[go: up one dir, main page]

CN1063775C - Method and device for making gasoline and diesel oil using waste plastics - Google Patents

Method and device for making gasoline and diesel oil using waste plastics Download PDF

Info

Publication number
CN1063775C
CN1063775C CN95106412A CN95106412A CN1063775C CN 1063775 C CN1063775 C CN 1063775C CN 95106412 A CN95106412 A CN 95106412A CN 95106412 A CN95106412 A CN 95106412A CN 1063775 C CN1063775 C CN 1063775C
Authority
CN
China
Prior art keywords
pipe
reactor
waste
circulation
gasoline
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 - Fee Related
Application number
CN95106412A
Other languages
Chinese (zh)
Other versions
CN1137057A (en
Inventor
白秀全
赵景州
王玉卿
王双德
万明
朱明德
董根全
史建中
刘玉英
李文怀
何国洲
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.)
JIANGXI HUALONG CHEMICAL CO Ltd
Shanxi Institute of Coal Chemistry of CAS
Original Assignee
JIANGXI HUALONG CHEMICAL CO Ltd
Shanxi Institute of Coal Chemistry of CAS
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 JIANGXI HUALONG CHEMICAL CO Ltd, Shanxi Institute of Coal Chemistry of CAS filed Critical JIANGXI HUALONG CHEMICAL CO Ltd
Priority to CN95106412A priority Critical patent/CN1063775C/en
Publication of CN1137057A publication Critical patent/CN1137057A/en
Application granted granted Critical
Publication of CN1063775C publication Critical patent/CN1063775C/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

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

Abstract

The present invention provides a method for preparing gasoline and diesel oil by using waste plastic. The method adopts a multi-tube reactor, waste plastic which is inputted into the reactor is decomposed into small molecule compounds whose carbon number is less than 100, distillates whose temperature is less than 360 DEG C are outputted for catalytic reforming reaction, and through fractionation or direct fractionation, gasoline and diesel oil are obtained. The method of the present invention and the multi-tube recirculation reactor which is especially made can effectively shorten time for leading the cracking temperature of the waste plastic to be reached, can enhance the cracking reaction speed of raw material, and can increase the yield of purpose products. No waste water, no waste gas and no waste slag are generated by the method, or little waste water, little waste gas and little waste slag are generated by the method. Through preliminary estimate, each ton of waste plastic can be used for preparing 700kg of gasoline and diesel oil, 100kg of gas and 200kg of slag. Therefore, the benefit of preapring gasoline and diesel oil by the waste plastic is obvious.

Description

废塑料制汽柴油的方法与装置Method and device for producing gasoline and diesel from waste plastics

本发明涉及一种用废塑料为原料制取燃料油的方法和装置。The invention relates to a method and a device for preparing fuel oil from waste plastics.

