapezoidal cross section, and the bottom of the vortex chamber is connected with the ash chamber. After the second-stage treatment, the dust containing finer particles enters the dust inlet pipe, passes through the wind deflector, deflects the airflow downward, and enters the turbulent vortex chamber, where the finer particles diffuse and collide with the inner wall of the turbulent vortex to promote the fine particles Particle precipitation separates fine particulate matter from the soot. However, in this treatment process, the turbulent vortex chamber is used alone for the physical-chemical coagulation of fine particles, and the coagulation efficiency is not high.
中国专利CN 102423599 A公开了一种一体化脱除工业排放超细和微量污染物的电袋复合净化装置和净化方法。采用沿气流方向依次设置有吸附剂预喷涂装置、静电除尘装置、超细颗粒凝并装置、吸附剂喷入装置和布袋除尘装置的结构形式,提供了一种结构紧凑、运行成本低、检修和运行维护方便、在脱除常量粉尘污染物的同时高效脱除超细和微量污染物的一体化电袋复合净化装置和净化方法。超细颗粒凝并装置由正高压放电电极等组成。超细颗粒凝并装置没有具体的构造,且除荷电外没有形成良好的凝并条件。中国专利CN103007670 A控制细微颗粒,协同脱汞的电袋复合除尘器,涉及工业除尘器。电袋复合除尘器设有电袋过渡区,电袋过渡区设于电场区和袋式除尘区之间;灰斗设于壳体的底部,净气室设于袋式除尘区顶部,出口烟道设于净气室顶部并与净气室连通;吸附剂喷入装置和吸附剂容器设于电袋过渡区的顶部,吸附剂容器的出料口与吸附剂喷入装置的进料口连接。可以使吸咐剂与烟气充分混合,吸咐剂分布更均匀,吸咐剂脱汞效果更好。电袋过渡区设有至少2组阳极板和放电极,阳极板和放电极构成电场通道。Chinese patent CN 102423599 A discloses an electric bag composite purification device and purification method for integrated removal of ultrafine and trace pollutants discharged from industry. Adopting the structural form of adsorbent pre-spraying device, electrostatic precipitator, ultrafine particle coagulation device, adsorbent spraying device and bag dust removal device arranged in sequence along the airflow direction, it provides a compact structure, low operating cost, maintenance and The integrated electric bag composite purification device and purification method are convenient for operation and maintenance, and can efficiently remove ultrafine and trace pollutants while removing constant dust pollutants. The superfine particle coagulation device is composed of positive high voltage discharge electrodes and so on. The superfine particle coalescence device has no specific structure, and does not form a good coalescence condition except charging. Chinese patent CN103007670 A is an electric bag composite dust collector for controlling fine particles and synergistically removing mercury, which relates to industrial dust collectors. The electric bag composite dust collector is equipped with an electric bag transition area, which is set between the electric field area and the bag type dust removal area; the ash hopper is set at the bottom of the shell, and the clean air chamber is set The channel is set on the top of the clean gas chamber and communicated with the clean gas room; the adsorbent injection device and the adsorbent container are set on the top of the transition zone of the electric bag, and the outlet of the adsorbent container is connected with the inlet of the adsorbent injection device . The sorbent can be fully mixed with the flue gas, the sorbent can be distributed more uniformly, and the sorbent can have a better mercury removal effect. There are at least two sets of anode plates and discharge electrodes in the transition zone of the electric bag, and the anode plates and discharge electrodes form an electric field channel.
以上工艺设备,方法复杂、控制运行难、设备投资和运行费用高。The above process equipment has complex methods, difficult control and operation, high equipment investment and operation costs.
因而,针对凝并效率不高、工艺设备复杂等问题,很有必要在现有技术的基础上,研究开发强化凝并的超细颗粒凝并箱。在传统的除尘器的基础上,增设凝并处理装置,使超细颗粒物通过物理方法或物化方法凝并成较大颗粒,从而在后续除尘器内顺利脱除,是现在除尘技术发展的趋势。Therefore, in view of the problems of low coagulation efficiency and complicated process equipment, it is necessary to research and develop ultra-fine particle coagulation boxes that strengthen coagulation on the basis of existing technologies. On the basis of the traditional dust collector, it is the current development trend of dust removal technology to add a coagulation treatment device to make the ultrafine particles condense into larger particles through physical or physical and chemical methods, so that they can be successfully removed in the subsequent dust collector.
