JP2922760B2 - Waste plastic oil production facility - Google Patents

Waste plastic oil production facility

Info

Publication number
JP2922760B2
JP2922760B2 JP24542593A JP24542593A JP2922760B2 JP 2922760 B2 JP2922760 B2 JP 2922760B2 JP 24542593 A JP24542593 A JP 24542593A JP 24542593 A JP24542593 A JP 24542593A JP 2922760 B2 JP2922760 B2 JP 2922760B2
Authority
JP
Japan
Prior art keywords
raw material
waste plastic
material mixing
tank
mixing tank
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
JP24542593A
Other languages
Japanese (ja)
Other versions
JPH07102264A (en
Inventor
淳志 小林
信行 三方
隆春 武内
渡 白水
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.)
NITSUTETSU PURANTO SETSUKEI KK
Nippon Steel Corp
Original Assignee
NITSUTETSU PURANTO SETSUKEI KK
Nippon Steel Corp
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 NITSUTETSU PURANTO SETSUKEI KK, Nippon Steel Corp filed Critical NITSUTETSU PURANTO SETSUKEI KK
Priority to JP24542593A priority Critical patent/JP2922760B2/en
Publication of JPH07102264A publication Critical patent/JPH07102264A/en
Application granted granted Critical
Publication of JP2922760B2 publication Critical patent/JP2922760B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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
    • 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

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、廃プラスチック材を溶
融・分解して、低分子炭化水素化合物を得る廃プラスチ
ック処理設備における廃プラスチックの溶融方法に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for melting waste plastic in a waste plastic treatment facility for melting and decomposing a waste plastic material to obtain a low molecular weight hydrocarbon compound.

【0002】[0002]

【従来の技術】従来、廃プラスチック材の溶融加熱分解
手段として、例えば、特公平3−86791号公報に記
載された方式のものがある。
2. Description of the Related Art Conventionally, as a means for melting and decomposing a waste plastic material, for example, there is a method described in Japanese Patent Publication No. 3-86691.

【0003】この方式は、図7に示すように、破砕装置
によって得た廃プラスチック破砕物Aを押出機(ルー
ダ)1によって加熱・混錬して一次溶融したのち、原料
混合槽2に供給し、この原料混合槽で二次溶融・分解し
て一次溶融物Bを熱分解槽3に供給し、この溶融物の気
化物を接触分解槽4において低分子炭化水素化合物に接
触転化するものである。
According to this method, as shown in FIG. 7, a waste plastic crushed material A obtained by a crushing device is heated and kneaded by an extruder (ruder) 1 to be primarily melted, and then supplied to a raw material mixing tank 2. The primary melt B is secondarily melted and decomposed in the raw material mixing tank, the primary melt B is supplied to the pyrolysis tank 3, and a vaporized product of the melt is catalytically converted into a low-molecular hydrocarbon compound in the catalytic cracking tank 4. .

【0004】このように、この従来の方式における熱分
解槽3に供給されるプラスチック材は、一旦、押出機
(ルーダ)1によって一次溶融されたのち原料混合槽2
において二次溶融・分解して、この原材料を熱分解槽3
に均一な溶融・分解状態で供給して、安定した熱分解プ
ロセスを達成しようとするものである。
[0004] As described above, the plastic material supplied to the pyrolysis tank 3 in this conventional method is firstly melted by the extruder (ruder) 1 and then mixed with the raw material mixing tank 2.
The raw material is secondarily melted and decomposed in
In a uniform molten and decomposed state to achieve a stable pyrolysis process.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、廃プラ
スチック材の中に塩化ビニルを多く含有する場合には、
この押出機において、多量の塩化水素ガスが発生し、原
材料に含まれる水分の共存下で該押出機の低温部にて塩
化水素ガスが凝縮して塩酸となるため、ハステロイなど
の高価な耐腐食材料を適用する必要があり、高価なもの
とならざるを得ない。
However, when waste plastic material contains a large amount of vinyl chloride,
In this extruder, a large amount of hydrogen chloride gas is generated, and in the coexistence of water contained in the raw materials, the hydrogen chloride gas is condensed to form hydrochloric acid in a low temperature part of the extruder. Materials have to be applied and must be expensive.

