CN1297781C - Method for treating solid organic waste substance using high frequency plasma - Google Patents
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Abstract
本发明提供了一种利用高频等离子体处理固体有机废弃物的方法,其特征是包括了由双级等离子体区构成的喷动床。该方法步骤包括在低压条件下产生第一等离子体区和第二等离子体区,由第一等离子体区和第二等离子体区构成一种喷动床,主要采用水蒸气为等离子体工作气体,并且将固体物料供给第二等离子体区。该发明克服了现有技术的局限性,具有良好的运行稳定性和连续性,能够处理大颗粒和块状固体物料,并且能够高效率地获得有价值的合成气。
The invention provides a method for treating solid organic waste with high-frequency plasma, which is characterized in that it includes a spouted bed composed of two-stage plasma regions. The method steps include generating a first plasma region and a second plasma region under low pressure conditions, a spouted bed is formed by the first plasma region and the second plasma region, water vapor is mainly used as a plasma working gas, And the solid material is supplied to the second plasma region. The invention overcomes the limitations of the prior art, has good operation stability and continuity, can handle large particles and massive solid materials, and can obtain valuable syngas with high efficiency.
Description
技术领域technical field
本发明涉及固体废弃物处理技术领域,特别是利用电学范畴的高频等离子体热解气化固体有机废弃物的技术。The invention relates to the technical field of solid waste treatment, in particular to the technology of pyrolysis and gasification of solid organic waste using high-frequency plasma in the electrical category.
背景技术Background technique
固体有机废弃物包括城市生活垃圾、高分子废弃物如塑料、橡胶、以及某些农林业生产废弃物和工业废弃物等。近年来国民经济发展迅速,固体有机废弃物产生量大为增加,2000年我国废旧塑料的产生量达370万吨,废橡胶达85万吨,引起日益严重的“白色污染”、“黑色污染”等问题。当前国内外有关固体废弃物的处理技术主要以填埋、焚烧、机械或者化学回收为主。例如,目前我国有小部分废塑料经过回收进行再生利用,但多数再生制品档次低,市场需求不大。大部分垃圾中的废弃塑料制品仍然与垃圾一起按填埋处理,由于塑料重量轻、体积大,填埋占地多,塑料大分子不能自行降解,长期不腐烂,不仅浪费资源,而且破坏土地,污染地下水。焚烧处理法有较好的减容、减量效果,但废塑料焚烧常产生大量含有毒污染物的烟气,引起严重的空气污染。近来,化学回收法例如废塑料催化裂解制汽油、柴油的方法也受到人们很大的重视。废塑料裂解制油需要在压力0.2-0.5MPa、温度500-800℃和催化剂作用条件下进行,废塑料原料在催化剂和热的作用下,通过热裂解反应和催化裂解反应,碳氢元素组成的高分子材料向低分子燃油转化,经分馏冷凝后获得类似汽油、柴油的产物。目前废塑料裂解制油技术的主要问题是产品质量难以控制达到生成符合国家标准的汽油和柴油的目的,催化剂的反应效果差、出油率低、耗能高。Solid organic waste includes municipal solid waste, polymer waste such as plastic, rubber, and some agricultural and forestry production waste and industrial waste. In recent years, the national economy has developed rapidly, and the amount of solid organic waste has increased greatly. In 2000, the amount of waste plastics in my country reached 3.7 million tons, and waste rubber reached 850,000 tons, causing increasingly serious "white pollution" and "black pollution". And other issues. At present, the treatment technologies for solid waste at home and abroad are mainly landfill, incineration, mechanical or chemical recycling. For example, at present, a small part of waste plastics in my country has been recycled for recycling, but most of the recycled products are of low grade and the market demand is not large. Most of the discarded plastic products in the garbage are still treated as landfills together with the garbage. Due to the light weight and large volume of plastics, landfills occupy a lot of land, and plastic macromolecules cannot degrade by themselves and will not rot for a long time. This not only wastes resources, but also destroys land. Pollution of ground water. The incineration treatment method has good volume reduction and volume reduction effects, but the incineration of waste plastics often produces a large amount of smoke containing toxic pollutants, causing serious air pollution. Recently, chemical recycling methods such as catalytic cracking of waste plastics to produce gasoline and diesel have also received great attention. Waste plastic cracking to oil needs to be carried out under the conditions of pressure 0.2-0.5MPa, temperature 500-800°C and catalyst action. Under the action of catalyst and heat, waste plastic raw materials undergo thermal cracking reaction and catalytic cracking reaction, and the carbon and hydrogen elements are composed of The high molecular material is converted into low molecular fuel oil, and after fractional distillation and condensation, products similar to gasoline and diesel are obtained. The main problem of the current waste plastic pyrolysis technology is that it is difficult to control the product quality to produce gasoline and diesel oil that meet the national standards, the reaction effect of the catalyst is poor, the oil yield is low, and the energy consumption is high.