发明内容Contents of the invention
发明目的:本发明的目的是为了解决现有技术的不足,提出一种针对性强、适应面广、构造优化、可靠性好的强化凝并的超细颗粒凝并箱。Purpose of the invention: The purpose of the invention is to solve the deficiencies of the prior art, and to propose an ultra-fine particle coagulation box with strong pertinence, wide adaptability, optimized structure, and good reliability for enhanced coagulation.
技术方案:为了实现本发明的目的,本发明采用如下的技术方案。Technical solution: In order to realize the object of the present invention, the present invention adopts the following technical solutions.
双喷式流线型超细颗粒凝并箱,整个凝并箱呈箱式,适于安装在电—袋除尘器之间;凝并箱由进气口、出气口、凝并区和灰斗组成;进气口为电除尘器之后的通道,烟气由电除尘器而来;凝并区中设置有2~4组横条,横条横置于凝并区中,横条的断面形状为流线型的导弹头状;出气口位于凝并区下部,灰斗上方,设置成过流通道,经凝并之后的烟气进入袋式除尘器进行处理;灰斗设置于凝并区下方,与电—袋除尘器的其它灰斗平齐。Double-spray streamline ultra-fine particle coagulation box, the whole coagulation box is box-shaped, suitable for installation between electrostatic-bag dust collectors; the coagulation box is composed of an air inlet, an air outlet, a coagulation area and an ash hopper; The air inlet is the channel behind the electrostatic precipitator, and the flue gas comes from the electrostatic precipitator; there are 2~4 sets of horizontal bars in the condensation area, and the horizontal bars are placed horizontally in the condensation area, and the cross-sectional shape of the horizontal bars is streamlined. The air outlet is located in the lower part of the condensation area and above the ash hopper, which is set as a flow passage, and the flue gas after condensation enters the bag filter for processing; The other ash hoppers of the bag filter are flush.
进一步地,凝并区中设置的每组横条上下排列,横条的断面形状导弹头部长度为10~15cm,水平部分长为20~30 cm;横条的高度为10~20cm;相邻两只横条之间的间距取横条高度的1.0~2.0倍;相邻两组横条之间的间距取横条断面长度的1.0~2.0倍,相邻两组横条之间错位设置。Further, each group of horizontal bars set in the coalescence zone is arranged up and down, the cross-sectional shape of the horizontal bars is 10-15 cm long for the missile head, and 20-30 cm long for the horizontal part; the height of the horizontal bars is 10-20 cm; The distance between two horizontal bars shall be 1.0 to 2.0 times the height of the horizontal bars; the distance between two adjacent groups of horizontal bars shall be 1.0 to 2.0 times the section length of the horizontal bars, and the offset between two adjacent groups of horizontal bars shall be set.
进一步地,在凝并区的入口处,设置筛孔板,让气流通过;筛孔板后竖向设置一组喷嘴,喷嘴通过管道与气泵相连,可将活性炭等吸附剂通过引导管经喷嘴喷入凝并区。Further, at the entrance of the condensation area, a sieve plate is set to let the air flow pass through; a group of nozzles are vertically set behind the sieve plate, and the nozzles are connected to the air pump through a pipeline, and activated carbon and other adsorbents can be sprayed through the nozzles through the guide pipe. into the condensation zone.
进一步地,在凝并区内设置一组喷嘴,由配液泵将凝并促进剂和水充分混合,混合后的凝并促进剂溶液经雾化后,通过引导管接入喷嘴,喷入凝并区,形成雾云。Furthermore, a set of nozzles is set in the condensation area, and the coagulation accelerator and water are fully mixed by the liquid distribution pump. After the mixed coagulation accelerator solution is atomized, it is connected to the nozzle through the guide pipe and sprayed into the condensation. Combined area, forming fog cloud.
凝并箱工作原理:经过电除尘器处理的烟气然后进入凝聚区,这时烟气中以超细颗粒物居多,通过“湍流凝并”作用下碰撞凝聚,超细颗粒变成大颗粒,即为粒子粗大化;接着进入到后续袋式除尘器内部,粗大化的粒子便于除尘器收尘,这样便减少了超细颗粒的排放。The working principle of the condensing box: the flue gas treated by the electrostatic precipitator then enters the condensation zone. At this time, the flue gas is mostly composed of ultra-fine particles. Through collision and condensation under the action of "turbulent coagulation", the ultra-fine particles become large particles, that is, Coarse particles; then enter the follow-up bag filter, the coarse particles are easy for the dust collector to collect dust, thus reducing the emission of ultrafine particles.