【0006】また、製品油への塩化水素の混入による油
品質の劣化を防止するためには、前段である押出機に
て、発生する多量の塩化水素ガスを押出機内から外部へ
吸引等で完全に除去する必要があり、そのためには、押
出機の軸方向の長さを極端に長くし、押出機内で一次溶
融された廃プラスチック材を長時間にわたって攪拌・滞
流しなければならず、押出機の設備費が極端にアップす
ると共に廃プラスチック処理設備全体として連続処理を
行う中、前記押出機での長時間の攪拌・滞流時間は円滑
なる連続処理を阻害する。このため、従来、押出機の軸
方向の長さは、生産性を重視した連続処理を円滑に行え
るよう適度な軸方向長さとしている。
Further, in order to prevent deterioration of oil quality due to mixing of hydrogen chloride into product oil, a large amount of hydrogen chloride gas generated in the extruder, which is a former stage, is completely sucked from the inside of the extruder to the outside. In order to do so, the length of the extruder in the axial direction must be extremely long, and the waste plastic material that has been primarily melted in the extruder must be stirred and stagnated for a long time. During the continuous processing of the waste plastic processing equipment as a whole, while the facility cost of the extruder is extremely increased, the long stirring / flow time in the extruder hinders the smooth continuous processing. For this reason, conventionally, the axial length of the extruder is set to an appropriate axial length so that continuous processing with an emphasis on productivity can be smoothly performed.

【0007】それにより押出機以降の例えば原料混合
槽、熱分解槽において溶融プラスチック中から塩化水素
が発生し、これが製品の油の中へ混入するため、例えば
脱クロル槽等の脱クロル手段が必要であった。
[0007] As a result, hydrogen chloride is generated from the molten plastic in the raw material mixing tank and the pyrolysis tank, for example, after the extruder, and this is mixed into the oil of the product. Therefore, dechlorination means such as a dechlorination tank is required. Met.

【0008】また、廃プラスチック材を押出機において
溶融・混錬するには押出機内で溶融する廃プラスチック
材の粘性が高いため、多大の駆動力を要する。
Further, in order to melt and knead the waste plastic material in the extruder, a large driving force is required because the viscosity of the waste plastic material melted in the extruder is high.

【0009】このように従来の押出機においては、前記
のとおり、 塩化水素に耐える高価な耐腐食材料にて押出機を製
作しなければならない。
As described above, in the conventional extruder, as described above, the extruder must be made of an expensive corrosion-resistant material that can withstand hydrogen chloride.

【0010】 押出機の後流側の設備に別に脱クロル
手段が必要。
[0010] Separate dechlorination means is required for equipment downstream of the extruder.

【0011】 操業時に多大の電力を必要とする。[0011] A large amount of power is required during operation.

【0012】等の種々の課題がある。There are various problems such as:

【0013】したがって、押出機によるこの一次溶融を
省略できれば、廃プラスチック処理設備全体としての設
備費用・操業費用の低減のみならず、建設工程も短縮で
き、利点は多大なものである。
Therefore, if the primary melting by the extruder can be omitted, not only the equipment cost and operation cost of the entire waste plastic processing facility can be reduced, but also the construction process can be shortened, and the advantages are great.

【0014】ところが、この押出機を単に省略しただけ
では、原料混合槽内に常温で投入される廃プラスチック
破砕物Aと熱分解槽から供給される液状のプラスチック
溶融物との混合が十分に行われず、その均一溶融物を得
るのに時間と手間を要し、生産性及び油品質の低下をま
ねくと共に、塩化ビニルの加熱による塩化水素ガスの多
量の発生による設備への耐腐食対策を施す必要があり、
設備費用面で、押出機を設けた従来のものよりも逆に高
価なものとならざるを得ない。
However, simply omitting the extruder sufficiently mixes the waste plastic crushed material A charged into the raw material mixing tank at room temperature with the liquid plastic melt supplied from the pyrolysis tank. It takes time and effort to obtain a homogeneous melt, which leads to a decrease in productivity and oil quality, and it is necessary to take measures against corrosion of equipment due to the generation of a large amount of hydrogen chloride gas due to the heating of vinyl chloride. There is
In terms of equipment cost, it is inevitably more expensive than the conventional one provided with an extruder.