等离子体是被激发电离气体,由带负电的粒子如电子、带正电的粒子如正离子和中性粒子如原子等组成,电离气体内正负电荷数相等,其总体保持电中性,并具有导电性。等离子体能够提供一个能量集中、温度很高的反应环境,不仅可大幅度提高化学反应速率,而且产生其它反应体系下难以发生的化学反应,因此最近等离子体技术逐渐应用于许多工业领域如化工、冶金、电子、能源、材料等。在能源与环保方面,固体废弃物的等离子体热解气化技术也有较多报道。Plasma is an excited ionized gas, which is composed of negatively charged particles such as electrons, positively charged particles such as positive ions, and neutral particles such as atoms. The number of positive and negative charges in the ionized gas is equal, and its overall charge neutrality remains Conductive. Plasma can provide a reaction environment with concentrated energy and high temperature, which can not only greatly increase the chemical reaction rate, but also produce chemical reactions that are difficult to occur in other reaction systems. Therefore, plasma technology has been gradually applied to many industrial fields such as chemical industry, Metallurgy, electronics, energy, materials, etc. In terms of energy and environmental protection, there are many reports on the plasma pyrolysis gasification technology of solid waste.
利用直流电弧等离子体处理固体有机废弃物的技术可见于中国专利01129931和02250661等。通常在直流电弧等离子体发生器中工作气体被电离成高温等离子体,并喷射入等离子体气化反应器形成3000-10000K高温环境;固体有机废弃物经螺旋进料器被载气携带喷入等离子体气化反应器热解区,形成大量活性离子存在的高温反应环境;固体有机废弃物在反应器高温区进行快速热解气化反应,生成有回收利用价值的化学合成气。目前应用直流电弧等离子体处理固体有机废弃物有一些技术上的局限性,例如:(1)直流电弧放电为大电流强放电,电极容易烧蚀、寿命短,当使用惰性气体(Ar,He)、还原性气体(H2)或者中性气体(N2)作为工作气体时,电极寿命一般为600小时;当使用氧化性气体(O2,空气,H2O),电极寿命仅有200小时左右。(2)直流电弧等离子体温度高达3000-10000K,反应器壁材料难以长时间承受。(3)固体物料只能在等离子体射流的下游引入,难以进入等离子体中心区,等离子体气化反应器采用载流床形式,反应物的停留时间短(0.2~2ms),导致热解气化不完全。The technology of using DC arc plasma to treat solid organic waste can be found in Chinese patents 01129931 and 02250661. Usually, the working gas is ionized into high-temperature plasma in the DC arc plasma generator, and injected into the plasma gasification reactor to form a high-temperature environment of 3000-10000K; solid organic waste is carried by the carrier gas through the screw feeder and injected into the plasma The pyrolysis zone of the solid gasification reactor forms a high-temperature reaction environment in which a large number of active ions exist; solid organic waste undergoes rapid pyrolysis and gasification reactions in the high-temperature zone of the reactor to generate chemical synthesis gas with recycling value. At present, the application of DC arc plasma to treat solid organic waste has some technical limitations, for example: (1) DC arc discharge is a large current and strong discharge, the electrode is easy to ablate, and the service life is short. When using inert gas (Ar, He) , reducing gas (H 2 ) or neutral gas (N 2 ) as the working gas, the electrode life is generally 600 hours; when using oxidizing gas (O 2 , air, H 2 O), the electrode life is only 200 hours about. (2) The DC arc plasma temperature is as high as 3000-10000K, and the reactor wall material is difficult to withstand for a long time. (3) Solid materials can only be introduced in the downstream of the plasma jet, and it is difficult to enter the central area of the plasma. The plasma gasification reactor adopts the form of a flow-filled bed, and the residence time of the reactants is short (0.2~2ms), resulting in pyrolysis gas incomplete.