随着社会经济的发展,人类对塑料制品的需求量在不断增加,与此同时,每年也排放出大量的废塑料,这不仅对社会生态环境造成新的污染和破坏,而且也是一种能源浪费。利用废旧塑料制取汽柴油(或液体燃料)被普遍认为是目前诸多处理废旧塑料方法中最为合理有效的一种,在美、日、德、英和我国都有类似报导。从现有方法看,一般大都为将废望料经高温分解、催化重整和分馏而得到汽柴油,也有不经催化直接得到汽柴油的。上述反应是把废塑料直接加入或经螺旋推进器在冷态或低温下加入反应釜,釜底部加热,于高温下使废塑料熔化裂解。这种加热裂解方式,一方面由于塑料传热性能差,加热废塑料裂解温度要较长时间,从而使过程的处理能力下降。另一方面,由于只限于锅底加热,且高温,这就一定会造成局部过热,至使器壁生焦结灰,造成排渣困难,过程不能连续,生产能力低下。美国专利USP 4108730、4175217和4118281均是采用重循环油把废塑料溶解,然后再进行催化裂解,该过程虽然在塑料溶解速度上有所改进,但却需要大量的高沸点重油作为热循环油,不仅增加了工艺过程的复杂性,而且也增加了能耗。美国专利USP 4851601提出的方法是将废塑料粉碎,加热熔融后再进入裂解反应室裂解,日本专利JP 038690也提到先将废塑料熔融,然后在裂解釜中使其裂化直到催化分离。上述二个专利的特点是在前处理上都遵循先溶融,后热裂解再催化裂解的过程,设备复杂,工艺流程长。With the development of social economy, human demand for plastic products is increasing. At the same time, a large amount of waste plastics are discharged every year, which not only causes new pollution and damage to the social ecological environment, but also is a waste of energy. . Utilizing waste plastics to produce gasoline and diesel oil (or liquid fuel) is generally considered to be the most reasonable and effective method among many waste plastics methods, and there are similar reports in the United States, Japan, Germany, Britain and my country. According to the existing methods, gasoline and diesel are generally obtained by pyrolysis, catalytic reforming and fractionation of waste materials, and gasoline and diesel are obtained directly without catalysis. The above reaction is to add waste plastics directly or through a screw propeller into the reaction kettle in a cold state or at a low temperature, and heat the bottom of the kettle to melt and crack the waste plastics at high temperature. This heating cracking method, on the one hand, due to the poor heat transfer performance of plastics, it takes a long time to heat the cracking temperature of waste plastics, thereby reducing the processing capacity of the process. On the other hand, since it is only limited to the heating at the bottom of the pot, and the high temperature, it will definitely cause local overheating, so that the wall of the vessel will be coked and ash, making it difficult to discharge slag, the process cannot be continuous, and the production capacity is low. U.S. Patents USP 4108730, 4175217 and 4118281 all use heavy circulating oil to dissolve waste plastics, and then carry out catalytic cracking. Although this process improves the dissolution rate of plastics, it requires a large amount of high boiling point heavy oil as thermal circulating oil. Not only increases the complexity of the process, but also increases the energy consumption. The method proposed by U.S. Patent USP 4851601 is to crush waste plastics, heat and melt them and then enter the pyrolysis reaction chamber for cracking. Japanese Patent JP 038690 also mentions that waste plastics are first melted and then cracked in a cracking kettle until catalytic separation. The above-mentioned two patents are characterized in that they all follow the process of melting first, then thermal cracking and then catalytic cracking in the pretreatment, the equipment is complex, and the process flow is long.

本发明的目的在于克服上述方法的缺陷,提供一种使熔融、裂解、分离一步进行的连续化废塑料制汽柴油的方法,并提供为该方法而专门设计的反应器。The purpose of the present invention is to overcome the disadvantages of the above method, to provide a continuous method of producing gasoline and diesel from waste plastics in which melting, cracking and separation are carried out in one step, and to provide a reactor specially designed for the method.

本发明的废塑料制汽柴油的方法按如下步骤进行:The method of waste plastics gasoline and diesel oil of the present invention is carried out as follows:

(1)原料经分检、净化除尘后破碎至2-3厘米,(1) The raw materials are broken to 2-3 cm after sorting, purification and dust removal,

(2)常压下反应器升温至200-300℃(反应器在反应初期加入导热油)后,将物料输送至多管循环反应器内,(2) After the temperature of the reactor is raised to 200-300°C under normal pressure (heat transfer oil is added to the reactor at the initial stage of the reaction), the materials are transported to the multi-tube circulation reactor,

(3)反应温度升至350-500℃时,废塑料被分解为碳数小于100的小分子化合物,此时,≥360℃的馏份通过溢流管返回反应器,<360℃的馏份经导流管从反应器输出进入催化重整反应器,然后进分馏塔,焦渣进行沉降后从反应器底部排出,(3) When the reaction temperature rises to 350-500°C, waste plastics are decomposed into small molecular compounds with a carbon number less than 100. At this time, the fraction ≥360°C returns to the reactor through the overflow pipe, and the fraction <360°C The output from the reactor enters the catalytic reforming reactor through the draft tube, and then enters the fractionation tower, and the coke residue is discharged from the bottom of the reactor after settling.

(4)进入分馏塔的气体经分馏分别得到汽油、柴油和少量重油(或蜡)。(4) The gas entering the fractionation tower is fractionated to obtain gasoline, diesel oil and a small amount of heavy oil (or wax).

