CN104759190B - The removing collection device of a kind of sulfur dioxide gas and removing collection method thereof - Google Patents
The removing collection device of a kind of sulfur dioxide gas and removing collection method thereof Download PDFInfo
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Abstract
本发明涉及一种二氧化硫气体的脱除收集装置,包括氧硫离解器和硫固体聚集器,二者通过变径接头连为一体;同时,本发明还提供了采用上述装置脱除二氧化硫收集副产物硫的工艺方法,通过所述氧硫离解器将二氧化硫气体解离为硫原子和氧负离子,所述硫固体聚集器将所述硫原子和氧负离子分开,硫原子聚集在所示硫固体聚集器的筒子电极内壁上,所述氧负离子生成氧气从金属通风管排出。本发明提供的装置结构简单、造价低、维护成本低、安装简单、所用电压低、能耗低、脱硫效率高;提供的方法科学合理、步骤简单、操作性好,可以高效完成脱硫过程,避免了副产物存在二次污染的可能,较现有脱硫技术相比具有显著的优越性。
The invention relates to a device for removing and collecting sulfur dioxide gas, which includes an oxygen-sulfur dissociator and a sulfur solid accumulator, the two are connected as a whole through a variable diameter joint; at the same time, the invention also provides a device for removing sulfur dioxide and collecting by-products by using the above-mentioned device The process method of sulfur, the sulfur dioxide gas is dissociated into sulfur atoms and oxygen anions by the oxygen sulfur dissociator, the sulfur solid aggregator separates the sulfur atoms and oxygen anions, and the sulfur atoms gather in the sulfur solid aggregator On the inner wall of the tube electrode, the oxygen negative ions generate oxygen and discharge it from the metal ventilation pipe. The device provided by the invention has the advantages of simple structure, low cost, low maintenance cost, simple installation, low voltage, low energy consumption, and high desulfurization efficiency; the method provided is scientific and reasonable, with simple steps and good operability, and can efficiently complete the desulfurization process, avoid Compared with the existing desulfurization technology, it has obvious advantages compared with the existing desulfurization technology.
Description
技术领域technical field
本发明涉及一种废气处理装置及方法,具体地说涉及一种二氧化硫气体的脱除收集装置及其脱除方法。The invention relates to a waste gas treatment device and method, in particular to a device for removing and collecting sulfur dioxide gas and a method for removing it.
背景技术Background technique
随着人类社会的发展,尤其是重工业的飞速发展,大气污染已经成为了一个全球性的严峻问题。在大气污染物中,人为的污染物主要来源于燃料燃烧和许多工业生产,我国煤炭消费总量约40亿吨,占能源消费总量的65.7%,由于煤和石油通常都含有硫化合物,因此燃烧时会生成大量的二氧化硫。当二氧化硫溶于水中,会形成亚硫酸(酸雨的主要成分),对人体呼吸器官、皮肤有刺激,可引起支气管炎和肺气肿等疾病,造成严重的环境污染和社会经济损失。With the development of human society, especially the rapid development of heavy industry, air pollution has become a serious global problem. Among air pollutants, man-made pollutants mainly come from fuel combustion and many industrial productions. The total coal consumption in my country is about 4 billion tons, accounting for 65.7% of the total energy consumption. Since coal and petroleum usually contain sulfur compounds, so Large amounts of sulfur dioxide are produced during combustion. When sulfur dioxide dissolves in water, it will form sulfurous acid (the main component of acid rain), which can irritate human respiratory organs and skin, cause diseases such as bronchitis and emphysema, and cause serious environmental pollution and social and economic losses.
近年来,我国不断的建立健全、完善大气环境保护法规、煤炭消费的总量控制、大气污染物排放标准等,还大力发展清洁能源,积极推广风能、太阳能、核能等新能源和可再生能源的应用,同时在大气污染治理上,也加大了投入力度,相继出现了很多治理方法。到目前为止,二氧化硫的脱除方法主要分为:湿法、半干法和干法。In recent years, my country has continuously established and perfected laws and regulations on atmospheric environmental protection, the total amount control of coal consumption, and emission standards for air pollutants. At the same time, investment in air pollution control has also increased, and many control methods have emerged one after another. So far, the removal methods of sulfur dioxide are mainly divided into: wet method, semi-dry method and dry method.
其中湿法脱硫技术中,石灰石-石膏法脱硫工艺是世界上普遍使用的烟气脱硫技术,在行业中占90%以上。该法以石灰石为脱硫剂,通过向吸收塔内喷入吸收剂浆液,使之与烟气充分接触、混合,并对烟气进行洗涤,使得烟气中的SO2与浆液中CaCO3以及鼓入的强制氧化空气发生化学反应,最后生成石膏,达到脱硫的目的。该法具有脱硫反应速度快、设备简单、脱硫效率高等优点。但是,湿法普遍存在腐蚀严重、运行维护费用高,特别是二次污染问题,由于烟气中SO2的浓度始终处于变化中,脱硫剂石灰粉末或浆液的投入量难以精确控制,致使吸收塔中的吸收液不能处于最佳吸收状态,这就严重影响了脱硫率以及石膏的质量,致使石膏结构松软和使用价值低,不能进入消费市场。据报道,火电厂堆存的脱硫石膏已有上亿吨,所占用的土地已超过百万亩,并且还在不断增加,已经造成严重的白色污染。Among the wet desulfurization technologies, the limestone-gypsum desulfurization process is the flue gas desulfurization technology commonly used in the world, accounting for more than 90% of the industry. In this method, limestone is used as the desulfurizer, and the absorbent slurry is sprayed into the absorption tower to make it fully contact and mix with the flue gas, and to wash the flue gas, so that the SO 2 in the flue gas and the CaCO 3 in the slurry and the drum A chemical reaction occurs with the forced oxidizing air that enters, and finally generates gypsum to achieve the purpose of desulfurization. This method has the advantages of fast desulfurization reaction speed, simple equipment and high desulfurization efficiency. However, the wet process generally suffers from severe corrosion, high operation and maintenance costs, and especially the problem of secondary pollution. Since the concentration of SO 2 in the flue gas is always changing, it is difficult to accurately control the input amount of desulfurization agent lime powder or slurry, resulting in the absorption tower The absorption liquid in the gypsum cannot be in the best absorption state, which seriously affects the desulfurization rate and the quality of the gypsum, resulting in a soft structure and low use value of the gypsum, which cannot enter the consumer market. According to reports, there are hundreds of millions of tons of desulfurized gypsum piled up in thermal power plants, occupying more than one million mu of land, and it is still increasing, which has caused serious white pollution.
半干法脱硫技术主要包括喷雾干燥法脱硫、半干半湿法脱硫、粉末-颗粒喷动床脱硫、烟道喷射脱硫等。这些方法普遍具有工艺设备简单,设备无腐蚀和严重堵塞情况、设备易运行和维护、副产物容易处理等特点、但是由于这些方法中普遍存在气、液、固三相状态下进行,所以其各自用量的进程难以控制,自动化要求比较高,吸收剂的吸收效率较低,脱硫效率也较低。Semi-dry desulfurization technologies mainly include spray drying desulfurization, semi-dry and semi-wet desulfurization, powder-particle spouted bed desulfurization, flue injection desulfurization, etc. These methods generally have the characteristics of simple process equipment, no corrosion and serious blockage of equipment, easy operation and maintenance of equipment, and easy disposal of by-products. The dosage process is difficult to control, the automation requirements are relatively high, the absorption efficiency of the absorbent is low, and the desulfurization efficiency is also low.