利用高频等离子体处理固体有机废弃物的技术则以中国专利93102963为代表。高频等离子体是依靠高频耦合无极放电产生等离子体的,根据耦合方式的不同,高频等离子体分为容性耦合等离子体和感性耦合等离子体,如果等离子体中的能量耦合是主要由射频天线/电极的电压产生的(静止电荷)产生的,该耦合方式为容性耦合,产生的等离子体为容性耦合等离子体(CCP);如果等离子体中的能量耦合是主要由射频天线/电极的磁场产生的(运动电荷)产生的,对应的耦合方式为感性耦合,所产生的等离子体为感性耦合等离子体(ICP)。高频等离子体具有多方面的优越性,例如:(1)其它等离子体炬必须使用惰性气体作为工作气体以防烧蚀电极,而高频等离子体可在空气或氧气条件下工作,大大节约了运行成本。(2)高频等离子体区域较大,气流速度小,易于中心供粉,粉末在高温区的停留时间较长,等离子体炬有很长的高温射流尾焰。(3)由于高频电流的趋肤效应,高频等离子体可呈环状,载气能在等离子体中心形成一个通道,固体粉末在环状高温等离子体作用下迅速分解。The technology of using high-frequency plasma to treat solid organic waste is represented by Chinese patent 93102963. High-frequency plasma is generated by high-frequency coupling electrodeless discharge. According to different coupling methods, high-frequency plasma is divided into capacitively coupled plasma and inductively coupled plasma. If the energy coupling in the plasma is mainly composed of radio frequency Generated by the voltage of the antenna/electrode (static charge), the coupling method is capacitive coupling, and the generated plasma is capacitively coupled plasma (CCP); if the energy coupling in the plasma is mainly caused by the radio frequency antenna/electrode Generated by the magnetic field (moving charge), the corresponding coupling method is inductive coupling, and the generated plasma is inductively coupled plasma (ICP). High-frequency plasma has many advantages, such as: (1) Other plasma torches must use inert gas as the working gas to prevent ablation of electrodes, while high-frequency plasma can work under air or oxygen conditions, which greatly saves Operating costs. (2) The high-frequency plasma area is large, the air velocity is small, and it is easy to supply powder at the center. The powder stays in the high-temperature area for a long time, and the plasma torch has a long high-temperature jet tail flame. (3) Due to the skin effect of the high-frequency current, the high-frequency plasma can be in the form of a ring, and the carrier gas can form a channel in the center of the plasma, and the solid powder can be rapidly decomposed under the action of the ring-shaped high-temperature plasma.
中国专利93102963提出的无极等离子体喷射装置主要用于离解有害废料,采用了射频等离子体喷管激励自由电子,废料与可控自由电子源相结合,利用电子、分子所产生的碰撞和紫外线辐射,使得自由电子能够离解废料,成为可安全排放,对环境无害的简单化合物。尤其是离解过程采用非加热方式,依靠受激电子的键裂解作用,废料的离解程度受自由电子密度和温度以及废料在等离子体中的停留时间的影响,电子密度能够通过运载气体的流量进行控制,改变射频功率能够对温度进行控制。发明者曾提出该装置可以扩大到射频功率MW级,处理废料速率500kg/h规模使用。但其有待改善的主要问题是:(1)大气压下操作的射频等离子体喷管温度仍然偏高,需要外加水冷却。(2)射频等离子喷管对外界干扰敏感,当增大固体物料供给量时,等离子体不稳定而容易熄弧。(3)处理的固体物料必须为粉末状,而大颗粒、块状物料难以处理。The infinite plasma injection device proposed in Chinese patent 93102963 is mainly used to dissociate harmful wastes. A radio frequency plasma nozzle is used to excite free electrons. The waste materials are combined with a controllable free electron source, and the collision and ultraviolet radiation generated by electrons and molecules are used. Enabling free electrons to dissociate waste materials into simple compounds that can be safely discharged and are not harmful to the environment. In particular, the dissociation process adopts a non-heating method and relies on the bond cracking effect of excited electrons. The degree of dissociation of the waste is affected by the density and temperature of the free electrons and the residence time of the waste in the plasma. The electron density can be controlled by the flow rate of the carrier gas. , changing the RF power can control the temperature. The inventor once proposed that the device can be expanded to the MW level of radio frequency power, and the waste processing rate can be used on a scale of 500kg/h. However, the main problems to be improved are: (1) The temperature of the radio frequency plasma nozzle operated under the atmospheric pressure is still relatively high, and additional water cooling is required. (2) The radio frequency plasma nozzle is sensitive to external interference. When the supply of solid material is increased, the plasma is unstable and the arc is easily extinguished. (3) The solid material to be processed must be in the form of powder, while large particles and blocky materials are difficult to handle.