在上述方法中,催化重整这一过程可以根据需要选用,从反应器输出的<360℃的馏分也可不经催化重整而直接进入分馏塔进行分馏。催化重整及分馏均可采用石油炼制中的现有技术来实现。In the above method, the process of catalytic reforming can be selected according to needs, and the fraction <360°C output from the reactor can also directly enter the fractionation tower for fractionation without catalytic reforming. Both catalytic reforming and fractionation can be achieved using existing technologies in petroleum refining.

在本发明的方法中由于在一个反应器中必须实现物料熔融、裂解、分离三个过程,故需设计专用反应器来达到上述目的。In the method of the present invention, since the three processes of material melting, cracking and separation must be realized in one reactor, a special reactor needs to be designed to achieve the above-mentioned purpose.

本发明为上述方法所设计的多管循环反应器包括主循环管7,主循环管7内安装废塑料物流进料管8,溢流管9,主循环管的上部设塔板10,塔板上安装汽流导出管12及罩于管12上的泡罩11,塔板的上端还设有蛇管冷却器13及除沫器14,顶部设物流导出口16,主循环管的底部设有上下两个排渣隔离阀3和1,两阀之间为渣接受缸2,管7的外围设有与其相连通的上循环管25及下循环管4,在4与25之间设置高温裂解管5,上循环管还连接一个导热油缓冲缸24,缸上设置导热油加料口23及吹扫器入口21和放空口22。The multi-pipe circulating reactor designed for the above method of the present invention comprises a main circulation pipe 7, a waste plastics flow feed pipe 8 and an overflow pipe 9 are installed in the main circulation pipe 7, and a tray 10 is arranged on the top of the main circulation pipe, and the tray Install steam outlet pipe 12 and bubble cap 11 covered on the pipe 12, coil cooler 13 and demister 14 are arranged on the upper end of the tray, flow outlet 16 is arranged on the top, and upper and lower outlets are arranged on the bottom of the main circulation pipe. Two slag discharge isolation valves 3 and 1, between the two valves is the slag receiving cylinder 2, the upper circulation pipe 25 and the lower circulation pipe 4 connected with it are arranged on the periphery of the pipe 7, and the high temperature cracking pipe is set between 4 and 25 5. The upper circulation pipe is also connected to a heat transfer oil buffer cylinder 24, and the heat transfer oil feeding port 23, the purger inlet 21 and the vent port 22 are arranged on the cylinder.

本发明废塑料制汽柴油的方法与装置于现有技术相比具有如下优点:1.克服了塑料热传导性差,有效地缩短了废塑料到裂解温度的时间,同样温度条件下,采用热熔剂加热可比干法加热法缩短一倍时间;2.采用多管自循环式反应器改善了传热传质过程,提高了原料裂解反应速度。增加了过程的处理能力;3.多管自循环式反应器的结构可使物流运动速度加快,快速流的冲刷作用使反应生成的焦渣无机会滞留于反应器壁,而是随物流进入循环管,自上而下,较重物流沉于反应器底部,并通过渣排放器定时排放,从而有效地实现了过程连续化长期运转之目的;4.采用液渣法热熔融物料,节省了能耗;5.采用控制≥360℃以上馏份自动返回反应器,再反应的过程,增加了目的产品的得率;6.采用塔顶除雾器,避免了系统管道堵塞,保证了流程畅通;7.由于本过程采用了气渣充分利用的思路致使本过程无三废或少三废产生。Compared with the prior art, the method for producing gasoline and diesel from waste plastics of the present invention has the following advantages: 1. It overcomes the poor thermal conductivity of plastics and effectively shortens the time for waste plastics to reach the cracking temperature. Under the same temperature conditions, heating with hot melt can shorten the time by one time compared with dry heating; 2. The heat and mass transfer process is improved by adopting a multi-tube self-circulating reactor, and the raw material cracking reaction speed is increased. Increased processing capacity of the process; 3. The structure of the multi-tube self-circulation reactor can speed up the movement of the flow, and the scour effect of the fast flow makes the coke slag generated by the reaction have no chance to stay on the wall of the reactor, but enters the circulation pipe with the flow, from top to bottom, heavier The stream sinks to the bottom of the reactor and is regularly discharged through the slag discharger, thereby effectively realizing the purpose of continuous long-term operation of the process; 4. 4. Using liquid slag method to heat melt materials, saving energy consumption; 5. The process of controlling the fraction above 360°C to automatically return to the reactor and react again increases the yield of the target product; 6. The tower top demister is used to avoid the blockage of the system pipeline and ensure the smooth flow of the process; 7. Due to this The process adopts the idea of making full use of gas slag, so that there is no or less three wastes in this process.

