CN104741258A - Novel rotational flow atomization apparatus and application technology - Google Patents
Novel rotational flow atomization apparatus and application technology Download PDFInfo
- Publication number
- CN104741258A CN104741258A CN201310740300.9A CN201310740300A CN104741258A CN 104741258 A CN104741258 A CN 104741258A CN 201310740300 A CN201310740300 A CN 201310740300A CN 104741258 A CN104741258 A CN 104741258A
- Authority
- CN
- China
- Prior art keywords
- nozzle
- rotary
- gas
- spray
- bearing
- 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.)
- Pending
Links
- 238000000889 atomisation Methods 0.000 title claims abstract description 30
- 238000005516 engineering process Methods 0.000 title abstract description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 57
- 239000012530 fluid Substances 0.000 claims abstract description 22
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 21
- 239000003546 flue gas Substances 0.000 claims abstract description 21
- 238000005507 spraying Methods 0.000 claims abstract description 19
- 238000000034 method Methods 0.000 claims abstract description 13
- 238000012546 transfer Methods 0.000 claims abstract description 9
- 230000008569 process Effects 0.000 claims abstract description 7
- 239000003344 environmental pollutant Substances 0.000 claims abstract description 5
- 238000002156 mixing Methods 0.000 claims abstract description 5
- 231100000719 pollutant Toxicity 0.000 claims abstract description 5
- 230000000694 effects Effects 0.000 claims description 43
- 239000007789 gas Substances 0.000 claims description 43
- 239000007921 spray Substances 0.000 claims description 43
- 239000007788 liquid Substances 0.000 claims description 27
- 238000006243 chemical reaction Methods 0.000 claims description 7
- 239000006185 dispersion Substances 0.000 claims description 6
- 238000013461 design Methods 0.000 claims description 5
- 239000011148 porous material Substances 0.000 claims description 4
- 239000008358 core component Substances 0.000 claims description 3
- 239000000203 mixture Substances 0.000 claims description 3
- 239000002245 particle Substances 0.000 claims description 3
- 238000000926 separation method Methods 0.000 claims description 3
- 230000009466 transformation Effects 0.000 claims description 3
- 230000015572 biosynthetic process Effects 0.000 claims description 2
- 230000001737 promoting effect Effects 0.000 claims description 2
- 239000012071 phase Substances 0.000 claims 4
- 239000007791 liquid phase Substances 0.000 claims 3
- 241000883990 Flabellum Species 0.000 claims 1
- 240000007817 Olea europaea Species 0.000 claims 1
- 238000013019 agitation Methods 0.000 claims 1
- 238000004140 cleaning Methods 0.000 claims 1
- 230000003247 decreasing effect Effects 0.000 claims 1
- 230000003009 desulfurizing effect Effects 0.000 claims 1
- 235000013305 food Nutrition 0.000 claims 1
- 238000002347 injection Methods 0.000 claims 1
- 239000007924 injection Substances 0.000 claims 1
- 238000009434 installation Methods 0.000 claims 1
- 238000005304 joining Methods 0.000 claims 1
- 239000000463 material Substances 0.000 claims 1
- 239000002184 metal Substances 0.000 claims 1
- 239000007769 metal material Substances 0.000 claims 1
- 238000002663 nebulization Methods 0.000 claims 1
- 238000005086 pumping Methods 0.000 claims 1
- 238000003756 stirring Methods 0.000 claims 1
- 238000005728 strengthening Methods 0.000 claims 1
- 239000002912 waste gas Substances 0.000 claims 1
- 238000003466 welding Methods 0.000 claims 1
- 239000000428 dust Substances 0.000 abstract description 27
- 238000006477 desulfuration reaction Methods 0.000 abstract description 14
- 230000023556 desulfurization Effects 0.000 abstract description 14
- 238000000746 purification Methods 0.000 abstract description 8
- 239000000779 smoke Substances 0.000 abstract description 6
- 230000008901 benefit Effects 0.000 abstract description 2
- 238000005034 decoration Methods 0.000 abstract 1
- 230000004720 fertilization Effects 0.000 abstract 1
- 230000003116 impacting effect Effects 0.000 abstract 1
- 239000000575 pesticide Substances 0.000 abstract 1
- 238000012360 testing method Methods 0.000 description 17
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 14
- 238000009826 distribution Methods 0.000 description 13
- 239000002023 wood Substances 0.000 description 13
- 239000003595 mist Substances 0.000 description 8
- 239000003502 gasoline Substances 0.000 description 6
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 6
- 238000001816 cooling Methods 0.000 description 5
- 238000005265 energy consumption Methods 0.000 description 5
- 238000005259 measurement Methods 0.000 description 5
- 238000010521 absorption reaction Methods 0.000 description 4
- 238000011156 evaluation Methods 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 4
- JKFYKCYQEWQPTM-UHFFFAOYSA-N 2-azaniumyl-2-(4-fluorophenyl)acetate Chemical compound OC(=O)C(N)C1=CC=C(F)C=C1 JKFYKCYQEWQPTM-UHFFFAOYSA-N 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 3
- 229910021612 Silver iodide Inorganic materials 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 230000009471 action Effects 0.000 description 3
- 235000011089 carbon dioxide Nutrition 0.000 description 3
- 239000003054 catalyst Substances 0.000 description 3
- 238000006555 catalytic reaction Methods 0.000 description 3
- 238000002485 combustion reaction Methods 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 229940045105 silver iodide Drugs 0.000 description 3
- GGCZERPQGJTIQP-UHFFFAOYSA-N sodium;9,10-dioxoanthracene-2-sulfonic acid Chemical compound [Na+].C1=CC=C2C(=O)C3=CC(S(=O)(=O)O)=CC=C3C(=O)C2=C1 GGCZERPQGJTIQP-UHFFFAOYSA-N 0.000 description 3
- 125000006850 spacer group Chemical group 0.000 description 3
- 235000015842 Hesperis Nutrition 0.000 description 2
- 241000282414 Homo sapiens Species 0.000 description 2
- 235000012633 Iberis amara Nutrition 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
- 238000004887 air purification Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000002925 chemical effect Effects 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 238000007865 diluting Methods 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 230000002265 prevention Effects 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 229910052717 sulfur Inorganic materials 0.000 description 2
- 239000011593 sulfur Substances 0.000 description 2
- 238000009827 uniform distribution Methods 0.000 description 2
- MGWGWNFMUOTEHG-UHFFFAOYSA-N 4-(3,5-dimethylphenyl)-1,3-thiazol-2-amine Chemical compound CC1=CC(C)=CC(C=2N=C(N)SC=2)=C1 MGWGWNFMUOTEHG-UHFFFAOYSA-N 0.000 description 1
- 206010003497 Asphyxia Diseases 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 238000003916 acid precipitation Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000004888 barrier function Effects 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical class [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 238000009690 centrifugal atomisation Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 239000012717 electrostatic precipitator Substances 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 229920006351 engineering plastic Polymers 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000010921 in-depth analysis Methods 0.000 description 1
- 230000002262 irrigation Effects 0.000 description 1
- 238000003973 irrigation Methods 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- JCXJVPUVTGWSNB-UHFFFAOYSA-N nitrogen dioxide Inorganic materials O=[N]=O JCXJVPUVTGWSNB-UHFFFAOYSA-N 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 238000001694 spray drying Methods 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 238000007655 standard test method Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
Classifications
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62C—FIRE-FIGHTING
- A62C31/00—Delivery of fire-extinguishing material
- A62C31/02—Nozzles specially adapted for fire-extinguishing
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D47/00—Separating dispersed particles from gases, air or vapours by liquid as separating agent
