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CN108559543A - The technique that supercritical water is heat-treated waste plastics and stalk mixture production hydrocarbon ils - Google Patents

The technique that supercritical water is heat-treated waste plastics and stalk mixture production hydrocarbon ils Download PDF

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Publication number
CN108559543A
CN108559543A CN201810356084.0A CN201810356084A CN108559543A CN 108559543 A CN108559543 A CN 108559543A CN 201810356084 A CN201810356084 A CN 201810356084A CN 108559543 A CN108559543 A CN 108559543A
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reactor
straw
waste
cracking
oil
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李永红
刘志远
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Tianjin University
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    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G2300/00Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
    • C10G2300/10Feedstock materials
    • C10G2300/1003Waste materials
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G2300/00Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
    • C10G2300/10Feedstock materials
    • C10G2300/1011Biomass
    • C10G2300/1014Biomass of vegetal origin

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Wood Science & Technology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Abstract

本发明涉及一种超临界水热处理废塑料和秸秆混合物生产烃类油品的工艺,利用农田废弃植物的秸秆在超临界水热条件下容易裂解产生的活性物种,引发塑料大分子的裂解,不使用催化剂,避免了催化剂与产物分离困难的问题,同时,植物裂解产生的组分还具有溶剂作用,可显著降低塑料裂解油的黏度。超临界水在废弃塑料裂解的过程中不仅可以通过充当溶剂和分散剂以避免体系结焦,还能通过其自身的氢转移作用降低塑料裂解产物的不饱和度,提高产物的稳定性。该方法综合利用废弃塑料和农田废秸秆为原料,成本低,操作简易,不需要氢源,不需要催化剂,烃油收率高,对环境无污染。

The present invention relates to a supercritical hydrothermal treatment process of waste plastics and straw mixture to produce hydrocarbon oil products. The active species produced by the easy cracking of the straws of waste plants in the farmland under supercritical hydrothermal conditions can be used to trigger the cracking of plastic macromolecules, without The use of a catalyst avoids the problem of difficult separation of the catalyst and the product. At the same time, the components produced by the plant cracking also have a solvent effect, which can significantly reduce the viscosity of the plastic cracking oil. Supercritical water can not only act as a solvent and dispersant to avoid system coking in the process of waste plastic cracking, but also reduce the unsaturation of plastic cracking products through its own hydrogen transfer and improve the stability of the product. The method comprehensively utilizes waste plastics and farmland waste straw as raw materials, has low cost, simple operation, does not require hydrogen source, does not require catalyst, has high yield of hydrocarbon oil, and has no pollution to the environment.

Description

超临界水热处理废塑料和秸秆混合物生产烃油的工艺Process of supercritical hydrothermal treatment of waste plastic and straw mixture to produce hydrocarbon oil

技术领域technical field

本发明涉及一种超临界水热处理废塑料和秸秆混合物生产烃类油品的工艺,属于资源回收利用领域的固体废弃物处理和生物质能源领域。The invention relates to a process for producing hydrocarbon oil by supercritical hydrothermal treatment of waste plastics and straw mixture, which belongs to the field of solid waste treatment and biomass energy in the field of resource recovery and utilization.

背景技术Background technique

废弃的塑料制品已成为一种主要的城市固废,其中聚烯烃废塑料(如PE、PP、PS)占比例超过80%。由于塑料在自然界中长期难以降解,找到一种能够使其可再利用的处理废弃塑料方法关系到人类的发展和文明的延续。以机械加工或理化改性再生等技术手段生产的再生塑料制品的性能较差,只能降档使用。而通过热解等手段将废塑料转化成液态油品则是一种废旧塑料回收利用的有效途径。Discarded plastic products have become a major urban solid waste, among which polyolefin waste plastics (such as PE, PP, PS) account for more than 80%. Since plastics are difficult to degrade in nature for a long time, finding a way to make them reusable is related to the development of human beings and the continuation of civilization. Recycled plastic products produced by technical means such as mechanical processing or physical and chemical modification and regeneration have poor performance and can only be used in downgrades. Converting waste plastics into liquid oil by means of pyrolysis is an effective way to recycle waste plastics.

专利CN106520174公开了一种废聚烯烃塑料催化热解制备芳烃的方法。该方法以铌酸为催化剂,氮气为载气,在催化热解反应器中将聚烯烃塑料快速裂解合成液体芳烃。Patent CN106520174 discloses a method for preparing aromatics by catalytic pyrolysis of waste polyolefin plastics. In the method, niobic acid is used as a catalyst and nitrogen is used as a carrier gas, and polyolefin plastics are quickly cracked to synthesize liquid aromatics in a catalytic pyrolysis reactor.

专利CN107191950公开了一种废塑料悬浮催化裂化和催化氧化无焰燃烧方法。该方法是先用液态催化裂解助燃剂对废弃塑料进行均匀化改性,之后在干法水泥生产线系统的分解炉内以850℃~1200℃的温度下进行裂解,并将裂解油作为水泥生产过程的燃料。Patent CN107191950 discloses a method for suspension catalytic cracking and catalytic oxidation flameless combustion of waste plastics. The method is to homogenize and modify waste plastics with a liquid catalytic cracking combustion aid first, and then crack them in the decomposition furnace of the dry-process cement production line system at a temperature of 850°C to 1200°C, and use the cracked oil as a cement production process. fuel.