干法脱硫主要有喷雾干燥法、烟道喷钙法、循环硫化床法、催化氧化法、荷电法、氧化铜法、碱性铝酸盐法、熔融盐吸收法及等离子体法等。其中,等离子体法是行业内干法脱硫中研究较多、发展前景最为广阔的方法。等离子体按温度分类可分为高温等离子体和低温等离子体,低温等离子体又分为热等离子体和冷等离子体。其中粒子温度达到106~109K,属于高温等离子体,粒子温度从室温到104K属于低温等离子体。在低温等离子体中,当重粒子温度与电子温度达到热力学平衡状态时,称为热平衡等离子体或热等离子体,如电弧或高频等离子体;当重粒子温度为室温而电子温度达到上万度时,重粒子温度与电子温度远离热平衡状态,称为非热平衡等离子体或低温等离子体,如辉光放电或微波等离子体。Dry desulfurization mainly includes spray drying method, flue calcium spraying method, circulating fluidized bed method, catalytic oxidation method, charging method, copper oxide method, alkaline aluminate method, molten salt absorption method and plasma method. Among them, the plasma method is the method with the most research and the broadest development prospect in the dry desulfurization in the industry. Plasma can be classified into high-temperature plasma and low-temperature plasma according to temperature, and low-temperature plasma is further divided into hot plasma and cold plasma. Among them, when the particle temperature reaches 10 6 ~10 9 K, it belongs to high-temperature plasma, and when the particle temperature reaches from room temperature to 10 4 K, it belongs to low-temperature plasma. In low-temperature plasma, when the temperature of heavy particles and the temperature of electrons reach a state of thermodynamic equilibrium, it is called thermal equilibrium plasma or thermal plasma, such as arc or high-frequency plasma; when the temperature of heavy particles is room temperature and the temperature of electrons reaches tens of thousands of degrees When , the temperature of heavy particles and the temperature of electrons are far from the thermal equilibrium state, which is called non-thermal equilibrium plasma or low-temperature plasma, such as glow discharge or microwave plasma.
近年来,低温等离子体法已经成为国际上公认的具有极大市场潜力和良好应用前景的新方法。低温等离子体法主要包括电子束照射法、脉冲电晕放电法、直流电晕放电法、介质阻挡放电法、介质填充床放电等。特点是电子温度远远高于重粒子温度,通常采用微波放电、电晕放电或无声放电、辉光放电,产生高能电子与自由基,使气体分子发生电离,引发化学反应。众所周知,随着电压的升高,直流放电模式依次为起始流光、辉光、预击穿流光、火花放电。辉光放电充满整个电极空间,电流密度一般为1~5mA/cm2,整个间隙仍呈上升的伏安特性,其平均电子能量2~8eV。辉光放电的电流要比电晕放电高几个数量级,由于辉光的能耗高且化学效应很小,电晕放电平均电子能量小于3eV,火花放电平均电子能量约为1eV,并且宏观气体温度特别高,容易烧毁装置,所以在使用中应当避免辉光和火花放电的出现。但是,由于电晕放电、微波放电的强度又较低,产生的活性粒子的能量和浓度较低,所激发的化学反应的效能低,导致气体处理的效率低,实用性较差。所以,行业内的研究多集中在脉冲电晕法。In recent years, the low-temperature plasma method has become internationally recognized as a new method with great market potential and good application prospects. Low-temperature plasma methods mainly include electron beam irradiation method, pulsed corona discharge method, DC corona discharge method, dielectric barrier discharge method, dielectric packed bed discharge method, etc. The characteristic is that the temperature of electrons is much higher than that of heavy particles. Microwave discharge, corona discharge, silent discharge, and glow discharge are usually used to generate high-energy electrons and free radicals, ionize gas molecules, and trigger chemical reactions. As we all know, as the voltage increases, the DC discharge modes are initial streamer, glow, pre-breakdown streamer, and spark discharge. Glow discharge fills the entire electrode space, the current density is generally 1-5mA/cm 2 , the entire gap still shows rising volt-ampere characteristics, and its average electron energy is 2-8eV. The current of glow discharge is several orders of magnitude higher than that of corona discharge. Due to the high energy consumption of glow and the small chemical effect, the average electron energy of corona discharge is less than 3eV, the average electron energy of spark discharge is about 1eV, and the macroscopic gas temperature Especially high, it is easy to burn the device, so the appearance of glow and spark discharge should be avoided in use. However, due to the low intensity of corona discharge and microwave discharge, the energy and concentration of active particles generated are low, and the efficiency of the chemical reaction excited is low, resulting in low gas treatment efficiency and poor practicability. Therefore, the research in the industry mostly focuses on the pulsed corona method.
脉冲电晕法,是利用在电晕与电晕反应器电极的气隙间放电,使迁移率高的电子在自由程中受到突发强电场的加速而获得足够的能量(高于8.4eV)来电离烟气,在常温下获得非平衡等离子体,进而对SO2进行氧化去除。该方法最大优点就是能起到电子束法同样的作用而又克服了电子束法的缺点,它省掉了大功率、需长期稳定工作的昂贵电子枪,避免了电子枪寿命和X射线屏蔽问题。该方法虽然脱硫效率较高,但是整体能耗也较高,并且目前脉冲电源频率一般为几百Hz,电源的功率也只有几百kW,远不能满足工业化应用的要求。The pulse corona method is to use the discharge between the corona and the air gap between the electrodes of the corona reactor, so that the electrons with high mobility are accelerated by a sudden strong electric field in the free path to obtain sufficient energy (higher than 8.4eV) To ionize the flue gas, obtain non - equilibrium plasma at room temperature, and then oxidize and remove SO2. The biggest advantage of this method is that it can play the same role as the electron beam method and overcome the shortcomings of the electron beam method. It saves the expensive electron gun with high power and long-term stable work, and avoids the problems of electron gun life and X-ray shielding. Although the desulfurization efficiency of this method is high, the overall energy consumption is also high, and the frequency of the current pulse power supply is generally several hundred Hz, and the power of the power supply is only several hundred kW, which is far from meeting the requirements of industrial applications.
为解决传统脉冲电晕法存在的问题,随着研究的不断加深,近年来行业内的学者们也研究了一些能够产生流光放电来脱除二氧化硫的方法,如将放电极与交直流电叠加而成的高压电源连接来产生流光放电。虽然这些方法可以证明流光放电的可行性,但是由于目前人们还没有能力生产出交流频率大于100kHz,功率大于1000kW的高频、大功率的电源,以致于使所产生的流光放电功率较小,电源装置复杂,仅处在实验阶段,无法将其投入到工业废气处理的实际应用中。因此,能够研发出一种脱硫效率高、能耗低、操作维护简单、无二次污染、满足投产工业烟气二氧化硫的脱除中使用的装置和方法是行业内亟待解决的问题。In order to solve the problems existing in the traditional pulsed corona method, with the continuous deepening of research, in recent years, scholars in the industry have also studied some methods that can generate streamer discharge to remove sulfur dioxide, such as superimposing the discharge electrode with AC and DC. The high voltage power supply is connected to generate the streamer discharge. Although these methods can prove the feasibility of streamer discharge, people are still unable to produce a high-frequency, high-power power supply with an AC frequency greater than 100kHz and a power greater than 1000kW, so that the generated streamer discharge power is relatively small. The device is complex, and it is only in the experimental stage, so it cannot be put into the practical application of industrial waste gas treatment. Therefore, it is an urgent problem in the industry to develop a device and method that can be used in the removal of sulfur dioxide from industrial flue gas with high desulfurization efficiency, low energy consumption, simple operation and maintenance, and no secondary pollution.