【0015】本発明の目的は、原料廃プラスチック材の
溶融・分解による低分子炭化水素化合物化における原料
の溶融・分解・油化処理において、押出機のような一次
溶融装置を使用することなく、また、廃プラスチック処
理設備全体の連続操業を円滑に行うとともに油品質の低
下を起こすことなく、更に原材料中の塩化ビニルの分解
により発生する塩化水素ガスの凝縮による塩酸腐食被害
の発生がない手段を提供することにある。
An object of the present invention is to provide a low-molecular hydrocarbon compound by melting / decomposing a raw material waste plastic material, in which the raw material is melted / decomposed / oiled without using a primary melting device such as an extruder. In addition, measures shall be taken to ensure that continuous operation of the entire waste plastic processing facility is smoothly performed and that no deterioration in oil quality occurs and that no hydrochloric acid corrosion damage occurs due to condensation of hydrogen chloride gas generated by decomposition of vinyl chloride in raw materials. To provide.

【0016】[0016]

【課題を解決するための手段】本発明は、上部に廃プラ
スチックの投入口を有する少なくとも2個以上の原料混
合槽を配設し、該原料混合槽の後流側に熱分解槽及び接
触分解槽を直列に連設し、前記熱分解槽と前記複数の原
料混合槽とを両者の内容物を各々交互に循環せしめるよ
うに接続し、前記原料混合槽に内容物の攪拌手段および
または自己循環手段を設けるとともに塩化水素の除去手
段を各々配設してなる廃プラスチックの油化製造設備で
ある
According to the present invention , at least two or more raw material mixing tanks having a waste plastic inlet at the top are provided , and a pyrolysis tank and a catalytic cracking tank are provided downstream of the raw material mixing tank. The tanks are connected in series, and the pyrolysis tank and the plurality of raw material mixing tanks are connected so as to alternately circulate the contents of both, and the raw material mixing tank has a stirring means and / or self-circulation of the contents. in Yuka manufacturing facility waste plastic obtained by respectively arranged means for removing the hydrogen chloride is provided with the means
There is .

【0017】[0017]

【作用】複数の原料混合槽A、Bにより、交互に廃プラ
スチック原料を処理し、熱分解槽へ連続して供給するた
め結果的には、廃プラスチックの油化製造設備全体とし
て、連続して処理できる。
The waste plastic raw material is alternately processed by the plurality of raw material mixing tanks A and B and is continuously supplied to the pyrolysis tank. As a result, the waste plastic oil production facility is continuously operated. Can be processed.

【0018】原料混合槽において、廃プラスチック原料
に含まれている特に塩化水素等を完全に除去することが
できる。
In the raw material mixing tank, particularly, hydrogen chloride and the like contained in the waste plastic raw material can be completely removed.

【0019】以上により押出機を省略することができ
る。
As described above, the extruder can be omitted.

【0020】[0020]

【実施例】図1に、本発明の廃プラスチックの油化処理
設備の全体概要図を示す。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 shows an overall schematic diagram of a waste plastic oil treatment apparatus according to the present invention.

【0021】図中、2は原料混合槽、3は熱分解槽、4
は接触分解槽、5はポンプ、6はバルブ、7は排風機、
8は塩化水素の除去手段である水洗塔、9は原料混合槽
への廃プラスチック原料の投入口、10は攪拌手段であ
る回転式攪拌機、12は原料混合槽内での溶融ポンプに
よる自己循環手段を示す。
In the figure, 2 is a raw material mixing tank, 3 is a pyrolysis tank, 4
Is a catalytic cracking tank, 5 is a pump, 6 is a valve, 7 is an exhaust fan,
8 is a washing tower as a means for removing hydrogen chloride, 9 is an inlet for the waste plastic raw material into the raw material mixing tank, 10 is a rotary stirrer as a stirring means, and 12 is a self-circulating means by a melting pump in the raw material mixing tank. Is shown.

【0022】以上の主な各部品より、本発明の廃プラス
チックの油化処理設備が構成される。
The above-mentioned main components constitute the waste plastic oil treatment equipment of the present invention.

【0023】図2〜図5を用いて、本発明の廃プラスチ
ックの油化処理設備を使用した廃プラスチックの油化処
理方法を説明する。
2 to 5, a method of liquefying waste plastic using the waste plastic liquefaction equipment of the present invention will be described.