专利CN107446610公开了一种专门用于分类垃圾中塑料工业化处理的方法。该方法是先将废弃塑料送往液化釜中在350℃下进行液化处理,之后将液化后的塑料送往裂解釜中进行裂解反应。Patent CN107446610 discloses a method specially used for industrial processing of plastics in sorted garbage. The method is to send waste plastics to a liquefaction tank for liquefaction treatment at 350°C, and then send the liquefied plastics to a cracking tank for cracking reaction.

专利CN107434979公开了一种废塑料炼油方法,该方法是先将废弃塑料在350℃下与脱氯剂和溶剂油混合,之后将脱除氯化物和脱氯剂的混合油打入到下一个反应釜中进行催化裂解反应。Patent CN107434979 discloses a method of refining waste plastics. The method is to mix waste plastics with dechlorination agent and solvent oil at 350°C, and then inject the mixed oil of dechlorination and dechlorination agent into the next reaction The catalytic cracking reaction is carried out in the kettle.

我国是农业大国,每年产生大量的农田废秸秆,传统的焚烧处理会产生大量有害气体污染环境,如果将其转化成生物质油品加以利用则是既符合循环经济理念又避免环境污染的双赢途径。my country is a large agricultural country, and a large amount of waste straw is produced every year. The traditional incineration treatment will produce a large amount of harmful gas and pollute the environment. If it is converted into biomass oil for use, it is a win-win way that not only conforms to the concept of circular economy but also avoids environmental pollution. .

专利CN102618312公开了一种生物质与废塑料共热解制备燃料油的方法,是将生物质与废塑料混合均匀,置于裂解反应器中,加热开始热解反应。热解所产生的气体进入精制反应塔进行催化改质,改质后的液体产物经精馏后得到不同馏分的燃料油,产生的可燃性气体及残渣返回裂解反应器中燃烧作为辅助热源利用。生物质包括水生生物质、农业生产废弃物和林业生产废弃物,废塑料包括PP、HDPE、LDPE。该热解需要使用催化剂,存在催化剂与残渣分离困难的问题。Patent CN102618312 discloses a method for co-pyrolyzing biomass and waste plastics to prepare fuel oil. The biomass and waste plastics are evenly mixed, placed in a cracking reactor, and heated to start the pyrolysis reaction. The gas produced by pyrolysis enters the refining reaction tower for catalytic reforming. The liquid product after reforming is rectified to obtain different fractions of fuel oil. The flammable gas and residue produced are returned to the pyrolysis reactor for combustion as an auxiliary heat source. Biomass includes aquatic biomass, agricultural production waste and forestry production waste, and waste plastics include PP, HDPE, LDPE. This pyrolysis requires the use of a catalyst, and there is a problem that it is difficult to separate the catalyst from the residue.

专利CN106433733公开了一种秸秆与废塑料裂解产液体燃料的装置及方法。该方法是将秸秆同废塑料颗粒经低温(100℃~150℃)预热系统预热后,向其中加入Ni/HZSM-5或Ni/HZSM-22作为催化剂,然后送入高温(500℃)裂解系统进行裂解,产生的气体进入固气分离系统,残炭会被截留下来,挥发气体进入冷凝回收系统,可凝气体冷却后即为液体燃料,不可凝气体将通过回收管导入低温预热系统。其中所述的秸秆与废塑料的质量比为(1:5)~(5:1),催化剂的添加量为秸秆与废塑料总重的5%~20%。尽管该方法利用秸秆和废塑料共热裂解提高了液体燃料的产率和品质,但该方法需要使用固体催化剂,裂解产生的焦炭容易使催化剂失活,操作周期短,难以工业化。Patent CN106433733 discloses a device and method for cracking straw and waste plastics to produce liquid fuel. The method is to preheat the straw and waste plastic particles through a low-temperature (100°C-150°C) preheating system, add Ni/HZSM-5 or Ni/HZSM-22 as a catalyst, and then send them into a high-temperature (500°C) The pyrolysis system conducts pyrolysis, the generated gas enters the solid-gas separation system, the carbon residue will be intercepted, and the volatile gas enters the condensation recovery system. The condensable gas will become liquid fuel after cooling, and the non-condensable gas will be introduced into the low-temperature preheating system through the recovery pipe. . The mass ratio of the straw to the waste plastic is (1:5) to (5:1), and the amount of the catalyst added is 5% to 20% of the total weight of the straw and the waste plastic. Although this method uses co-thermal cracking of straw and waste plastics to improve the yield and quality of liquid fuels, this method requires the use of solid catalysts, and the coke produced by the cracking is likely to deactivate the catalysts. The operation period is short and it is difficult to industrialize.

