Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS5822067B2 - Method for thermal decomposition of polyolefin plastics - Google Patents
[go: Go Back, main page]

JPS5822067B2 - Method for thermal decomposition of polyolefin plastics - Google Patents

Method for thermal decomposition of polyolefin plastics

Info

Publication number
JPS5822067B2
JPS5822067B2 JP54122179A JP12217979A JPS5822067B2 JP S5822067 B2 JPS5822067 B2 JP S5822067B2 JP 54122179 A JP54122179 A JP 54122179A JP 12217979 A JP12217979 A JP 12217979A JP S5822067 B2 JPS5822067 B2 JP S5822067B2
Authority
JP
Japan
Prior art keywords
temperature
molecular weight
particle size
zone
glass beads
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
Application number
JP54122179A
Other languages
Japanese (ja)
Other versions
JPS5645984A (en
Inventor
斎藤喜代志
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.)
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
Agency of Industrial Science and Technology
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 Agency of Industrial Science and Technology filed Critical Agency of Industrial Science and Technology
Priority to JP54122179A priority Critical patent/JPS5822067B2/en
Publication of JPS5645984A publication Critical patent/JPS5645984A/en
Publication of JPS5822067B2 publication Critical patent/JPS5822067B2/en
Expired legal-status Critical Current

Links

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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

Landscapes

  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Coke Industry (AREA)

Description

【発明の詳細な説明】 本発明は、ポリオレフィン系プラスチックを熱分解して
、工業用原料や燃料として有用な炭化水素を得るための
方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for thermally decomposing polyolefin plastics to obtain hydrocarbons useful as industrial raw materials or fuels.

さらに詳しくいえば本発明は、ポリオレフィン系プラス
チックを熱分解して低分子量でかつ分子量の分布範囲の
狭い液体炭化水素を選択的に生成させる方法に関するも
のである。
More specifically, the present invention relates to a method for selectively producing liquid hydrocarbons having a low molecular weight and a narrow molecular weight distribution range by thermally decomposing polyolefin plastics.

ポリオレフィン系プラスチックは、プラスチック全生産
量の約30%を占め、現在、日用品から工業用品まで広
範囲かつ多量に使用されているものである。
Polyolefin plastics account for about 30% of the total plastic production, and are currently used in large quantities in a wide range of applications from daily necessities to industrial products.

ところで、この使用済の廃プラスチックは、その一部が
都市ゴミなどと共に焼却されたり、適当な処理を施した
後で埋立て用、建材用に利用されているとはいえ、大部
分はそのまま廃棄されている。
By the way, although some of this used waste plastic is incinerated along with municipal garbage, or is used for landfill or building materials after undergoing appropriate treatment, the majority of it is simply disposed of. has been done.

しかし、この種のプラスチックは、微生物による分解を
ほとんど受けないため、現形のまま長期間放置してもな
んら腐敗等により自然に消滅することはなく、次第に蓄
積量が増大することになり、その処置は社会上重要な問
題となっている。
However, this type of plastic is hardly decomposed by microorganisms, so even if it is left in its current form for a long period of time, it will not disappear naturally due to decay etc., and the amount accumulated will gradually increase. has become an important social issue.

したがって、このような廃プラスチックを、なんらかの
手段で工業用原料や燃料として再生することができれば
廃プラスチックの蓄積量を減少しうるだげでな(、資源
、エネルギーの節約にもつながり、資源の乏しいわが国
において重要な意義を有することになる。
Therefore, if such waste plastics could be recycled as industrial raw materials or fuel by some means, it would not only be possible to reduce the amount of waste plastics accumulated (it would also lead to resource and energy savings, It will have important significance in our country.

これまで、廃プラスチックを熱分解して、有用な炭化水
素を回収する方法は知られている。
Until now, methods are known for pyrolyzing waste plastics to recover useful hydrocarbons.