发明内容Contents of the invention
本发明的目的是克服现有技术的局限性,提供一种利用高频等离子体热解气化固体有机废弃物的方法,具有良好的运行稳定性和连续性,能够处理大颗粒和块状固体物料,并且能够高效率地获得有价值的合成气。The purpose of the present invention is to overcome the limitations of the prior art and provide a method for pyrolysis and gasification of solid organic waste using high-frequency plasma, which has good operational stability and continuity, and can handle large particles and massive solids materials, and can efficiently obtain valuable syngas.
首先,高频等离子体状态参数(如电子密度、电子温度、气体温度)受操作压力的影响很大,若放电在接近大气压的高气压条件下进行,则电子、离子、中性粒子会通过激烈碰撞而充分交换能量,从而使等离子体达到或接近热平衡状态;反之,数百帕或者数千帕低气压等离子体常常处于非热平衡状态,此时,气体粒子数密度低,电子与离子或中性粒子的碰撞几率很小,电子温度与重粒子温度的差别较大,其电子温度可高达上万度,而重粒子温度只有几百度。我们的实验结果显示:对于内径30mm的射频等离子体炬管,当炬管内工作气体压力为50Pa(绝对压力)时,等离子体点火所需高频功率为50W,用热电偶测得温度为150℃;气体压力为3000Pa时,点火功率为700W,热电偶测得温度为500℃;气体压力为5000-10000Pa时,点火功率约为1-2kW,温度为1000-1500℃。利用高频等离子体热解气化固体有机废弃物如塑料、橡胶时,较佳的操作压力为5000-10000Pa,温度为1000-1500℃。First of all, high-frequency plasma state parameters (such as electron density, electron temperature, and gas temperature) are greatly affected by operating pressure. If the discharge is carried out under high-pressure conditions close to atmospheric pressure, electrons, ions, and neutral particles will pass through the intense Collisions fully exchange energy, so that the plasma reaches or is close to a thermal equilibrium state; on the contrary, hundreds of Pa or thousands of Pa low-pressure plasmas are often in a non-thermal equilibrium state. At this time, the number density of gas particles is low, and electrons and ions or neutral The collision probability of particles is very small, and the difference between the temperature of electrons and the temperature of heavy particles is relatively large. The temperature of electrons can be as high as tens of thousands of degrees, while the temperature of heavy particles is only a few hundred degrees. Our experimental results show that: for a radio frequency plasma torch with an inner diameter of 30mm, when the working gas pressure in the torch is 50Pa (absolute pressure), the high-frequency power required for plasma ignition is 50W, and the temperature measured by a thermocouple is 150°C When the gas pressure is 3000Pa, the ignition power is 700W, and the temperature measured by the thermocouple is 500°C; when the gas pressure is 5000-10000Pa, the ignition power is about 1-2kW, and the temperature is 1000-1500°C. When using high-frequency plasma to pyrolyze and gasify solid organic wastes such as plastics and rubber, the preferred operating pressure is 5000-10000Pa and the temperature is 1000-1500°C.