发明内容Contents of the invention

本发明提供了一种将废塑料与秸秆共同用超临界水热处理生产烃油的工艺。本发明的目的在于,利用农田废弃植物的秸秆在超临界水热条件下容易裂解产生的活性物种,引发塑料大分子的裂解,不使用催化剂,避免了催化剂与产物分离困难的问题,同时,植物裂解产生的组分还具有溶剂作用,可显著降低塑料裂解油的黏度。超临界水在废弃塑料裂解的过程中不仅可以通过充当溶剂和分散剂以避免体系结焦,还能通过其自身的氢转移作用降低塑料裂解产物的不饱和度,提高产物的稳定性。该方法综合利用废弃塑料和农田废秸秆为原料,成本低,操作简易,不需要氢源,不需要催化剂,烃油收率高,对环境无污染。The invention provides a process for producing hydrocarbon oil by supercritical hydrothermal treatment of waste plastics and straw. The purpose of the present invention is to use the active species produced by the easy cracking of the stalks of abandoned plants in the farmland under supercritical hydrothermal conditions to trigger the cracking of plastic macromolecules without using a catalyst and avoiding the problem of difficult separation of the catalyst and the product. At the same time, the plant The components produced by cracking also have a solvent effect, which can significantly reduce the viscosity of plastic cracking oil. Supercritical water can not only act as a solvent and dispersant to avoid system coking in the process of waste plastic cracking, but also reduce the unsaturation of plastic cracking products through its own hydrogen transfer, and improve the stability of the product. The method comprehensively utilizes waste plastics and waste straw from farmland as raw materials, has low cost, simple operation, does not require hydrogen source, does not require catalyst, has high yield of hydrocarbon oil, and has no pollution to the environment.

一种超临界水热处理废塑料和秸秆混合物生产烃油的工艺,包括以下步骤:A process for producing hydrocarbon oil by supercritical hydrothermal treatment of waste plastics and straw mixture, comprising the following steps:

1)将废塑料和秸秆类植物进行粉碎;1) Crushing waste plastics and straw plants;

2)将粉碎的废塑料和秸秆类植物按照质量比0.1~10∶1混合得到混合原料,将所述的混合原料与水混合搅拌成浆态物料,水与混合原料的质量比为0.5~2∶1;2) Mix crushed waste plastics and straw plants according to a mass ratio of 0.1-10:1 to obtain a mixed raw material, mix and stir the mixed raw material with water to form a slurry material, and the mass ratio of water to mixed raw material is 0.5-2 : 1;

3)将所述的浆态物料加入到反应器中,密封反应器;3) adding the slurry material into the reactor, and sealing the reactor;

4)分两步加热反应器,第一步加热至200~380℃,维持恒温5~30分钟,第二步升温至400~430℃,在恒温下使反应进行10~40分钟,反应器内的压力为自生压;4) Heating the reactor in two steps. The first step is to heat to 200-380°C and maintain a constant temperature for 5-30 minutes. The second step is to raise the temperature to 400-430°C. The pressure is self-generated pressure;

5)从反应器排放出流体混合物至冷凝器,使该混合物经过换热单元降温至20℃以下,收集冷凝液,该冷凝液为油水混合物;5) discharge the fluid mixture from the reactor to the condenser, let the mixture pass through the heat exchange unit to cool down to below 20°C, and collect the condensate, which is an oil-water mixture;

6)通过离心或者静置分层将油和水分离,得到超临界水热处理废塑料和秸秆混合物裂解产生的烃油。6) Oil and water are separated by centrifugation or static stratification to obtain hydrocarbon oil produced by pyrolysis of waste plastic and straw mixture through supercritical hydrothermal treatment.

所述废塑料包括:聚乙烯(PE)、聚丙烯(PP)、聚苯乙烯(PS)、聚碳酸酯(PC)等材质的塑料,所述农田废秸秆包括玉米芯、玉米秆、高粱秆、葵花秆、稻草或麦草。The waste plastics include: polyethylene (PE), polypropylene (PP), polystyrene (PS), polycarbonate (PC) and other plastics, and the farmland waste straw includes corn cobs, corn stalks, sorghum stalks , sunflower stalks, straw or wheat straw.

优选的第一阶段反应温度250~310℃,反应时间10~20分钟。The preferred first-stage reaction temperature is 250-310° C., and the reaction time is 10-20 minutes.

优选的第二阶段反应温度410~420℃,反应时间20~30分钟。The preferred second-stage reaction temperature is 410-420° C., and the reaction time is 20-30 minutes.

优选塑料与秸秆的质量比为1~5∶1Preferably the mass ratio of plastic to straw is 1-5:1

优选水与所述粉碎塑料和秸秆混合原料的质量比为1~1.5∶1。Preferably, the mass ratio of water to the mixed raw material of pulverized plastic and straw is 1-1.5:1.

