[go: up one dir, main page]

CN201567310U - A biomass spiral pyrolysis device - Google Patents

A biomass spiral pyrolysis device Download PDF

Info

Publication number
CN201567310U
CN201567310U CN2009201803469U CN200920180346U CN201567310U CN 201567310 U CN201567310 U CN 201567310U CN 2009201803469 U CN2009201803469 U CN 2009201803469U CN 200920180346 U CN200920180346 U CN 200920180346U CN 201567310 U CN201567310 U CN 201567310U
Authority
CN
China
Prior art keywords
pyrolysis
biomass
cylinder
bio
oil
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
CN2009201803469U
Other languages
Chinese (zh)
Inventor
江鸿
郭庆祥
俞汉青
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
University of Science and Technology of China USTC
Original Assignee
University of Science and Technology of China USTC
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by University of Science and Technology of China USTC filed Critical University of Science and Technology of China USTC
Priority to CN2009201803469U priority Critical patent/CN201567310U/en
Application granted granted Critical
Publication of CN201567310U publication Critical patent/CN201567310U/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel

Landscapes

  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Abstract

本实用新型涉及生物质热解装置。该装置由加料系统、带有外加热系统和保温系统的热解反应器及热解产品收集系统构成,该热解反应器是螺旋热解反应器,它包括一个两端由盖体密封的圆形筒体,通过两盖体的中孔支撑安装有能相对于筒体转动的转动轴,在筒体腔内的转动轴上设有作为螺旋推进器的螺旋叶片,该叶片顶端与筒体内壁面间隙配合,转动轴在筒体外的伸出端连接有变频电机;圆形筒体侧壁上分别设有生物质进料管和热解产品出口管,进料管与进料仓连通,出口管通入到焦碳收集罐中,收集罐通过出气管道依次和冷凝器、生物油收集罐、尾气排放管连通。本实用新型能精确控制生物质停留时间,分区控制热解过程的温度,使生物油成分可控,易精炼提取化学品。

Figure 200920180346

The utility model relates to a biomass pyrolysis device. The device consists of a feeding system, a pyrolysis reactor with an external heating system and a heat preservation system, and a pyrolysis product collection system. Shaped cylinder, through the middle holes of the two covers, a rotating shaft that can rotate relative to the cylinder is installed. A helical blade as a screw propeller is arranged on the rotating shaft in the cavity of the cylinder. The gap between the top of the blade and the inner wall of the cylinder is Cooperate, the extension end of the rotating shaft outside the cylinder is connected with a frequency conversion motor; the side wall of the circular cylinder is respectively provided with a biomass feed pipe and a pyrolysis product outlet pipe, the feed pipe is connected to the feed bin, and the outlet pipe is connected to the into the coke collection tank, and the collection tank is connected to the condenser, the bio-oil collection tank, and the exhaust gas discharge pipe in sequence through the gas outlet pipeline. The utility model can precisely control the residence time of the biomass, control the temperature of the pyrolysis process in different regions, make the components of the bio-oil controllable, and easily refine and extract chemicals.

Figure 200920180346

Description

一种生物质螺旋热解装置 A biomass spiral pyrolysis device

技术领域technical field

本实用新型涉及生物质的热解装置。The utility model relates to a biomass pyrolysis device.

背景技术Background technique

目前,世界各国尤其是发达国家,为实现国家经济的可持续发展提供根本保障,都在致力于开发高效、无污染的生物质能利用技术,以保护本国的矿物能源资源。生物质热解是指生物质在没有氧化剂(空气、氧气、水蒸气等)存在或只提供有限氧的条件下,加热到逾500℃,通过热化学反应将生物质大分子物质(木质素、纤维素和半纤维素)分解成较小分子的燃料物质(固态炭、可燃气、生物油)的热化学转化技术方法。生物质热解的燃料能源转化率可达95.5%,最大限度的将生物质能量转化为能源产品,物尽其用,而热解也是燃烧和气化必不可少的初始阶段At present, all countries in the world, especially developed countries, are devoting themselves to the development of highly efficient and non-polluting biomass energy utilization technologies to protect their own mineral energy resources in order to provide a fundamental guarantee for the sustainable development of the national economy. Biomass pyrolysis means that biomass is heated to more than 500°C in the absence of oxidants (air, oxygen, water vapor, etc.) or only limited oxygen is provided, and biomass macromolecules (lignin, Cellulose and hemicellulose) are decomposed into smaller molecular fuel substances (solid carbon, combustible gas, bio-oil) thermochemical conversion technology method. The fuel energy conversion rate of biomass pyrolysis can reach 95.5%, which can maximize the conversion of biomass energy into energy products and make the best use of it. Pyrolysis is also an essential initial stage of combustion and gasification