【0024】なお、図2〜図5において、バルブ6の開
閉状態については、◇を開、◆を閉として各図共通で表
す。
In FIGS. 2 to 5, the open / closed state of the valve 6 is indicated by ◇ as open and ◆ as closed in each drawing.

【0025】<工程1>図2を参照して、予め破砕機等
により切断・破砕された廃プラスチックの原料を原料混
合槽Aに、廃プラスチック原料の投入口9を開口して内
部に投入し、その後、該投入口9を閉める。つぎに熱分
解槽4から約400〜450℃の熱分解油を原料混合槽
Aに搬入する。
<Step 1> Referring to FIG. 2, waste plastic raw material previously cut and crushed by a crushing machine or the like is introduced into raw material mixing tank A, and waste plastic raw material input port 9 is opened and opened. Then, the inlet 9 is closed. Next, a pyrolysis oil of about 400 to 450 ° C. is carried into the raw material mixing tank A from the pyrolysis tank 4.

【0026】原料混合槽Aでは、投入した廃プラスチッ
クの原料が、熱分解槽4から供給される約400〜45
0℃の熱分解油により溶融されていくが、この時、溶融
促進、溶融プラスチック表面更新のために、回転式攪拌
機10を回転または原料混合槽A内の溶融物を自己循環
手段により循環させる。
In the raw material mixing tank A, the input waste plastic raw material is supplied from the pyrolysis tank 4 to about 400-45.
It is melted by the pyrolysis oil at 0 ° C. At this time, in order to promote melting and renew the surface of the molten plastic, the rotary stirrer 10 is rotated or the melt in the raw material mixing tank A is circulated by the self-circulation means.

【0027】原料混合槽Aでの溶融・反応温度は、約2
50〜350℃であり、従って、投入した廃プラスチッ
クの原料にPVCの混入がない場合には、約1時間以
上、またPVCが混入する場合には、約3〜5時間以上
この温度状態を保持し、投入した廃プラスチック原料に
含まれている特に塩化水素を全て離脱させる。離脱した
塩化水素は、水洗塔に送られ無害化され、その後大気中
に放散される。
The melting and reaction temperature in the raw material mixing tank A is about 2
The temperature is 50 to 350 ° C. Therefore, when PVC is not mixed in the raw material of the waste plastic, about 1 hour or more, and when PVC is mixed, the temperature is maintained for about 3 to 5 hours or more. Then, particularly, all the hydrogen chloride contained in the input waste plastic raw material is removed. The separated hydrogen chloride is sent to a washing tower, where it is rendered harmless, and then released into the atmosphere.

【0028】<工程2>図3を参照して、一方、前記の
処理の間、好ましくは原料混合槽Aでの必要な溶融・混
合時間の約半分経過後に、原料混合槽Bにおいては、前
記原料混合槽Aと同じ処理をする。
<Step 2> Referring to FIG. 3, on the other hand, in the raw material mixing tank B, preferably after about half of the required melting and mixing time in the raw material mixing tank A, The same processing as in the raw material mixing tank A is performed.

【0029】詳しく説明すると、予め破砕機等により切
断・破砕された廃プラスチックの原料を原料混合槽B
に、廃プラスチック原料の投入口9を開口し内部に投入
し、その後該投入口9を閉める。つぎに熱分解槽4から
約400〜450℃の熱分解油を原料混合槽Bに搬入す
る。
More specifically, the raw plastic material cut and crushed by a crusher or the like in advance is mixed with a raw material mixing tank B.
Then, the input port 9 of the waste plastic raw material is opened and charged into the inside, and then the input port 9 is closed. Next, a pyrolysis oil of about 400 to 450 ° C. is carried into the raw material mixing tank B from the pyrolysis tank 4.

【0030】原料混合槽Bでは、投入した廃プラスチッ
クの原料が、熱分解槽4から供給される約350〜40
0℃の熱分解油により溶融されていくが、この時、溶融
促進、溶融プラスチックの表面更新のために、回転式攪
拌機10を回転または原料混合槽B内の溶融物を自己循
環手段により循環させる。
In the raw material mixing tank B, the input waste plastic raw material is supplied from the pyrolysis tank 4 to about 350 to 40.
It is melted by the pyrolysis oil at 0 ° C. At this time, in order to promote melting and renew the surface of the molten plastic, the rotary stirrer 10 is rotated or the melt in the raw material mixing tank B is circulated by the self-circulating means. .