第二,关于高频等离子体稳定性问题,主要是等离子体工作气体与被处理固体物料性质的差别对于高频能量耦合过程的影响所引起的。本专利采用如下所述的双级等离子体以改善高频等离子体稳定性:(1)使用较小直径的第一等离子体炬管,内通等离子体工作气体,通过第一电感耦合线圈产生第一等离子体区,其高温射流尾焰由第一等离子体炬管出口进入第二等离子体区。(2)使用较大直径的第二等离子体炬管,在第一等离子体炬管高温射流尾焰的辅助作用下,通过第二电感耦合线圈产生第二等离子体区。(3)固体物料供给第二等离子体区,并在等离子体高温反应氛围中热解气化。在上述双级等离子体中,第一等离子体区不受固体物料影响,易于保持稳定操作;当第二等离子体区受固体物料供给的影响,出现不稳定情况时,由于第一等离子体炬管高温射流尾焰含有高能电子、离子、激发原子、分子和自由基等各种活性粒子,在第二电感耦合线圈的共同作用下可以保持第二等离子体炬管不容易熄弧。Second, regarding the stability of high-frequency plasma, it is mainly caused by the influence of the difference between the properties of the plasma working gas and the processed solid material on the high-frequency energy coupling process. This patent adopts the following two-stage plasma to improve the stability of high-frequency plasma: (1) use the first plasma torch with a smaller diameter, the plasma working gas is passed through inside, and the first inductive coupling coil is used to generate the first plasma torch. A plasma area, the high-temperature jet tail flame enters the second plasma area from the outlet of the first plasma torch. (2) Using a second plasma torch with a larger diameter, with the assistance of the high-temperature jet tail flame of the first plasma torch, a second plasma region is generated through a second inductively coupled coil. (3) The solid material is supplied to the second plasma area, and is pyrolyzed and gasified in the plasma high-temperature reaction atmosphere. In the above two-stage plasma, the first plasma region is not affected by solid materials, and it is easy to maintain stable operation; when the second plasma region is affected by the supply of solid materials and becomes unstable, due to the first plasma torch The high-temperature jet plume contains various active particles such as high-energy electrons, ions, excited atoms, molecules, and free radicals. Under the joint action of the second inductively coupled coil, the second plasma torch can not be easily extinguished.
第三,为了处理大颗粒和块状固体物料,第一等离子体区和第二等离子体区构成一种喷动床形式,方法如下:在第二等离子体区下部配置半锥型布风板,半锥型布风板底部连接第一等离子体炬管出口,第一等离子体炬管高温射流尾焰成为第二等离子体区喷动床的中心喷动气流,半锥型布风板上对应的第二等离子体的那部分区域成为喷动床的向下回流区;固体物料供给第二等离子体区后,将被中心喷动气流夹带而向上喷动,然后粗大颗粒由于重力作用从射流中分离出来,返回向下回流区,再进入下一喷动循环。这样,大颗粒和块状固体物料在喷动床有足够的停留时间,直至完成热解气化反应,成为小颗粒灰分,随气流到达除灰系统。Third, in order to deal with large particles and massive solid materials, the first plasma zone and the second plasma zone form a spouted bed form, the method is as follows: a semi-conical air distribution plate is arranged at the lower part of the second plasma zone, The bottom of the semi-conical air distribution plate is connected to the outlet of the first plasma torch, and the high-temperature jet tail flame of the first plasma torch becomes the central jet flow of the spouted bed in the second plasma area, and the corresponding part of the semi-conical air distribution plate The part of the second plasma area becomes the downward recirculation area of the spouted bed; after the solid material is supplied to the second plasma area, it will be entrained by the central jet flow and spray upward, and then the coarse particles will be separated from the jet due to gravity out, return to the downflow area, and then enter the next injection cycle. In this way, large particles and massive solid materials have sufficient residence time in the spouted bed until the pyrolysis and gasification reaction is completed, and become small particle ash, which reaches the ash removal system with the airflow.