从化学反应的角度对其进行分析,生物质在热解过程中发生了复杂的热化学反应,包括分子键断裂、异构化和小分子聚合等反应。木材、林业废弃物和农作物废弃物等的主要成分是纤维素、半纤维素和木质素。热重分析结果表明,纤维素在52℃时开始热解,随着温度的升高,热解反应速度加快,到350~370℃时,分解为低分子产物。根据热解过程的温度变化和生成产物的情况等,可以分为干燥阶段、预热解阶段、固体分解阶段和煅烧阶段。干燥阶段(温度为120~150℃),生物质中的水分进行蒸发,物料的化学组成几乎不变。预热解阶段(温度为150~275℃),物料的热反应比较明显,化学组成开始变化,生物质中的不稳定成分如半纤维素分解成二氧化碳、一氧化碳和少量醋酸等物质。上述两个阶段均为吸热反应阶段。固体分解阶段(温度为275~475℃),热解的主要阶段,物料发生了各种复杂的物理、化学反应,产生大量的分解产物。生成的液体产物中含有醋酸、木焦油和甲醇(冷却时析出来);气体产物中有CO2、CO、CH4、H2等,可燃成分含量增加。这个阶段要放出大量的热。煅烧阶段(温度为450~500℃),生物质依靠外部供给的热量进行木炭的燃烧,使木炭中的挥发物质减少,固定碳含量增加,为放热阶段。实际上,上述四个阶段的界限难以明确划分,各阶段的反应过程会相互交叉进行。Analyzing it from the perspective of chemical reaction, biomass undergoes complex thermochemical reactions during the pyrolysis process, including reactions such as molecular bond breaking, isomerization, and small molecule polymerization. The main components of wood, forestry residues and agricultural crop residues are cellulose, hemicellulose and lignin. The results of thermogravimetric analysis showed that cellulose began to pyrolyze at 52°C, and as the temperature increased, the pyrolysis reaction speed increased, and at 350-370°C, it decomposed into low-molecular products. According to the temperature change and product formation during the pyrolysis process, it can be divided into drying stage, pre-pyrolysis stage, solid decomposition stage and calcination stage. In the drying stage (temperature is 120-150°C), the moisture in the biomass is evaporated, and the chemical composition of the material is almost unchanged. In the pre-pyrolysis stage (temperature is 150-275°C), the thermal reaction of the material is relatively obvious, the chemical composition begins to change, and the unstable components in the biomass such as hemicellulose decompose into carbon dioxide, carbon monoxide and a small amount of acetic acid and other substances. The above two stages are all endothermic reaction stages. In the solid decomposition stage (temperature is 275-475°C), the main stage of pyrolysis, various complex physical and chemical reactions occur in the material, and a large number of decomposition products are produced. The generated liquid products contain acetic acid, wood tar and methanol (precipitated during cooling); the gas products include CO2, CO, CH4, H2, etc., and the content of combustible components increases. This stage releases a lot of heat. In the calcination stage (the temperature is 450-500°C), the biomass relies on the heat supplied from the outside to burn the charcoal, which reduces the volatile matter in the charcoal and increases the fixed carbon content, which is the exothermic stage. In fact, it is difficult to clearly define the boundaries of the above four stages, and the reaction processes of each stage will cross each other.

从对生物质的加热速率和完成反应所用时间的角度来看,生物质热解工艺基本上可以分为两种类型:一种是慢速热解,一种是快速热解。在快速热解中,当完成反应时间甚短(<0.5s)时,又称为闪速热解。根据工艺操作条件,生物质热解工艺又可分为慢速、快速和反应性热解三种。在慢速热解工艺中又可以分为炭化和常规热解。From the perspective of the heating rate of the biomass and the time taken to complete the reaction, the biomass pyrolysis process can basically be divided into two types: one is slow pyrolysis, and the other is fast pyrolysis. In fast pyrolysis, when the reaction time is very short (<0.5s), it is also called flash pyrolysis. According to the process operating conditions, the biomass pyrolysis process can be divided into three types: slow, fast and reactive pyrolysis. In the slow pyrolysis process, it can be divided into carbonization and conventional pyrolysis.

慢速热解(又称干馏工艺、传统热解)工艺具有几千年的历史,是一种以生成木炭为目的的炭化过程,低温干馏的加热温度为500~580℃,中温干馏温度为660~750℃,高温干馏的温度为900~1100℃。将木材放在窑内,在隔绝空气的情况下加热,可以得到占原料质量30%~35%的木炭产量。Slow pyrolysis (also known as dry distillation process, traditional pyrolysis) process has a history of thousands of years. It is a carbonization process for the purpose of producing charcoal. ~750°C, and the temperature of high-temperature dry distillation is 900-1100°C. Put the wood in the kiln and heat it in the absence of air, and you can get a charcoal output accounting for 30% to 35% of the raw material mass.

快速热解是将磨细的生物质原料放在快速热解装置中,严格控制加热速率(一般大致为10~200℃/s)和反应温度(控制在500℃左右),生物质原料在缺氧的情况下,被快速加热到较高温度,从而引发大分子的分解,产生了小分子气体和可凝性挥发分以及少量焦炭产物。可凝性挥发分被快速冷却成可流动的液体,成为生物油或焦油,其比例一般可达原料质量的40%~60%。Fast pyrolysis is to place finely ground biomass raw materials in a fast pyrolysis device, and strictly control the heating rate (generally approximately 10-200°C/s) and reaction temperature (controlled at about 500°C). In the case of oxygen, it is rapidly heated to a higher temperature, thereby initiating the decomposition of macromolecules, producing small molecule gases and condensable volatiles and a small amount of coke products. The condensable volatile matter is rapidly cooled into a flowable liquid and becomes bio-oil or tar, and its proportion can generally reach 40% to 60% of the raw material mass.

与慢速热解相比,快速热解的传热反应过程发生在极短的时间内,强烈的热效应直接产生热解产物,再迅速淬冷,通常在0.5s内急冷至350℃以下,最大限度地增加了液态产物(油)。Compared with slow pyrolysis, the heat transfer reaction process of fast pyrolysis occurs in a very short time, and the strong thermal effect directly produces pyrolysis products, which are then rapidly quenched, usually to below 350°C within 0.5s, the maximum Liquid product (oil) is increased to a minimum.

总的来讲,影响热解的主要因素包括化学和物理两大方面。化学因素包括一系列复杂的一次反应和二次反应;物理因素主要是反应过程中的传热、传质以及原料的物理特性等。具体的操作条件表现为:温度、物料特性、催化剂、滞留时间、压力和升温速率。Generally speaking, the main factors affecting pyrolysis include chemical and physical aspects. Chemical factors include a series of complex primary reactions and secondary reactions; physical factors are mainly heat transfer, mass transfer and physical properties of raw materials during the reaction process. The specific operating conditions are: temperature, material characteristics, catalyst, residence time, pressure and heating rate.