しかし、ポリオレフィン系プラスチックを熱分解した場
合、その留分から回収される生成物は、低沸点成分から
高沸点成分までの分子量分布が広い低品位のものとなり
、室温ではグリース状を呈するため、その利用範囲が制
限されるのを免れない。
However, when polyolefin plastics are thermally decomposed, the products recovered from the fraction are low-grade products with a wide molecular weight distribution from low-boiling point components to high-boiling point components, and have a grease-like appearance at room temperature. The range is inevitably limited.

したがって、簡単な手段によって、低分子量で分子量分
布範囲が狭い分解生成物を得る方法の出現が、この技術
分野において要望されていた。
Therefore, there has been a demand in this technical field for a method for obtaining decomposition products with a low molecular weight and a narrow molecular weight distribution range by simple means.

本発明者は、ポリオレフィン系プラスチック廃棄物の有
効利用を目的とした処理方法を開発するために種々研究
を重ねた結果、その熱分解生成物の分子量及び分布範囲
を熱分解温度の選択及びその生成物を特定の充てん材で
形成されかつ特定の温度に制御された充てん帯域に通す
ことによって調整しうろことを見出し、この知見に基づ
いて本発明をなすに至った。
As a result of various studies to develop a treatment method for the effective use of polyolefin plastic waste, the present inventor has determined the molecular weight and distribution range of the pyrolysis products by selecting the pyrolysis temperature and the formation of the pyrolysis products. It has been discovered that objects can be conditioned by passing them through a filling zone made of a specific filling material and controlled at a specific temperature, and the present invention has been developed based on this knowledge.

すなわち、本発明に従えば、ポリオレフィン系プラスチ
ックを熱分解し、その蒸気状生成物をさらに加熱された
充てん帯域に通して炭化水素油を製造する際に、前記熱
分解温度を430〜470°Cの範囲に保ち、また充て
ん帯域を粒径6.5 mm以下のガラスピーズにより形
成し、かつこれを250℃以下の温度に保つことにより
、低分子量で分子量分布範囲が狭く、室温で液状の高品
位炭化水素油を得ることができる。
That is, according to the present invention, when producing hydrocarbon oil by thermally decomposing a polyolefin plastic and passing the vaporized product through a heated packed zone, the thermal decomposition temperature is set at 430 to 470°C. In addition, by forming the filling zone with glass beads with a particle size of 6.5 mm or less, and keeping this at a temperature of 250°C or less, it has a low molecular weight, a narrow molecular weight distribution range, and a liquid state at room temperature. grade hydrocarbon oil can be obtained.

次に添附図面により本発明の実施態様を説明する。Next, embodiments of the present invention will be described with reference to the accompanying drawings.

図は、本発明方法を実施するのに好適な装置の1例を示
す断面略解図であって、ポリオレフィン系プラスチック
廃棄物は、原料供給口4より熱分解反応器1に供給され
、そこで電熱線10により430〜470℃に加熱され
て熱分解される。
The figure is a schematic cross-sectional view showing one example of an apparatus suitable for carrying out the method of the present invention, in which polyolefin plastic waste is supplied to a pyrolysis reactor 1 from a raw material supply port 4, and there 10 to be heated to 430-470°C and thermally decomposed.

この処理により生成する蒸気物質は、上昇して、熱分解
反応器1の上部に連結された充てん塔2に送られる。
The vaporous material produced by this process rises and is sent to a packed column 2 connected to the top of the pyrolysis reactor 1.

この充てん塔2には、粒径6.5闘のガラスピーズが充
てんされ、電熱線11により内部温度250℃以下に保
たれている。
This packed tower 2 is filled with glass beads having a particle size of 6.5 mm, and the internal temperature is maintained at 250° C. or lower by a heating wire 11.

前記の蒸気物質は充てん塔2を通過する間にさらに熱分
解され、排出口3を通って受器6に至る。
Said vaporous material is further thermally decomposed while passing through the packed column 2 and passes through the outlet 3 to the receiver 6 .