- B01D47/06—Spray cleaning
- B01D47/08—Spray cleaning with rotary nozzles
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/60—Simultaneously removing sulfur oxides and nitrogen oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
- B01D53/79—Injecting reactants
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B05—SPRAYING OR ATOMISING IN GENERAL; APPLYING FLUENT MATERIALS TO SURFACES, IN GENERAL
- B05B—SPRAYING APPARATUS; ATOMISING APPARATUS; NOZZLES
- B05B13/00—Machines or plants for applying liquids or other fluent materials to surfaces of objects or other work by spraying, not covered by groups B05B1/00 - B05B11/00
- B05B13/02—Means for supporting work; Arrangement or mounting of spray heads; Adaptation or arrangement of means for feeding work
- B05B13/0278—Arrangement or mounting of spray heads
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B05—SPRAYING OR ATOMISING IN GENERAL; APPLYING FLUENT MATERIALS TO SURFACES, IN GENERAL
- B05B—SPRAYING APPARATUS; ATOMISING APPARATUS; NOZZLES
- B05B3/00—Spraying or sprinkling apparatus with moving outlet elements or moving deflecting elements
- B05B3/02—Spraying or sprinkling apparatus with moving outlet elements or moving deflecting elements with rotating elements
- B05B3/04—Spraying or sprinkling apparatus with moving outlet elements or moving deflecting elements with rotating elements driven by the liquid or other fluent material discharged, e.g. the liquid actuating a motor before passing to the outlet
- B05B3/06—Spraying or sprinkling apparatus with moving outlet elements or moving deflecting elements with rotating elements driven by the liquid or other fluent material discharged, e.g. the liquid actuating a motor before passing to the outlet by jet reaction, i.e. creating a spinning torque due to a tangential component of the jet
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Analytical Chemistry (AREA)
- Biomedical Technology (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Public Health (AREA)
- Business, Economics & Management (AREA)
- Emergency Management (AREA)
- Nozzles (AREA)
Abstract
Description
技术领域 technical field
本发明涉及一类借助流体自身动力产生高速旋转和雾化,显著提升过程强化效果的新型旋流雾化装置与应用技术,可广泛用于流体雾化、烟道气及空气净化、喷雾干燥或浓缩、消烟灭火等工农业领域。 The invention relates to a new type of swirl atomization device and application technology that can generate high-speed rotation and atomization by means of the fluid's own power, which can significantly improve the process intensification effect, and can be widely used in fluid atomization, flue gas and air purification, spray drying or Industrial and agricultural fields such as concentration, smoke elimination and fire extinguishing. the
背景技术 Background technique
喷雾技术在浓缩、干燥、吸收、烟道气及空气净化等传质传热过程广泛应用。传统的雾化技术是以气体为连续相,液体为分散相,通过把带压流体压入喷头细孔造成高速流雾化,该技术存在液体通过细孔产生的摩擦阻力导致动能损失大,雾化效果差,细孔容易堵塞等诸多弊端。一种改进的喷雾技术是使带压液体通过离心或前置螺旋结构使其雾化,大的液体流道虽然缓解了微孔堵塞问题,但仍然存着螺旋或喷口结垢和堵塞,影响雾化效果的问题。这种传统改进型雾化喷头,均采用了喷头固定流体通过特殊结构进行快速运动或碰撞分散的方式,绝大部分能量并迎面撞击的结构件吸收,液体在空间的分布范围、分布效果和气液接触时间及机会有限,会显著影响传质传热和反应效果。 Spray technology is widely used in mass transfer and heat transfer processes such as concentration, drying, absorption, flue gas and air purification. The traditional atomization technology uses gas as the continuous phase and liquid as the dispersed phase. Pressurized fluid is pressed into the pores of the nozzle to cause high-speed flow atomization. This technology has a large kinetic energy loss due to the frictional resistance generated by the liquid passing through the pores. There are many disadvantages such as poor chemical effect and easy clogging of pores. An improved spray technology is to atomize the pressurized liquid through a centrifugal or pre-screw structure. Although the large liquid flow channel alleviates the problem of micropore blockage, there is still scaling and blockage of the spiral or nozzle, which affects the mist. The problem of chemical effects. This traditional improved atomizing nozzle adopts the way that the fixed fluid of the nozzle moves quickly or collides and disperses through a special structure. Most of the energy is absorbed by the structural parts that collide head-on. The distribution range of the liquid in the space, the distribution effect and the gas-liquid The limited contact time and opportunity will significantly affect the mass transfer, heat transfer and reaction effect. the
离心雾化喷头是由雾化片、旋流片、和分流片三部分组成。流体在一定压力下经分流片的小孔汇合到一个环形槽中,然后经过旋流片的切向进入旋流中心的旋流室,产后高速的旋转运动,并经中心孔喷出。流体在离心力的作用下克服了本身的粘性力和表面张力,被粉碎成细小液滴,并形成具有一定角度的圆锥形雾化区,然而这种离心雾化喷头仍然存在雾滴分布不均,中间水量小,水滴大甚至呈水柱状态,覆盖面积小,雾化效果差。因此,尽可能“因势利导”地将带压流体的动能转化为充分雾化的有效能的新型高效雾化喷头的创新很有价值。 The centrifugal atomizing nozzle is composed of three parts: atomizing sheet, swirl sheet, and shunt sheet. Under a certain pressure, the fluid merges into an annular groove through the small hole of the shunt plate, and then enters the swirl chamber in the center of the swirl through the tangential direction of the swirl plate, rotates at a high speed after delivery, and is sprayed out through the center hole. Under the action of centrifugal force, the fluid overcomes its own viscous force and surface tension, and is crushed into fine droplets, forming a conical atomization area with a certain angle. However, this centrifugal atomization nozzle still has uneven distribution of droplets. The amount of water in the middle is small, the water droplets are large or even in the state of water column, the coverage area is small, and the atomization effect is poor. Therefore, the innovation of a new type of high-efficiency atomizing nozzle that converts the kinetic energy of the pressurized fluid into the effective energy of sufficient atomization as much as possible is very valuable. the
通过旋风除尘、旋液分离不失为除尘除雾的有效方式。但同样因为完全依靠了进塔流体的初始动能,经引入管切向进入筒体受阻改变方向而产生旋转运动,虽然产生的离心力可将比重大的粉尘或/和液滴等带向壁面,实现气液或气固初步分离。但是,旋风除尘的结构同样使流体的动能很快被设备吸收只能形成效果有限的局部旋流,因此,旋风除尘或除雾作用有限,处理效果有待提升。虽然增加鼓风和排放设备可以提高流体流速,能耗将显著增加,同时气体流速加快也会影响脱硫效果。目前,烟道气中的PM10,PM2.5等粉尘必须经过布袋或静电除尘才能大部分去除,达到排放标准。 Cyclone dust removal and liquid cyclone separation are effective ways to remove dust and fog. However, because it completely relies on the initial kinetic energy of the fluid entering the tower, it enters the cylinder tangentially through the introduction pipe and changes its direction to produce rotational motion. Although the centrifugal force generated can bring the specific heavy dust or/and liquid droplets to the wall surface, realizing Preliminary separation of gas-liquid or gas-solid. However, the structure of the cyclone dust removal also makes the kinetic energy of the fluid quickly absorbed by the equipment and can only form a local swirl flow with limited effect. Therefore, the cyclone dust removal or demisting effect is limited, and the treatment effect needs to be improved. Although increasing the blast and exhaust equipment can increase the fluid flow rate, the energy consumption will increase significantly, and the faster gas flow rate will also affect the desulfurization effect. At present, most of the dust such as PM10 and PM2.5 in the flue gas must be removed by bagging or electrostatic precipitator to meet the emission standards. the