在生物质热解过程中,温度是一个很重要的影响因素,它对热解产物分布、组分、产率和热解气热值都有很大的影响。生物质热解最终产物中气、油、炭各占比例的多少,随反应温度的高低和加热速度的快慢有很大差异。一般地说,低温、长期滞留的慢速热解主要用于最大限度地增加炭的产量,其质量产率和能量产率分别达到30%和50%(质量分数)。温度小于600℃的常规热解时,采用中等反应速率,生物油、不可凝气体和炭的产率基本相等;闪速热解温度在500~650℃范围内,主要用来增加生物油的产量,生物油产率可达80%(质量分数);同样的闪速热解,若温度高于700℃,在非常高的反应速率和极短的气相滞留期下,主要用于生产气体产物,其产率可达80%(质量分数)。当升温速率极快时,半纤维素和纤维素几乎不生成炭。In the process of biomass pyrolysis, temperature is a very important factor, which has a great influence on the distribution, composition, yield and calorific value of pyrolysis products. The proportion of gas, oil and charcoal in the final product of biomass pyrolysis varies greatly with the reaction temperature and heating speed. Generally speaking, low-temperature, long-term retention slow pyrolysis is mainly used to maximize the yield of char, and its mass yield and energy yield reach 30% and 50% (mass fraction), respectively. For conventional pyrolysis at a temperature lower than 600°C, medium reaction rate is adopted, and the yields of bio-oil, non-condensable gas and charcoal are basically equal; flash pyrolysis temperature is in the range of 500-650°C, which is mainly used to increase the yield of bio-oil , the bio-oil yield can reach 80% (mass fraction); the same flash pyrolysis, if the temperature is higher than 700 ° C, is mainly used to produce gaseous products at a very high reaction rate and a very short gas phase residence period. Its yield can reach 80% (mass fraction). When the heating rate is extremely fast, hemicellulose and cellulose hardly generate char.

滞留时间在生物质热解反应中有固相滞留时间和气相滞留时间之分。固相滞留时间越短,热解的固态产物所占的比例就越小,总的产物量越大,热解越完全。在给定的温度和升温速率的条件下,固相滞留时间越短,反应的转化产物中的固相产物就越少,气相产物的量就越大。气相滞留期时间一般并不影响生物质的一次裂解反应过程,而只影响到液态产物中的生物油发生的二次裂解反应的进程。当生物质热解产物中的一次产物进入围绕生物质颗粒的气相中,生物油就会发生进一步的裂化反应,在炽热的反应器中,气相滞留时间越长,生物油的二次裂解发生的就越严重,二次裂解反应增多,放出H2、CH4、CO等,导致液态产物迅速减少,气体产物增加。所以,为获得最大生物油产量,应缩短气相滞留期,使挥发产物迅速离开反应器,减少焦油二次裂解的时间。Residence time In biomass pyrolysis reaction, there are solid phase residence time and gas phase residence time. The shorter the solid phase residence time, the smaller the proportion of pyrolyzed solid products, the larger the total product amount, and the more complete the pyrolysis. Under the conditions of a given temperature and heating rate, the shorter the solid phase residence time, the less solid phase products and the greater the amount of gas phase products in the converted products of the reaction. The gas phase residence time generally does not affect the process of the primary cracking reaction of biomass, but only affects the process of the secondary cracking reaction of the bio-oil in the liquid product. When the primary products of biomass pyrolysis products enter the gas phase surrounding biomass particles, the bio-oil will undergo further cracking reactions. In the hot reactor, the longer the gas phase residence time, the secondary cracking of bio-oil will occur. The more serious, the more secondary cracking reactions, releasing H2, CH4, CO, etc., resulting in a rapid decrease in liquid products and an increase in gas products. Therefore, in order to obtain the maximum yield of bio-oil, the gas phase residence period should be shortened so that the volatile products can leave the reactor quickly and the time for the secondary cracking of tar should be reduced.

现有技术中常规热解方法是将生物质原料放在现有的热解装置中,例如流化床热解。这种热解通常是在低于600℃的中等温度及中等反应速率(0.1~1℃/s)条件下,经过几个小时的热解,得到占原料质量的20%~25%的生物质炭及30%~40%的生物油。在流化床反应器中,生物质颗粒加热到合适温度后其固体颗粒在氮气的带动下呈流化状态,生物质在1-3秒的停留时间内完成热解过程,然后被裂解的各种有机物和焦碳进入旋风分离器,焦碳分离后收集回用,气体则进入冷凝器,冷凝后即得到成分复杂的生物油。由于热解过程中生物质颗粒在流化床反应器内的停留时间无法准确控制,热解温度也难以控制,因此得到的热解产品成分复杂,无法实现热解产品即生物油成分的可控,不容易精炼提取化学品。也就是说现有热解技术得到的生物油成分和浓度是随机的。因此其得到的生物油只能作为低品位的燃料,附加值比较低,这限制了热解技术的推广。The conventional pyrolysis method in the prior art is to place the biomass raw material in an existing pyrolysis device, such as fluidized bed pyrolysis. This kind of pyrolysis is usually under the conditions of moderate temperature below 600°C and moderate reaction rate (0.1-1°C/s), after several hours of pyrolysis, biomass accounting for 20%-25% of the raw material mass is obtained Charcoal and 30% to 40% bio-oil. In the fluidized bed reactor, after the biomass particles are heated to a suitable temperature, the solid particles are in a fluidized state under the drive of nitrogen, and the biomass completes the pyrolysis process within a residence time of 1-3 seconds, and then the pyrolysis process is completed. The organic matter and coke enter the cyclone separator, the coke is separated and collected for reuse, and the gas enters the condenser, and the bio-oil with complex composition is obtained after condensation. Since the residence time of biomass particles in the fluidized bed reactor cannot be accurately controlled during the pyrolysis process, and the pyrolysis temperature is also difficult to control, the composition of the obtained pyrolysis product is complex, and the controllable composition of the pyrolysis product, namely bio-oil, cannot be realized , not easily refined to extract chemicals. That is to say, the bio-oil composition and concentration obtained by the existing pyrolysis technology are random. Therefore, the obtained bio-oil can only be used as a low-grade fuel, and the added value is relatively low, which limits the promotion of pyrolysis technology.