下面通过附图及实施例详细说明本发明的方法及反应器。The method and reactor of the present invention will be described in detail below with reference to the accompanying drawings and examples.

图1所示为根据本发明的方法而专门设计的多管反应器结构示意图。Fig. 1 shows that according to the method of the present invention and specially designed multi-tubular reactor structure schematic diagram.

图2是图1的俯视图。FIG. 2 is a top view of FIG. 1 .

如图所示,该反应器包括一个主循环管7,在管7内安装废塑料物流进料管8,溢流管9,管7的上部设塔板10,塔板上安装汽流导出管12及罩于管12上的泡罩11,塔板的上端设有蛇管冷却器13及除沫器14,上述部件通过法兰20和19与主循环管连接,其顶部设安全阀15、物流导出口16、压力表17及热偶管18。主循环管7的外围设有与其相连通的上循环管25及下循环管4,在4与25之间设置高温裂解管5,管5的顼部安装液位测定传感器6。上循环管25还连接导热油缓冲缸24,缸上设置吹扫气入口21,放空口22及导热油加料口23。26是压力表,27是热电偶。主循环管7的下部为排渣部分,分别设置上下两个排渣隔离阀3和1,两阀之间为渣接受缸2,这样的排渣设计可以保证热量不外泄,以维持过程的连续化。在使用上述反应器时,反应初期要加入导热油,导热油从加料口23加入,经缓冲缸24、上下循环管25、4进入主循环管7及裂解管5,通过液位测定仪6控制液位至裂解管2/3处,然后用隋性气体吹扫。所述的隋性气体可以是氮气、水蒸汽,烟道气等。吹扫气经吹扫气入口21进入吹扫整个反应器,吹扫后的气体从导管16排出后再经后面连接的二段催化反应器后捧入大气,测尾气氧含量<1%以下时,关闭吹扫气。吹扫完成后,开始升温,裂解管最终温度500℃,主循环管最终温度450℃。当升温至200-3000℃时,物料经进料管8进入循环管7,在这里新鲜物料与主循环管中来自塔顶溢流管9的高沸点热流(<360℃)以及经裂解管5,沿上循环管25的高温液流(<400℃)直接接触融化,并使主循环管中温度下降,物料由上而下运动,至下循环管4处,由于下循环管处温度高于主循环管中温度,故物料温度升高并沿下循管4逐渐向上移动,直至高温裂解管5(温度为460℃),在此物料被迅速裂解,由于主循环管7与裂解管5之间的温度差,造成不同压域的密度差,从而造成物料的自行循环。经裂解管5裂解的物料沿上循环管25至主循环管7,物料速度突然减慢,经气液分离,液相部分返回主循环管7,气相部分通过塔板10沿导管12经泡罩11汽液传质热交换,再经冷却器13最后把关控制物流温度≤360℃,≥360℃的物料被冷却于泡罩11并经溢流管9返回主循环管7,<360℃的馏份则经除沫器14沿导管16进入二段催化重整反应器,或直接入分馏塔。As shown in the figure, the reactor includes a main circulation pipe 7, a waste plastics flow feed pipe 8 and an overflow pipe 9 are installed in the pipe 7, and a tray 10 is arranged on the top of the pipe 7, and a vapor flow outlet pipe is installed on the tray 12 and the bubble cap 11 covered on the pipe 12, the upper end of the tray is provided with a coil cooler 13 and a demister 14, and the above parts are connected with the main circulation pipe through flanges 20 and 19, and a safety valve 15, a logistics Outlet 16, pressure gauge 17 and thermocouple tube 18. The periphery of the main circulation pipe 7 is provided with an upper circulation pipe 25 and a lower circulation pipe 4 communicating with it, a high-temperature cracking pipe 5 is set between 4 and 25, and a liquid level measurement sensor 6 is installed on the fork of the pipe 5 . The upper circulation pipe 25 is also connected to the heat transfer oil buffer cylinder 24, which is provided with a purge gas inlet 21, a vent port 22 and a heat transfer oil feed port 23. 26 is a pressure gauge, and 27 is a thermocouple. The lower part of the main circulation pipe 7 is the slag discharge part, and the upper and lower slag discharge isolation valves 3 and 1 are set respectively, and the slag receiving cylinder 2 is located between the two valves. Such a slag discharge design can ensure that the heat will not leak out to maintain the process Serialization. When using the above-mentioned reactor, heat conduction oil should be added at the initial stage of the reaction. The heat conduction oil is added from the feed port 23, enters the main circulation pipe 7 and the cracking pipe 5 through the buffer cylinder 24, the upper and lower circulation pipes 25, 4, and is controlled by the liquid level measuring instrument 6. The liquid level reaches 2/3 of the cracking tube, and then purged with an inert gas. The inert gas may be nitrogen, water vapor, flue gas, etc. The purge gas enters through the purge gas inlet 21 to purge the entire reactor, and the purge gas is discharged from the conduit 16 and then enters the atmosphere through the second-stage catalytic reactor connected behind. When the oxygen content of the tail gas is measured <1% , turn off the purge gas. After the purging is completed, start to heat up, the final temperature of the cracking tube is 500°C, and the final temperature of the main circulation tube is 450°C. When the temperature rises to 200-3000°C, the material enters the circulation pipe 7 through the feed pipe 8, where the fresh material and the high-boiling heat stream (<360°C) from the tower top overflow pipe 9 in the fresh material and the main circulation pipe pass through the cracking pipe 5 , the high-temperature liquid flow (<400°C) along the upper circulation pipe 25 directly contacts and melts, and makes the temperature in the main circulation pipe drop, and the material moves from top to bottom to 4 places in the lower circulation pipe. Since the temperature at the lower circulation pipe is higher than The temperature in the main circulation pipe, so the temperature of the material rises and gradually moves upward along the lower circulation pipe 4 until the high temperature cracking pipe 5 (the temperature is 460 ° C), where the material is rapidly cracked, due to the gap between the main circulation pipe 7 and the cracking pipe 5 The temperature difference between them causes the density difference in different pressure zones, thus causing the self-circulation of materials. The material cracked by the cracking pipe 5 goes to the main circulation pipe 7 along the upper circulation pipe 25, and the material speed suddenly slows down. After gas-liquid separation, the liquid phase part returns to the main circulation pipe 7, and the gas phase part passes through the tray 10 and passes through the bubble cap along the conduit 12. 11 Vapor-liquid mass transfer and heat exchange, and then through the cooler 13 to finally control the flow temperature ≤ 360 ° C, the material ≥ 360 ° C is cooled in the bubble cap 11 and returned to the main circulation pipe 7 through the overflow pipe 9, the distillation of < 360 ° C The part then enters the second-stage catalytic reforming reactor through the demister 14 along the conduit 16, or directly enters the fractionation tower.