水雾除尘脱硫是烟道气净化的最常用方式,它是通过喷淋稀碱水的方式使尘粒、二氧化硫、氮氧化物等污染物与液滴或液膜在空中或填料表面充分接触被俘获,除尘效率可以达到80%~90%,可以同时脱除二氧化硫、氮氧化物等有害气体,但由于气量大、水量小、水滴分散性差、接触时间短、相间接触效果不理想,仍存在上述污染物净化脱除效果差、能耗和处理费用较高的问题。因为喷入的雾滴未能形成液体旋流,也未能带动气体旋流,从上向下喷出的液体在重力和初始动能的双重作用下,迅速落入塔底或形成壁流,存在严重的壁流和粘壁现象,传质传热效果还有待提升。目前只能采用加大直径、增加塔高、减少气速、增加多层喷头的形式以保证脱硫效果,造成投资大、设备占用空间大、能耗高、处理效果差,特别是燃煤锅炉尾气净化后,很难达到燃气锅炉的二氧化硫和粉尘排放标准。大量排放的粉尘和酸性气体,已经造成了经常的、持续的、大范围的雾霾天气,严重影响人们的正常生活。即使符合国家排放标准,实际上也是造成酸雨和雾霾的重大污染源。目前采取的控制煤炭使 用量,从主城区撤出燃煤锅炉,限制锅炉使用价廉的煤炭燃烧,改用稀缺天然气作为燃料并不能治本。只会加重燃气资源的紧缺和企业和人们的生活成本。因此开发高效节能效果显著的雾化技术意义重大。 Water mist dedusting and desulfurization is the most commonly used method for flue gas purification. It sprays dilute alkaline water to make dust particles, sulfur dioxide, nitrogen oxides and other pollutants fully contact with droplets or liquid films in the air or on the surface of the filler to be fully contacted. Capture, the dust removal efficiency can reach 80% to 90%, and it can remove harmful gases such as sulfur dioxide and nitrogen oxides at the same time. Poor purification and removal of pollutants, high energy consumption and high treatment costs. Because the sprayed droplets failed to form a liquid swirl, nor did they drive the gas swirl, the liquid sprayed from top to bottom quickly fell into the bottom of the tower or formed a wall flow under the double action of gravity and initial kinetic energy, and there was Severe wall flow and wall sticking phenomenon, the mass and heat transfer effect needs to be improved. At present, it is only possible to increase the diameter, increase the tower height, reduce the gas velocity, and increase the multi-layer nozzle to ensure the desulfurization effect, resulting in large investment, large equipment space, high energy consumption, and poor treatment effect, especially for the tail gas of coal-fired boilers. After purification, it is difficult to meet the sulfur dioxide and dust emission standards of gas boilers. A large amount of dust and acid gas has caused frequent, continuous, and large-scale haze weather, seriously affecting people's normal life. Even if it meets the national emission standards, it is actually a major source of pollution causing acid rain and smog. The current measures taken to control coal consumption, withdraw coal-fired boilers from the main urban area, restrict boilers from using cheap coal to burn, and switch to scarce natural gas as fuel cannot cure the root cause. It will only increase the shortage of gas resources and the cost of living of enterprises and people. Therefore, it is of great significance to develop a high-efficiency and energy-saving atomization technology. the
失去控制的火,就会给人类造成灾难。在各种灾害中,火灾是最经常、最普遍地威胁公众安全和社会发展的主要灾害之一。当今,火灾是世界各国人民所面临的一个共同的灾难性问题。人类能够对火进行利用和控制,是文明进步的一个重要标志。消防工作的重要性是不言而喻的。预防火灾和减少火灾的危害是消防工作的两大重要任务,因此有效防范火灾的发生和高效快速灭火的技术开发很有价值。 Fire out of control will cause disaster to human beings. Among various disasters, fire is one of the main disasters that most frequently and commonly threaten public safety and social development. Today, fire is a common catastrophic problem faced by people all over the world. Human beings can use and control fire, which is an important symbol of civilization progress. The importance of firefighting work is self-evident. Fire prevention and fire hazard reduction are two important tasks of firefighting work, so the development of effective fire prevention and efficient and rapid fire extinguishing technology is very valuable. the
目前,消防灭火主要采用了以隔绝空气和覆盖燃烧区域为主的覆盖灭火和降温灭火及稀释或隔绝空气三种单独或其组合形式。现有的灭火实际上是通过降低温度或浓度或减少接触等手段,达到快速终止氧化反应使火焰熄灭的目的。 At present, fire extinguishing mainly adopts three separate or combined forms of covering fire extinguishing and cooling fire extinguishing and diluting or isolating air, which are mainly based on isolating air and covering the burning area. Existing fire extinguishing actually achieves the purpose of quickly terminating the oxidation reaction and extinguishing the flame by reducing the temperature or concentration or reducing contact. the
扑灭大火所使用的大型消防装备,虽然水压和水量很大,但雾化效果差,喷洒面积小,用水量大,对大面积火灾往往难以奏效,常常造成重大的人身财产损失和社会恐慌。因此,研究可瞬间扑灭大火的高效节水灭火装备意义重大。 Although the large-scale fire-fighting equipment used to extinguish the fire has a large water pressure and water volume, the atomization effect is poor, the spraying area is small, and the water consumption is large. It is often difficult to be effective for large-scale fires, often causing major personal and property losses and social panic. Therefore, it is of great significance to study high-efficiency water-saving fire extinguishing equipment that can instantly extinguish large fires. the
人工降雨,是根据不同云层的物理特性,选择合适时机,用飞机、火箭向云中播撒干冰、碘化银、盐粉等催化剂,使云层降水或增加降水量,以解除或缓解农田干旱、增加水库灌溉水量或供水能力,或增加发电水量等。 Artificial rainfall is based on the physical characteristics of different cloud layers, and at the right time, airplanes and rockets are used to sow catalysts such as dry ice, silver iodide, and salt powder into the clouds to make the clouds rain or increase the amount of precipitation, so as to relieve or alleviate farmland drought and increase reservoir irrigation. Water volume or water supply capacity, or increasing water volume for power generation, etc. the
目前,人工降雨主要采用冷云催化、暖云催化、动力催化等方法,采用的催化剂主要有干冰、碘化银、盐粉等,存在着耗能大、气候云层条件要求苛刻、成本高等问题。 At present, artificial rainfall mainly uses methods such as cold cloud catalysis, warm cloud catalysis, and dynamic catalysis. The catalysts used mainly include dry ice, silver iodide, and salt powder, etc., which have problems such as high energy consumption, harsh climate and cloud conditions, and high cost. the
发明内容 Contents of the invention
综上所述,液体的充分雾化的应用需求广泛,技术存在瓶颈,具有挑战性。现有各种固定雾化喷头动能损失大,雾化效果不理想。虽然也有旋转浇水的喷头,但由于其转速低或喷嘴设计未优化,雾化效果差,未见在其它领域的应用。利用电机高速旋转虽然能够改善分散效果,但存在成本高、结构复杂、能耗高,使用范围有限等诸多问题,难以推广。 To sum up, the application requirements of sufficient atomization of liquids are extensive, and there are bottlenecks in the technology, which is challenging. The kinetic energy loss of various fixed atomizing nozzles is large, and the atomization effect is not ideal. Although there are also rotary watering nozzles, they have not been used in other fields due to their low speed or unoptimized nozzle design and poor atomization effect. Although the use of high-speed rotation of the motor can improve the dispersion effect, there are many problems such as high cost, complex structure, high energy consumption, and limited application range, so it is difficult to popularize. the
需要指出的是,带压流体在从容器或管道中喷出时的动能一直没有受到重视和很好利用。我们在高效喷头的研发中发现,将喷头分为固定部份和用轴承相连接的可用喷嘴促进高速旋转的两个部份,通过“因势利导”的喷嘴设计,不但可以将一直被忽视传动能很好转化为转动能,而且可以有效避免动能损失,最大程度转化为充分雾化的表面能。这种新型旋转喷头借助流体对外喷射时的反作用力和小阻力优势可产生高速旋转,在液体或空气中旋转速度每分钟可达数百次到数万次不等,高速旋转的气流和液流不但可以带动周边气体和液体旋转,而且可以大大促进分散流体与介质的摩擦,强化雾化或分散效果。在旋转喷头上增加旋流叶片,更能加强体系旋流效果。三孔射流旋转喷头(附图1~附图9所示多种三孔射流旋转喷头优选结构)或子弹头形的多孔射流喷头(附图10所示子弹头形多孔射流喷头优选结构)可以克服现有喷头的弊端,实现长距离、宽范围、充分雾化、大面积覆盖、水雾在径向和环向分布更为均匀。通过中心喷嘴的孔眼形状、大小及角度、流量和水压的调节可以使旋转水雾达到数十米外的距离,顺风可以飘得更远;两侧的旋转喷嘴在液体喷出时曲面产生的反作用力可以带动喷嘴高速旋转,可大大扩展雾滴的有效雾化区域,中间喷头的雾化设计和高速旋转正好克服了现有喷头的空心化,提高了均匀度,更有效的保证宽范围覆盖,更重要的是成为了大范围、长距离、产生持续旋流的动力源,发挥了龙卷风“风眼”的效果。调节旋转喷嘴的水平角、改变喷嘴结构及液体的压力和流量可以方便的控制水雾量大小和分布范围,适应 不同情况下的需要。 It should be pointed out that the kinetic energy of fluid under pressure when it is ejected from a container or pipeline has not been paid attention to and well utilized. In the research and development of high-efficiency nozzles, we found that the nozzles are divided into two parts: the fixed part and the available nozzles connected by bearings to promote high-speed rotation. It can be easily converted into rotational energy, and can effectively avoid the loss of kinetic energy, and convert it into fully atomized surface energy to the greatest extent. This new type of rotary nozzle can generate high-speed rotation by taking advantage of the reaction force and small resistance when the fluid is sprayed to the outside. The rotation speed in liquid or air can range from hundreds to tens of thousands of times per minute. High-speed rotating air and liquid flow It can not only drive the surrounding gas and liquid to rotate, but also greatly promote the friction between the dispersion fluid and the medium, and strengthen the atomization or dispersion effect. Adding swirl vanes to the rotary nozzle can further enhance the swirl effect of the system. Three-hole jet rotary nozzle (the preferred structure of multiple three-hole jet rotary nozzles shown in accompanying drawing 1~accompanying drawing 9) or bullet-shaped porous jet nozzle (the preferred structure of bullet-shaped porous jet nozzle shown in accompanying drawing 10) can overcome The disadvantages of the existing nozzles are to achieve long distance, wide range, full atomization, large area coverage, and more uniform distribution of water mist in the radial and circumferential directions. Through the adjustment of the hole shape, size and angle, flow rate and water pressure of the central nozzle, the rotating water mist can reach a distance of tens of meters, and it can float farther with the wind; The reaction force can drive the nozzle to rotate at a high speed, which can greatly expand the effective atomization area of the droplets. The atomization design and high-speed rotation of the middle nozzle just overcome the hollowing of the existing nozzle, improve the uniformity, and more effectively ensure a wide range of coverage. , and more importantly, it has become a large-scale, long-distance, power source that generates continuous swirl, and exerts the effect of the "eye of the wind" of the tornado. Adjusting the horizontal angle of the rotating nozzle, changing the structure of the nozzle and the pressure and flow of the liquid can easily control the size and distribution range of the water mist, and adapt to the needs of different situations. the