发明内容Contents of the invention

本实用新型的目的在于,提供一种能准确控制生物质颗粒热解时间和热解温度的螺旋热解装置,从而有效控制生物油成分和浓度,使生物质热解技术能进一步得到推广。The purpose of the utility model is to provide a spiral pyrolysis device that can accurately control the pyrolysis time and temperature of biomass particles, thereby effectively controlling the composition and concentration of bio-oil, so that the biomass pyrolysis technology can be further promoted.

本实用新型的生物质螺旋热解装置,由加料系统、热解反应器以及热解产品收集系统构成,该热解反应器带有外加热系统和保温系统,其特征在于,所述热解反应器是螺旋热解反应器,它包括一个两端由盖体密封的圆形筒体,通过两盖体的中孔支撑安装有一能相对于圆形筒体转动的转动轴,在筒体腔内的转动轴上设有作为螺旋推进器的螺旋叶片,该螺旋叶片顶端与圆形筒体内壁面间隙配合,转动轴在圆形筒体外的伸出端连接有变频电机;在圆形筒体侧壁上分别设有生物质进料管和热解产品的出口管,其进料管与进料仓连通,其出口管垂直通入到热解产品收集系统的焦碳收集罐中,在焦碳收集罐侧壁上设有一出气管道,该出气管道依次和冷凝器、生物油收集罐、尾气排放管连通。所述安装在转动轴上的螺旋推进器的螺距l满足公式 t = L l &CenterDot; n 60 , 其中,L为螺旋推进器的轴向长度,t为设定的生物质在螺旋反应器内的停留时间,通常为t=1-3秒,n为转动轴的转动速度,通常为100-400转/分。The biomass spiral pyrolysis device of the utility model is composed of a feeding system, a pyrolysis reactor and a pyrolysis product collection system. The pyrolysis reactor is equipped with an external heating system and a heat preservation system. It is characterized in that the pyrolysis reaction The device is a spiral pyrolysis reactor, which includes a circular cylinder with both ends sealed by covers, and a rotating shaft that can rotate relative to the circular cylinder is installed through the middle holes of the two covers. The rotating shaft is provided with a helical blade as a screw propeller, and the top of the helical blade is in clearance with the inner wall of the circular cylinder, and the extension end of the rotating shaft outside the circular cylinder is connected with a frequency conversion motor; The feed pipe for biomass and the outlet pipe for pyrolysis products are respectively provided. The feed pipe is connected with the feed bin, and the outlet pipe is vertically connected to the coke collection tank of the pyrolysis product collection system. In the coke collection tank A gas outlet pipe is arranged on the side wall, and the gas outlet pipe communicates with the condenser, the bio-oil collection tank and the tail gas discharge pipe in sequence. The pitch l of the screw propeller installed on the rotating shaft satisfies the formula t = L l &CenterDot; no 60 , Among them, L is the axial length of the screw propeller, t is the residence time of the set biomass in the screw reactor, usually t=1-3 seconds, n is the rotation speed of the rotating shaft, usually 100-400 rpm.

上述装置中,所述热解反应器带有的外加热系统是整体的或者是分离的可调功率的电加热板,每块电加热板设有测温的热电偶。In the above device, the external heating system of the pyrolysis reactor is an integral or separated electric heating plate with adjustable power, and each electric heating plate is provided with a thermocouple for temperature measurement.

上述装置中,所述作为螺旋推进器的螺旋叶片、圆形筒体内壁和转动轴表面均由耐腐蚀材料构成,以防止因腐蚀现象影响生物油的品质。In the above device, the helical blade as the helical propeller, the inner wall of the circular cylinder and the surface of the rotating shaft are all made of corrosion-resistant materials to prevent the quality of the bio-oil from being affected by corrosion.

利用本实用新型的螺旋热解装置对生物质进行热解的工艺过程,包括首先启动外加热系统,使螺旋热解反应器内的反应区温度稳定在500-550℃;再将生物质颗粒原料通过进口管输送进入螺旋热解反应器,其特征在于,同时启动变频电机,并根据设定的生物质在螺旋热解反应器内的停留时间t,以及螺旋推进器的轴向长度L和螺距l,使用公式 t = L l &CenterDot; n 60 , 确定变频电机的转速n,通常转动速度在100-400转/分范围内;然后启动热解产品收集系统,即可得到液体生物油和其它热解产物。所述生物质颗粒原料是被粉碎的生物质颗粒,其粒径为20-200目。The process of using the spiral pyrolysis device of the present invention to pyrolyze biomass includes first starting the external heating system to stabilize the temperature of the reaction zone in the spiral pyrolysis reactor at 500-550°C; It is transported into the spiral pyrolysis reactor through the inlet pipe, which is characterized in that the variable frequency motor is started at the same time, and according to the set residence time t of the biomass in the spiral pyrolysis reactor, as well as the axial length L and pitch of the screw propeller l, using the formula t = L l &CenterDot; no 60 , Determine the rotational speed n of the variable frequency motor, usually in the range of 100-400 rpm; then start the pyrolysis product collection system to obtain liquid bio-oil and other pyrolysis products. The biomass particle raw material is pulverized biomass particles with a particle size of 20-200 mesh.

在实际操作中,可根据得到的生物油的品质分析,然后适当调整变频电机转速,即调整生物质在螺旋反应器内的停留时间,以得到合适的生物油品质和产量。In actual operation, according to the quality analysis of the obtained bio-oil, the speed of the variable frequency motor can be adjusted appropriately, that is, the residence time of the biomass in the screw reactor can be adjusted to obtain the appropriate quality and yield of bio-oil.

所述“启动外加热系统,使螺旋热解反应器内的反应区温度稳定在500-550℃”,可以是通过控制不同的电加热板将螺旋反应器在长度方向上分成不同温区,从500℃沿着生物质运动方向逐渐升温至550℃,更有利提高生物油的产率和油品。The "starting the external heating system to stabilize the temperature of the reaction zone in the spiral pyrolysis reactor at 500-550°C" can be divided into different temperature zones in the length direction of the spiral reactor by controlling different electric heating plates, from 500°C is gradually raised to 550°C along the direction of biomass movement, which is more beneficial to improve the yield and oil quality of bio-oil.