发明内容Contents of the invention
本发明的目的之一就是提供一种二氧化硫气体的脱除收集装置,以解决现有流光放电脱除收集装置的电源功率低、电源装置复杂,无法投入工业应用,而且产生的副产物存在二次污染的问题。One of the purposes of the present invention is to provide a device for removing and collecting sulfur dioxide gas, so as to solve the problem that the current streamer discharge removing and collecting device has low power and complicated power supply devices, which cannot be put into industrial application, and the by-products produced have secondary pollution problem.
本发明的目的之二就是提供一种二氧化硫气体的脱除收集方法,以解决现有二氧化硫气体脱除方法脱硫工序繁琐、脱硫效率低的问题。The second object of the present invention is to provide a method for removing and collecting sulfur dioxide gas, so as to solve the problems of cumbersome desulfurization process and low desulfurization efficiency of existing sulfur dioxide gas removal methods.
本发明的目的是这样实现的:一种二氧化硫气体的脱除收集装置,包括氧硫离解器和硫固体聚集器;The object of the present invention is achieved like this: a kind of removal collection device of sulfur dioxide gas, comprises oxygen sulfur dissociator and sulfur solid accumulator;
所述氧硫离解器包括微波谐振腔、绝缘子、离解电晕线、微波发生器以及微波屏蔽罩,所述微波屏蔽罩分别设置在所述微波谐振腔的上、下两端,在所述微波屏蔽罩内侧的上、下端分别设置有1个绝缘子,所述两个绝缘子之间固定设置有所述离解电晕线;所述离解电晕线位于所述微波谐振腔的几何中心;所述微波发生器设置在所述微波谐振腔的腔体上;所述离解电晕线接电源正极,所述微波谐振腔接电源负极或接地;所述电源为高压直流电或脉冲直流电中的一种,所述电源的起晕电压为5 kV -40 kV;所述高压直流电源的电压为5 kV -50 kV;所述脉冲直流电源的电压为5 kV -50 kV、频率为10 kHz -15 kHz;The oxygen-sulfur dissociator includes a microwave resonant cavity, an insulator, a dissociated corona wire, a microwave generator, and a microwave shield. The microwave shield is respectively arranged at the upper and lower ends of the microwave resonant cavity. The upper and lower ends of the inner side of the shielding cover are respectively provided with an insulator, and the dissociation corona wire is fixedly arranged between the two insulators; the dissociation corona wire is located at the geometric center of the microwave resonator; the microwave The generator is arranged on the cavity of the microwave resonant cavity; the dissociated corona wire is connected to the positive pole of the power supply, and the microwave resonant cavity is connected to the negative pole of the power supply or grounded; the power supply is one of high-voltage direct current or pulsed direct current, and the The corona inception voltage of the power supply is 5 kV-40 kV; the voltage of the high-voltage DC power supply is 5 kV-50 kV; the voltage of the pulsed DC power supply is 5 kV-50 kV, and the frequency is 10 kHz-15 kHz;
所述硫固体聚集器包括外套筒、若干筒子电极、金属通风管、冷却液以及设置在所述外套筒上部的绝缘密封盖,所述筒子电极设置在所述外套筒内,所述每个筒子电极中心处设置有所述金属通风管,所述金属通风管的上端穿出所述绝缘密封盖,所述金属通风管与筒子电极相互绝缘且分别连接电压为4 kV -20 kV直流电源的正极和负极;The sulfur solid collector includes an outer sleeve, several bobbin electrodes, metal ventilation pipes, cooling liquid and an insulating sealing cover arranged on the upper part of the outer sleeve, the bobbin electrodes are arranged in the outer sleeve, the The metal ventilation tube is arranged at the center of each tube electrode, and the upper end of the metal ventilation tube passes through the insulating sealing cover. The metal ventilation tube and the tube electrode are insulated from each other and the connection voltage is 4 kV-20 kV DC respectively. Positive and negative poles of the power supply;
所述氧硫离解器的下端设有烟气进气口,所述外套筒与所述微波谐振腔通过变径接头将所述氧硫离解器的与所述硫固体聚集器连为一体。The lower end of the oxygen-sulfur dissociator is provided with a flue gas inlet, and the outer sleeve and the microwave resonant cavity are connected together with the sulfur solid collector through a variable-diameter joint.
本发明中所述微波发生器包括磁控管和波导管,所述磁控管为一个或若干个,所述若干磁控管通过所述波导管连接在一起;所述微波发生器的频率为915 MHz,所述磁控管通过所述波导管设置在所述微波振谐腔上。The microwave generator described in the present invention comprises a magnetron and a waveguide, and the magnetron is one or several, and the several magnetrons are connected together through the waveguide; the frequency of the microwave generator is 915 MHz, the magnetron is set on the microwave resonant cavity through the waveguide.
本发明中所述绝缘子为陶瓷绝缘子;所述离解电晕线为钨丝或不锈钢丝;所述微波屏蔽罩为带有小孔的金属板或不锈钢金属网;所述微波谐振腔为不锈钢材料制成。In the present invention, the insulator is a ceramic insulator; the dissociated corona wire is a tungsten wire or a stainless steel wire; the microwave shield is a metal plate with small holes or a stainless steel mesh; the microwave resonator is made of stainless steel become.
本发明中所述外套筒的直径是微波谐振腔直径的1.5-2.5倍,所述外套筒的容积是所述微波谐振腔容积的3-5倍。In the present invention, the diameter of the outer sleeve is 1.5-2.5 times the diameter of the microwave resonant cavity, and the volume of the outer sleeve is 3-5 times the volume of the microwave resonant cavity.
本发明中所述微波谐振腔的直径30 cm -90 cm,所述离解电晕线的半径为0.5mm-1.5mm。The diameter of the microwave resonant cavity in the present invention is 30 cm-90 cm, and the radius of the dissociated corona wire is 0.5 mm-1.5 mm.
本发明中所述筒子电极的内壁上涂覆有一层0.5 mm-1.5mm厚的单质硫,用于更为有效地诱导吸附解离的硫原子。The inner wall of the tube electrode in the present invention is coated with a layer of elemental sulfur with a thickness of 0.5mm-1.5mm, which is used to more effectively induce the adsorption and dissociation of sulfur atoms.
本发明中所述外套筒与所述筒子电极外围的间隙处设有循环冷却液。In the present invention, a circulating cooling liquid is provided at the gap between the outer sleeve and the periphery of the bobbin electrode.