この際、所望ならばガス導入管5より分解反応器1に不
活性ガスを吹き込んで、蒸気物質の発生を促進すること
ができる。
At this time, if desired, an inert gas can be blown into the decomposition reactor 1 through the gas introduction pipe 5 to promote the generation of vaporous substances.

受器6で捕集されなかった生成物は、ドライアイストラ
ップ7でほとんど捕集され、そこで凝縮しないガス状物
は、ガストラップ8で捕集される。
Most of the products not collected in the receiver 6 are collected in the dry ice trap 7, and gaseous substances that do not condense there are collected in the gas trap 8.

分解反応器1及び充てん塔2の内部温度は熱電対9によ
って測定され、その結果によって制御が行われている。
The internal temperatures of the decomposition reactor 1 and the packed tower 2 are measured by a thermocouple 9, and controlled based on the results.

本発明方法においては、オレフィン系プラスチックの熱
分解を430〜470℃の範囲内の温度で行うことが必
要である。
In the method of the present invention, it is necessary to thermally decompose the olefinic plastic at a temperature within the range of 430 to 470°C.

この温度範囲外で行うと、分子量分布範囲の狭い生成物
の収率が低下する。
If carried out outside this temperature range, the yield of products with a narrow molecular weight distribution range will be reduced.

また、充てん帯域としては、粒径6.5 mm以下のガ
ラスピーズを充てん材とし、温度を250℃以下に保っ
たものを用いることが必要である。
Furthermore, it is necessary to use glass beads with a particle size of 6.5 mm or less as a filler and keep the temperature at 250° C. or less as a filling zone.

そ。して、ガラスピーズの粒径を小さくするほど分子量
分布範囲を狭くすることができる。
So. Thus, the smaller the particle size of the glass beads, the narrower the molecular weight distribution range.

すなわち、充てん材を全く用いない場合には、炭素数分
布C5〜C40という広い分子量分布範囲の生成物が得
られるにすぎないが、粒径6.151mのガラスビ。
That is, when no filler is used at all, a product with a wide molecular weight distribution range of carbon number distribution C5 to C40 is obtained, but glass vinyl with a particle size of 6.151 m.

−ズを充てんした場合は炭素数分布C5〜C24の分子
量分布範囲の生成物が得られ、粒径2.39mrnのガ
ラスピーズを充てんした場合は炭素数分布05〜C2□
の分子量分布範囲の生成物が得られる。
- When filled with glass beads, a product with a molecular weight distribution range of carbon number distribution C5 to C24 is obtained, and when filled with glass beads with a particle size of 2.39 mrn, a product with a carbon number distribution of 05 to C2□
A product with a molecular weight distribution range of is obtained.

このように、ガラスピーズの粒径を小さくし、蒸気物質
の接触面積を大きくすることにより、充てん材との接触
効果を向上させることができる。
In this way, by reducing the particle size of the glass beads and increasing the contact area of the vapor substance, the effect of contact with the filler material can be improved.

本発明においては、分解反応域で熱分解され気化した蒸
気物質は、ある組成と温度を有し、上昇して充てん帯域
のガラスピーズに接触するが、このビーズの温度は蒸気
物質の温度よりも低(保たれているので、その一部が凝
縮し、分解反応域に戻り、再分解されて再び充てん帯域
に上昇してくる。
In the present invention, the vaporized material pyrolyzed and vaporized in the cracking reaction zone has a certain composition and temperature and rises to contact the glass beads in the filling zone, the temperature of which is higher than the temperature of the vaporous material. As it remains low, some of it condenses and returns to the decomposition reaction zone, where it is re-decomposed and rises again to the packed zone.

他方、充てん帯域内に入った低沸点成分の蒸気は、ガラ
スピーズの間を通り、充てん帯域内の温度で再分解され
、低沸点成分に富んだ蒸気物質として留出し回収される
On the other hand, the vapor of low-boiling components that has entered the filled zone passes between the glass beads, is re-decomposed at the temperature within the packed zone, and is distilled and recovered as a vapor substance rich in low-boiling components.