使用本实用新型的螺旋热解装置对生物质进行热解,与现有技术相比,有两个主要优点:Using the spiral pyrolysis device of the utility model to pyrolyze biomass has two main advantages compared with the prior art:

(1)能精确的控制生物质在反应器器内的停留时间:(1) The residence time of biomass in the reactor can be precisely controlled:

生物质在流化床反应器中的停留时间一般与进料量及流化床反应器的有效容积有关,它是一个平均停留时间,由于流化床内的混合物料运动状态复杂,往往存在短路、返混与死角现象,而且由于生物质颗粒在热解过程中不断失重等,生物质个体的停留时间差异很大。因此平均停留时间无法准确反映个体停留时间。本螺旋热解反应器则完全不同,只要设计合理的螺距,避免物料打滑和反喷现象,则生物质的个体停留时间也就是平均停留时间。The residence time of biomass in the fluidized bed reactor is generally related to the amount of feed and the effective volume of the fluidized bed reactor. It is an average residence time. Due to the complex movement state of the mixed material in the fluidized bed, there is often a short circuit , back-mixing and dead angle phenomena, and due to the continuous weight loss of biomass particles during the pyrolysis process, the residence time of biomass individuals varies greatly. Therefore, the average residence time cannot accurately reflect the individual residence time. This spiral pyrolysis reactor is completely different. As long as the screw pitch is designed reasonably to avoid material slipping and back spraying, the individual residence time of biomass is also the average residence time.

从理论上讲,生物质颗粒在反应器内停留时间不同,即发生反应的时间不同,其热解生成物的成分即会有区别,也即生物油成分和浓度会有变化。本实用新型的螺旋热解装置,由于转动轴的转动速度可由变频电机调节,使得生物质颗粒的行进速度,即生物质颗粒在反应器内的停留时间能得到精确控制,(可精确到0.1秒),因此热解得到的生物油成分和浓度比较一致,这对于产品的进一步优化具有很大的优势。Theoretically speaking, the residence time of biomass particles in the reactor is different, that is, the reaction time is different, and the composition of the pyrolysis products will be different, that is, the composition and concentration of bio-oil will change. In the spiral pyrolysis device of the present utility model, since the rotational speed of the rotating shaft can be adjusted by the frequency conversion motor, the advancing speed of the biomass particles, that is, the residence time of the biomass particles in the reactor can be precisely controlled (accurate to 0.1 second) ), so the composition and concentration of the bio-oil obtained by pyrolysis are relatively consistent, which has great advantages for further optimization of the product.

(2)能分区控制热解过程的温度:(2) The temperature of the pyrolysis process can be controlled in different regions:

根据热解原理,生物质在不同温区热解可以提高生物油的产率和油品。因为在生物质热解过程中,温度是一个很重要的影响因素,它对热解产物分布、组分、产率和热解气热值都有很大的影响。生物质热解最终产物中气、油、炭各占比例的多少,随反应温度的高低和加热速度的快慢有很大差异。一般地说,低温、长期滞留的慢速热解主要用于最大限度地增加炭的产量,其质量产率和能量产率分别达到30%和50%(质量分数)。如果温度小于600℃的常规热解时、并采用中等反应速率,则生物油、不可凝气体和炭的产率基本相等;如果采用闪速热解温度在500~650℃范围内,可以增加生物油的产量,生物油产率可高达80%(质量分数);同样的闪速热解,若温度高于700℃,在非常高的反应速率和极短的气相滞留期下,会增加气体产物产出,其产率可达80%(质量分数)。According to the principle of pyrolysis, pyrolysis of biomass in different temperature zones can improve the yield and oil quality of bio-oil. Because in the process of biomass pyrolysis, temperature is a very important factor, which has a great influence on the distribution, composition, yield and calorific value of pyrolysis products. The proportion of gas, oil and charcoal in the final product of biomass pyrolysis varies greatly with the reaction temperature and heating speed. Generally speaking, low-temperature, long-term retention slow pyrolysis is mainly used to maximize the yield of char, and its mass yield and energy yield reach 30% and 50% (mass fraction), respectively. If the conventional pyrolysis temperature is less than 600°C and the medium reaction rate is adopted, the yields of bio-oil, non-condensable gas and charcoal are basically equal; if the flash pyrolysis temperature is in the range of 500-650°C, the biological The yield of oil, the bio-oil yield can be as high as 80% (mass fraction); the same flash pyrolysis, if the temperature is higher than 700 ° C, at a very high reaction rate and a very short gas phase residence period, the gas product will increase Output, its productive rate can reach 80% (mass fraction).

流化床热解反应器尽管可以采用电加热,也可以采用热电偶分区控制,但由于流化床内物料处于流化状态,往往会出现返混现象,热量对流传递,使得反应器内的温度较均匀分布,很难通过热电偶控制温度分区。本螺旋热解反应器中不存在流化和返混现象,热量传递完全靠热传导方式,因此传热速率小,便于温度控制,这有利于产品的优化。Although the fluidized bed pyrolysis reactor can be heated by electricity, it can also be controlled by thermocouple partitions, but because the material in the fluidized bed is in a fluidized state, back-mixing often occurs, and the heat is convectively transferred, making the temperature in the reactor More uniform distribution, it is difficult to control the temperature partition by thermocouple. There is no fluidization and back-mixing phenomenon in the spiral pyrolysis reactor, and the heat transfer is entirely by heat conduction, so the heat transfer rate is small, which is convenient for temperature control, which is conducive to product optimization.

本实用新型通过螺旋热解装置直接将生物质热解生成生物油,不仅便于储存运输,而且生物油成分可控,易精炼提取化学品。The utility model directly pyrolyzes biomass to generate bio-oil through a spiral pyrolysis device, which is not only convenient for storage and transportation, but also has controllable components of bio-oil, and is easy to refine and extract chemicals.

下面通过实施例和附图对本实用新型作进一步描述。Below by embodiment and accompanying drawing, the utility model will be further described.