本发明还提供了一种二氧化硫气体的脱除收集方法,包括以下步骤:The present invention also provides a method for removing and collecting sulfur dioxide gas, comprising the following steps:
(a)按所述二氧化硫气体的脱除收集装置组装设备;其中设置所述微波谐振腔的直径30-90 cm,所述离解电晕线的半径为0.5 mm -1.5mm;所述微波发生器的频率为915MHz;所述外套筒的直径是微波谐振腔直径的1.5-2.5倍;所述外套筒内设置有若干个筒子电极,在所外套筒与所述筒子电极外围之间的间隙处设置有循环冷却液;(a) Assemble the equipment according to the removal and collection device of sulfur dioxide gas; the diameter of the microwave resonant cavity is set to 30-90 cm, and the radius of the dissociated corona wire is 0.5 mm to 1.5 mm; the microwave generator The frequency is 915MHz; the diameter of the outer sleeve is 1.5-2.5 times the diameter of the microwave resonant cavity; several bobbin electrodes are arranged inside the outer sleeve, and the outer sleeve and the periphery of the bobbin electrodes The gap is provided with circulating coolant;
(b)在所述筒子电极的内壁上涂覆有一层0.5 mm -1.5mm厚的单质硫;(b) A layer of elemental sulfur with a thickness of 0.5 mm to 1.5 mm is coated on the inner wall of the tube electrode;
(c)分别接通氧硫离解器和硫固体聚集器的电源,给所述氧硫离解器施加5 kV-50kV的高压直流电或5 kV-50 kV、频率为10kHz-15kHz的脉冲直流电,其起晕电压为5 kV -40kV,同时启动微波发生器;给所述硫固体聚集器施加电压为4kV-20kV的直流电源;(c) Turn on the power supplies of the oxygen-sulfur dissociator and the sulfur solid concentrator respectively, and apply a high-voltage direct current of 5 kV-50 kV or a pulsed direct current of 5 kV-50 kV with a frequency of 10 kHz-15 kHz to the oxygen-sulfur dissociator, and The corona inception voltage is 5 kV-40kV, and the microwave generator is started simultaneously; it is a DC power supply with a voltage of 4kV-20kV to the sulfur solid aggregator;
(d)将含有二氧化硫的烟气引入所述氧硫离解器下部设置的进风口中,烟气的温度为150-250℃;使烟气中的二氧化硫在所述氧硫离解器流光放电的作用下离解为硫原子和氧负离子;(d) Introduce the flue gas containing sulfur dioxide into the air inlet provided at the lower part of the oxygen-sulfur dissociator, the temperature of the flue gas is 150-250°C; the effect of making the sulfur dioxide in the flue gas streamer discharge in the oxygen-sulfur dissociator dissociate into sulfur atoms and oxygen negative ions;
(e)解离后的硫原子和氧负离子通过变径接头减压降温,进入所述硫固体聚集器中,调节所述硫固体聚集器中循环冷却液的流速,使筒子电极内的温度控制在80-100℃,硫原子在所述直流电场力和筒子电极内壁硫晶核吸附的作用下向所述筒子电极内壁聚集,氧负离子经过碰撞后两两结合生成氧气,通过金属通风管排出,所述筒子电极内壁聚集的硫单质回收即可。(e) The dissociated sulfur atoms and oxygen negative ions are decompressed and cooled through the variable diameter joint, and enter the sulfur solid collector, and adjust the flow rate of the circulating cooling liquid in the sulfur solid collector, so that the temperature in the bobbin electrode can be controlled At 80-100°C, sulfur atoms gather to the inner wall of the bobbin electrode under the action of the direct current electric field force and the adsorption of sulfur crystal nuclei on the inner wall of the bobbin electrode, and the oxygen negative ions are combined to generate oxygen after collision, and are discharged through the metal ventilation pipe. The sulfur element accumulated on the inner wall of the tube electrode can be recovered.
本发明步骤(d)中烟气中含有二氧化硫的密度控制在为1.0-2.5 kg/m3;烟气的流速为0.1-0.164m/s。In the step (d) of the present invention, the density of sulfur dioxide contained in the flue gas is controlled at 1.0-2.5 kg/m 3 ; the flow velocity of the flue gas is 0.1-0.164m/s.
本发明步骤(a)中所述外套筒内均匀设置有5-7个横截面为圆形的筒子电极。In the step (a) of the present invention, 5-7 bobbin electrodes with a circular cross section are uniformly arranged inside the outer sleeve.
本发明步骤(a)中筒子电极优选7个,每个筒子电极的外径为外套筒内径的1/3。In step (a) of the present invention, there are preferably 7 package electrodes, and the outer diameter of each package electrode is 1/3 of the inner diameter of the outer sleeve.
本发明步骤(a)中循环冷却液优选去离子软化水。The circulating cooling liquid in step (a) of the present invention is preferably deionized demineralized water.
传统研究中的工业性除尘,一般采用负电晕放电的形式,而本发明采用的是正电晕。本发明采用正电晕,这在电压、极距等相同的条件下,能够达到发展速度更快、放电伸展范围更广、光强更强、电晕放电的辉光更明亮、产生的高能电子更强以及化学反应的转化率更高的目的,同时,在微波场的作用下,极性分子由原来杂乱无章的热运动,改变为按电场方向做规则运动,分子间相互作用力的干扰和阻碍则起着类似于内摩擦的作用,将所吸收的电场能量转化为热能,使电介质的温度随之升高,这样,微波场不但利用了微波使极性分子高速旋转、振动、加热,而且将微波场作为一种高频、大功率的开关电源,把直流电晕调制成有一定频率的脉冲电晕,产生了流光放电。The industrial dust removal in traditional research generally adopts the form of negative corona discharge, but what the present invention adopts is positive corona. The present invention adopts positive corona, which can achieve faster development speed, wider discharge extension range, stronger light intensity, brighter glow of corona discharge, and high-energy electrons produced under the same conditions of voltage and pole distance. Stronger and higher conversion rate of chemical reaction, at the same time, under the action of microwave field, polar molecules change from chaotic thermal motion to regular motion in the direction of electric field, interference and hindrance of intermolecular interaction force It plays a role similar to internal friction, converting the absorbed electric field energy into heat energy, and increasing the temperature of the dielectric. In this way, the microwave field not only uses microwaves to make polar molecules rotate, vibrate, and heat at high speed, but also converts As a high-frequency, high-power switching power supply, the microwave field modulates the DC corona into a pulsed corona with a certain frequency, producing streamer discharge.
本发明通过独自研发的特定脱硫收集装置,通过装置中特定部件、尺寸及参数的设置,以及所接电源电压、频率和微波场的巧妙设定,将所产生的直流电晕与微波场相结合,利用氧硫离解器中产生大功率的流光放电产生的高能电子对二氧化硫气体进行离解和促发化学反应,最终实现高效脱硫的发明目的。通过实验证明,本发明提供的脱硫收集装置可以实现流光放电功率高达2-10 kW,其脱硫效率高达98%,较现有同领域的脱硫装置相比具有显著的提高,克服了现有脱硫设备由于电源功率小、所产生的放电功率小而导致脱硫效率低、无法在工业中推广应用的难题;同时,本发明还巧妙设计硫固体聚集器,该收集器可以将解离后的气体减压降温,在静电场中电场力的作用下,将S与O分离,形成单质的硫,并通过硫固体聚集器将硫固体有效回收。由此可见,本发明不仅实现了二氧化硫气体的高效脱硫处理,而且对装置无腐蚀、能够将脱硫产生的硫固体无任何污染地聚集回收和二次利用。The present invention combines the generated DC corona with the microwave field through the specific desulfurization collection device independently developed, through the setting of specific components, dimensions and parameters in the device, and the ingenious setting of the connected power supply voltage, frequency and microwave field. The high-energy electrons generated by the high-power streamer discharge in the oxygen-sulfur dissociator are used to dissociate the sulfur dioxide gas and promote the chemical reaction, and finally realize the invention goal of efficient desulfurization. It is proved by experiments that the desulfurization collection device provided by the present invention can realize streamer discharge power as high as 2-10 kW, and its desulfurization efficiency is as high as 98%, which is significantly improved compared with the existing desulfurization devices in the same field, and overcomes the existing desulfurization equipment. Due to the small power of the power supply and the small discharge power generated, the desulfurization efficiency is low and it cannot be popularized and applied in the industry; at the same time, the invention also cleverly designs the sulfur solid collector, which can reduce the decompression of the dissociated gas Cool down, under the action of the electric field force in the electrostatic field, S and O are separated to form elemental sulfur, and the sulfur solid is effectively recovered through the sulfur solid collector. It can be seen that the present invention not only realizes the efficient desulfurization treatment of sulfur dioxide gas, but also has no corrosion to the device, and can gather, recycle and recycle the sulfur solids produced by desulfurization without any pollution.