反应器中的液固两相在主循环管7内沉降分离,焦渣通过底部的渣隔离阀3进入渣接受缸2,最后从阀1排出。而熔融的液体物料则重新返回主循环管7再行反应。在上述反应中,物料不断加入反应器后,所产生的气液固物质通过反应器分离并分别排出,形成了连续地反应过程。The liquid-solid two-phase in the reactor settles and separates in the main circulation pipe 7, and the coke slag enters the slag receiving cylinder 2 through the slag isolation valve 3 at the bottom, and finally discharges from the valve 1. The molten liquid material then returns to the main circulation pipe 7 for further reaction. In the above reaction, after the materials are continuously added to the reactor, the gas, liquid and solid substances produced are separated through the reactor and discharged separately, forming a continuous reaction process.

在上述多管循环反应器中,主循环管7与上下循环管25和4及裂解管5的设计可有多种形式,附图中画出的是上下循环管及裂解管依主循环管为中心呈放射状排列的一种形式。In the above-mentioned multi-tubular circulation reactor, the design of the main circulation pipe 7 and the upper and lower circulation pipes 25 and 4 and the cracking pipe 5 can have multiple forms. What are drawn in the accompanying drawing is that the upper and lower circulation pipes and the cracking pipe are based on the main circulation pipe. A form in which the centers are arranged radially.