脱硫除尘一典型和有价值的实际应用:将未经脱硫除尘处理的高温热烟道气用旋流板或切线进料方式,引入净化塔中,使气体沿着水平切线方向旋转并螺旋上升,形成第一种气体旋流,但效果有限(气速仅增加一倍左右,约10m/s左右);在烟道气入口附近使用雾化旋转喷头或其与扇叶的组合喷头,可大大强化烟道气的旋流速度(气速增加3~5倍,最高可达35m/s左右)。显然从循环泵获得动量的循环液从喷嘴喷出时产生的反作用力推动活动喷嘴高速旋转,同时有效带动了气流的旋转。证明了雾化旋转喷嘴可将流体的能量转化为推动喷嘴和物流旋转的动能以及促进液滴进一步分散的表面能,成为了第二种旋流推动力;小流量即可高速旋转的雾化喷头可以在极短时间内大大增加气液接触的机会,使水雾汽化及烟道气快速降温,体积骤降形成负压,产生第三种旋流拉力。气体自身的动能,液体旋转产生的动能和体积收缩产生的自身的有效能合力促使流体更强、更快、作用范围更大的定向旋流运动,可产生类似龙卷风的快速旋流效果,并沿塔体快速螺旋上升,从整体向上运动方向改变为螺旋上升运动,旋转喷头起到了形成负压、促进旋流的龙卷风眼作用,可以更好地使物系自身的能量转化为有效能,强化过程混合,提高传质传热效果。夹带的灰尘、二氧化硫和二氧化氮等在自身动力和旋转力推动下有更多机会与悬浮在体系中雾化的弱碱水充分接触反应或被捕获,潮湿的环境和弱碱性的水雾可以显著消除体系静电,增强捕捉和沉降灰尘和有害气体效果。快速运动的气液旋流加速和促进了比重大的灰尘、液体朝着壁面富集,可显著增强除雾除尘效果,大大减少夹带。此外,富含水蒸汽的烟道气在旋转和冷却过程中会冷却成二次水雾,也可以协助吸尘和被有效分离。多塔串联、多位置和上下方向合理配置的旋喷雾装置可以进一步确保效果。其他有明显体积收缩或显著压差、能形成周边比中心压高且可持续大流量补充气体的体系,也可以诱导形成沿径向或轴向的大范围、长距离类似龙卷风的强烈旋流;烟道气中夹带的粉尘固体和液滴在获得数十倍的离心力帮助下可实现快速分离,二氧化硫等污染物也可充分地与稀碱水接触与反应被捕获,以旋流喷雾为核心的旋流净化塔装置可大大提升烟道气的处理量和除尘脱硫效果,可使燃煤锅炉达到和优于燃气锅炉的排放标准(SO2和粉尘的排放浓度均可低于50mg/m3),烟道气中的低品位余热借助塔壁换热夹套可有效换热可用于供热和制冷。 A typical and valuable practical application of desulfurization and dust removal: the high-temperature hot flue gas without desulfurization and dust removal treatment is introduced into the purification tower by swirl plate or tangential feeding method, so that the gas rotates along the horizontal tangential direction and spirally rises. The first type of gas swirl is formed, but the effect is limited (the gas velocity only doubles, about 10m/s); using an atomizing rotary nozzle or a combined nozzle with fan blades near the flue gas inlet can greatly strengthen The swirl velocity of the flue gas (gas velocity increases by 3 to 5 times, up to about 35m/s). Apparently, the reaction force generated when the circulation fluid obtained momentum from the circulation pump is ejected from the nozzle pushes the movable nozzle to rotate at a high speed, and at the same time effectively drives the rotation of the airflow. It proves that the atomizing rotary nozzle can convert the energy of the fluid into the kinetic energy that drives the nozzle and the stream to rotate, and the surface energy that promotes the further dispersion of the droplets, which becomes the second swirl driving force; the atomizing nozzle that can rotate at a high speed with a small flow rate It can greatly increase the chance of gas-liquid contact in a very short time, so that the water mist vaporizes and the flue gas cools down quickly, and the volume drops suddenly to form a negative pressure, generating the third swirling force. The kinetic energy of the gas itself, the kinetic energy generated by the liquid's rotation, and the effective energy generated by the volume shrinkage promote the directional swirl movement of the fluid stronger, faster, and with a wider range of action, which can produce a rapid swirl effect similar to a tornado, and along the The tower body spirals up quickly, changing from the overall upward movement direction to the spiral upward movement. The rotating nozzle plays the role of forming a negative pressure and promoting the tornado eye of the swirling flow, which can better convert the energy of the system itself into effective energy and strengthen the process. Mix to improve the mass and heat transfer effect. The entrained dust, sulfur dioxide and nitrogen dioxide have more chances to fully contact and react with the weak alkaline water suspended in the system and atomized under the driving force of its own power and rotation or to be captured. The humid environment and weak alkaline water mist It can significantly eliminate static electricity in the system, and enhance the effect of capturing and settling dust and harmful gases. The fast-moving gas-liquid swirl accelerates and promotes the accumulation of heavy dust and liquid toward the wall, which can significantly enhance the effect of fog and dust removal and greatly reduce entrainment. In addition, the flue gas rich in water vapor will be cooled into secondary water mist during the rotation and cooling process, which can also assist dust suction and be effectively separated. The rotary spray device with multi-tower series, multi-position and reasonable configuration in the up and down directions can further ensure the effect. Other systems with obvious volume shrinkage or significant pressure difference, which can form a peripheral pressure higher than the central pressure and sustain a large flow of supplementary gas, can also induce the formation of a large-scale and long-distance strong swirl similar to a tornado along the radial or axial direction; The dust solids and liquid droplets entrained in the flue gas can be quickly separated with the help of dozens of times the centrifugal force. Pollutants such as sulfur dioxide can also be fully contacted and reacted with dilute alkaline water to be captured. The swirling spray as the core The cyclone purification tower device can greatly improve the flue gas treatment capacity and dust removal and desulfurization effect, and can make the coal-fired boiler meet or exceed the emission standard of the gas-fired boiler (the emission concentration of SO 2 and dust can be lower than 50mg/m 3 ) , the low-grade waste heat in the flue gas can be used for heating and cooling by means of the heat exchange jacket on the tower wall.
高效灭火应用:从化工的原理深入的分析灭火过程可以得知,水喷雾灭火主要是利用降温,驱赶和稀释氧气达到阻止燃烧反应,熄灭火焰的目的。显然,雾化水的表面积可以增加成千上万倍,汽化水的体积可以增加上千倍。因此,使水充分雾化是有效增加吸热和蒸发面,同时产生快速吸热降温和高效窒息效果的关键。因此,雾化效果极好的旋流雾化装置可能会产生使大面积火场温度和氧浓度迅速下降,同时瞬间大量吸热产生的水蒸汽将导致燃烧区急剧膨胀,产生迅速阻隔和稀释空气快速消烟灭火的效果。本发明很好地解决达到快速高效灭火在空间中均匀分布、长距离、大面积覆盖的关键问题。 High-efficiency fire extinguishing application: From the in-depth analysis of the fire extinguishing process of the chemical industry, we can know that the water spray fire extinguishing mainly uses cooling, driving and diluting oxygen to prevent the combustion reaction and extinguish the flame. Obviously, the surface area of atomized water can be increased thousands of times, and the volume of vaporized water can be increased thousands of times. Therefore, fully atomizing water is the key to effectively increase the heat absorption and evaporation surface, and at the same time produce rapid heat absorption cooling and efficient suffocation effect. Therefore, the swirling atomization device with excellent atomization effect may cause a rapid drop in temperature and oxygen concentration in a large area of the fire scene, and at the same time, the water vapor generated by a large amount of heat absorption in an instant will cause the combustion zone to expand rapidly, resulting in rapid barrier and dilution of air. The effect of extinguishing smoke and fire. The invention well solves the key problems of uniform distribution in space, long-distance and large-area coverage of fast and efficient fire extinguishing. the
人工降雨应用:目前人工降雨所用的干冰、碘化银、盐粉等催化剂,必须用飞机喷撒,或者用火箭发射,成本高、云层条件要求苛刻、效果不稳定。本发明仅需利用水,达到均匀分布、长距离、大面积覆盖的旋流雾化效果,可诱发云层中分散的水蒸气的迅速聚集,形成局部低压,诱导利用大气本身的能量,形成降雨,成本低、效果显著。 Application of artificial rainfall: At present, catalysts such as dry ice, silver iodide, and salt powder used in artificial rainfall must be sprayed by aircraft or launched by rockets. The cost is high, the cloud conditions are harsh, and the effect is unstable. The invention only needs to use water to achieve evenly distributed, long-distance, and large-area coverage of the swirl atomization effect, which can induce the rapid accumulation of dispersed water vapor in the cloud layer, form local low pressure, induce the use of the energy of the atmosphere itself, and form rainfall. The cost is low and the effect is remarkable. the
附图说明 Description of drawings
图1单轴承三孔射流旋转喷头90°优选结构1-扇形喷嘴2-广角扇形喷嘴3-旋转头4-轴承5-锁紧螺母6-管接头 Figure 1 Single-bearing three-hole jet rotary nozzle 90° optimal structure 1-fan nozzle 2-wide-angle fan nozzle 3-rotary head 4-bearing 5-lock nut 6-pipe joint