此外,本发明采用直流基压与微波交流叠加而成,节省了开关元件及复杂的电路,交流频率即为微波频率915 MHz,频率高流光放电的效率就高。将发射微波的磁控管作为电源,它的生产、应用技术十分成熟,工业用微波磁控管的功率从5 kW-100 kW、有的一个几百kW,元件少电路简单,优势明显;另外,微波场本身还具有催化剂的作用,微波分解反应的活化能为18 kJ/mol,远低于常规的热化学反应的活化能,可增加脱硫效果,采用微波场产生流光放电,可谓一举两得。本发明采用干法烟气脱硫,不采用喷雾器装置、干燥器、吸收剂等,装置简单无腐蚀,回收的产物单质硫可作为工业原料广泛应用。In addition, the present invention adopts the superposition of DC base voltage and microwave AC, which saves switching elements and complex circuits. The AC frequency is the microwave frequency of 915 MHz, and the higher the frequency, the higher the efficiency of streamer discharge. The magnetron that emits microwaves is used as the power supply. Its production and application technologies are very mature. The power of industrial microwave magnetrons ranges from 5 kW to 100 kW, and some have hundreds of kW. The components are few and the circuit is simple, and the advantages are obvious; , The microwave field itself also acts as a catalyst. The activation energy of the microwave decomposition reaction is 18 kJ/mol, which is much lower than that of the conventional thermochemical reaction, which can increase the desulfurization effect. Using the microwave field to generate streamer discharge can kill two birds with one stone. The invention adopts dry flue gas desulfurization, does not use sprayer device, drier, absorbent, etc., the device is simple and corrosion-free, and the recovered product elemental sulfur can be widely used as industrial raw material.
本发明提供的所述脱硫收集装置相配套的工艺方法,其步骤简单,操作容易,维护方便,工作效率高,能够高效地实现高功率流光放电高效脱除废气中SO2的目的,而且能够很好地回收固体硫,无二次污染,可重复利用。可见,本发明提供的方法与传统脱硫方法相比,是一种简单、经济、低能耗、高效率的脱硫新方法。The process method matched with the desulfurization collection device provided by the present invention has simple steps, easy operation, convenient maintenance, high work efficiency, and can efficiently realize the purpose of high - power streamer discharge to efficiently remove SO2 in exhaust gas, and can be easily Good recovery of solid sulfur, no secondary pollution, reusable. It can be seen that, compared with the traditional desulfurization method, the method provided by the present invention is a new desulfurization method that is simple, economical, low in energy consumption and high in efficiency.
本发明提供的装置结构简单、造价低、维护成本低、安装简单、所用电压低、使用安全性高、能耗低、脱硫效率高;提供的方法科学合理、步骤简单、操作性好,可以高效完成脱硫过程,避免了副产物存在二次污染的可能,较现有脱硫技术相比具有显著的优越性。The device provided by the invention has the advantages of simple structure, low cost, low maintenance cost, simple installation, low voltage used, high safety in use, low energy consumption, and high desulfurization efficiency; the method provided is scientific and reasonable, with simple steps, good operability, and high efficiency Completing the desulfurization process avoids the possibility of secondary pollution by by-products, and has significant advantages over existing desulfurization technologies.
附图说明Description of drawings
图1是本发明脱除收集装置的结构示意图。Figure 1 is a schematic structural view of the removal and collection device of the present invention.
图2是图1的A-A向剖视图。Fig. 2 is a sectional view taken along line A-A of Fig. 1 .
图3是微波谐振腔的电场分布图。Figure 3 is a diagram of the electric field distribution of the microwave resonator.
图4是图3的B-B向的电场分布图。FIG. 4 is an electric field distribution diagram in the B-B direction of FIG. 3 .
图中:1、氧硫离解器,2、硫固体聚集器,3、变径接头,4、离解电晕线,5、进气口,6、微波屏蔽罩,7、微波谐振腔,8、微波发生器,9、绝缘子,10、筒子电极,11、金属通风管,12、绝缘密封盖,13、冷却液,14、外套筒。In the figure: 1. Oxygen-sulfur dissociator, 2. Sulfur solid concentrator, 3. Reducing joint, 4. Dissociation corona wire, 5. Air inlet, 6. Microwave shielding cover, 7. Microwave resonant cavity, 8. Microwave generator, 9, insulator, 10, bobbin electrode, 11, metal ventilation pipe, 12, insulating sealing cover, 13, cooling liquid, 14, outer sleeve.
具体实施方式detailed description
下面实施例用于进一步详细说明本发明,但不以任何形式限制本发明。The following examples are used to further describe the present invention in detail, but do not limit the present invention in any form.
实施例1Example 1
如图1所示,本实施例提供的二氧化硫气体的脱除收集装置,主要包括氧硫离解器1和硫固体聚集器2;二者通过变径接头3连为一体组成一种能够实现流光放电解离二氧化硫气体并收集固体硫的新装置。As shown in Figure 1, the device for removing and collecting sulfur dioxide gas provided in this embodiment mainly includes an oxygen-sulfur dissociator 1 and a sulfur solid collector 2; New device for electrolysis of sulfur dioxide gas and collection of solid sulfur.