“湍流凝并”是指通过特殊的构造,造成烟气气流的变化,形成接近湍流的状态。凝并的主要影响因素是颗粒大小、颗粒的凝聚性能与碰撞几率。湍流大大增加了烟气中颗粒的碰撞几率。由于凝并箱的特殊构造,使得凝并箱内分部气流交汇处成为湍流凝并主要发生区域。化学凝并的基础上,进一步通过湍流凝并,强化了整体的凝并效果。筛孔板起到整流和均布气流的作用。横条的断面形状呈导弹头形,导弹头部呈流线型,便于气流分流,且流线型压力降较小。横条断面的水平部分,起分隔气流和引导气流的作用。流线型的横条使得气流分分合合,分合交替进行,实现了湍流凝并的优化。"Turbulent condensation" refers to the change of the flue gas flow through a special structure, forming a state close to turbulence. The main influencing factors of coagulation are particle size, coagulation performance and collision probability of particles. Turbulence greatly increases the chances of particle collisions in the flue gas. Due to the special structure of the condensation box, the intersection of the sub-airflows in the condensation box becomes the main area for turbulent condensation. On the basis of chemical coagulation, the overall coagulation effect is enhanced through turbulent coagulation. The sieve plate plays the role of rectifying and evenly distributing the airflow. The cross-sectional shape of the horizontal bar is in the shape of a missile head, and the missile head is streamlined, which is convenient for airflow diversion, and the streamlined shape has a small pressure drop. The horizontal part of the bar section plays the role of separating and guiding the airflow. The streamlined horizontal bar makes the air flow separate and close alternately, realizing the optimization of turbulent flow condensation.
化学凝并原理:喷入的凝并促进剂在雾化器作用下经破碎后形成有一定扩散角度、且表面具有较高粘附活性的雾云,雾云吸附于飞灰颗粒表面,在颗粒之间产生液桥,在布袋除尘器前的烟道里,进而转化为固桥,促进颗粒凝并,使细小颗粒形成较大的聚团,以及细小颗粒被粗颗粒吸附。The principle of chemical coagulation: the sprayed coagulation accelerator is broken under the action of the atomizer to form a mist cloud with a certain diffusion angle and a high adhesion activity on the surface. The mist cloud is adsorbed on the surface of the fly ash particles, A liquid bridge is formed between them, and in the flue in front of the bag filter, it is transformed into a solid bridge, which promotes the coagulation of particles, makes fine particles form larger agglomerates, and fine particles are adsorbed by coarse particles.
本发明采用的活性炭吸附剂喷射装置,是在颗粒凝并前喷入粉末状活性炭,通过活性炭吸附剂的吸附作用来除去烟气中的汞。在烟气中喷入活性炭吸附剂是最有效除汞的方法之一。吸附剂为具有一定含碳量的粉煤灰经改性活化后形成的多孔状、比表面积丰富的颗粒物,同时具有物理和化学吸附功能,其平均粒径在20μm左右,比表面积>55m2/g,飞灰含碳量在6%~7%左右。The activated carbon adsorbent injection device used in the present invention sprays powdered activated carbon before the particles are coagulated, and removes mercury in the flue gas through the adsorption of the activated carbon adsorbent. Spraying activated carbon adsorbent in flue gas is one of the most effective methods for mercury removal. The adsorbent is a porous particle with a rich specific surface area formed by modifying and activating fly ash with a certain carbon content. It has both physical and chemical adsorption functions. g, the carbon content of fly ash is about 6%~7%.
有益效果:本发明提供的装置和现有装置相比具有以下优点。Beneficial effects: compared with the existing devices, the device provided by the invention has the following advantages.
(1)通过本发明所提供的特殊构造,多种凝并协同作用,提高了凝并效率,PM2.5占烟尘中颗粒的数量浓度较凝并前下降40%~60%,质量浓度较凝并前下降5~15%。(1) Through the special structure provided by the present invention, a variety of coagulation synergies have improved the coagulation efficiency, and the number concentration of PM 2.5 in the dust particles is reduced by 40% to 60% compared with that before coagulation, and the mass concentration is higher than that of coagulation The previous drop was 5~15%.