このようにして、分解反応域と充てん帯域との間での環
流によって順次分縮され、分子量分布範囲の狭い生成物
が形成される。
In this way, products with a narrow molecular weight distribution range are formed through sequential fractionation by reflux between the cracking reaction zone and the packed zone.

そして、炭化水素油として最も好ましい炭素数範囲C5
〜C20のものについての収率に関し、次てん帯域内の
温度を約250℃として比較すると、充てん材がない場
合85〜94.2重量%、粒径6.1−5mmのガラス
ピーズを充てんした場合95.7〜987重量%、粒径
2.39mmのガラスピーズを充てんした場合96.0
〜99.95重量%という結果が得られる。
And the most preferable carbon number range C5 as a hydrocarbon oil
Regarding the yield of ~C20, when the temperature in the next filling zone is about 250 ° C., it is found that in the case of no filler, 85 to 94.2% by weight was filled with glass beads with a particle size of 6.1 to 5 mm. 95.7 to 987% by weight, 96.0 when filled with glass beads with a particle size of 2.39 mm
A result of ˜99.95% by weight is obtained.

また、平均分子量(Mw)について比較すると、充てん
材のない場合が190〜210の範囲であるのに対し、
粒径6.151mのガラスピーズの場合は172〜18
7の範囲であり、粒径2.39mmの場合は150〜1
72の範囲であってそれぞれ低分子量で分子量分布範囲
が狭くなっている。
Also, when comparing the average molecular weight (Mw), it is in the range of 190 to 210 in the case without filler, while
In the case of glass beads with a particle size of 6.151 m, it is 172 to 18
7, and in the case of particle size 2.39 mm, it is 150 to 1
72, each having a low molecular weight and a narrow molecular weight distribution range.

このように、充てん帯域の温度が低く、充てん材の粒径
が小さいほど留出する蒸気状生成物の平均分子量が小さ
く、分子量分布範囲も狭くなり、かつその分子量分布状
態が低分子側に片寄り室温で液体のものとなるので、工
業用原料や燃料として好適なものとなる。
In this way, the lower the temperature of the filled zone and the smaller the particle size of the filler, the lower the average molecular weight of the distilled vapor product, the narrower the molecular weight distribution range, and the more the molecular weight distribution state is shifted toward the low molecular side. Since it is liquid at room temperature, it is suitable as an industrial raw material or fuel.

したがって、本発明においては、充てん帯域の充てん材
の粒径を6.5 mm以下とし、この帯域の温度を分解
反応温度よりも低く、すなわち250℃以下にするのが
必要である。
Therefore, in the present invention, it is necessary that the particle size of the filler in the filling zone is 6.5 mm or less, and that the temperature of this zone is lower than the decomposition reaction temperature, that is, 250° C. or lower.

本発明方法で供給原料として用いられるポリオレフィン
系プラスチックには、ポリエチレン、ポリプロピレン、
ポリブチレンのようなオレフィンの単独重合体のほか、
エチレン、プロピレン、ブチレンその他のオレフィンと
共重合可能な単量体との共重合体あるいは架橋ポリエチ
レンなども包含される。
Polyolefin plastics used as feedstock in the method of the present invention include polyethylene, polypropylene,
In addition to olefin homopolymers such as polybutylene,
Copolymers of ethylene, propylene, butylene and other olefins with copolymerizable monomers, crosslinked polyethylene, and the like are also included.

本発明方法における、これらプラスチックの熱分解に要
する時間は、プラスチックの種類により若干変わるが通
常、数分ないし数時間の範囲である。
The time required for thermal decomposition of these plastics in the method of the present invention varies slightly depending on the type of plastic, but is usually in the range of several minutes to several hours.