所述的反应器为列管式反应器,反应器中的列管排布形式依据常规列管换热器的列管排布,所述浆态物料在列管式反应器的管程发生超临界水热裂解反应,生成烃油和水的混合物,列管式反应器的壳程通入加热介质,反应器的一端通过阀门与浆料输送泵连接,反应器的另一端通过阀门与换热单元相连接,换热单元与相分离器相连。The reactor is a tube-and-tube reactor, and the arrangement of the tubes and tubes in the reactor is based on that of a conventional tube-and-tube heat exchanger. Critical aquathermolysis reaction to generate a mixture of hydrocarbon oil and water. The shell side of the tubular reactor is fed with heating medium. One end of the reactor is connected to the slurry delivery pump through a valve, and the other end of the reactor is connected to the heat exchange pump through a valve. The unit is connected, and the heat exchange unit is connected with the phase separator.

本发明提供的超临界水热处理废塑料和秸秆混合物生产烃油的工艺的有益效果为:超临界水环境可以抑制裂解体系结焦,减少有毒有害气体的产生;秸秆在超临界水环境中分解出活性分子,可以促进塑料大分子的裂解,提高裂解油的产量,降低裂解烃油的黏度,增加其流动性。塑料和秸秆混合物超临界水热裂解产物主要为饱和烃和芳烃,而不饱和烃和含氧化合物的含量很低,油的稳定性好。该工艺技术简单,易于控制,不需要用氢气和供氢剂,不需要催化剂,也无需稀释原料,还能解决农田废秸秆的处理问题,节能环保。The beneficial effects of the process of supercritical hydrothermal treatment of waste plastics and straw mixture to produce hydrocarbon oil provided by the present invention are: the supercritical water environment can inhibit the coking of the cracking system and reduce the generation of toxic and harmful gases; the straw decomposes in the supercritical water environment to produce active Molecules can promote the cracking of plastic macromolecules, increase the yield of cracked oil, reduce the viscosity of cracked hydrocarbon oil, and increase its fluidity. The supercritical hydrothermal cracking products of plastic and straw mixture are mainly saturated hydrocarbons and aromatics, while the content of unsaturated hydrocarbons and oxygenated compounds is very low, and the oil has good stability. The process technology is simple, easy to control, does not need to use hydrogen and hydrogen supply agent, does not need catalyst, and does not need to dilute raw materials. It can also solve the problem of waste straw treatment in farmland, and is energy-saving and environmentally friendly.

附图说明Description of drawings

图1列管式反应装置;Fig. 1 tubular reaction device;

其中:1-列管式反应器、2-温度监控仪、3-压力表、4-防爆阀、5-螺杆泵、6-原料混合槽、7-换热单元、8-相分离器、9-气体产物储罐、10-液体产物储罐、11-残渣油储罐、12-进料管线阀门、13-清洗备用口阀门、14-出料管线阀门、15-气相采出管线阀门、16-液相采出管线阀门、17-渣油采出管线阀门、18-加热介质入口、19-加热介质出口,20-反应器保温层。Among them: 1-tube reactor, 2-temperature monitor, 3-pressure gauge, 4-explosion-proof valve, 5-screw pump, 6-raw material mixing tank, 7-heat exchange unit, 8-phase separator, 9 - gas product storage tank, 10-liquid product storage tank, 11-residual oil storage tank, 12-feeding pipeline valve, 13-cleaning spare port valve, 14-discharging pipeline valve, 15-gas phase production pipeline valve, 16 -Liquid phase production pipeline valve, 17-residual oil production pipeline valve, 18-heating medium inlet, 19-heating medium outlet, 20-reactor insulation layer.

具体实施方式Detailed ways

下面通过实施例对本发明作进一步的阐述,其目的在于更好的理解本发明的内容而非限制本发明的保护范围。The present invention is further elaborated below by embodiment, and its purpose is to understand content of the present invention better but not limit the protection scope of the present invention.

实施例1Example 1

本实施例采用图1所示的反应装置,该装置由水平放置的列管式反应器1连接进料泵5、换热单元7、相分离器8、气体储罐9、液体储罐10和残渣油储罐11所组成。所述的反应器长60cm,直径12cm,反应器内设置7根反应管,反应管直径2cm。反应器的一端通过阀门12与螺杆泵5相连接,反应器的另一端通过阀门14与换热单元7相连接,换热单元与气液分离器8相连。This embodiment adopts the reaction device shown in Fig. 1, and this device is connected feed pump 5, heat exchange unit 7, phase separator 8, gas storage tank 9, liquid storage tank 10 and Residual oil storage tank 11 is formed. The reactor is 60cm long and 12cm in diameter, and 7 reaction tubes are arranged in the reactor, and the diameter of the reaction tubes is 2cm. One end of the reactor is connected to the screw pump 5 through the valve 12 , the other end of the reactor is connected to the heat exchange unit 7 through the valve 14 , and the heat exchange unit is connected to the gas-liquid separator 8 .