实施例1Example 1

将废塑料破碎至2-3cm过筛除尘后待用。反应器升温至250-300℃时,将破碎后的废塑料经料斗通过螺旋推进器(螺杆保温230℃)由进料管进入多管反应器的主循环管,上下循环管及裂解管。主循环管升温至400℃,裂解管460℃时反应开始进行,产生气液固三相流体,气相部分经塔板10沿导管12泡罩11与塔板上的积液进行传热传质交换,再经冷却器13最后把关控制塔顶温度360℃。>360℃(沸点)的物流被冷却于泡罩11,并经溢流管9返回主循环管7,≤360℃的馏分经除沫器14沿导管16进入催化重整反应器进行催化重整。催化重整采用ZSM-5分子筛作催化剂,反应温度280-380℃,常压。经催化重整后的产物进入分馏塔分馏,分馏塔温度釜底400℃、塔顶195℃,压力为常压,最后分别得到汽油、柴油、少量重油及部分高热不凝气体。而在多管反应器中生成的渣,经主循环管7沉降,在不停车的情况下,通过反应器底部的隔离阀3进入渣接受器2,再经阀1排出。上述过程所产生的不凝气、少量重油液相渣可作为本过程的加热燃料回收使用,少量重油亦可通过重油加料管回炉裂解。上述反应生成产物收率(以重量百分比计)如下:Crush waste plastics to 2-3cm, sieve and remove dust for later use. When the temperature of the reactor rises to 250-300°C, the crushed waste plastics will enter the main circulation pipe, upper and lower circulation pipes and cracking pipes of the multi-tube reactor through the hopper through the screw propeller (screw insulation 230°C) from the feed pipe. The temperature of the main circulation pipe is raised to 400°C, and the reaction starts at 460°C in the cracking pipe, producing a gas-liquid-solid three-phase fluid, and the gas phase passes through the tray 10 along the conduit 12 bubble cap 11 to exchange heat and mass with the accumulated liquid on the tray , and then through the cooler 13 to finally check and control the tower top temperature to 360°C. The stream >360°C (boiling point) is cooled in the bubble cap 11, and returns to the main circulation pipe 7 through the overflow pipe 9, and the fraction ≤360°C enters the catalytic reforming reactor along the conduit 16 through the demister 14 for catalytic reforming . Catalytic reforming uses ZSM-5 molecular sieve as the catalyst, the reaction temperature is 280-380°C and normal pressure. The products after catalytic reforming enter the fractionation tower for fractionation. The temperature of the bottom of the fractionation tower is 400°C and the top of the tower is 195°C. The slag generated in the multi-tube reactor settles through the main circulation pipe 7, and enters the slag receiver 2 through the isolation valve 3 at the bottom of the reactor without stopping the machine, and then is discharged through the valve 1. The non-condensable gas and a small amount of heavy oil liquid phase slag produced in the above process can be recycled and used as heating fuel in this process, and a small amount of heavy oil can also be returned to the furnace for cracking through the heavy oil feeding pipe. Above-mentioned reaction generates product yield (in weight percentage) as follows:

汽油  42.82    气体  9.74Gasoline 42.82 Gas 9.74

柴油  29.55    残渣  17.89Diesel 29.55 Residue 17.89

实施例2Example 2

反应过程同实施例1。不同之处在于≤360℃的馏分从多管反应器排出后不经催化裂解反应器而直接进入分馏塔分馏。所得产物收率(以重量百分比计)如下:Reaction process is with embodiment 1. The difference is that the fraction ≤ 360 ° C is discharged from the multi-tube reactor and directly enters the fractionation tower for fractionation without passing through the catalytic cracking reactor. The resulting product yield (in weight percent) is as follows:

汽油  22.6    气体  5.63Gasoline 22.6 Gas 5.63

柴油  48.8    残渣  22.97Diesel 48.8 Residue 22.97

Claims (3)