其氧硫离解器1包括圆筒状的微波谐振腔7、绝缘子9、离解电晕线4、微波发生器8以及微波屏蔽罩6。微波屏蔽罩6分别安装在微波谐振腔7的上、下两端,在微波屏蔽罩7的内侧的上、下端中心位置处分别固定设置有1个绝缘子9,离解电晕线4固定安装在两个绝缘子9之间,且保证离解电晕线4位于圆筒状微波谐振腔7的几何中心处;微波发生器8安装在微波谐振腔7的腔体的侧壁上;其微波发生器包括一个磁控管和波导管,其频率为915MHz,磁控管通过波导管向微波谐振腔7中发射微波场。其中离解电晕线4接电源的正极,微波谐振腔7接电源的负极,在氧硫离解器1的下端设有含二氧化硫烟气的进气口5。离解电晕线4和微波谐振腔7所接电源为高压直流电或者脉冲直流电,其起晕电压为5-40 kV,如果为高压直流电源,其电压为5-50kV;如果为脉冲直流电源,其电压为5-50 kV、频率为10-15kHz。The oxygen-sulfur dissociator 1 includes a cylindrical microwave resonant cavity 7 , an insulator 9 , a dissociation corona wire 4 , a microwave generator 8 and a microwave shield 6 . The microwave shielding cover 6 is respectively installed on the upper and lower ends of the microwave resonant cavity 7, and an insulator 9 is fixedly arranged at the upper and lower center positions of the inner side of the microwave shielding cover 7, and the dissociated corona wire 4 is fixedly installed on the two ends. between two insulators 9, and ensure that the dissociated corona wire 4 is located at the geometric center of the cylindrical microwave resonator 7; the microwave generator 8 is installed on the side wall of the cavity of the microwave resonator 7; its microwave generator includes a The frequency of the magnetron and the waveguide is 915 MHz, and the magnetron emits a microwave field into the microwave resonant cavity 7 through the waveguide. Wherein the dissociation corona wire 4 is connected to the positive pole of the power supply, the microwave resonant cavity 7 is connected to the negative pole of the power supply, and the lower end of the oxygen-sulfur dissociator 1 is provided with an air inlet 5 containing sulfur dioxide flue gas. The power supply connected to the dissociation corona wire 4 and the microwave resonator 7 is high-voltage direct current or pulsed direct current, and its corona inception voltage is 5-40 kV. If it is a high-voltage direct-current power supply, its voltage is 5-50 kV; if it is a pulsed direct-current power supply, its The voltage is 5-50 kV and the frequency is 10-15kHz.
其上述的微波谐振腔7的直径需设置为30-90cm,离解电晕线4的半径为0.5-1.5mm;其上述的绝缘子9的材料为陶瓷;离解电晕线4为钨丝或不锈钢丝;微波屏蔽罩6为带有小孔的金属板或不锈钢金属网;微波谐振腔7为不锈钢材料制成。The diameter of the above-mentioned microwave resonant cavity 7 needs to be set to 30-90cm, and the radius of the dissociated corona wire 4 is 0.5-1.5mm; the material of the above-mentioned insulator 9 is ceramic; the dissociated corona wire 4 is tungsten wire or stainless steel wire ; The microwave shield 6 is a metal plate with small holes or a stainless steel mesh; the microwave resonator 7 is made of stainless steel.
如图1和2所示,其硫固体聚集器2包括外套筒14、筒子电极10、金属通风管11以及设置在外套筒14上部绝缘密封盖12。其横截面呈圆形的筒子电极10为5-7个,可均匀排布设置在外套筒14内,每个筒子电极10中心处设置有一个金属通风管11,金属通风管11的上端穿出并高于绝缘密封盖12,金属通风管11与筒子电极10相互绝缘且分别接直流电源的正极和负极,其直流电源的电压为4-20kV,外套筒14内壁与筒子电极10的外壁之间形成可以用于装循环冷却液13的空腔。As shown in FIGS. 1 and 2 , the sulfur solid collector 2 includes an outer sleeve 14 , a bobbin electrode 10 , a metal ventilation pipe 11 and an insulating sealing cover 12 arranged on the upper part of the outer sleeve 14 . There are 5-7 bobbin electrodes 10 with a circular cross section, which can be evenly arranged in the outer sleeve 14. A metal ventilation pipe 11 is arranged at the center of each bobbin electrode 10, and the upper end of the metal ventilation pipe 11 passes through And higher than the insulating sealing cover 12, the metal ventilation pipe 11 and the bobbin electrode 10 are insulated from each other and respectively connected to the positive pole and the negative pole of the DC power supply. The voltage of the DC power supply is 4-20kV. A cavity that can be used to hold circulating cooling fluid 13 is formed between them.
本发明中外套筒14的直径是微波谐振腔7直径的1.5-2.5倍,外套筒14的容积应为微波谐振腔7容积的3-5倍。The diameter of the outer sleeve 14 in the present invention is 1.5-2.5 times of the diameter of the microwave resonant cavity 7, and the volume of the outer sleeve 14 should be 3-5 times of the volume of the microwave resonant cavity 7.
根据上述装置的结构特征组装制备二氧化硫气体的脱除收集装置,在脱硫时,按照以下步骤操作:According to the structural features of the above-mentioned device, assemble and prepare the removal and collection device for sulfur dioxide gas. When desulfurization, follow the steps below:
(1)在筒子电极10的内壁上涂覆有一层1mm厚的单质硫(硫磺);将硫放置在一个金属容器内,使硫均匀加入,当温度达到120℃左右的熔点时,硫将熔融成具有流动性质的液体硫,此时可将硫涂在筒子电极10的内壁上,这样能够更好的诱导解离后的硫原子吸附在筒子电极10的内壁上,便于回收利用;(1) A layer of elemental sulfur (sulfur) with a thickness of 1mm is coated on the inner wall of the bobbin electrode 10; place the sulfur in a metal container to add sulfur evenly, and when the temperature reaches the melting point of about 120°C, the sulfur will melt Become liquid sulfur with flowing properties, at this time, sulfur can be coated on the inner wall of the bobbin electrode 10, so that the dissociated sulfur atoms can be better induced to adsorb on the inner wall of the bobbin electrode 10, which is convenient for recycling;
(2)分别接通氧硫离解器1和硫固体聚集器2的电源,在氧硫离解器1接通电源的同时启动微波发生器;连接氧硫离解器的电源为高压直流电源或脉冲直流电源,其起晕电压为5 kV -40 kV,若为高压直流电源,其电压为5 kV -50 kV;若为脉冲直流电源,其电压为5kV -50 kV、频率为10-15kHz;连接硫固体聚集器2的电源为直流电源,其电压为4 kV -20kV;(2) Turn on the power of the oxygen-sulfur dissociator 1 and the sulfur solid concentrator 2 respectively, and start the microwave generator at the same time when the oxygen-sulfur dissociator 1 is powered on; the power supply connected to the oxygen-sulfur dissociator is a high-voltage DC power supply or pulsed DC Power supply, its corona inception voltage is 5 kV -40 kV, if it is a high voltage DC power supply, its voltage is 5 kV -50 kV; if it is a pulsed DC power supply, its voltage is 5kV -50 kV, and its frequency is 10-15kHz; The power supply of the solid collector 2 is a DC power supply, and its voltage is 4 kV-20kV;
操作中,当向离解电晕线4和微波谐振腔7间加入直流高压电或脉冲直流电,微波谐振腔体与离解电晕线间将产生电晕;这时再将微波引入,利用微波场中电场和磁场正弦周期转换的特点,使微波产生的电场与电晕场叠加,增加了微波谐振腔内的电场强度,将电晕放电过程转化成化学效应较高的流光放电,而当微波场中的电场转换为磁场时,微波电场与电晕场叠加效应结束,流光放电停止。这样就会在微波谐振腔内产生与微波频率相关频率的脉冲流光放电,利用流光放电的高能电子将二氧化硫气体处理成离子态的硫与氧,因为在微波场中,电场和磁场是以正弦周期转换的,假设电场是正半个周期,则磁场是负半个周期。In operation, when DC high voltage or pulsed DC is added between the dissociation corona wire 4 and the microwave resonator 7, a corona will be generated between the microwave resonator body and the dissociation corona wire; The characteristics of the sinusoidal periodic conversion of the electric field and the magnetic field make the electric field generated by the microwave superimpose with the corona field, increase the electric field intensity in the microwave resonant cavity, and convert the corona discharge process into a streamer discharge with high chemical effect, and when the microwave field When the electric field in the medium is converted into a magnetic field, the superposition effect of the microwave electric field and the corona field ends, and the streamer discharge stops. In this way, a pulsed streamer discharge with a frequency related to the microwave frequency will be generated in the microwave resonator cavity, and the high-energy electrons of the streamer discharge will be used to process the sulfur dioxide gas into ionic sulfur and oxygen, because in the microwave field, the electric field and magnetic field are in a sinusoidal cycle Converted, assuming that the electric field is a positive half cycle, the magnetic field is a negative half cycle.