【0031】原料混合槽Bでの溶融・反応温度は、約2
50〜350℃であり、従って、投入した廃プラスチッ
クの原料にPVCの混入がない場合には、約1時間以
上、またPVCが混入する場合には、約3〜5時間以上
この温度状態を保持し、投入した廃プラスチック原料に
含まれている特に塩化水素を全て離脱させる。
The melting and reaction temperature in the raw material mixing tank B is about 2
The temperature is 50 to 350 ° C. Therefore, when PVC is not mixed in the raw material of the waste plastic, about 1 hour or more, and when PVC is mixed, the temperature is maintained for about 3 to 5 hours or more. Then, particularly, all the hydrogen chloride contained in the input waste plastic raw material is removed.

【0032】離脱した塩化水素は、水洗塔に送られて無
害化され、その後大気中に放散される。
The separated hydrogen chloride is sent to a washing tower to be rendered harmless, and then released into the atmosphere.

【0033】<工程3>図4を参照して、前記原料混合
槽Bへの熱分解油の搬送の後、原料混合槽Aにおいて、
混合物の溶融・反応が完了、つまり廃プラスチック原料
に含まれている特に塩化水素が全て離脱された後、該溶
融プラスチックは、熱分解槽4へ戻される。熱分解槽4
には、外部からの加熱手段により約400〜450℃に
保たれ溶融プラスチックの熱分解反応が促進され、熱分
解ガスは、後流側に配設された接触分解槽4に搬送され
油化される。
<Step 3> Referring to FIG. 4, after transporting the pyrolysis oil to the raw material mixing tank B, in the raw material mixing tank A,
After the melting and reaction of the mixture are completed, that is, after all the hydrogen chloride contained in the waste plastic raw material is completely removed, the molten plastic is returned to the pyrolysis tank 4. Pyrolysis tank 4
The pyrolysis reaction of the molten plastic is maintained at about 400 to 450 ° C. by an external heating means, and the pyrolysis gas is conveyed to the catalytic cracking tank 4 arranged on the downstream side to be turned into oil. You.

【0034】<工程4>内部が空になった原料混合槽A
には、前記<工程1>を繰り返し行う。
<Step 4> Raw material mixing tank A whose interior is empty
, The <Step 1> is repeated.

【0035】<工程5>前記原料混合槽Aへの熱分解油
の搬送の後、原料混合槽Bにおいて、混合物の溶融・反
応が完了、つまり廃プラスチック原料に含まれている特
に塩化水素が全て離脱された後、該溶融プラスチック
は、熱分解槽4へ戻される。熱分解槽4には、外部から
の加熱手段により約400〜450℃に保たれ溶融プラ
スチックの熱分解反応が促進され、熱分解ガスは、後流
側に配設された接触分解槽4に搬送され油化処理され
る。
<Step 5> After the pyrolysis oil is conveyed to the raw material mixing tank A, the melting and reaction of the mixture is completed in the raw material mixing tank B, that is, all the hydrogen chloride contained in the waste plastic raw material is completely removed. After being separated, the molten plastic is returned to the pyrolysis tank 4. The pyrolysis tank 4 is maintained at about 400 to 450 ° C. by an external heating means to promote the pyrolysis reaction of the molten plastic, and the pyrolysis gas is transported to the catalytic cracking tank 4 arranged on the downstream side. And oiled.

【0036】<工程6>内部が空になった原料混合槽B
には、前記<工程2>を繰り返し行う。
<Step 6> A raw material mixing tank B having an empty interior
The <Step 2> is repeated.

【0037】上記の工程1から工程5を原料混合槽A及
び原料混合槽Bでの繰り返しを行うことにより、熱分解
槽4において、連続的に安定した熱分解を行うことがで
き、その結果、連続的に安定した油化ができる。
By repeating the above steps 1 to 5 in the raw material mixing tank A and the raw material mixing tank B, it is possible to continuously and stably perform pyrolysis in the pyrolysis tank 4. Continuous stable oiling is possible.