(2)本发明所提供的凝并箱显著减少PM2.5的排放。本发明主要通过在袋式除尘器前对超细颗粒物进行凝并,使之能够在袋式除尘器的作用下加以脱除,本发明提供的装置可以提高电—袋除尘器对超细颗粒物的脱除效率,减少超细烟尘的排放。可以在同等的除尘器的工作状态和收集方式的条件下,烟尘中PM2.5去除率提高40%~60%。(2) The condensation tank provided by the present invention significantly reduces the emission of PM 2.5 . The present invention mainly condenses ultrafine particles before the bag filter so that they can be removed under the action of the bag filter. Removal efficiency, reduce the emission of ultra-fine smoke. Under the same working condition and collection mode of the dust collector, the removal rate of PM 2.5 in the dust can be increased by 40%~60%.
(3)本发明所提供的凝并箱的各部分,分区合理,功能兼容匹配。(3) Each part of the condensing tank provided by the present invention has reasonable divisions and compatible functions.
(4)本发明所提供的凝并箱为电—袋除尘器的减容创造了条件。(4) The condensing box provided by the present invention creates conditions for the capacity reduction of the electric-bag dust collector.
(5)本发明所提供的凝并箱功能多样,调节灵活,喷入活性炭等吸附剂加强除汞、砷等有毒重金属,喷入化学高分子吸附剂即可强化凝并效果;与多种污染物控制的体系相比,在实现多功能的前提下,减少了投资,简化了运行,阻力损失小,压力降低,减少了能耗,运行成本低。(5) The coagulation box provided by the present invention has multiple functions and flexible adjustment. It can be sprayed into activated carbon and other adsorbents to strengthen the removal of mercury, arsenic and other toxic heavy metals, and sprayed with chemical polymer adsorbents can enhance the coagulation effect; it is compatible with various pollution Compared with the physical control system, on the premise of realizing multi-function, it reduces investment, simplifies operation, has small resistance loss, reduces pressure, reduces energy consumption, and low operating cost.
(6)本发明所提供的凝并箱安装方便,适应面广,适于各种袋式除尘器之前预处理,也提高了电—袋除尘器对各种不同工业烟尘的适应性。(6) The condensing box provided by the present invention is easy to install and has a wide range of applications. It is suitable for pretreatment before various bag-type dust collectors, and also improves the adaptability of electric-bag dust collectors to various industrial fumes.
(7)本发明所提供的凝并箱为电除尘器的改造提供了新的思路。(7) The condensation box provided by the present invention provides a new idea for the transformation of the electrostatic precipitator.
附图说明Description of drawings
图1为本发明提供的双喷式流线型超细颗粒凝并箱构造示意图。Fig. 1 is a schematic diagram of the structure of the double-jet streamlined superfine particle coagulation box provided by the present invention.
图2为本发明中超细颗粒凝并原理示意图。Fig. 2 is a schematic diagram of the coagulation principle of ultrafine particles in the present invention.
在图1,2中:1:电除尘器, 2:袋式除尘器,3: 凝并箱,4: 进气口,5:凝并区,6:出气口,7:灰斗,8: 横条,9: 凝并前颗粒,10: 凝并后结大的颗粒,11:筛孔板,12:引导管Ⅰ,13:喷嘴,14:引导管Ⅱ,15:挡板,A:湍流凝并主要发生区域。In Figure 1, 2: 1: Electrostatic precipitator, 2: Bag filter, 3: Condensation box, 4: Air inlet, 5: Condensation area, 6: Air outlet, 7: Ash hopper, 8: Horizontal bar, 9: particles before coagulation, 10: large particles after coagulation, 11: sieve plate, 12: guide pipe I, 13: nozzle, 14: guide pipe II, 15: baffle, A: turbulent flow Condensation mainly occurs in the area.
具体实施方式detailed description
下面结合附图和具体实施例,进一步阐明本发明。The present invention will be further explained below in conjunction with the accompanying drawings and specific embodiments.