附图说明Description of drawings

图1是本实用新型的螺旋热解装置的实施例示意图。Fig. 1 is a schematic diagram of an embodiment of a spiral pyrolysis device of the present invention.

具体实施方式Detailed ways

实施例1Example 1

参见图1,园筒形反应器的筒体5的一头为法兰盘状,起保温作用的外套筒6的两端也为法兰盘状,筒体5和外套筒6相互套在一起,加上左右两端盖4、11和螺纹连接件构或一个整体,外套筒6的内壁与筒体5的外壁间有足够大的间隙,四块电加热板8设置在此间隙中,并包围在筒体5的外壁面上。该电加热板为4×1KW的可调功率的电加热板,分别由四个热电偶9控制,达到设定温度后,自动减小加热功率,因此能有效控制反应器内的反应温度在一定的范围内(500-550℃)。四个热电偶独立控制四个加热板,可以实现螺旋反应器内有四个不同温区,以实现在圆形筒体长度方向上不同温度的需要。热电偶9的一端与筒体5的外壁面接触,另一端穿过外套筒到达外部空间,接仪表以方便观察。生物质进料管7设置在靠近左端的上方,其轴线与筒体5垂直,出口管12设置在靠近右端的下方,其轴线也与筒体5垂直。在左右两端盖4、11的中轴孔中通过轴承支撑有转动轴3,并有耐高温密封圈1密封。变频电机2与转动轴3左端连接,使转动轴3能跟随电机主轴一起转动,该变频电机的转速在100-400转/分范围内可调。在转动轴的被包容在筒体内腔部分安装有作为螺旋推进器的螺旋叶片10,螺旋叶片顶端与筒体内壁面间隙配合。本实施例选择筒体内径为52毫米,叶片外径50毫米,转动轴直径为30毫米;螺旋推进部分的长度240毫米,设定生物质停留时间在1-3秒内,根据上述有关公式计算得到螺距为16-48毫米,本实施例选择螺距为30毫米,并选用了螺旋推进器常用的螺旋角15°。出口管12通入到下方的焦碳收集罐13中,然后由出气管道14与冷凝器15、生物油收集罐16和尾气排放管17连接成整体。Referring to Fig. 1, one end of the cylinder body 5 of the cylindrical reactor is flange-shaped, and the two ends of the outer sleeve 6, which plays a role in heat preservation, are also flange-shaped, and the cylinder body 5 and the outer sleeve 6 are sheathed on each other. Together, plus the left and right end covers 4, 11 and the threaded connector structure or a whole, there is a large enough gap between the inner wall of the outer sleeve 6 and the outer wall of the cylinder 5, and four electric heating plates 8 are arranged in this gap , and surround the outer wall of the cylinder 5. The electric heating plate is a 4×1KW electric heating plate with adjustable power, which is controlled by four thermocouples 9 respectively. After reaching the set temperature, the heating power is automatically reduced, so the reaction temperature in the reactor can be effectively controlled at a certain temperature. range (500-550°C). Four thermocouples independently control four heating plates, so that there are four different temperature zones in the spiral reactor, so as to meet the needs of different temperatures in the length direction of the circular cylinder. One end of the thermocouple 9 is in contact with the outer wall of the cylinder 5, and the other end passes through the outer sleeve to reach the outer space, and is connected to a meter for convenient observation. The biomass feed pipe 7 is arranged above the left end, its axis is perpendicular to the cylinder 5 , and the outlet pipe 12 is arranged below the right end, its axis is also perpendicular to the cylinder 5 . In the axis holes of the left and right end covers 4, 11, a rotating shaft 3 is supported by a bearing, and a high temperature resistant sealing ring 1 is arranged for sealing. The variable frequency motor 2 is connected with the left end of the rotating shaft 3, so that the rotating shaft 3 can rotate together with the motor main shaft, and the rotating speed of the variable frequency motor is adjustable in the range of 100-400 rpm. A helical blade 10 as a screw propeller is installed on the part of the rotating shaft that is contained in the inner cavity of the cylinder, and the tip of the helical blade is in clearance fit with the inner wall surface of the cylinder. In this embodiment, the internal diameter of the cylinder is selected to be 52 millimeters, the outer diameter of the blade is 50 millimeters, and the diameter of the rotating shaft is 30 millimeters; the length of the screw propulsion part is 240 millimeters, and the residence time of biomass is set within 1-3 seconds, calculated according to the above-mentioned relevant formula Obtaining pitch is 16-48 millimeter, and present embodiment selects pitch to be 30 millimeters, and has selected the common helix angle of screw propeller 15 ° for use. The outlet pipe 12 leads into the coke collection tank 13 below, and then is connected as a whole with the condenser 15, the bio-oil collection tank 16 and the tail gas discharge pipe 17 by the gas outlet pipe 14.

本实施例中,所述作为螺旋推进装置的螺旋叶片、园筒形反应器和转动轴均由不锈钢材料制造。所述变频电机由市场购得,型号为CHF100-1R5G-4(INVT ELECTRIC CO.LTD)In this embodiment, the helical blades as the helical propulsion device, the cylindrical reactor and the rotating shaft are all made of stainless steel. The frequency conversion motor is purchased from the market, the model is CHF100-1R5G-4 (INVT ELECTRIC CO.LTD)

下面利用上述装置进行实际应用并测试有关数据。Next, use the above-mentioned device for practical application and test relevant data.