第四,为了充分利用固体废物的有机组分制取合成气,等离子体工作气体可以采用过热水蒸气、或者过热水蒸气与空气、氧气或者其它气体的混合物。水蒸气、氧气在高频等离子体作用下离解为O、OH自由基,因此在本方法中,固体废物的热解气化反应本质上是氧化反应性质的。等离子体含有的高能电子、离子等活性粒子对于高分子有机物也有键裂解作用。固体废物的有机组分与过热水蒸气反应制取合成气的总包反应式为:
基于以上要点,本专利提出一种利用高频等离子体处理固体有机废弃物的方法,由以下步骤构成:Based on the above points, this patent proposes a method for treating solid organic waste using high-frequency plasma, which consists of the following steps:
(1)在低压条件下,通过第一电感耦合线圈产生第一等离子体区,其高温射流尾焰进入第二等离子体区;(1) Under low pressure conditions, the first plasma region is generated by the first inductively coupled coil, and its high-temperature jet tail flame enters the second plasma region;
(2)第一等离子体高温射流尾焰的辅助作用下,通过第二电感耦合线圈产生第二等离子体区;(2) Under the auxiliary effect of the first plasma high-temperature jet tail flame, the second plasma region is generated through the second inductively coupled coil;
(3)第一等离子体区和第二等离子体区构成一种喷动床,其中第一等离子体高温射流尾焰为第二等离子体区的中心喷动气流,第二等离子体的其它区域为喷动床的向下回流区;(3) The first plasma region and the second plasma region constitute a spouted bed, wherein the high-temperature jet tail flame of the first plasma is the central jet flow of the second plasma region, and the other regions of the second plasma are Downward recirculation zone of the spouted bed;
(4)固体物料供给第二等离子体区,在等离子体作用下完成热解气化反应。(4) The solid material is supplied to the second plasma area, and the pyrolysis and gasification reaction is completed under the action of the plasma.
其中,第一等离子体区和第二等离子体区较佳的操作压力为5000-10000Pa,温度为1000-1500℃;等离子体工作气体采用过热水蒸气、或者过热水蒸气与空气、氧气的混合物或者其它气体及其混合物。Among them, the preferred operating pressure of the first plasma region and the second plasma region is 5000-10000Pa, and the temperature is 1000-1500°C; the plasma working gas adopts superheated steam, or superheated steam and air, oxygen Mixtures or other gases and their mixtures.
与现有技术相比较,本发明有以下突出优点:(1)由于采用低压操作条件,高频等离子体温度可以控制在1500℃以下,使用常规材料(如铸造陶瓷)即可制造等离子体反应器,并且有利于装置的长时间连续运行。(2)由于采用双级等离子体,高频等离子体稳定性得到了很大改善,等离子体点火过程也更为容易。(3)由于采用喷动床形式,大颗粒和块状固体物料也能够得到处理。(4)等离子体工作气体主要采用水蒸气,有利于从固体废物的有机组分制取合成气。Compared with the prior art, the present invention has the following outstanding advantages: (1) Due to the low-pressure operating conditions, the high-frequency plasma temperature can be controlled below 1500 ° C, and the plasma reactor can be manufactured using conventional materials (such as cast ceramics) , and is conducive to long-term continuous operation of the device. (2) Due to the use of dual-stage plasma, the stability of high-frequency plasma has been greatly improved, and the plasma ignition process is also easier. (3) Due to the spouted bed form, large particles and massive solid materials can also be processed. (4) The plasma working gas mainly uses water vapor, which is beneficial to the preparation of synthesis gas from the organic components of solid waste.
附图说明Description of drawings
以下结合附图对本专利的实质内容进一步详细说明。Below in conjunction with accompanying drawing, the substantive content of this patent is described in further detail.
图一是本专利实施例示意图。图中:1,第一等离子体区,2,第二等离子体区,3,第一电感耦合线圈,4,第一等离子体炬管,5,半锥型布风板,6,第二电感耦合线圈,7,第二等离子体炬管,8,水蒸气发生器,9,螺旋进料器,10,料仓,11,第一匹配网络,12,第一晶控RF高频电源,13,第二匹配网络,14,第二晶控RF高频电源,15,除灰系统,16,灰仓,17,抽气系统。Figure 1 is a schematic diagram of an embodiment of this patent. In the figure: 1, the first plasma area, 2, the second plasma area, 3, the first inductively coupled coil, 4, the first plasma torch, 5, the semi-conical air distribution plate, 6, the second inductance Coupling coil, 7, second plasma torch, 8, steam generator, 9, screw feeder, 10, feed bin, 11, first matching network, 12, first crystal-controlled RF high-frequency power supply, 13 , the second matching network, 14, the second crystal-controlled RF high-frequency power supply, 15, the ash removal system, 16, the ash bin, 17, the air extraction system.