本発明方法によれば、これまでなんら利用されることな
く廃棄されていたポリオレフィン系プラスチック廃棄物
を主原料として、有用な炭化水素油を製造しうるので、
資源の有効利用及び公害防止の面で非常に有意義な技術
ということができる。
According to the method of the present invention, useful hydrocarbon oil can be produced using polyolefin plastic waste, which has been discarded without being used in any way, as a main raw material.
It can be said that this is a very meaningful technology in terms of effective use of resources and prevention of pollution.

次に実施例によって本発明をさらに詳細に説明する。Next, the present invention will be explained in more detail with reference to Examples.

実施例 図面と同じ構造をもつ反応装置において、分解反応器1
を高さ150mm、内径31mm、また、充てん塔2を
高さ50mm、内径31朋のそれぞれパイレックスガラ
ス製のものとし、これに粒径の異なるガラスピーズを詰
め、熱分解温度を変えてポリエチレン10グを熱分解し
た。
In the reactor having the same structure as the example drawings, the decomposition reactor 1
The packed tower 2 was made of Pyrex glass with a height of 150 mm and an inner diameter of 31 mm, and filled with glass beads of different particle sizes. was thermally decomposed.

この際の充てん塔の温度としては250℃を用いた。The temperature of the packed tower at this time was 250°C.

またポリエチレンは、粒径約37rL7ILのベレット
状で、密度0.952、発熱量11000 cal/P
のものを用いた。
Polyethylene is pellet-shaped with a particle size of approximately 37rL7IL, a density of 0.952, and a calorific value of 11000 cal/P.
I used the one from

。このようにして得られた炭化水素油の分析結果を次
表に示す。
. The analysis results of the hydrocarbon oil thus obtained are shown in the following table.

【図面の簡単な説明】[Brief explanation of the drawing]

図は本発明方法を実施するのに好適な装置の断面略解図
であり、図中符号は以下のものを示す。 1・・・・・・熱分解反応器、2・・・・・・充てん塔
、3・・・・・・排出口、4・・・・・・原料供給口、
6・・・・・・受器、10゜11・・・・・・電熱線。
The figure is a schematic cross-sectional view of an apparatus suitable for carrying out the method of the present invention, and the reference numerals in the figure indicate the following. 1... Pyrolysis reactor, 2... Packed tower, 3... Discharge port, 4... Raw material supply port,
6... Receiver, 10°11... Heating wire.

Claims (1)

【特許請求の範囲】 1 ポリオレフィン系プラスチックを熱分解し、その蒸
気状生成物をさらに加熱された充てん帯域に通して炭化
水素油を製造する方法において、熱分解温度を430〜
470℃の範囲に保つこと及び充てん帯域を粒径6.5
mm以下のガラスピーズにより形成し、かつ250℃
以下の温度に保つことを特徴とする熱分解方法。 2 ポリオレフィン系プラスチックがポリエチレン、ポ
リプロピレン、ポリブチレン又はエチレンとプロピレン
との共重合体である特許請求の範囲第1項記載の方法。
[Claims] 1. A method for producing hydrocarbon oil by thermally decomposing a polyolefin plastic and passing the vaporized product through a heated packed zone, wherein the thermal decomposition temperature is 430 to 430°C.
Keeping the temperature within the range of 470℃ and filling zone with particle size 6.5
Formed with glass beads of mm or less, and heated at 250°C
A pyrolysis method characterized by maintaining the temperature at: 2. The method according to claim 1, wherein the polyolefin plastic is polyethylene, polypropylene, polybutylene, or a copolymer of ethylene and propylene.
JP54122179A 1979-09-22 1979-09-22 Method for thermal decomposition of polyolefin plastics Expired JPS5822067B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP54122179A JPS5822067B2 (en) 1979-09-22 1979-09-22 Method for thermal decomposition of polyolefin plastics