将透明PE管和玉米芯进行粉碎,将粉碎的塑料和玉米芯按照质量比5∶1混合得到混合原料,将粉碎的混合原料与蒸馏水在原料混合槽6中混合成浆态物料,水与混合原料的质量比为1.5∶1。用螺杆泵5将所述的浆态料送入到反应器1的管程中,密封反应器。在反应器的壳方循环熔盐给反应管加热升温,分两步加热反应器,第一步加热至300℃,在该温度下维持恒温10分钟,第二步升温至410℃,反应进行30分钟,反应器列管内的压力为自生压。反应结束后迅速开启阀门14,利用反应器内部的压力快速排放出流体混合物,该混合物通过管道阀门14进入换热单元7降温至20℃,然后进入相分离器8分离得到油水混合物凝液,收集在液体储罐10中,将未凝气体收集在气体储罐9中,残渣油收集在残渣油储罐11中。通过离心将冷凝液分离成油相和水相,油相为超临界水热处理废塑料和秸秆混合物裂解产生的烃油。烃油收率为88.61%,残渣油5.72%,气体5.67%。气体主要包含碳3~碳5的链烃。分析烃油产物的粘度和族组成,结果为:其黏度47cP(50℃),饱和烃63.40wt%,芳烃30.47wt%,烯烃4.67wt%,含氧有机化合物1.46wt%。Grinding the transparent PE pipe and corn cob, mixing the crushed plastic and corn cob according to the mass ratio of 5:1 to obtain the mixed raw material, mixing the pulverized mixed raw material and distilled water in the raw material mixing tank 6 to form a slurry material, and mixing the water and The mass ratio of raw materials is 1.5:1. The slurry state material is sent into the tube side of the reactor 1 with a screw pump 5, and the reactor is sealed. Circulate molten salt on the shell side of the reactor to heat the reaction tube, and heat the reactor in two steps. The first step is to heat to 300°C, and the temperature is maintained at this temperature for 10 minutes. The second step is to raise the temperature to 410°C, and the reaction proceeds for 30 minutes. Minutes, the pressure in the reactor tube is autogenous. After the reaction is over, open the valve 14 quickly, and use the pressure inside the reactor to quickly discharge the fluid mixture. The mixture enters the heat exchange unit 7 through the pipeline valve 14 and cools down to 20°C, and then enters the phase separator 8 to separate the oil-water mixture condensate, collect In the liquid storage tank 10 , the uncondensed gas is collected in the gas storage tank 9 , and the residual oil is collected in the residual oil storage tank 11 . The condensate is separated into an oil phase and a water phase by centrifugation, and the oil phase is the hydrocarbon oil produced by cracking the waste plastic and straw mixture through supercritical hydrothermal treatment. The yield of hydrocarbon oil was 88.61%, residual oil was 5.72%, and gas was 5.67%. The gas mainly contains chain hydrocarbons with carbon 3 to carbon 5. The viscosity and group composition of hydrocarbon oil products were analyzed, and the results were as follows: the viscosity was 47cP (50°C), saturated hydrocarbons were 63.40wt%, aromatics were 30.47wt%, olefins were 4.67wt%, and oxygen-containing organic compounds were 1.46wt%.

实施例2Example 2

本实施例采用的反应装置同实施例1。将PP膜和玉米秸秆进行粉碎,将粉碎的塑料和玉米秸秆按照质量比1∶1混合得到混合原料,将粉碎的混合原料与蒸馏水在原料混合槽6中混合成浆态物料,水与混合原料的质量比为1∶1。用螺杆泵5将所述的浆态料送入到反应器1的管程中,密封反应器。在反应器的壳方循环熔盐给反应管加热升温,分两步加热反应器,第一步加热至250℃,维持恒温20分钟,第二步升温至420℃,反应进行20分钟,反应器列管内的压力为自生压。反应结束后迅速开启阀门14,利用反应器内部的压力快速排放出流体混合物,该混合物通过管道阀门14进入换热单元7降温至20℃,然后进入相分离器8分离得到油水混合物凝液,收集在液体储罐10中,将未凝气体收集在气体储罐9中,残渣油收集在残渣油储罐11中。通过离心将冷凝液分离成油相和水相,油相为超临界水热处理废塑料和秸秆混合物裂解产生的烃油。烃油收率为89.69%,残渣油6.15%,气体4.16%。气体主要包含碳3~碳5的链烃。分析烃油产物的粘度和族组成,结果为:其黏度50cP(50℃),饱和烃62.05wt%,芳烃31.17wt%,烯烃5.53wt%,含氧有机化合物1.25wt%。The reaction device used in this embodiment is the same as in Example 1. Grinding the PP film and corn stalks, mixing the crushed plastic and corn stalks at a mass ratio of 1:1 to obtain a mixed raw material, mixing the crushed mixed raw material and distilled water in the raw material mixing tank 6 to form a slurry material, water and mixed raw material The mass ratio is 1:1. The slurry state material is sent into the tube side of the reactor 1 with a screw pump 5, and the reactor is sealed. Circulate the molten salt on the shell side of the reactor to heat the reaction tube, and heat the reactor in two steps. The first step is to heat to 250°C and maintain a constant temperature for 20 minutes. The second step is to raise the temperature to 420°C, and the reaction is carried out for 20 minutes. The pressure inside the tube is self-generated pressure. After the reaction is over, open the valve 14 quickly, and use the pressure inside the reactor to quickly discharge the fluid mixture. The mixture enters the heat exchange unit 7 through the pipeline valve 14 and cools down to 20°C, and then enters the phase separator 8 to separate the oil-water mixture condensate, collect In the liquid storage tank 10 , the uncondensed gas is collected in the gas storage tank 9 , and the residual oil is collected in the residual oil storage tank 11 . The condensate is separated into an oil phase and a water phase by centrifugation, and the oil phase is the hydrocarbon oil produced by cracking the waste plastic and straw mixture through supercritical hydrothermal treatment. The yield of hydrocarbon oil was 89.69%, residual oil was 6.15%, and gas was 4.16%. The gas mainly contains chain hydrocarbons with carbon 3 to carbon 5. The viscosity and group composition of the hydrocarbon oil product were analyzed, and the results were as follows: the viscosity was 50cP (50°C), saturated hydrocarbons were 62.05wt%, aromatics were 31.17wt%, olefins were 5.53wt%, and oxygen-containing organic compounds were 1.25wt%.