具体实施方式Detailed ways
实施例一Embodiment one
如图一所示,水蒸气发生器(8)产生过热水蒸气,经计量和调节后提供给第一等离子体区(1),同时过热水蒸气通过均匀分布有多个系列进风小孔的半锥型布风板(5)提供给第二等离子体区(2);第一晶控RF高频电源(12)的型号为JG-2K-B,输出功率0-2kW,输出频率为工业专用高频13.56MHz;第一匹配网络(11)型号为JG-2KW,配备正向功率计和反向功率计;第一电感耦合线圈(3)用铜管绕制,并且成螺旋状环绕在用耐高温陶瓷铸造成的第一等离子体炬管(4)外壁;第二晶控RF高频电源(14)型号为JG-10K-B,输出功率0-10kW,频率13.56MHz,以及第二匹配网络(13)型号为JG-10KW,配备正向功率计和反向功率计;第二电感耦合线圈(6)用铜管绕制,并且成螺旋状环绕在用耐高温陶瓷铸造成的第二等离子体炬管(7)外壁;抽气系统(17)为水环式真空泵,抽气速率12L/s,极限压力4000Pa,经过除灰系统(15)抽取等离子体反应器气体,使得第一等离子体区和第二等离子体区压力约为5000Pa;启动第一晶控RF高频电源(12),调节第一匹配网络(11),使得第一等离子体区(1)起辉;然后启动第二晶控RF高频电源(14),调节第二匹配网络(13),使得第二等离子体区(2)起辉;调节晶控RF高频电源(12,14)输出功率以及匹配网络(11,13),使得第一等离子体区和第二等离子体区温度达1000℃以上;启动螺旋进料器(9),将储存于料仓(10)的聚丙烯PP塑料颗粒加入等离子体反应器,在等离子体高温作用下,聚丙烯PP塑料颗粒热解气化,气体经过除灰系统(15)和抽气系统(17)排出,气体取样后用色谱分析,主要成分有H2、CO、CH4、C2H4、C2H2、CO2、C2H6、C3H6、C3H8等,气体热值约22MJ/Nm3,适合用作化工合成气、原料气或者燃料气等。灰仓(16)可收集到极少量的灰分。As shown in Figure 1, the water steam generator (8) generates superheated steam, which is supplied to the first plasma area (1) after metering and adjustment. The semi-conical air distribution plate (5) of the hole is provided to the second plasma area (2); the model of the first crystal-controlled RF high-frequency power supply (12) is JG-2K-B, the output power is 0-2kW, and the output frequency It is a high-frequency 13.56MHz dedicated to industry; the first matching network (11) is JG-2KW, equipped with a forward power meter and a reverse power meter; the first inductive coupling coil (3) is wound with a copper tube and is in a spiral shape Surrounded by the outer wall of the first plasma torch (4) cast from high-temperature-resistant ceramics; the second crystal-controlled RF high-frequency power supply (14) is JG-10K-B, with an output power of 0-10kW and a frequency of 13.56MHz, and The model of the second matching network (13) is JG-10KW, and it is equipped with a forward power meter and a reverse power meter; the second inductive coupling coil (6) is wound with a copper tube, and is wound in a spiral shape and is casted with high temperature resistant ceramics. The outer wall of the second plasma torch (7); the pumping system (17) is a water ring vacuum pump, the pumping rate is 12L/s, and the ultimate pressure is 4000Pa, and the plasma reactor gas is extracted through the ash removal system (15), so that The pressure of the first plasma region and the second plasma region is about 5000Pa; start the first crystal-controlled RF high-frequency power supply (12), adjust the first matching network (11), so that the first plasma region (1) glows; Then start the second crystal-controlled RF high-frequency power supply (14), adjust the second matching network (13), so that the second plasma region (2) glows; adjust the crystal-controlled RF high-frequency power supply (12,14) output power and matching network (11, 13), so that the temperature of the first plasma zone and the second plasma zone reaches above 1000°C; start the screw feeder (9), and add the polypropylene PP plastic particles stored in the silo (10) Plasma reactor, under the high temperature of plasma, polypropylene PP plastic particles are pyrolyzed and gasified, and the gas is discharged through the ash removal system (15) and the exhaust system (17). The gas is sampled and analyzed by chromatography. The main components are H 2. CO, CH 4 , C 2 H 4 , C 2 H 2 , CO 2 , C 2 H 6 , C 3 H 6 , C 3 H 8 , etc., the gas calorific value is about 22MJ/Nm 3 , suitable for chemical synthesis gas, raw material gas or fuel gas, etc. The ash bin (16) can collect a very small amount of ash.
