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 PDFInfo
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- 238000000034 method Methods 0.000 title claims abstract description 40
- 239000002699 waste material Substances 0.000 title claims abstract description 35
- 239000004033 plastic Substances 0.000 title claims abstract description 34
- 229920003023 plastic Polymers 0.000 title claims abstract description 34
- 239000003502 gasoline Substances 0.000 title claims abstract description 17
- 239000002283 diesel fuel Substances 0.000 title claims abstract description 9
- 238000005336 cracking Methods 0.000 claims abstract description 25
- 239000002893 slag Substances 0.000 claims abstract description 22
- 238000006243 chemical reaction Methods 0.000 claims abstract description 19
- 238000005194 fractionation Methods 0.000 claims abstract description 18
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 3
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 3
- 239000000463 material Substances 0.000 claims description 14
- 239000003921 oil Substances 0.000 claims description 9
- 238000012546 transfer Methods 0.000 claims description 9
- 239000000295 fuel oil Substances 0.000 claims description 7
- 238000002955 isolation Methods 0.000 claims description 5
- 238000004519 manufacturing process Methods 0.000 claims description 4
- 239000000428 dust Substances 0.000 claims description 3
- 239000003054 catalyst Substances 0.000 claims description 2
- 150000001875 compounds Chemical class 0.000 claims description 2
- 238000000746 purification Methods 0.000 claims description 2
- 150000003384 small molecules Chemical class 0.000 claims 1
- 239000007789 gas Substances 0.000 abstract description 15
- 238000001833 catalytic reforming Methods 0.000 abstract description 11
- 239000002994 raw material Substances 0.000 abstract description 3
- 230000036632 reaction speed Effects 0.000 abstract description 2
- 239000002912 waste gas Substances 0.000 abstract 2
- 239000002351 wastewater Substances 0.000 abstract 2
- -1 small molecule compounds Chemical class 0.000 abstract 1
- 239000007788 liquid Substances 0.000 description 10
- 238000010926 purge Methods 0.000 description 7
- 238000010438 heat treatment Methods 0.000 description 5
- 239000012071 phase Substances 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 238000009835 boiling Methods 0.000 description 3
- 238000004523 catalytic cracking Methods 0.000 description 3
- 239000000571 coke Substances 0.000 description 3
- 238000002844 melting Methods 0.000 description 3
- 230000008018 melting Effects 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 239000010724 circulating oil Substances 0.000 description 2
- 238000013461 design Methods 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 239000011261 inert gas Substances 0.000 description 2
- 239000007791 liquid phase Substances 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000000197 pyrolysis Methods 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 238000011437 continuous method Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
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- 230000000694 effects Effects 0.000 description 1
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- 239000003546 flue gas Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000012943 hotmelt Substances 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 239000011344 liquid material Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
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- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000013021 overheating Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 238000005504 petroleum refining Methods 0.000 description 1
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000004227 thermal cracking Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
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Abstract
Description
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,
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
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
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
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)
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 |
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| 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 |
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| Country | Link |
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| CN (1) | CN1063775C (en) |
Families Citing this family (2)
| 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)
| 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 |
-
1995
- 1995-05-31 CN CN95106412A patent/CN1063775C/en not_active Expired - Fee Related
Patent Citations (3)
| 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 |
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| Publication number | Publication date |
|---|---|
| CN1137057A (en) | 1996-12-04 |
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