实施例3Example 3

本实施例采用的反应装置同实施例1。将透明PS餐盒和高粱秸秆进行粉碎,将粉碎的塑料和高粱秸秆按照质量比1∶5混合得到混合原料,将粉碎的混合原料与蒸馏水在原料混合槽6中混合成浆态物料,水与混合原料的质量比为1∶2。用螺杆泵5将所述的浆态料送入到反应器1的管程中,密封反应器。在反应器的壳方循环熔盐给反应管加热升温,分两步加热反应器,第一步加热至200℃,维持恒30分钟,第二步升温至430℃,反应进行10分钟,反应器列管内的压力为自生压。反应结束后迅速开启阀门14,利用反应器内部的压力快速排放出流体混合物,该混合物通过管道阀门14进入换热单元7降温至20℃,然后进入相分离器8分离得到油水混合物凝液,收集在液体储罐10中,将未凝气体收集在气体储罐9中,残渣油收集在残渣油储罐11中。通过离心将冷凝液分离成油相和水相,油相为超临界水热处理废塑料和秸秆混合物裂解产生的烃油。烃油收率为86.82%,残渣油7.31%,气体5.87%。分析烃油产物的粘度和族组成,结果为:其黏度95cP(50℃),饱和烃48.99wt%,芳烃34.30wt%,烯烃2.92wt%,含氧有机化合物13.79wt%。The reaction device used in this embodiment is the same as in Example 1. Grinding the transparent PS lunch box and sorghum stalks, mixing the crushed plastic and sorghum stalks at a mass ratio of 1:5 to obtain mixed raw materials, mixing the crushed mixed raw materials and distilled water in the raw material mixing tank 6 to form a slurry material, water and The mass ratio of the mixed raw materials is 1:2. The slurry state material is sent into the tube side of the reactor 1 with a screw pump 5, and the reactor is sealed. Circulate the molten salt on the shell side of the reactor to heat the reaction tube, and heat the reactor in two steps. The first step is to heat to 200°C and keep it constant for 30 minutes. The second step is to raise the temperature to 430°C, and the reaction is carried out for 10 minutes. The pressure inside the tube is self-generated pressure. After the reaction is over, open the valve 14 quickly, and use the pressure inside the reactor to quickly discharge the fluid mixture. The mixture enters the heat exchange unit 7 through the pipeline valve 14 and cools down to 20°C, and then enters the phase separator 8 to separate the oil-water mixture condensate, collect In the liquid storage tank 10 , the uncondensed gas is collected in the gas storage tank 9 , and the residual oil is collected in the residual oil storage tank 11 . The condensate is separated into an oil phase and a water phase by centrifugation, and the oil phase is the hydrocarbon oil produced by cracking the waste plastic and straw mixture through supercritical hydrothermal treatment. The yield of hydrocarbon oil was 86.82%, residual oil was 7.31%, and gas was 5.87%. The viscosity and family composition of the hydrocarbon oil product were analyzed, and the results were as follows: its viscosity was 95cP (50°C), saturated hydrocarbons were 48.99wt%, aromatics were 34.30wt%, olefins were 2.92wt%, and oxygen-containing organic compounds were 13.79wt%.