在负半个周期时,当二氧化硫气体进入微波谐振腔内,此时电晕场仍旧产生电晕,在曲率半径很小的电极附近,由于局部电场强度超过气体的电离场强,气体发生电离和激励,出现电晕等离子体。等离子体中的自由电子能量分布在2-20eV范围,而一般电子轰击气体分子,发生离解和电离所需电子能量是在5-15eV范围内,因此电晕放电可以离解部分SO2,但效率有限。SO2是极性分子,在微波场中,无论那个周期,都随着微波的频率而来回转动,使分子间相互碰撞摩擦,吸收了微波的能量而使温度升高,增大了气体分子的碰撞频率,导致气体激发、电离,最终发生击穿,产生等离子体。在微波场中,高能电子能量为3-10eV,微波能量相对较小,其能量离解SO2的效果及其有限。但是,微波具有催化剂的作用,微波分解反应的活化能为18kJ/mol,远低于常规的热化学反应的活化能。In the negative half cycle, when the sulfur dioxide gas enters the microwave resonant cavity, the corona field still generates corona at this time, and near the electrode with a small curvature radius, because the local electric field strength exceeds the ionization field strength of the gas, the gas is ionized and Excited, corona plasma appears. The energy distribution of free electrons in plasma is in the range of 2-20eV, while the electron energy required for dissociation and ionization of general electron bombardment gas molecules is in the range of 5-15eV, so corona discharge can dissociate part of SO 2 , but the efficiency is limited . SO 2 is a polar molecule. In the microwave field, regardless of the period, it rotates back and forth with the frequency of the microwave, causing the molecules to collide and rub each other, absorbing the energy of the microwave to increase the temperature and increase the density of the gas molecules. The collision frequency causes the gas to be excited, ionized, and finally breakdown to generate plasma. In the microwave field, the energy of high-energy electrons is 3-10eV , and the microwave energy is relatively small, and the effect of its energy dissociation SO2 is extremely limited. However, microwave has the function of catalyst, and the activation energy of microwave decomposition reaction is 18kJ/mol, which is far lower than that of conventional thermochemical reaction.
在正半个周期,此时微波的电场与电晕场叠加时,会在正、负电极间产生流光放电,此时的二氧化硫气体在前一个周期的(微波加热与电晕等离子体的碰撞)“预热”,自身能量已经得到提高,这时又受到流光放电,高能电子与气体分子发生非弹性碰撞,使气体分子发生电离,生成电子和强氧化性自由基,形成了一种高度电离的气体,电子通过电场获得能量,这些高能电子的能量可达到10-12eV,在运动过程中会与谐振腔内的分子、电子等粒子发生碰撞,所携带能量一部分转化为粒子动能,使碰撞后的粒子再去碰撞其他粒子,维持放电的继续;另一部分能量则转化为粒子内能,导致粒子发生电离、激发、离解,转变为活性物质,发生一系列化学反应,最终产生生成物和反应热;In the positive half cycle, when the microwave electric field and the corona field are superimposed, a streamer discharge will be generated between the positive and negative electrodes. "Preheating", its own energy has been improved, and at this time it is discharged by the streamer, the high-energy electrons collide with the gas molecules inelastically, ionize the gas molecules, generate electrons and strong oxidizing free radicals, and form a highly ionized Gas, electrons obtain energy through the electric field, and the energy of these high-energy electrons can reach 10-12eV. During the movement, they will collide with molecules, electrons and other particles in the resonant cavity, and part of the energy carried is converted into kinetic energy of the particles. The particles then collide with other particles to maintain the continuation of the discharge; another part of the energy is converted into the internal energy of the particles, causing the particles to ionize, excite, dissociate, and transform into active substances, a series of chemical reactions occur, and finally produce products and reaction heat;
(3)通过引风机将含有二氧化硫的烟气引入所述氧硫离解器1下端的进风口5中,控制烟气流速在(0.4~2.5)/s范围,所述为微波发生器产生微波的波长,烟气中含二氧化硫的密度为1.0-2.5kg/m3,烟气温度为150-250℃,使烟气中的二氧化硫在氧硫离解器1中流光放电的作用下离解为硫原子和氧负离子;(3) Introduce the flue gas containing sulfur dioxide into the air inlet 5 at the lower end of the oxygen-sulfur dissociator 1 through the induced draft fan, and control the flue gas flow rate at (0.4-2.5) /s range, the The wavelength of the microwave generated by the microwave generator, the density of sulfur dioxide in the flue gas is 1.0-2.5kg/m 3 , the temperature of the flue gas is 150-250°C, so that the sulfur dioxide in the flue gas is discharged in the oxygen-sulfur dissociator 1 Under the action, it dissociates into sulfur atoms and oxygen negative ions;
根据孙斌等著《SO2的等离子体解离及其反应途径研究》一文(化学式中带*的电子是高能电子):According to the article "Study on the Plasma Dissociation and Reaction Pathway of SO 2 " by Sun Bin et al. (The electrons with * in the chemical formula are high-energy electrons):
一个O2分子分裂为两个O原子需要的离解能是5.12eV,SO2的离解能为5.65eV,所以微波的电场与电晕场叠加时产生流光放电,其高能电子能量足以打开气体O2、SO2等分子的化学键,从而实现硫、氧离解;The dissociation energy required to split an O 2 molecule into two O atoms is 5.12eV, and the dissociation energy of SO 2 is 5.65eV, so when the electric field of the microwave and the corona field are superimposed, a streamer discharge is generated, and its high-energy electron energy is enough to open the gas O 2 , SO 2 and other molecular chemical bonds, so as to realize the dissociation of sulfur and oxygen;
(4)解离后的硫原子和氧负离子进入硫固体聚集器2中,由于筒子电极10和金属通风管11施加了直流高压电,筒子电极10与金属通风管11之间构成一个静电场;且硫原子和氧负离子在进入硫固体聚集器中,通过减压降温,在静电场中电场力和晶核吸附的作用下,S原子与O负离子分别向晶核、正电极金属通风管运动并聚集,S原子与O离子开始分离;氧负离子在正极金属通风管上释放电荷,生成氧原子,氧原子和器壁或其他原子碰撞后就会两两结合生成氧气,经排气孔排出。(4) The dissociated sulfur atoms and negative oxygen ions enter the sulfur solid concentrator 2, and since the bobbin electrode 10 and the metal ventilation pipe 11 apply DC high voltage, an electrostatic field is formed between the bobbin electrode 10 and the metal ventilation pipe 11 ; and sulfur atoms and oxygen negative ions enter the sulfur solid collector, through decompression and cooling, under the action of electric field force and crystal nucleus adsorption in the electrostatic field, S atoms and O negative ions move to the crystal nucleus and the positive electrode metal ventilation pipe respectively And gather, S atoms and O ions begin to separate; Oxygen negative ions release charges on the positive metal ventilation tube to generate oxygen atoms. After the oxygen atoms collide with the wall or other atoms, they will combine to generate oxygen, which will be discharged through the vent hole.