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP54122179A JPS5822067B2 (en) 1979-09-22 1979-09-22 Method for thermal decomposition of polyolefin plastics

Publications (2)

Publication Number Publication Date
JPS5645984A JPS5645984A (en) 1981-04-25
JPS5822067B2 true JPS5822067B2 (en) 1983-05-06

Family

ID=14829526

Family Applications (1)

Application Number Title Priority Date Filing Date
JP54122179A Expired JPS5822067B2 (en) 1979-09-22 1979-09-22 Method for thermal decomposition of polyolefin plastics

Country Status (1)

Country Link
JP (1) JPS5822067B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6023480A (en) * 1983-07-18 1985-02-06 Mikami Junichi Carbonization apparatus for oil-containing material such as rubber
JPS63282166A (en) * 1987-05-11 1988-11-18 Agency Of Ind Science & Technol High-density metal boride-base sintered ceramics body
JPH0386791A (en) * 1989-08-31 1991-04-11 Mobil Oil Corp Method for producing low-boiling hydrocarbon oil
CN107849361B (en) 2015-07-06 2020-10-16 三菱瓦斯化学株式会社 Resin compositions, prepregs, resin sheets, metal-clad laminates and printed circuit boards

Also Published As

Publication number Publication date
JPS5645984A (en) 1981-04-25

Similar Documents

Publication Publication Date Title
Das et al. The effect of slow pyrolysis on the conversion of packaging waste plastics (PE and PP) into fuel
Williams et al. The pyrolysis of individual plastics and a plastic mixture in a fixed bed reactor
Park et al. Clean bio-oil production from fast pyrolysis of sewage sludge: effects of reaction conditions and metal oxide catalysts
Mastral et al. Pyrolysis of high-density polyethylene in a fluidised bed reactor. Influence of the temperature and residence time
Kholidah et al. Polystyrene plastic waste conversion into liquid fuel with catalytic cracking process using Al2O3 as catalyst
Kaminsky et al. Pyrolysis of mixed plastics into aromatics
Undri et al. Efficient disposal of waste polyolefins through microwave assisted pyrolysis
Wu et al. Pyrolysis behavior of low-density polyethylene over HZSM-5 via rapid infrared heating
Kaminsky Chemical recycling of mixed plastics of pyrolysis
Lin et al. Catalytic conversion of commingled polymer waste into chemicals and fuels over spent FCC commercial catalyst in a fluidised-bed reactor
Aisien et al. Production and characterization of liquid oil from the pyrolysis of waste high-density polyethylene plastics using spent fluid catalytic cracking catalyst
JPH06500592A (en) Monomer recovery from polymers
Martynis et al. Thermal pyrolysis of polypropylene plastic waste into liquid fuel: reactor performance evaluation
EP3311969A1 (en) Device for thermally decomposing polyethylene and polypropylene waste
Ahmad et al. Oil recovery from microwave co-pyrolysis of polystyrene and polypropylene plastic particles for pollution mitigation
EP3312223B1 (en) Method for thermally decomposing polyethylene and polypropylene waste
US6193780B1 (en) Process and apparatus for the recovery of aluminum and energy from used aluminum-plastic packages
Lee Pyrolysis of waste polystyrene and high-density polyethylene
JPS5822067B2 (en) Method for thermal decomposition of polyolefin plastics
He et al. Study on the synergistic effect during co-pyrolysis of chlorella and polyvinyl chloride: Thermal behavior, kinetic and thermodynamic analysis
CN1102605C (en) Process for treating waste rubber or plastics and its gasifying equipment
Ani et al. Microwave induced fast pyrolysis of scrap rubber tires
Alla et al. Simulation and design for process to convert plastic waste to liquid fuel using Aspen HYSYS Program
US10774269B2 (en) Method of preparation of hydrocarbon fuels from polyolefin waste materials
Aswan et al. Re-Design Pyrolysis Reactor Prototype for the Conversion of Plastic Waste into Liquid Fuel