实施例4Example 4

本实施例采用的反应装置同实施例1。将无色PC蜂窝板和葵花秸秆进行粉碎,将粉碎的塑料和葵花秸秆按照质量比10∶1混合得到混合原料,将粉碎的混合原料与蒸馏水在原料混合槽6中混合成浆态物料,水与混合原料的质量比为2∶1。用螺杆泵5将所述的浆态料送入到反应器1的管程中,密封反应器。在反应器的壳方循环熔盐给反应管加热升温,分两步加热反应器,第一步加热至350℃,维持恒温5分钟,第二步升温至400℃,反应进行40分钟,反应器列管内的压力为自生压。反应结束后迅速开启阀门14,利用反应器内部的压力快速排放出流体混合物,该混合物通过管道阀门14进入换热单元7降温至20℃,然后进入相分离器8分离得到油水混合物凝液,收集在液体储罐10中,将未凝气体收集在气体储罐9中,残渣油收集在残渣油储罐11中。通过离心将冷凝液分离成油相和水相,油相为超临界水热处理废塑料和秸秆混合物裂解产生的烃油。烃油收率为90.75%,残渣油3.95%,气体5.30%。分析气体组成主要是碳3~碳5的链烃。分析烃油产物的粘度和族组成,结果为:其黏度84cP(50℃),饱和烃59.26wt%,芳烃28.73wt%,烯烃2.76wt%,含氧有机化合物9.25wt%。The reaction device used in this embodiment is the same as in Example 1. Grinding the colorless PC honeycomb board and sunflower stalks, mixing the crushed plastic and sunflower stalks at a mass ratio of 10:1 to obtain mixed raw materials, mixing the crushed mixed raw materials and distilled water in the raw material mixing tank 6 to form slurry materials, water The mass ratio to the mixed raw material is 2:1. The slurry state material is sent into the tube side of the reactor 1 with a screw pump 5, and the reactor is sealed. Circulate the molten salt on the shell side of the reactor to heat the reaction tube, and heat the reactor in two steps. The first step is to heat to 350°C and maintain a constant temperature for 5 minutes. The second step is to raise the temperature to 400°C, and the reaction is carried out for 40 minutes. The pressure inside the tube is self-generated pressure. After the reaction is over, open the valve 14 quickly, and use the pressure inside the reactor to quickly discharge the fluid mixture. The mixture enters the heat exchange unit 7 through the pipeline valve 14 and cools down to 20°C, and then enters the phase separator 8 to separate the oil-water mixture condensate, collect In the liquid storage tank 10 , the uncondensed gas is collected in the gas storage tank 9 , and the residual oil is collected in the residual oil storage tank 11 . The condensate is separated into an oil phase and a water phase by centrifugation, and the oil phase is the hydrocarbon oil produced by cracking the waste plastic and straw mixture through supercritical hydrothermal treatment. The yield of hydrocarbon oil was 90.75%, residual oil was 3.95%, and gas was 5.30%. The analyzed gas composition is mainly chain hydrocarbons with carbon 3 to carbon 5. The viscosity and family composition of the hydrocarbon oil product were analyzed, and the results were as follows: its viscosity was 84cP (50°C), saturated hydrocarbons were 59.26wt%, aromatics were 28.73wt%, olefins were 2.76wt%, and oxygen-containing organic compounds were 9.25wt%.

Claims (7)