图2单轴承三孔射流旋转喷头45°优选结构 Fig. 2 Optimum structure of single-bearing three-hole jet rotary nozzle at 45°
图3单轴承三孔射流双针雾化喷头优选结构 Figure 3 Optimum structure of single-bearing three-hole jet and double-needle atomizing nozzle
图4单轴承螺旋雾化旋转喷头优选结构 Figure 4 Optimum structure of single-bearing spiral atomizing rotary nozzle
图5三孔射流单针雾化喷头优选结构 Figure 5 Optimum structure of three-hole jet single-needle atomizing nozzle
图6双轴承三孔射流旋转喷头优选结构1-扇形喷嘴2-旋转头3-广角扇形喷嘴4-卡簧5-密封圈6-推力轴承7-轴承套8-螺钉9-接头10-螺钉11-锁紧螺母 Figure 6 Optimum structure of double-bearing three-hole jet rotary nozzle 1-fan nozzle 2-rotary head 3-wide-angle fan nozzle 4-circlip 5-sealing ring 6-thrust bearing 7-bearing sleeve 8-screw 9-joint 10-screw 11 -fasten the screw nut
图7三轴承三孔射流旋转喷头优选结构1-扇形喷嘴2-旋转头3-广角扇形喷嘴4-卡簧5-深沟球轴承6-推力轴承7-轴承隔套8-轴承座9-螺钉10-锁紧螺母11-螺钉12-管接头连接螺母 Figure 7. Optimal structure of three-bearing three-hole jet rotary nozzle 1-fan nozzle 2-rotary head 3-wide-angle fan nozzle 4-circlip 5-deep groove ball bearing 6-thrust bearing 7-bearing spacer 8-bearing seat 9-screw 10-lock nut 11-screw 12-pipe joint connection nut
图8带扇叶三孔射流旋转喷头优选结构1-扇形喷嘴2-旋转头3-广角扇形喷嘴4-卡簧5-深沟球轴承6-推力轴承7-轴承隔套8-轴承座9-螺钉10-锁紧螺母11-螺钉12-管接头连接螺母13-扇叶14-锁紧螺母 Fig. 8 Optimum structure of three-hole jet rotary nozzle with fan blades 1-fan-shaped nozzle 2-rotary head 3-wide-angle fan-shaped nozzle 4-circlip 5-deep groove ball bearing 6-thrust bearing 7-bearing spacer 8-bearing seat 9- Screw 10-lock nut 11-screw 12-pipe joint connection nut 13-blade 14-lock nut
图9带扇叶三孔射流旋转喷头优选结构1-扇形喷嘴2-旋转头3-广角扇形喷嘴4-卡簧5-深沟球轴承6-推力轴承7-轴承隔套8-轴承座9-螺钉10-锁紧螺母11-螺钉12-管接头连接螺母13-扇叶14-锁紧螺母 Figure 9 Optimum structure of three-hole jet rotary nozzle with fan blades 1-fan-shaped nozzle 2-rotary head 3-wide-angle fan-shaped nozzle 4-circlip 5-deep groove ball bearing 6-thrust bearing 7-bearing spacer 8-bearing seat 9- Screw 10-lock nut 11-screw 12-pipe joint connection nut 13-blade 14-lock nut
图10子弹头形旋转喷头优选结构 Figure 10 Optimum structure of bullet-shaped rotary nozzle
图11单臂单喷嘴旋转喷头优选结构 Figure 11 Optimum structure of single-arm single-nozzle rotary nozzle
图12单臂双喷嘴旋转喷头优选结构 Figure 12 Optimum structure of single-arm double-nozzle rotary nozzle
图13单臂双喷嘴单螺旋旋转喷头优选结构 Figure 13 Optimum structure of single-arm double-nozzle single-spiral rotary nozzle
图14双层多喷嘴旋转喷头优选结构 Figure 14 Optimum structure of double-layer multi-nozzle rotary nozzle
图15四喷嘴旋转喷头优选结构 Figure 15 Optimum structure of four-nozzle rotary nozzle
图16三孔射流旋转喷头在不同压力下的流量 Figure 16 The flow rate of the three-hole jet rotary nozzle under different pressures
图17 3公斤压力下三孔射流旋转喷头下喷和上喷时径向水量分布 Figure 17 Radial water volume distribution of the three-hole jet rotary nozzle when spraying downward and upward under the pressure of 3 kg
图18 3公斤压力下三孔射流旋转喷头(45°)下喷和上喷时径向水量分布 Figure 18 Radial water volume distribution of the three-hole jet rotary nozzle (45°) when spraying downwards and upwards under a pressure of 3 kg
图19 3公斤压力下90°三孔双针射流旋转喷头下喷和上喷时径向水量分布 Figure 19 Radial water volume distribution of 90° three-hole double-needle jet rotary nozzle for downspray and upspray under 3 kg pressure
图20 3公斤压力下单螺旋混合喷头下喷和上喷时径向水量分布 Figure 20 Radial water volume distribution of single spiral mixing nozzle when spraying downward and upward under 3 kg pressure
图21风速测试点位置示意图1-边上点2-1/2中心点3-中心点4-1/2中心点5-边上 Figure 21 Schematic diagram of the position of the wind speed test point 1-side point 2-1/2 center point 3-center point 4-1/2 center point 5-side
具体实施方式 Detailed ways
通过下面给出的本发明的实施例可进一步了解本发明,以下实施例仅为本发明的几个具体实施例,但本发明的范围并不局限于此,凡利用此方法或方案对本发明进行非实质性的改动,均应属于侵犯本发明保护范围的行为。以下实施例中,喷头均是设计流量参数为0.3MPa(3公斤)下流量为3m3/h的旋转喷头,其中广角扇形喷嘴喷射角度均为75°,扇形喷嘴喷射角度均为60°,喷嘴的主流道直径均为2mm。 Can further understand the present invention by the embodiment of the present invention that provides below, following embodiment is only several specific embodiments of the present invention, but the scope of the present invention is not limited thereto, all utilize this method or scheme to carry out the present invention Any non-substantial changes shall belong to the act of violating the protection scope of the present invention. In the following examples, the nozzles are all rotary nozzles with a design flow parameter of 0.3MPa (3 kg) and a flow rate of 3m 3 /h, wherein the wide-angle fan-shaped nozzles have a spray angle of 75°, and the fan-shaped nozzles have a spray angle of 60°. The main channel diameter is 2mm.
一、旋转喷头在不同压力下的转速与流量测定 1. Measurement of rotational speed and flow rate of the rotary nozzle under different pressures
实施例1:三孔射流旋转喷头在不同压力下的流量 Embodiment 1: The flow rate of the three-hole jet rotary nozzle under different pressures
将一只的三孔射流旋转喷头安装在有压力表和水泵的试验装置上,试验采用自来水,喷口水压为0.05、0.15、0.20、0.25、0.30、0.35MPa。采用专用水箱和称重器收集水量并称重,每次喷水时间为2min。测量不同压力下喷头的流量,如附图16所示。 Install a three-hole jet rotary nozzle on the test device with pressure gauge and water pump. The test uses tap water, and the nozzle water pressure is 0.05, 0.15, 0.20, 0.25, 0.30, 0.35MPa. Use a special water tank and a weighing device to collect and weigh the water, and the water spraying time is 2 minutes each time. Measure the flow rate of the nozzle under different pressures, as shown in Figure 16. the
实验结果表明:喷头的流量与压力有很好的线性关系,可以根据需要进行调节。 The experimental results show that: the flow rate of the nozzle has a good linear relationship with the pressure, which can be adjusted according to the needs. the
实施例2:不同喷头在3公斤压力下的转速 Embodiment 2: Rotating speed of different nozzles under 3 kilograms of pressure
将不同旋转喷头安装分别在试验装置上,试验采用净水,同样3公斤水压下,测量不同喷头的转速,如表1所示。实验结果表明,同样3公斤压力下,各种类型的喷头转速都大于2000r/min,其中螺旋雾化旋转喷头的转速最低,为2018r/min左右,三孔射流旋转喷头的转速最高,达7991r/min。三孔射流双针雾化喷头的稳定性最好。 Install different rotating nozzles on the test device respectively. The test uses clean water. Under the same water pressure of 3 kg, the rotational speed of different nozzles is measured, as shown in Table 1. The experimental results show that under the same pressure of 3 kg, the rotation speed of various types of nozzles is greater than 2000r/min, among which the rotation speed of the spiral atomization rotary nozzle is the lowest at about 2018r/min, and the rotation speed of the three-hole jet rotary nozzle is the highest at 7991r/min min. The stability of the three-hole jet and double-needle atomizing nozzle is the best. the
表1不同喷头在3公斤压力下的转速 Table 1 Rotation speed of different nozzles under 3 kg pressure
实施例3:不同喷头通入空气在空气介质中的转速 Embodiment 3: The rotating speed of different nozzles feeding air in the air medium
从喷头中通入空气,在空气介质中测试不同喷头在不同压力下的转速,如表2所示。在0.5公斤压力下,三孔射流双针雾化喷头的转速相对较高,最大转速为11132r/min。在相同压力下,螺旋雾化旋转喷头的转速相对较低。 Air was introduced from the nozzle, and the rotational speeds of different nozzles under different pressures were tested in the air medium, as shown in Table 2. Under the pressure of 0.5 kg, the speed of the three-hole jet and double-needle atomizing nozzle is relatively high, and the maximum speed is 11132r/min. Under the same pressure, the rotational speed of the spiral atomizing rotary nozzle is relatively low. the
表2不同喷头通入空气在空气介质中的转速 Table 2 Rotational speeds of air fed into air medium by different nozzles
二、喷头不同情况下水量分布、喷雾半径和最远喷射距离测试 2. Tests of water volume distribution, spray radius and longest spray distance of nozzles under different conditions
实施例4:不同喷头下喷和上喷时径向水量分布 Example 4: Radial water distribution of different nozzles when spraying downwards and upwards
喷头向下喷射和向上喷射时的水量分布状况分析:喷头距地面高度2.5m,从喷头正下方中心开始,径向放一排集水盒(S=0.08m2),在3公斤压力下开喷头3min后,称量距离中心喷头不同距离(即径向距离)的每个集水盒中收集到的水质量或体积,可以得到喷雾密度、有效喷雾半径和最远喷雾距离等径向流量分布情况,结果如图17~20所示。 Analysis of the water volume distribution when the nozzle is sprayed downwards and upwards: the height of the nozzle is 2.5m from the ground, starting from the center directly below the nozzle, a row of water collection boxes (S=0.08m 2 ) is placed radially, and it is opened under a pressure of 3 kg After 3 minutes from the nozzle, weigh the mass or volume of water collected in each water collection box at different distances (that is, the radial distance) from the center nozzle, and obtain the radial flow distribution such as spray density, effective spray radius, and the farthest spray distance situation, the results are shown in Figures 17-20.