实施例1Example 1
某工业烟尘废气,处理量为80000m3/h采用本发明提供的凝并箱。整个凝并箱呈箱式,适于安装在电—袋除尘器之间;凝并箱由进气口、出气口、凝并区和灰斗组成;进气口为电除尘器之后的通道,烟气由电除尘器而来;凝并区中设置有3组横条,横条横置于凝并区中,横条的断面形状为流线型的导弹头状;出气口位于凝并区下部,灰斗上方,设置成过流通道,经凝并之后的烟气进入袋式除尘器进行处理;灰斗设置于凝并区下方,与电—袋除尘器的其它灰斗平齐。An industrial smoke and dust waste gas with a treatment capacity of 80,000m 3 /h adopts the condensing box provided by the present invention. The entire condensing box is box-shaped, suitable for installation between electrostatic-bag dust collectors; the condensing box is composed of an air inlet, an air outlet, a condensing area and an ash hopper; the air inlet is the passage behind the electrostatic precipitator, The flue gas comes from the electrostatic precipitator; there are 3 sets of horizontal bars in the condensation area, and the horizontal bars are placed horizontally in the condensation area. Above the ash hopper, it is set as a flow channel, and the flue gas after condensation enters the bag filter for treatment; the ash hopper is set under the condensation area, flush with other ash hoppers of the electrostatic-bag filter.
凝并区中设置的每组横条上下排列,横条的断面形状导弹头部长度为10cm,水平部分长为20 cm;横条的高度为20cm;相邻两只横条之间的间距取横条高度的1.0倍;相邻两组横条之间的间距取横条断面长度的1.0倍,相邻两组横条之间错位设置。在图2中,A为湍流凝并主要发生的区域。Each group of horizontal bars set in the condensate area is arranged up and down, the cross-sectional shape of the horizontal bar is 10 cm long for the missile head, and the length of the horizontal part is 20 cm; the height of the horizontal bar is 20 cm; the distance between two adjacent horizontal bars is taken as 1.0 times the height of the horizontal bars; the distance between two adjacent groups of horizontal bars is 1.0 times the length of the horizontal bar section, and the two adjacent groups of horizontal bars are misplaced. In Fig. 2, A is the region where turbulent condensation mainly occurs.
在凝并区的入口处,设置筛孔板,让气流通过;筛孔板后竖向设置一组喷嘴,喷嘴通过管道与气泵相连,可将活性炭等吸附剂通过引导管经喷嘴喷入凝并区。At the entrance of the condensation area, a sieve plate is set to let the air flow through; a group of nozzles are vertically installed behind the sieve plate, and the nozzles are connected to the air pump through a pipeline, and activated carbon and other adsorbents can be sprayed into the condensation through the nozzles through the guide pipe. Area.
在凝并区内设置一组喷嘴,由配液泵将凝并促进剂和水充分混合,混合后的凝并促进剂溶液经雾化后,通过引导管接入喷嘴,喷入凝并区,形成雾云。凝并促进剂占水的质量百分比为1.5%;凝并促进剂溶液流量占烟气流量体积百分比为0.1%。经袋式除尘处理后的烟气,通过引风机将净化后达到排放标准的烟气从排气筒排出。Set a group of nozzles in the condensation area, and the coagulation accelerator and water are fully mixed by the liquid distribution pump. After the mixed coagulation accelerator solution is atomized, it is connected to the nozzle through the guide pipe and sprayed into the condensation area. Fog clouds form. The mass percentage of the coagulation accelerator in water is 1.5%; the volume percentage of the coagulation accelerator solution in the flue gas flow is 0.1%. The flue gas treated by bag dust removal is discharged from the exhaust pipe through the induced draft fan.
采用该装置处理使超细烟尘凝并成较大粒径的颗粒,并通过袋式除尘器加以脱除。采用本发明提供的凝并箱,进行强化凝并,后接袋式除尘器,整个工艺总除尘效率99.98%以上,烟气含尘排放浓度小于20mg/Nm3, PM2.5去除率提高60%。The device is used to condense the ultra-fine dust into particles with larger particle size, and remove them through the bag filter. The coagulation box provided by the present invention is used to carry out enhanced coagulation, followed by a bag filter. The total dust removal efficiency of the whole process is over 99.98%, the dust emission concentration of the flue gas is less than 20mg/Nm 3 , and the removal rate of PM 2.5 is increased by 60%.
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CN111871141A (en) * | 2020-08-09 | 2020-11-03 | 盐城工学院 | A fan-shaped pipeline type ultra-fine particle condenser |
CN111871140A (en) * | 2020-08-09 | 2020-11-03 | 盐城工学院 | An oval ultrafine particle condensing box |
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CN111871135A (en) * | 2020-08-07 | 2020-11-03 | 盐城工学院 | Oval horizontal bar pipeline type ultrafine particle condenser |
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