生物质原料是木屑,被粉碎后的粒径约为40-80目。首先将电加热板加热到设定的温度:四个热电偶从左至右分别分别设定为500℃,520℃,530℃,550℃,反应器内实际温度会有少许变动。然后将生物质原料从进料器加入到螺旋热解反应器的进料口中,同时启动变频电机,并开通冷凝器和尾气排放系统。调节转动轴以300转/分的转速转动,即生物质原料在反应器内的停留时间1.6秒。生物质在反应器内迅速产生热解,其产品为有机物分子气体和固体焦碳,螺旋推进装置将焦碳推出经出口管到焦碳收集罐中,气体经出口管并从焦碳收集罐的出气口进入冷凝器,冷凝后得到生物油进入生物油收集罐,其余尾气从尾气排放管5排出。The biomass raw material is sawdust, and the particle size after crushing is about 40-80 mesh. First, heat the electric heating plate to the set temperature: the four thermocouples are respectively set to 500°C, 520°C, 530°C, and 550°C from left to right, and the actual temperature in the reactor will vary slightly. Then feed the biomass raw material from the feeder to the feed port of the spiral pyrolysis reactor, start the frequency conversion motor at the same time, and open the condenser and tail gas discharge system. Adjust the rotating shaft to rotate at a rotational speed of 300 rpm, that is, the residence time of the biomass raw material in the reactor is 1.6 seconds. Biomass pyrolyzes rapidly in the reactor, and its products are organic molecular gas and solid coke. The screw propulsion device pushes the coke out through the outlet pipe into the coke collection tank, and the gas passes through the outlet pipe and is released from the coke collection tank. The gas outlet enters the condenser, and the bio-oil obtained after condensation enters the bio-oil collection tank, and the rest of the tail gas is discharged from the tail gas discharge pipe 5 .

具体的反应条件和有关检测数据如下:Concrete reaction conditions and relevant detection data are as follows:

生物质原料的进入流量为18公斤/小时,得到的生物油产量8.6公斤/小时。The incoming flow rate of the biomass feedstock was 18 kg/h, resulting in a bio-oil production of 8.6 kg/h.

初步检测分析显示,得到的生物油含水率<30%,高位热值为21MJ/kg。Preliminary detection and analysis show that the water content of the obtained bio-oil is less than 30%, and the high calorific value is 21MJ/kg.

与现有技术中的流化床热解得到的生物油相比,本螺旋热解的生物油中苯酚类含量比流化床热解提高40%左右,含量大于1%的有机物达到22种,使用通常流化床的只有10-15种。Compared with the bio-oil obtained by fluidized bed pyrolysis in the prior art, the content of phenols in the bio-oil obtained by spiral pyrolysis is about 40% higher than that of fluidized bed pyrolysis, and the organic matter with a content greater than 1% reaches 22 kinds, There are only 10-15 kinds of common fluidized beds.

Claims (3)

1. biomass screw pyrolysis installation, by charging system, pyrolysis reactor and pyrolysis product gathering system constitute, this pyrolysis reactor has outer heating system and heat-insulation system, it is characterized in that, described pyrolysis reactor is a spiral pyrolysis reactor, it comprises the circular cylinder body of two ends by the lid sealing, mesopore by two lids supports a rotation axis that can rotate with respect to circular cylinder body is installed, be provided with screw-blade on the rotation axis in cylinder chamber as spiral propeller, this screw-blade top and circular cylinder body inner-wall surface running fit, the external part of rotation axis outside circular cylinder body is connected with variable-frequency motor; On the circular cylinder body sidewall, be respectively equipped with the outlet pipe of biomass feed-pipe and pyrolysis product, its feed-pipe is communicated with feeding warehouse, its outlet pipe vertically is passed in the coke holding tank of pyrolysis product gathering system, be provided with an outlet pipe on coke holding tank sidewall, this outlet pipe is communicated with condenser, bio oil holding tank, tail gas discharging pipe successively.
2. biomass screw pyrolysis installation as claimed in claim 1 is characterized in that, described outer heating system is an electric heating panel whole or isolating power-adjustable, and every electric heating panel is provided with thermometric thermopair.
3. biomass screw pyrolysis installation as claimed in claim 1 is characterized in that, the described pitch 1 that is installed in the spiral propeller on the rotation axis satisfies formula
Figure F2009201803469C00011
Wherein, L is the axial length of spiral propeller, and biomass the residence time helical reactors in of t for setting, n is the velocity of rotation of rotation axis.
CN2009201803469U 2009-11-06 2009-11-06 A biomass spiral pyrolysis device Expired - Lifetime CN201567310U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2009201803469U CN201567310U (en) 2009-11-06 2009-11-06 A biomass spiral pyrolysis device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2009201803469U CN201567310U (en) 2009-11-06 2009-11-06 A biomass spiral pyrolysis device

Publications (1)

Publication Number Publication Date
CN201567310U true CN201567310U (en) 2010-09-01

Family

ID=42659596

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2009201803469U Expired - Lifetime CN201567310U (en) 2009-11-06 2009-11-06 A biomass spiral pyrolysis device

Country Status (1)

Country Link
CN (1) CN201567310U (en)

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2012055123A1 (en) * 2010-10-26 2012-05-03 西峡龙成特种材料有限公司 External heating type coal material decomposition apparatus with multiple tubes
WO2012055124A1 (en) * 2010-10-26 2012-05-03 Zhu Shucheng Coal material decomposition apparatus
CN102618303A (en) * 2012-03-28 2012-08-01 苏忠 Coal low-temperature pyrolysis reactor
CN101709224B (en) * 2009-11-06 2012-11-07 中国科学技术大学 Biomass spiral pyrolysis device and pyrolysis process
CN102873073A (en) * 2012-08-30 2013-01-16 山东十方环保能源股份有限公司 Device for preparing natural gas for vehicles by using kitchen waste and working method
CN102952554A (en) * 2011-08-26 2013-03-06 北京低碳清洁能源研究所 Carbonaceous material dry distillation system
CN103450913A (en) * 2013-09-23 2013-12-18 高州市中亮机械制造有限公司 Garbage thermal cracking machine
CN103464448A (en) * 2013-09-23 2013-12-25 高州市中亮机械制造有限公司 Garbage thermal cracking treatment technology
CN103557516A (en) * 2013-11-18 2014-02-05 黎明 Biomass burning device for butt-jointed boilers, heat exchangers and heat supply systems
CN104147988A (en) * 2014-07-25 2014-11-19 高剑峰 Coagulator and process for removing catalyst in unsaturated polymer hydrogenation solution by applying coagulator
CN105623685A (en) * 2015-12-09 2016-06-01 华中师范大学 Method and equipment for continuous co-production of gas and charcoal through biomass material in-situ catalytic cracking
CN107903948A (en) * 2017-12-20 2018-04-13 常州至拓新能源开发有限公司 A kind of segmented pyrolysis gasifying device
WO2019162577A1 (en) * 2018-02-26 2019-08-29 Teknologian Tutkimuskeskus Vtt Oy Method of carrying out thermolysis and thermolysis apparatus