如附图17所示,实验结果表明:90°三孔射流旋转喷头下喷时的雾滴主要分散在直径2米左右的区域内,上喷时雾滴可更好分散在直径5米以上的区域内。向上喷雾灭火可以覆盖更大范围,在直径3米左右达到最大。显然向上喷可使雾化水覆盖更大范围。 As shown in Figure 17, the experimental results show that the droplets are mainly dispersed in the area with a diameter of about 2 meters when the 90° three-hole jet rotary nozzle is sprayed downward, and the droplets can be better dispersed in the area with a diameter of more than 5 meters when sprayed upward. within the area. Upward spray fire extinguishing can cover a larger area, reaching the maximum at a diameter of about 3 meters. Obviously, spraying upwards can make the atomized water cover a wider area. the
如附图18所示,实验结果表明:45°三孔射流旋转喷头下喷时的雾滴也主要分散在直径2米左右的区域内,上喷时雾滴可更广分散在直径4米左右的区域内。显然45°三孔射流旋转喷头向上喷雾同样比向下喷雾覆盖范围大很多,而且更均匀。 As shown in Figure 18, the experimental results show that the droplets of the 45° three-hole jet rotary nozzle are mainly dispersed in the area with a diameter of about 2 meters when spraying downward, and the droplets can be more widely dispersed in a diameter of about 4 meters when spraying upward. within the area. Obviously, the 45° three-hole jet rotary nozzle sprays upwards and sprays downwards, and the coverage is much larger and more uniform. the
如附图19所示,实验结果表明:90°三孔双针射流旋转喷头上下喷时的雾滴分散性可以更好改善,雾滴可达直径5米左右的区域,上喷时可以显著增加5米以区域内的喷雾量,在直径2米左右达到最大。 As shown in Figure 19, the experimental results show that the droplet dispersion can be better improved when the 90° three-hole double-needle jet rotary nozzle sprays up and down, and the droplet can reach an area with a diameter of about 5 meters. The amount of spray in the area within 5 meters reaches the maximum at a diameter of about 2 meters. the
如附图20所示,实验结果表明:单螺旋混合旋转喷头上下喷时的雾滴分散性也很好,雾滴可达直径3米左右的区域,上喷时可以显著增加4米左右区域内的喷雾量,在3米直径以内分布均匀。 As shown in Figure 20, the experimental results show that the droplet dispersibility of the single-helical mixing rotary nozzle is also very good when spraying up and down, and the droplet can reach an area with a diameter of about 3 meters. The amount of spray is evenly distributed within a diameter of 3 meters. the
实施例5:不同旋转喷头在不同压力和喷射状态下的喷雾半径和最远喷射距离 Embodiment 5: The spray radius and the farthest spray distance of different rotary nozzles under different pressures and spray states
如实施例4所述的试验方法,测量在2公斤和3公斤压力下三孔射流旋转喷头(附图1)、三孔射流旋转喷头45°(附图2)、螺旋雾化旋转喷头(附图3)、三孔射流双针雾化喷头(附图4)、子弹头式旋转喷头(附图10)从上往下喷时的喷射半径,从下往向上喷射时的喷射半径和喷雾高度以及侧喷时的喷雾宽度和最远喷射距离。 Test method as described in embodiment 4, measure three-hole jet rotary nozzle (accompanying drawing 1), three-hole jet rotary nozzle 45 ° (accompanying drawing 2), spiral atomization rotary nozzle (accompanying drawing 2) under 2 kilograms and 3 kilograms of pressures Fig. 3), spray radius of three-hole jet two-needle atomizing nozzle (accompanying drawing 4), bullet-type rotating nozzle (accompanying drawing 10) when spraying from top to bottom, spray radius and spray height when spraying from bottom to top As well as the spray width and the farthest spray distance when spraying from the side. the
表3不同类型旋转喷头在不同压力和不同喷射状态下的喷雾半径和最远喷射距离 Table 3 The spray radius and the farthest spray distance of different types of rotary nozzles under different pressures and different spray states
表4现有类型喷头在不同压力和不同喷射状态下的喷雾半径和最远喷射距离 Table 4 The spray radius and the farthest spray distance of existing types of nozzles under different pressures and different spray states
为了进一步验证旋流雾化技术在一定限制的空间内的效果,我们另外进行了在直径1200mm高10.5m的锅炉烟囱(不锈钢塔)进行了,塔内气速测定和二氧化硫脱除效果评价。三、燃气锅炉烟道气塔内气速及脱硫效果评价 In order to further verify the effect of swirling atomization technology in a certain limited space, we also carried out a boiler chimney (stainless steel tower) with a diameter of 1200mm and a height of 10.5m. The gas velocity in the tower was measured and the sulfur dioxide removal effect was evaluated. 3. Evaluation of gas velocity and desulfurization effect in gas boiler flue gas tower
实施例6:燃气锅炉烟道气塔内气速测定(塔内测试点分布如附图21所示) Embodiment 6: Measurement of gas velocity in the gas boiler flue gas tower (the distribution of test points in the tower is shown in Figure 21)
试验1:没有燃气,只开引风机(额定负荷40HZ,引风量为51000-69000m3/h),塔内温度塔顶57℃,塔底76℃,进行空白实验,不同测试点的塔内气速如表5所示,塔径1.2m,塔高10m。 Test 1: No gas, only the induced draft fan (rated load 40HZ, induced air volume 51000-69000m3/h), the temperature inside the tower is 57°C at the top of the tower, and 76°C at the bottom of the tower, conduct a blank experiment, and the gas velocity in the tower at different test points As shown in Table 5, the tower diameter is 1.2m and the tower height is 10m. the
表5只开引风机下塔内各个点气速 Table 5 Gas velocity at each point in the tower with the induced draft fan only
试验2:开燃气,煤气量为1176m3/h,开鼓风机(7600-15000m3/h)和引风机(40HZ,引风量为51000-69000m3/h),塔内温度塔顶146℃,塔底156℃,不开喷头,进行第二组空白实验,不同测试点的塔内气速如表6所示。 Test 2: Turn on the gas, the gas volume is 1176m 3 /h, turn on the blower (7600-15000m 3 /h) and the induced draft fan (40HZ, the induced air volume is 51000-69000m 3 /h), the temperature inside the tower is 146°C at the top of the tower, The bottom temperature is 156°C, the nozzle is not turned on, and the second set of blank experiments is carried out. The gas velocity in the tower at different test points is shown in Table 6.
表6开燃气和鼓风机不喷水条件下各个点气速 Table 6 Gas velocity at each point under the condition of gas and blower without water spraying
试验3:开燃气时开中下喷头,喷水流量中部5.7-7.5m3/h,下部1.1-2.3m3/h,引风机和鼓风机都开,温度上下均为43℃。煤气量为1138m3/h。不同测试点的塔内气速如表7所示。 Test 3: When the gas is turned on, the middle and lower nozzles are turned on, the water spray flow is 5.7-7.5m 3 /h in the middle, and 1.1-2.3m 3 /h in the lower part, both the induced draft fan and the blower are turned on, and the temperature is 43°C. The gas volume is 1138m 3 /h. The gas velocity in the tower at different test points is shown in Table 7.