实施例二Embodiment two
与实施例一相同,调节抽气系统(17),使得第一等离子体区和第二等离子体区压力约为10000Pa;调节晶控RF高频电源(12,14)输出功率以及匹配网络(11,13),使得第一等离子体区和第二等离子体区温度约为1300℃;聚丙烯PP塑料颗粒热解气化,气体取样后用色谱分析,主要成分种类与实施例一相同。Same as embodiment one, adjust the pumping system (17), so that the pressure of the first plasma region and the second plasma region is about 10000Pa; adjust the output power of the crystal-controlled RF high-frequency power supply (12,14) and the matching network (11 , 13), so that the temperature of the first plasma region and the second plasma region is about 1300 ° C; polypropylene PP plastic particles are pyrolyzed and gasified, and the gas is sampled and analyzed by chromatography. The main components are the same as in Example 1.
实施例三Embodiment Three
与实施例一相同,当固体物料进料为废轮胎粉碎颗粒,产气主要成分有H2、CO、CH4、C2H4、C2H2、CO2、C2H6、C3H6、C3H8等、以及硫化氢H2S,气体热值约20MJ/Nm3。灰仓(16)可收集到固体产物,即热解碳黑,其元素分析为:85%C,0.5%H,12%O,0.4%N,1.9%S;工业分析其灰分为16.2%,热值28500kJ/kg,BET比表面积70m2/g;扫描电镜分析(SEM)表明热解碳黑颗粒形成一种原生粒子聚集体结构,大小为50-2000μm;光电子能谱分析(XPS)显示热解碳黑中的碳主要以石墨结构碳存在,硫的形态与FeS2和ZnS类似;核磁共振波谱分析(NMR)表明热解碳黑的主体化学性质为芳香碳C=C键结构。因此,这些固体产物可用作工业半补强碳黑,还可以经过进一步处理后作为活性炭使用。Same as Example 1, when the solid material feed is waste tire crushed particles, the main components of gas production are H 2 , CO, CH 4 , C 2 H 4 , C 2 H 2 , CO 2 , C 2 H 6 , C 3 H 6 , C 3 H 8 , etc., and hydrogen sulfide H 2 S, the gas calorific value is about 20MJ/Nm 3 . Ash bin (16) can collect solid product, i.e. pyrolysis carbon black, and its elemental analysis is: 85%C, 0.5%H, 12%O, 0.4%N, 1.9%S; Its ash of industrial analysis is 16.2%, Calorific value is 28500kJ/kg, BET specific surface area is 70m 2 /g; scanning electron microscope analysis (SEM) shows that pyrolytic carbon black particles form a primary particle aggregate structure with a size of 50-2000μm; photoelectron spectroscopy (XPS) shows that thermal The carbon in pyrolysis carbon black mainly exists as graphite structure carbon, and the form of sulfur is similar to FeS2 and ZnS; nuclear magnetic resonance spectroscopy (NMR) shows that the main chemical property of pyrolysis carbon black is aromatic carbon C=C bond structure. Therefore, these solid products can be used as industrial semi-reinforcing carbon black and can also be used as activated carbon after further processing.
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| CN2469328Y (en) * | 2001-04-23 | 2002-01-02 | 王忠义 | Plasma incineration furnace for special garbage |
| CN1425873A (en) * | 2001-12-11 | 2003-06-25 | 北京机电研究所 | Plasma high temperature processing process and equipment for refuses |
| JP2003336818A (en) * | 2002-05-17 | 2003-11-28 | Hitachi Zosen Corp | Waste pyrolysis furnace equipment |
| CN2593067Y (en) * | 2002-12-26 | 2003-12-17 | 中国科学院广州能源研究所 | Plasma pyrolytic gasifying apparatus for polymeric rejected material |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE102022209215A1 (en) | 2022-09-05 | 2024-03-07 | Sms Group Gmbh | Process for processing plastic waste using plasmalysis |
| WO2024052056A1 (en) | 2022-09-05 | 2024-03-14 | Sms Group Gmbh | Method for the preparation of plastic waste by means of plasmalysis |
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| CN1683828A (en) | 2005-10-19 |
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