Cited By (20)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101709224B (en) * 2009-11-06 2012-11-07 中国科学技术大学 Biomass spiral pyrolysis device and pyrolysis process
WO2012055123A1 (en) * 2010-10-26 2012-05-03 西峡龙成特种材料有限公司 External heating type coal material decomposition apparatus with multiple tubes
WO2012055124A1 (en) * 2010-10-26 2012-05-03 Zhu Shucheng Coal material decomposition apparatus
AU2010362962B2 (en) * 2010-10-26 2014-07-10 Xixia Dragon Into Special Material Co., Ltd. Multi-pipe external-heating coal decomposition equipment
RU2521647C2 (en) * 2010-10-26 2014-07-10 Сися Дрэгон Инто Спэшл Мэтириэл Ко., Лтд. Multitubular device for coal decomposition with external heating
CN102952554A (en) * 2011-08-26 2013-03-06 北京低碳清洁能源研究所 Carbonaceous material dry distillation system
CN102952554B (en) * 2011-08-26 2014-05-07 北京低碳清洁能源研究所 Carbonaceous material dry distillation system
CN102618303A (en) * 2012-03-28 2012-08-01 苏忠 Coal low-temperature pyrolysis reactor
CN102873073A (en) * 2012-08-30 2013-01-16 山东十方环保能源股份有限公司 Device for preparing natural gas for vehicles by using kitchen waste and working method
CN103450913B (en) * 2013-09-23 2014-10-22 高州市中亮机械制造有限公司 Garbage thermal cracking machine
CN103464448A (en) * 2013-09-23 2013-12-25 高州市中亮机械制造有限公司 Garbage thermal cracking treatment technology
CN103450913A (en) * 2013-09-23 2013-12-18 高州市中亮机械制造有限公司 Garbage thermal cracking machine
CN103464448B (en) * 2013-09-23 2015-10-21 高州市中亮机械制造有限公司 A kind of rubbish thermal cracking treatment process
CN103557516A (en) * 2013-11-18 2014-02-05 黎明 Biomass burning device for butt-jointed boilers, heat exchangers and heat supply systems
CN103557516B (en) * 2013-11-18 2016-04-27 黎明 For docking the biomass combustion device of boiler, heat exchanger, heating system
CN104147988A (en) * 2014-07-25 2014-11-19 高剑峰 Coagulator and process for removing catalyst in unsaturated polymer hydrogenation solution by applying coagulator
CN105623685A (en) * 2015-12-09 2016-06-01 华中师范大学 Method and equipment for continuous co-production of gas and charcoal through biomass material in-situ catalytic cracking
CN107903948A (en) * 2017-12-20 2018-04-13 常州至拓新能源开发有限公司 A kind of segmented pyrolysis gasifying device
WO2019162577A1 (en) * 2018-02-26 2019-08-29 Teknologian Tutkimuskeskus Vtt Oy Method of carrying out thermolysis and thermolysis apparatus
US12030232B2 (en) 2018-02-26 2024-07-09 Teknologian Tutkimuskeskus Vtt Oy Method of carrying out thermolysis and thermolysis apparatus

Similar Documents

Publication Publication Date Title
CN101709224B (en) Biomass spiral pyrolysis device and pyrolysis process
CN201567310U (en) A biomass spiral pyrolysis device
Luo et al. In-depth exploration of the energy utilization and pyrolysis mechanism of advanced continuous microwave pyrolysis
CN102559220B (en) Precisely controlled biomass gas and biomass carbon preparation system
CN201896159U (en) Biomass fuel gas and biomass charcoal preparation system with accurate control
CN101230280B (en) A vertical continuous dry distillation device for solid biomass
CN106430891B (en) A pyrolysis method and device for high-humidity sludge
Fu et al. Fast pyrolysis of corn stovers with ceramic ball heat carriers in a novel dual concentric rotary cylinder reactor
CN110194959A (en) A kind of microwave-heating bio oil, the system of active carbon and synthesis gas
CN102010730A (en) Biomass spiral pyrolytic process and antipyretic device
CN102071042A (en) Intelligentized continuous quick microwave cracking device for biomass and waste of biomass
WO2022016800A1 (en) Biomass pyrolysis device and method with optimized matching of thermal energy and microwave energy
CN202465598U (en) Continuous reaction device for pyrolyzing microwave biomass
WO2021169535A1 (en) Double-helix pyrolysis reactor based on pyrolytic carbon internal circulation enhanced heat transfer
Zou et al. The effects of conventional and microwave torrefaction on waste distiller’s grains and its steam gasification characteristics
CN102249225B (en) System using biomass for heat supply for producing activated carbon by fly ash
Zhang et al. Pyrolysis characteristics, kinetics, and its product characteristics of grape stem
CN102719262A (en) Destructive distillation and gasification method of solid biomass
CN201883073U (en) Device for co-producing biological oil and biological carbon by utilizing crop straws
CN109957410A (en) A biomass pyrolysis reaction device and pyrolysis system
CN105925282A (en) Biomass thermal conversion device and method based on carbon cycle
CN210030576U (en) Biomass pyrolysis reaction device and pyrolysis system
CN113025354B (en) Self-heating type vertical axial flow roller ablation pyrolysis reaction device
CN1962818A (en) Method for preparing biomass oil by rapid pyrolysis technology
CN206318709U (en) Utilize system of the vinegar lees for activated carbon

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
AV01 Patent right actively abandoned

Granted publication date: 20100901

Effective date of abandoning: 20091106

AV01 Patent right actively abandoned

Granted publication date: 20100901

Effective date of abandoning: 20091106

RGAV Abandon patent right to avoid regrant