收集历程具体如下(M为其他气体分子或器壁):The collection process is as follows (M is other gas molecules or walls):
硫原子两两结合生成S2,压降和温降导致硫在气体中的溶解度降低,随着温度和压力的降低,气态硫(S2)开始发生液化,硫以S2、S4、S6、S8混合体形式存在,当温度低于159℃时,硫表面发生非均相反应,硫固化成S8环状结构,并形成稳定的附聚体(所谓附聚,就是在范德华力、自粘力、附着力以及毛细管力和物质之间的紧密接触而形成的表面张力等力的作用下,微粒物质自发和定向的连结在一起的现象)。硫在晶核吸引力的作用下向筒子内壁移动,附着在晶核上并结晶,即生成不溶性硫磺。Sulfur atoms combine in pairs to form S 2 , pressure drop and temperature drop cause the solubility of sulfur in the gas to decrease. As the temperature and pressure decrease, gaseous sulfur (S 2 ) begins to liquefy . 6. S 8 exists in the form of a mixture. When the temperature is lower than 159°C, a heterogeneous reaction occurs on the surface of sulfur, and the sulfur solidifies into a S 8 ring structure and forms a stable agglomerate (the so-called agglomeration refers to the process of van der Waals force , Self-adhesive force, adhesion force, capillary force and surface tension formed by the close contact between substances, the phenomenon that particulate matter is spontaneously and directionally linked together). Sulfur moves to the inner wall of the cylinder under the action of the attractive force of the crystal nucleus, attaches to the crystal nucleus and crystallizes to form insoluble sulfur.
收集S的历程具体如下:The process of collecting S is as follows:
每根金属通风管11排出的气体,经汇总、检测,可直接排放或进入下一道工序。在筒子内壁聚集的不溶性硫磺,可定期收集。The gas discharged from each metal ventilation pipe 11 can be discharged directly or enter the next process after being collected and tested. The insoluble sulfur accumulated on the inner wall of the cylinder can be collected periodically.
同时,在收集过程中调节硫固体聚集器2中循环冷却液13的流速,使筒子电极10内的温度控制在80-100℃,硫原子在电场力和筒子电极内壁硫晶核吸附的作用下向筒子电极10内壁聚集,氧负离子经过碰撞后两两结合生成氧气,通过金属通风管11排出,筒子电极10内壁聚集的硫单质回收即可。操作过程中控制筒子电极10的温度为80-100℃范围之内,其主要是由于温度过高时,筒子电极10的内壁上涂的硫膜易软化脱落,温度过低则易产生“结露”,影响硫的结晶,此外筒子电极10可设计成两个半筒的形式,便于取出结晶硫。At the same time, during the collection process, adjust the flow rate of the circulating cooling liquid 13 in the sulfur solid collector 2, so that the temperature in the bobbin electrode 10 is controlled at 80-100°C, and the sulfur atoms are adsorbed by the electric field force and the sulfur crystal nucleus on the inner wall of the bobbin electrode. Accumulate to the inner wall of the bobbin electrode 10, and the oxygen negative ions combine in pairs after collision to generate oxygen, which is discharged through the metal ventilation pipe 11, and the sulfur element accumulated on the inner wall of the bobbin electrode 10 can be recovered. During the operation, the temperature of the package electrode 10 is controlled within the range of 80-100°C. The main reason is that when the temperature is too high, the sulfur film coated on the inner wall of the package electrode 10 is easy to soften and fall off, and if the temperature is too low, it is easy to produce "condensation". ", which affects the crystallization of sulfur, and in addition, the tube electrode 10 can be designed in the form of two half tubes, which is convenient for taking out crystalline sulfur.
实际应用中,该装置可以将微波谐振腔7的直径设置为32cm,高度为80cm,体积约为64300 cm3,离解电晕线4的半径为1mm,离解电晕线4距离微波谐振腔7的距离16cm,微波发生器8的频率为915MHz;外套筒14的内径设置为68cm,高度为70cm,体积约为254100 cm3;外套筒14内均匀设置有7个内径为22cm的横截面为圆形的筒子电极10;在外套筒14和筒子电极10之间装有循环冷却液13,冷却液13首选软化水;起晕电压约为23kV,所施加在氧硫离解器1上的直流电压为25kV,所施加在硫固体聚集器2上的直流电压为10kV左右,所处理的烟气密度为1.3 kg/m3左右,烟气温度为150-250℃之间,烟气流速为小于或等于0.164 m/s,,按照上述脱硫方法接通电源,通入烟气,其微波谐振腔7中产生流光放电,微波谐振腔7沿中心线纵剖面电场分布如图3所示,其图3中B-B横剖面电场分布如图4所示。由公知技术客户自,通过如下公式计算:In practical applications, the device can set the diameter of the microwave resonator 7 to 32 cm, the height to 80 cm, the volume to be about 64300 cm 3 , the radius of the dissociated corona wire 4 to be 1 mm, and the distance between the dissociated corona wire 4 and the microwave resonator 7 The distance is 16cm, and the frequency of microwave generator 8 is 915MHz; the inner diameter of outer sleeve 14 is set to 68cm, the height is 70cm, and the volume is about 254100 cm Circular bobbin electrode 10; a circulating cooling liquid 13 is installed between the outer sleeve 14 and the bobbin electrode 10, and the cooling liquid 13 is preferably demineralized water; is 25kV, the DC voltage applied to the sulfur solid collector 2 is about 10kV, the density of the treated flue gas is about 1.3 kg/m 3 , the flue gas temperature is between 150-250°C, and the flue gas flow rate is less than or It is equal to 0.164 m/s. According to the above-mentioned desulfurization method, the power is turned on, and the flue gas is introduced, and streamer discharge is generated in the microwave resonant cavity 7. The electric field distribution of the microwave resonant cavity 7 along the longitudinal section of the center line is shown in Figure 3. Figure 3 The electric field distribution in the middle BB cross section is shown in Fig. 4. From known technical customers, it is calculated by the following formula:
其中V为微波振谐腔的体积,能量利用率取=75%;W 0:一次流光放电能量(0.3mJ);氧硫离解器的高度为H1,直径为D1,v0为烟气流速,将烟气流速控制在(0.4~2.5)λ/s,v为流光速度(约为2×105m/s)。Where V is the volume of the microwave resonator, and the energy utilization rate is taken as =75%; W 0 : energy of a streamer discharge (0.3mJ); the height of the oxygen-sulfur dissociator is H 1 , the diameter is D 1 , v 0 is the flue gas flow rate, and the flue gas flow rate is controlled at (0.4~2.5)λ /s, v is the streamer speed (about 2×10 5 m/s).
通过计算结果显示,在该应用中单位体积烟气能耗约为17.86kJ/m3~25.44kJ/m3,其微波场贡献约为60%、电晕场贡献约为40%,其流光放电功率高达2-10 kW,其脱硫效率高达98%。The calculation results show that in this application, the energy consumption per unit volume of flue gas is about 17.86kJ/m 3 ~ 25.44kJ/m 3 , the microwave field contributes about 60%, the corona field contributes about 40%, and the streamer discharge The power is as high as 2-10 kW, and its desulfurization efficiency is as high as 98%.
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