【0038】前記の各工程を図にしたものを図5に示
す。
FIG. 5 is a diagram illustrating the above steps.

【0039】なお、本実施例においては、原料混合槽の
数をA、Bの2つ配設し使用したが、連続した処理の途
中で、原料混合槽に投入する廃プラスチック原料に含ま
れている特に塩化水素等の量が異なる場合は、原料混合
槽をもう一つ余分に配設しておくと容易に連続処理に対
応することができる。
In the present embodiment, the number of the raw material mixing tanks A and B is set to two and used. However, during the continuous processing, the raw plastic mixing tank is included in the waste plastic raw material charged into the raw material mixing tank. In particular, when the amounts of hydrogen chloride and the like are different, it is possible to easily cope with the continuous processing by providing another extra raw material mixing tank.

【0040】この場合の各工程を図6に示す。FIG. 6 shows each step in this case.

【0041】溶融・混合槽での廃プラスチックの滞留時
間をより大きく取ることにより、高塩化水素混入プラス
チックでの高い脱塩化水素除去率を得ることができる。
By increasing the residence time of the waste plastic in the melting / mixing tank, it is possible to obtain a high removal rate of hydrogen chloride from the plastic containing a large amount of hydrogen chloride.

【0042】[0042]

【発明の効果】【The invention's effect】

(1)原料混合槽において、廃プラスチック原料に含ま
れている特に塩化水素等を完全に除去することができ、
後流側に脱塩化水素等の除去の設備が不要となるととも
に、製品の油化中に脱塩化水素等が混入することがなく
なり、製品の品質が高品位で安定する。
(1) In the raw material mixing tank, it is possible to completely remove particularly hydrogen chloride and the like contained in the waste plastic raw material,
Equipment for removing dehydrochloride and the like is not required on the downstream side, and dehydrochloride and the like are not mixed during the oilification of the product, so that the quality of the product is high and stable.

【0043】(2)高価で保守が複雑な押出機を使用し
なくても、安価で保守の容易な原料混合槽を1つ増設す
ることにより連続処理が可能となる。
(2) Even if an extruder that is expensive and complicated to maintain is not used, continuous processing can be performed by adding one raw material mixing tank that is inexpensive and easy to maintain.

【図面の簡単な説明】[Brief description of the drawings]

【図1】 本発明の廃プラスチックの油化処理設備の全
体概要図を示す。
FIG. 1 is an overall schematic view of a waste plastic oil treatment apparatus of the present invention.

【図2】 本発明の廃プラスチックの油化処理設備を使
用した油化処理方法の工程説明図を示す。
FIG. 2 is a process explanatory view of an oil treatment method using the waste plastic oil treatment equipment of the present invention.

【図3】 本発明の廃プラスチックの油化処理設備を使
用した油化処理方法の工程説明図を示す。
FIG. 3 is a process explanatory view of an oil treatment method using the waste plastic oil treatment equipment of the present invention.

【図4】 本発明の廃プラスチックの油化処理設備を使
用した油化処理方法の工程説明図を示す。
FIG. 4 is a process explanatory view of an oil treatment method using the waste plastic oil treatment equipment of the present invention.

【図5】 原料混合槽A、Bでの工程簡略図を示す。FIG. 5 shows a simplified process diagram in raw material mixing tanks A and B.

【図6】 原料混合槽A、B、Cでの工程簡略図を示
す。
FIG. 6 shows a simplified process diagram in raw material mixing tanks A, B, and C.

【図7】 従来の油化処理設備の全体概要図を示す。FIG. 7 shows an overall schematic diagram of a conventional oil treatment apparatus.