1.一种废塑料制汽柴油的方法,其特征是按如下步骤进行:1. A method for producing gasoline and diesel from waste plastics is characterized in that it proceeds in the following steps:     (1)将废塑料分检。(1) Sorting waste plastics. 净化除尘后破碎至2-3厘米,After purification and dust removal, it is broken to 2-3 cm.     (2)多管循环反应器在反应初期加入导热油,常压条件下升温200-300℃(2) Heat transfer oil is added to the multi-tube circulating reactor at the initial stage of the reaction, and the temperature is raised to 200-300°C under normal pressure conditions 后,将物料输送至多管循环反应器;After that, the material is transported to the multi-tubular circulation reactor;     (3)反应温度升至350-500℃时,废塑料被分解为碳数小于100的小分子(3) When the reaction temperature rises to 350-500°C, waste plastics are decomposed into small molecules with a carbon number less than 100 化合物,此时,≥360℃的馏份通过溢流管返回多管循环反应器,<360℃Compound, at this time, the fraction ≥360°C returns to the multi-tube circulation reactor through the overflow pipe, <360°C 的馏份经导流管从多管循环反应器进入装有ZSM-5催化剂的反应器中,反应The fraction enters the reactor equipped with ZSM-5 catalyst from the multi-tubular circulation reactor through the draft tube, and the reaction 温度280-380℃,常压,反应后的产物进入分馏塔;焦渣进行沉降后从多管The temperature is 280-380 ℃, normal pressure, the product after the reaction enters the fractionation tower; 循环反应器底部排出;Discharge from the bottom of the circulating reactor;     (4)进入分馏塔的气体经分馏分别得到汽油、柴油和少量重油(或蜡),(4) The gas entering the fractionation tower is fractionated to obtain gasoline, diesel oil and a small amount of heavy oil (or wax), 从塔顶放出的气体收集。The gas released from the top of the tower is collected. 2.如权利要求1所述的方法,其特征是从多管循环反应器输出的<360℃馏2. The method according to claim 1, characterized in that the <360°C distillate output from the multi-tubular circulation reactor 份可直接进入分馏塔进行分馏。Parts can directly enter the fractionation tower for fractionation. 3.一种根据权利要求1或2所述的废塑料制汽柴油的方法所使用的多管循环3. A kind of multi-pipe circulation used in the method for producing gasoline and diesel from waste plastics according to claim 1 or 2 反应器,其特征是包括主循环管(7),主循环管(7)内安装废塑料物流进料管The reactor is characterized in that it comprises a main circulation pipe (7), and a waste plastic flow feed pipe is installed in the main circulation pipe (7) (8),溢流管(9),主循环管的上部设塔板(10),塔板上安装汽流导出管(12)(8), the overflow pipe (9), the upper part of the main circulation pipe is provided with a tray (10), and the vapor flow outlet pipe (12) is installed on the tray 及罩于管(12)上的泡罩(11),塔板的上端还设有蛇管冷却器(13)及除沫器And cover the bubble cap (11) on the pipe (12), the upper end of the tray is also provided with a coil cooler (13) and a demister (14),顶部设物流导出口(16),主循环管的底部设有上下两个排渣隔离阀(14), the top is provided with a flow outlet (16), and the bottom of the main circulation pipe is provided with two slag discharge isolation valves up and down (3)和(1),两阀之间为渣接受缸(2),管(7)的外围设有与其相连通的上循(3) and (1), between the two valves is a slag receiving cylinder (2), and the periphery of the pipe (7) is provided with an upper circulation cylinder connected to it. 环管(25)及下循环管(4),在(4)与(25)之间设置高温裂解管(5),上循环管Ring pipe (25) and lower circulation pipe (4), high temperature cracking pipe (5) is set between (4) and (25), upper circulation pipe 还连接一个导热油缓冲缸(24)。Also connect a thermal oil buffer cylinder (24).
CN95106412A 1995-05-31 1995-05-31 Method and device for making gasoline and diesel oil using waste plastics Expired - Fee Related CN1063775C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN95106412A CN1063775C (en) 1995-05-31 1995-05-31 Method and device for making gasoline and diesel oil using waste plastics

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN95106412A CN1063775C (en) 1995-05-31 1995-05-31 Method and device for making gasoline and diesel oil using waste plastics