表7开燃气和鼓风机开中下喷头喷水条件下各个点气速 Table 7 Gas velocity at each point under the condition of gas and blower on, middle and lower nozzles spraying water
试验4:喷头上加扇叶(扇叶为ABS工程塑料材质,叶片数为3个,半径为375mm,),其他条件同上述试验3相同,不同测试点下的塔内气速如表8所示。 Test 4: Fan blades are added to the nozzle (the fan blades are made of ABS engineering plastics, the number of blades is 3, and the radius is 375mm). Other conditions are the same as the above test 3. The air velocity in the tower under different test points is shown in Table 8 Show. the
表8喷头上加扇叶条件下各个点塔内气速 Table 8 Air velocity in the tower at each point under the condition of adding fan blades to the nozzle
对只开引风机、增开燃气、增开喷头、喷头加扇叶四种不同条件下,整理不同风向的风速,如表9~表12所示。 For the four different conditions of only opening the induced draft fan, adding gas, adding nozzles, and adding fan blades, the wind speeds of different wind directions are sorted out, as shown in Tables 9 to 12. the
表9风速测定(下风向) Table 9 Wind speed measurement (downwind direction)
表10风速测定(上风向) Table 10 Wind speed measurement (upwind direction)
表12风速测定(左风向) Table 12 Wind speed measurement (left wind direction)
可以明显看出,在下风向,开喷头的风速比不开喷头要大,说明气体旋流湍动大。喷头加扇叶比喷头不加扇叶的风速要大,最大可以达到22.5m/s。而与旋流方向一致的右风向的风速比左风向风速要大,更说明旋流的效果。 It can be clearly seen that in the downwind direction, the wind speed with the nozzle turned on is greater than that without the nozzle turned on, indicating that the gas swirl is turbulent. The wind speed of nozzles with fan blades is higher than that of nozzles without fan blades, and the maximum can reach 22.5m/s. The wind speed in the right wind direction, which is consistent with the direction of the swirl, is greater than the wind speed in the left wind direction, which further explains the effect of the swirl. the
实施例7:燃煤锅炉烟道气脱硫除尘效果评价 Example 7: Evaluation of desulfurization and dust removal effect of coal-fired boiler flue gas
双碱法除尘脱硫实验。相关条件和结果如下:烟道气流量55000Nm3/h,烟气温度180℃,进口SO2浓度为2000mg/Nm3。塔径1.2m,塔高9m,液气比为2/1000,脱硫液为饱和石灰水和1%的氢氧化钠的混合液。改造前脱硫效率为90%,出口硫含量在400mg/Nm3,改造后脱硫率可达到99%左右,出口硫含量小于50mg/Nm3,粉尘含量可降低到10mg/Nm3,充分证明以旋转喷头为核心构件的旋流塔可以高效脱硫除尘,可以使燃煤锅炉烟道气净化后的二氧化硫及粉尘的排放浓度低于燃气锅炉尾气排放标准,对雾霾治理意义重大。 Double alkali dust removal and desulfurization experiment. The relevant conditions and results are as follows: the flue gas flow rate is 55000Nm 3 /h, the flue gas temperature is 180°C, and the inlet SO 2 concentration is 2000mg/Nm 3 . The diameter of the tower is 1.2m, the height of the tower is 9m, the ratio of liquid to gas is 2/1000, and the desulfurization liquid is a mixture of saturated lime water and 1% sodium hydroxide. Before transformation, the desulfurization efficiency was 90%, and the outlet sulfur content was 400mg/Nm 3 . After transformation, the desulfurization rate can reach about 99%, the outlet sulfur content is less than 50mg/Nm 3 , and the dust content can be reduced to 10mg/Nm 3 , which fully proves that the rotation The swirl tower with the nozzle as the core component can efficiently desulfurize and remove dust, and can make the emission concentration of sulfur dioxide and dust after the flue gas purification of coal-fired boilers lower than the exhaust gas emission standards of gas-fired boilers, which is of great significance to haze control.
表13燃煤锅炉烟道气脱硫除尘效果评价 Table 13 Evaluation of desulfurization and dust removal effect of coal-fired boiler flue gas
实施例8:应用于灭火的效果评价 Embodiment 8: be applied to the effect evaluation of fire extinguishing
按照国家的自动喷水灭火系统(GB5135-2006)中的灭火标准实验方法:木垛的尺寸(500*500*380mm),由相互正交的10层杉木组成,每层5条,均匀分布,木条尺寸(38*38*500mm),干燥到湿度为6-12%,称重。木垛放在钢制油盘上,盘中适量深度水>15mm,倒入200mL汽油。喷头在木垛正上方2.5m。2min预燃,待汽油燃完后开启喷头,自点火起实验10min,关闭喷头,如木垛未熄灭,小心扑灭木垛,干燥到湿度在6-12%,称重,计算质量损失。在下风向6m处监测灭火前后的PM10和PM2.5变化。 According to the fire extinguishing standard test method in the national automatic sprinkler system (GB5135-2006): the size of the wooden pile (500*500*380mm), is composed of 10 layers of fir that are orthogonal to each other, and each layer is 5, evenly distributed, Wood strip size (38*38*500mm), dried to a humidity of 6-12%, weighed. The wooden stack is placed on a steel oil pan, and an appropriate amount of water in the pan is >15mm, and 200mL of gasoline is poured into it. The nozzle is 2.5m directly above the wood stack. 2min pre-combustion, turn on the nozzle after the gasoline is burned, test for 10min from the ignition, turn off the nozzle, if the wood pile is not extinguished, carefully extinguish the wood pile, dry until the humidity is 6-12%, weigh it, and calculate the mass loss. The changes of PM10 and PM2.5 before and after fire extinguishing were monitored at 6m downwind. the
使用三孔射流旋转喷头(附图2),第一次结果如下:在2公斤压力下,下喷扑灭用200ml汽油已经引燃2分钟的木材火焰仅用10秒,消耗水量6.25L,烟雾全灭用时70秒,木垛的平均质量损失为8.6%。 Using the three-hole jet rotary nozzle (accompanying drawing 2), the first result is as follows: under the pressure of 2 kg, it only takes 10 seconds to extinguish the wood flame that has been ignited for 2 minutes with 200ml of gasoline, and the water consumption is 6.25L, and the smoke is all When extinguished for 70 seconds, the average mass loss of the wood crib is 8.6%. the
使用三孔射流旋转喷头(附图2),第二次结果如下在:2公斤压力下下喷,扑灭用200ml汽油已经引燃2分钟的木材火焰仅用8秒,消耗水量5L,烟雾全灭用时70秒,木垛的平均质量损失为5.9%。 Using the three-hole jet rotary nozzle (attached figure 2), the second result is as follows: Spray under 2 kg of pressure, extinguish the wood flame that has been ignited for 2 minutes with 200ml gasoline, only 8 seconds, consume 5L of water, and the smoke is completely extinguished Taking 70 seconds, the average mass loss of the wood stack was 5.9%. the
如上所述木垛灭火实验方法,使用三孔射流双针雾化喷头45°,结果如下:在2公斤压力下下喷扑灭用200ml汽油已经引燃2分钟的木材火焰仅用6秒,消耗水量3.75L,烟雾全灭用时40秒,木垛的平均质量损失为6.4%。 As mentioned above, using the three-hole jet and double-needle atomizing nozzle at 45°, the results are as follows: It takes only 6 seconds to extinguish a wood flame that has been ignited for 2 minutes with 200ml gasoline under a pressure of 2 kg, and consumes less water. 3.75L, when the smoke is completely extinguished in 40 seconds, the average mass loss of the wood stack is 6.4%. the
如上所述木垛灭火实验方法,使用现有的洒水喷头,结果在2公斤压力下,下喷扑灭用200ml汽油已经引燃2分钟的木材火焰在10min内未把火扑灭,消耗水量1626.1L,木垛的平均质量损失为19.7%。 As mentioned above, the wood pile fire extinguishing experiment method used the existing sprinkler head. As a result, under the pressure of 2 kg, the wood flame that had been ignited for 2 minutes with 200ml gasoline was not extinguished within 10 minutes, and the water consumption was 1626.1L. The average mass loss of wood stacks was 19.7%. the
Claims (8)
Priority Applications (8)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310740300.9A CN104741258A (en) | 2013-12-30 | 2013-12-30 | Novel rotational flow atomization apparatus and application technology |
KR1020167020760A KR101955780B1 (en) | 2013-12-30 | 2014-12-26 | Automatic high-speed rotary atomizing device, use thereof and a fire extinguishing method by using same |
PCT/CN2014/095156 WO2015101227A1 (en) | 2013-12-30 | 2014-12-26 | Automatic high-speed rotary atomizing device, use thereof and a fire extinguishing method by using same |
CN201480071723.9A CN106029236B (en) | 2013-12-30 | 2014-12-26 | A kind of automatic high-speed rotation atomising device and its application and extinguishing method using it |
AU2014375596A AU2014375596B2 (en) | 2013-12-30 | 2014-12-26 | Automatic high-speed rotary atomizing device, use thereof and a fire extinguishing method by using same |
JP2016544512A JP6495302B2 (en) | 2013-12-30 | 2014-12-26 | Automatic high-speed rotary atomizer and its application and fire extinguishing method using it |
EP14876920.1A EP3090808B1 (en) | 2013-12-30 | 2014-12-26 | Automatic high-speed rotary atomizing device, use thereof and a fire extinguishing method by using same |
US15/109,355 US10632413B2 (en) | 2013-12-30 | 2014-12-26 | Automatic high-speed rotary atomizing device and a fire extinguishing method by using the same |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201310740300.9A CN104741258A (en) | 2013-12-30 | 2013-12-30 | Novel rotational flow atomization apparatus and application technology |
Publications (1)
Publication Number | Publication Date |
---|---|
CN104741258A true CN104741258A (en) | 2015-07-01 |
Family
ID=53581841
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201310740300.9A Pending CN104741258A (en) | 2013-12-30 | 2013-12-30 | Novel rotational flow atomization apparatus and application technology |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104741258A (en) |