【符号の説明】[Explanation of symbols]

1 押出機 2 原料混合槽 3 熱分解槽 4 接触分解槽 5 ポンプ 6 バルブ 7 排風機 8 水洗塔 9 原料投入口 10 回転式攪拌機 11 自己循環手段 REFERENCE SIGNS LIST 1 extruder 2 raw material mixing tank 3 thermal decomposition tank 4 catalytic cracking tank 5 pump 6 valve 7 exhaust fan 8 washing tower 9 raw material inlet 10 rotary stirrer 11 self-circulation means

───────────────────────────────────────────────────── フロントページの続き (72)発明者 三方 信行 福岡県北九州市戸畑区大字中原46−59 新日本製鐵株式会社 機械・プラント事 業部内 (72)発明者 武内 隆春 福岡県北九州市戸畑区大字中原46−59 新日本製鐵株式会社 機械・プラント事 業部内 (72)発明者 白水 渡 福岡県北九州市戸畑区大字中原46番地の 59 日鐵プラント設計株式会社内 (56)参考文献 特開 昭49−66776(JP,A) 特開 昭48−26869(JP,A) (58)調査した分野(Int.Cl.6,DB名) C10G 1/10 B09B 3/00 C08J 11/12 ──────────────────────────────────────────────────続 き Continued on front page (72) Inventor Nobuyuki Mikata 46-59 Ohara Nakahara, Tobata-ku, Kitakyushu-shi, Fukuoka Nippon Steel Corporation Machinery & Plant Business Department (72) Inventor Takaharu Takeuchi Tobata-ku, Kitakyushu-shi, Fukuoka 46-59 Ohara Nakahara Nippon Steel Corporation Machinery & Plant Division (72) Inventor Wataru Shiramizu 59 Nippon Steel Plant Design Co., Ltd., 46 Ohara Nakahara, Tobata-ku, Kitakyushu, Fukuoka Prefecture (56) References 49-66776 (JP, A) JP-A-48-26869 (JP, A) (58) Fields investigated (Int. Cl. 6 , DB name) C10G 1/10 B09B 3/00 C08J 11/12

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 上部に廃プラスチックの投入口を有する
少なくとも2個以上の原料混合槽を配設し、該原料混合
槽の後流側に熱分解槽及び接触分解槽を直列に連設し、
前記熱分解槽と前記複数の原料混合槽とを両者の内容物
各々交互に循環せしめるように接続し、前記原料混合
槽に内容物の攪拌手段およびまたは自己循環手段を設け
るとともに塩化水素の除去手段を各々配設してなる廃プ
ラスチックの油化製造設備。
At least two or more raw material mixing tanks having a waste plastic inlet at an upper portion thereof are disposed, and a pyrolysis tank and a catalytic cracking tank are connected in series on a downstream side of the raw material mixing tank,
The pyrolysis tank and the plurality of raw material mixing tanks are connected so as to alternately circulate the contents of both, and the raw material mixing tank is provided with a means for stirring the contents and / or a means for self-circulation, while removing hydrogen chloride. Yuka production equipment waste plastic obtained by respectively disposed means.
JP24542593A 1993-09-30 1993-09-30 Waste plastic oil production facility Expired - Fee Related JP2922760B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24542593A JP2922760B2 (en) 1993-09-30 1993-09-30 Waste plastic oil production facility

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24542593A JP2922760B2 (en) 1993-09-30 1993-09-30 Waste plastic oil production facility

Publications (2)

Publication Number Publication Date
JPH07102264A JPH07102264A (en) 1995-04-18
JP2922760B2 true JP2922760B2 (en) 1999-07-26

Family

ID=17133470

Family Applications (1)

Application Number Title Priority Date Filing Date
JP24542593A Expired - Fee Related JP2922760B2 (en) 1993-09-30 1993-09-30 Waste plastic oil production facility

Country Status (1)

Country Link
JP (1) JP2922760B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20030010364A (en) * 2001-07-26 2003-02-05 김동춘 Sulfuration apparatus by cracking reaction of atalyzer-down type and fabrication method for volatile-oil·whale-oil thereby
KR100517898B1 (en) * 2001-07-31 2005-09-30 김범진 Downflow type catalytic cracking reaction apparatus and method for producing gasoline and light oil using waste synthetic resins using the same
KR100782381B1 (en) * 2006-08-03 2007-12-07 한국에너지기술연구원 Method and apparatus for improving fuel quality of pyrolysis reclaimed fuel from wasted plastic and reclaimed fuel manufactured thereof
CN111750358B (en) * 2020-05-29 2021-09-10 浙江科茂环境科技有限公司 Waste plastic green oiling technology embedded garbage incineration method

Also Published As

Publication number Publication date
JPH07102264A (en) 1995-04-18

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