1.一种超临界水热处理废塑料和秸秆混合物生产烃油的工艺,其特征是包括以下步骤:1. A kind of supercritical hydrothermal treatment waste plastics and the technology of stalk mixture production hydrocarbon oil, it is characterized in that comprising the following steps: 1)将废塑料和秸秆类植物进行粉碎;1) Crushing waste plastics and straw plants; 2)将粉碎的废塑料和秸秆类植物按照质量比0.1~10∶1混合得到混合原料,将混合原料与水混合搅拌成浆态物料,水与混合原料的质量比为0.5~2∶1;2) Mixing the crushed waste plastics and straw plants according to the mass ratio of 0.1-10:1 to obtain a mixed raw material, mixing the mixed raw material with water and stirring to form a slurry material, and the mass ratio of water to the mixed raw material is 0.5-2:1; 3)将浆态物料加入到反应器中,密封反应器;3) adding the slurry material into the reactor, and sealing the reactor; 4)分两步加热反应器,第一步加热至200~380℃,维持恒温5~30分钟,第二步升温至400~430℃,在恒温下使反应进行10~40分钟,反应器内的压力为自生压;4) Heating the reactor in two steps. The first step is to heat to 200-380°C and maintain a constant temperature for 5-30 minutes. The second step is to raise the temperature to 400-430°C. The pressure is self-generated pressure; 5)从反应器排放出流体混合物至冷凝器,使该混合物经过换热单元降温至20℃以下,收集冷凝液,该冷凝液为油水混合物;5) discharge the fluid mixture from the reactor to the condenser, let the mixture pass through the heat exchange unit to cool down to below 20°C, and collect the condensate, which is an oil-water mixture; 6)通过离心或者静置分层将油和水分离,得到超临界水热处理废塑料和秸秆混合物裂解产生的烃油。6) Oil and water are separated by centrifugation or static stratification to obtain hydrocarbon oil produced by pyrolysis of waste plastic and straw mixture through supercritical hydrothermal treatment. 2.如权利要求1所述的工艺,其特征是所述废塑料包括:聚乙烯(PE)、聚丙烯(PP)、聚苯乙烯(PS)或聚碳酸酯(PC)的材质的塑料;所述农田废秸秆包括玉米芯、玉米秆、高粱秆、葵花秆、稻草或麦草。2. The process according to claim 1, wherein said waste plastics comprise: polyethylene (PE), polypropylene (PP), polystyrene (PS) or polycarbonate (PC) plastics; The farmland waste straw includes corn cobs, corn stalks, sorghum stalks, sunflower stalks, rice straw or wheat straw. 3.如权利要求1所述的工艺,其特征是第一步反应温度250~310℃,反应时间10~20分钟。3. The process according to claim 1, characterized in that the first step reaction temperature is 250-310° C., and the reaction time is 10-20 minutes. 4.如权利要求1所述的工艺,其特征是第二步反应温度410~420℃,反应时间20~30分钟。4. The process according to claim 1, characterized in that the reaction temperature of the second step is 410-420° C., and the reaction time is 20-30 minutes. 5.如权利要求1所述的工艺,其特征是塑料与秸秆的质量比为1~5∶1。5. The process according to claim 1, characterized in that the mass ratio of plastics to straw is 1 to 5:1. 6.如权利要求1所述的工艺,其特征是水与粉碎塑料和秸秆混合原料的质量比为1~1.5∶1。6. The process according to claim 1, characterized in that the mass ratio of water to the mixed raw material of crushed plastics and straw is 1 to 1.5:1. 7.如权利要求1所述的工艺,其特征是反应器为列管式反应器,反应器中的列管排布形式依据常规列管换热器的列管排布,浆态物料在列管式反应器的管程发生超临界水热裂解反应,生成烃油和水的混合物,列管式反应器的壳程通入加热介质,反应器的一端通过阀门与浆料输送泵连接,反应器的另一端通过阀门与换热单元相连接,换热单元与相分离器相连。7. The process as claimed in claim 1, characterized in that the reactor is a tube-and-tube reactor, and the arrangement of the tubes and tubes in the reactor is based on the arrangement of the tubes and tubes of a conventional tube-and-tube heat exchanger. The tube side of the tubular reactor undergoes a supercritical hydrothermal cracking reaction to generate a mixture of hydrocarbon oil and water. The shell side of the tubular reactor is fed with a heating medium, and one end of the reactor is connected to the slurry delivery pump through a valve. The other end of the device is connected to the heat exchange unit through a valve, and the heat exchange unit is connected to the phase separator.
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110078075A (en) * 2019-06-06 2019-08-02 上海纳米技术及应用国家工程研究中心有限公司 A method of utilizing supercritical water hot preparation porous carbon materials
CN112662417A (en) * 2020-12-08 2021-04-16 杨清萍 Continuous production system and method for preparing liquid fuel by directly liquefying biomass
CN115197735A (en) * 2022-08-02 2022-10-18 中国矿业大学 Method for preparing oil from superheated steam type efficient liquefied plastic garbage
CN117126680A (en) * 2023-10-26 2023-11-28 江苏江天新材料科技有限公司 Process and device for preparing hydrocarbon oil by supercritical water and pyrolysis treatment of waste plastics
CN117208887A (en) * 2023-08-30 2023-12-12 湖北航天长征装备有限公司 Low-temperature carbonization method of waste polyolefin and its composite materials
US20240043756A1 (en) * 2022-08-02 2024-02-08 China University Of Mining And Technology Method for regulating quality of oil derived from plastic wastes by supercritical hydrothermal liquefaction

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101113348A (en) * 2007-09-06 2008-01-30 昆明理工大学 Process for preparing biofuel by high-pressure fluid conversion technology
CN101691494A (en) * 2009-10-16 2010-04-07 江南大学 Method for circulating and liquefying the mixture of plant biomass and waste polyester in supercritical fluid

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101113348A (en) * 2007-09-06 2008-01-30 昆明理工大学 Process for preparing biofuel by high-pressure fluid conversion technology
CN101691494A (en) * 2009-10-16 2010-04-07 江南大学 Method for circulating and liquefying the mixture of plant biomass and waste polyester in supercritical fluid

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
曹洪涛: "生物质在超/亚临界水条件下液化研究", 《中国优秀硕士学位论文全文数据库 工程科技Ⅱ辑》 *
王文兴: "《工业催化》", 31 December 1978, 化学工业出版社 *

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110078075A (en) * 2019-06-06 2019-08-02 上海纳米技术及应用国家工程研究中心有限公司 A method of utilizing supercritical water hot preparation porous carbon materials
CN112662417A (en) * 2020-12-08 2021-04-16 杨清萍 Continuous production system and method for preparing liquid fuel by directly liquefying biomass
CN115197735A (en) * 2022-08-02 2022-10-18 中国矿业大学 Method for preparing oil from superheated steam type efficient liquefied plastic garbage
US20240043756A1 (en) * 2022-08-02 2024-02-08 China University Of Mining And Technology Method for regulating quality of oil derived from plastic wastes by supercritical hydrothermal liquefaction
US12454651B2 (en) * 2022-08-02 2025-10-28 China University Of Mining And Technology Method for regulating quality of oil derived from plastic wastes by supercritical hydrothermal liquefaction
CN117208887A (en) * 2023-08-30 2023-12-12 湖北航天长征装备有限公司 Low-temperature carbonization method of waste polyolefin and its composite materials
CN117126680A (en) * 2023-10-26 2023-11-28 江苏江天新材料科技有限公司 Process and device for preparing hydrocarbon oil by supercritical water and pyrolysis treatment of waste plastics
CN117126680B (en) * 2023-10-26 2024-01-26 江苏江天新材料科技有限公司 A process and device for preparing hydrocarbon oil through supercritical water and cracking treatment of waste plastics

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