Cited By (15)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106423676A (en) * | 2016-12-01 | 2017-02-22 | 无锡溥汇机械科技有限公司 | Turntable bearing sealing structure and method for lithium battery isolating membrane spray coating machine |
CN106984455A (en) * | 2016-01-20 | 2017-07-28 | 北京中科净原环保科技有限公司 | A kind of multi-arm type auto-rotating spray head |
CN107537338A (en) * | 2016-06-28 | 2018-01-05 | 厦门大学 | A kind of efficiently hybrid technology is equipped with energy-conservation |
CN107694313A (en) * | 2017-10-10 | 2018-02-16 | 国电环境保护研究院 | It is a kind of based on artificial meteorological purifying coal-fired flue gas system and method |
CN107926618A (en) * | 2017-11-09 | 2018-04-20 | 深圳市晟祥知识产权有限公司 | A kind of municipal administration gard watering atomization injection water sprinkler |
CN110090524A (en) * | 2019-06-13 | 2019-08-06 | 浙江洪韬建设有限公司 | A kind of construction device for reducing dust |
CN110394245A (en) * | 2019-08-28 | 2019-11-01 | 广州百海工程机械有限公司 | a liquid disperser |
CN111249496A (en) * | 2020-03-18 | 2020-06-09 | 湖南翰坤实业有限公司 | Intelligent atomization sterilizer |
CN111535234A (en) * | 2020-05-08 | 2020-08-14 | 广东博智林机器人有限公司 | Concrete spraying equipment |
CN111996974A (en) * | 2020-07-07 | 2020-11-27 | 中交机电工程局有限公司 | Intelligent water spraying, dust removing and spraying system of stacker-reclaimer |
CN112963865A (en) * | 2021-03-31 | 2021-06-15 | 西北工业大学 | Oil thrower capable of controlling oil injection speed |
CN113736520A (en) * | 2021-08-18 | 2021-12-03 | 中国神华煤制油化工有限公司 | Equipment for rapidly reducing temperature of furnace blowing out in low-temperature zone and process treatment method |
CN114191762A (en) * | 2021-12-13 | 2022-03-18 | 浙江省邮电工程建设有限公司 | Intelligent fire-fighting management system based on big data Internet of things |
CN114392849A (en) * | 2021-12-09 | 2022-04-26 | 华能伊春热电有限公司 | An improved dry mist dust removal nozzle |
CN118454941A (en) * | 2024-07-12 | 2024-08-09 | 常州中铁城建构件有限公司 | Shield segment release agent spraying device |
-
2013
- 2013-12-30 CN CN201310740300.9A patent/CN104741258A/en active Pending
Cited By (21)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106984455A (en) * | 2016-01-20 | 2017-07-28 | 北京中科净原环保科技有限公司 | A kind of multi-arm type auto-rotating spray head |
CN106984455B (en) * | 2016-01-20 | 2019-08-09 | 北京中科净原环保科技有限公司 | A kind of multi-arm type auto-rotating spray head |
CN107537338A (en) * | 2016-06-28 | 2018-01-05 | 厦门大学 | A kind of efficiently hybrid technology is equipped with energy-conservation |
CN106423676A (en) * | 2016-12-01 | 2017-02-22 | 无锡溥汇机械科技有限公司 | Turntable bearing sealing structure and method for lithium battery isolating membrane spray coating machine |
CN107694313A (en) * | 2017-10-10 | 2018-02-16 | 国电环境保护研究院 | It is a kind of based on artificial meteorological purifying coal-fired flue gas system and method |
CN107694313B (en) * | 2017-10-10 | 2023-10-20 | 国电环境保护研究院有限公司 | Coal-fired flue gas purification system and method based on artificial weather |
CN107926618A (en) * | 2017-11-09 | 2018-04-20 | 深圳市晟祥知识产权有限公司 | A kind of municipal administration gard watering atomization injection water sprinkler |
CN110090524A (en) * | 2019-06-13 | 2019-08-06 | 浙江洪韬建设有限公司 | A kind of construction device for reducing dust |
CN110394245A (en) * | 2019-08-28 | 2019-11-01 | 广州百海工程机械有限公司 | a liquid disperser |
CN111249496A (en) * | 2020-03-18 | 2020-06-09 | 湖南翰坤实业有限公司 | Intelligent atomization sterilizer |
CN111535234B (en) * | 2020-05-08 | 2022-03-01 | 广东博智林机器人有限公司 | Concrete spraying equipment |
CN111535234A (en) * | 2020-05-08 | 2020-08-14 | 广东博智林机器人有限公司 | Concrete spraying equipment |
CN111996974A (en) * | 2020-07-07 | 2020-11-27 | 中交机电工程局有限公司 | Intelligent water spraying, dust removing and spraying system of stacker-reclaimer |
CN111996974B (en) * | 2020-07-07 | 2021-11-09 | 中交机电工程局有限公司 | Intelligent water spraying, dust removing and spraying system of stacker-reclaimer |
CN112963865A (en) * | 2021-03-31 | 2021-06-15 | 西北工业大学 | Oil thrower capable of controlling oil injection speed |
CN113736520A (en) * | 2021-08-18 | 2021-12-03 | 中国神华煤制油化工有限公司 | Equipment for rapidly reducing temperature of furnace blowing out in low-temperature zone and process treatment method |
CN113736520B (en) * | 2021-08-18 | 2022-04-29 | 中国神华煤制油化工有限公司 | Equipment for rapidly reducing temperature of furnace blowing out in low-temperature zone and process treatment method |
CN114392849A (en) * | 2021-12-09 | 2022-04-26 | 华能伊春热电有限公司 | An improved dry mist dust removal nozzle |
CN114392849B (en) * | 2021-12-09 | 2022-12-09 | 华能伊春热电有限公司 | Improved dry fog dust removal nozzle |
CN114191762A (en) * | 2021-12-13 | 2022-03-18 | 浙江省邮电工程建设有限公司 | Intelligent fire-fighting management system based on big data Internet of things |
CN118454941A (en) * | 2024-07-12 | 2024-08-09 | 常州中铁城建构件有限公司 | Shield segment release agent spraying device |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106029236B (en) | A kind of automatic high-speed rotation atomising device and its application and extinguishing method using it | |
CN104741258A (en) | Novel rotational flow atomization apparatus and application technology | |
CN201140029Y (en) | Complex organic waste gas absorption and purification device | |
CN104128106A (en) | Novel swirl dispersing device | |
CN107551737B (en) | A kind of spiral atomization blowing and suction dust removal device of coal falling tower | |
CN108083371A (en) | A kind of low energy consumption block-resistant type atomization jetting device | |
CN101391175B (en) | Desulfurization dust collector for industrial furnace | |
CN107952292A (en) | A kind of efficient demisting coalescer of flux adjustable venturi-eddy flow coupled mode | |
CN101362043A (en) | Desulfurization dust removing method of industrial furnace | |
CN206613274U (en) | Wind guiding device and cyclonic separation unit | |
CN104998504B (en) | A kind of wet desulphurization tower desulfurization and dedusting demisting water saving art | |
CN106925459A (en) | Aerosol Spray-nozzle for removing dust | |
CN104740816A (en) | High efficiency fire extinguishing novel technology and device | |
CN213112594U (en) | Hot air distributor for rotary spray evaporation of desulfurization wastewater | |
CN105056671B (en) | A kind of wet desulphurization tower desulfurization and dedusting demisting water saving art and its device | |
CN209968001U (en) | Waste gas purification tower | |
CN204107255U (en) | A kind of combination venturi scrubber | |
CN202032599U (en) | Spray evaporation type cooler | |
CN211487045U (en) | Waste gas separation and purification equipment of tentering and setting machine | |
CN210251661U (en) | Hybrid condensation deep dehydration and whitening purification system | |
CN218795001U (en) | Pervaporation tempering tower used in front of electric tar precipitator | |
CN103406011B (en) | A kind of equipment of pesticides packaging castoff burning vent gas treatment | |
CN213912882U (en) | Counter-flow type tail gas treatment tower | |
CN206613273U (en) | Whirlwind module | |
CN209848663U (en) | Cyclone purification tower |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C41 | Transfer of patent application or patent right or utility model | ||
TA01 | Transfer of patent application right |
Effective date of registration: 20150916 Address after: 361005 Fujian city of Xiamen province Xiamen University South Building No. 2 Applicant after: Xiamen University Asset Management Co., Ltd. Address before: Xiamen University Department of science and technology, 422, Siming District of Xiamen city of Fujian Province in 361005 Applicant before: Xiamen University |
|
C41 | Transfer of patent application or patent right or utility model | ||
TA01 | Transfer of patent application right |
Effective date of registration: 20160308 Address after: Room 18, room 10, A5 A6 100085 in Beijing, Haidian District Qinghe anningzhuang East Applicant after: Beijing Zhongke Environmental Protection Technology Co., Ltd. Address before: 361005 Fujian city of Xiamen province Xiamen University South Building No. 2 Applicant before: Xiamen University Asset Management Co., Ltd. |
|
WD01 | Invention patent application deemed withdrawn after publication | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20150701 |