Publications (2)

Publication Number Publication Date
CN1137057A CN1137057A (en) 1996-12-04
CN1063775C true CN1063775C (en) 2001-03-28

Family

ID=5075919

Family Applications (1)

Application Number Title Priority Date Filing Date
CN95106412A Expired - Fee Related CN1063775C (en) 1995-05-31 1995-05-31 Method and device for making gasoline and diesel oil using waste plastics

Country Status (1)

Country Link
CN (1) CN1063775C (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1070526C (en) * 1997-10-13 2001-09-05 刘和生 Wet oil refining process utilizing waste plastics and its vaporizer
CN116064069A (en) * 2023-03-16 2023-05-05 浙江科茂环境科技有限公司 Systems and methods for producing fuel oil from waste plastics

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4851601A (en) * 1988-01-19 1989-07-25 Mobil Oil Corporation Processing for producing hydrocarbon oils from plastic waste
CN1092096A (en) * 1993-12-30 1994-09-14 姜皓 Utilize the method and apparatus of waste or used plastics extracting gasoline, diesel oil distillate and liquefied gas
CN1099766A (en) * 1993-08-28 1995-03-08 李强 Method for extracting gasoline, diesel oil from waste plastics

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4851601A (en) * 1988-01-19 1989-07-25 Mobil Oil Corporation Processing for producing hydrocarbon oils from plastic waste
CN1099766A (en) * 1993-08-28 1995-03-08 李强 Method for extracting gasoline, diesel oil from waste plastics
CN1092096A (en) * 1993-12-30 1994-09-14 姜皓 Utilize the method and apparatus of waste or used plastics extracting gasoline, diesel oil distillate and liquefied gas

Also Published As

Publication number Publication date
CN1137057A (en) 1996-12-04

Similar Documents

Publication Publication Date Title
CA2720815C (en) System and process for producing biodiesel
EP1707614A1 (en) Thermal or catalytic cracking process for hydrocarbon feedstocks and corresponding system
RU2686152C1 (en) Method of producing oil needle coke
CN101602953A (en) The purification system of straw quick thermal cracking products
JP2010077410A (en) Method for producing liquid fuel derived from biomass, and apparatus therefor
CN111518583A (en) Solid waste pyrolysis liquid phase product fused salt gradient treatment impurity removal and quality improvement device
CN101705109B (en) Method and device for catalytic cracking of heavy oil
CN202403609U (en) Device for paraffin deposition treatment of water cooler in methanol synthesis
CN1063775C (en) Method and device for making gasoline and diesel oil using waste plastics
CN103611328B (en) Process for extracting naphthalene by continuously rectifying heavy benzol
CN103484159B (en) Matching technology method for optimizing feeding of coal tar suspended bed hydrocracker
CN202337765U (en) Refining device of swill-cooked dirty oil and used oil
CN101255343A (en) Method for producing diesel oil by using waste plastics, waste oil or heavy oil and refining fuel
CN116064093A (en) A method and system for producing olefins by cracking heavy hydrocarbons
RU87163U1 (en) TWO-STAGE INSTALLATION OF THERMAL CRACKING OF OIL RAW MATERIALS
CN1923957A (en) Device and technology method of preparing diesel oil by thermo-cracking waste plastics
JP4286557B2 (en) Oil processing equipment for waste plastic containing PET
CN1689962A (en) Method for producing synthetic gas by gasifying super-heavy inferior oil mixture
CN103265973B (en) Method and equipment for producing automotive diesel fuel from medium temperature coal tar light oil as raw material
CN212335130U (en) Device for thermal cracking of heavy oil by using pulverized coal and petroleum coke gasification
CN210140559U (en) Pretreatment system of vacuum tower middle section oil
CN114410337A (en) Method and device for producing alkyl biofuel by hydrogenation
CN210765213U (en) Waste oil hydrogenation regenerating device
JP2964378B2 (en) Waste plastic oiling equipment
RU2804969C1 (en) Method for producing liquid hydrocarbons from thermoplastic waste and device for its implementation

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C19 Lapse of patent right due to non-payment of the annual fee
CF01 Termination of patent right due to non-payment of annual fee