JP3478324B2 - Gasification method of plastic - Google Patents

Gasification method of plastic

Info

Publication number
JP3478324B2
JP3478324B2 JP35451097A JP35451097A JP3478324B2 JP 3478324 B2 JP3478324 B2 JP 3478324B2 JP 35451097 A JP35451097 A JP 35451097A JP 35451097 A JP35451097 A JP 35451097A JP 3478324 B2 JP3478324 B2 JP 3478324B2
Authority
JP
Japan
Prior art keywords
reaction
plastic
gas
water
promoting substance
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
JP35451097A
Other languages
Japanese (ja)
Other versions
JPH11181449A (en
Inventor
建順 傳
基浩 境原
健 飯村
建二 西村
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.)
Mitsubishi Materials Corp
Original Assignee
Mitsubishi Materials 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 Mitsubishi Materials Corp filed Critical Mitsubishi Materials Corp
Priority to JP35451097A priority Critical patent/JP3478324B2/en
Publication of JPH11181449A publication Critical patent/JPH11181449A/en
Application granted granted Critical
Publication of JP3478324B2 publication Critical patent/JP3478324B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts
    • 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]

【発明の属する技術分野】本発明は廃棄されたプラスチ
ックを主に水素ガス等の有用なガスに分解し、再利用す
るプラスチックのガス化方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for gasifying plastics, in which discarded plastics are mainly decomposed into useful gas such as hydrogen gas and reused.

【0002】[0002]

【従来の技術】従来、プラスチック、例えばポリエチレ
ン、ポリプロピレン、ポリ塩化ビニル、ポリスチレン等
の熱可塑性樹脂、ポリウレタン、メラミン、PET(ポ
リエチレンテレフタレート)等の熱硬化性樹脂は生活廃
棄物、産業廃棄物として膨大な量が排出されており、そ
の処分又は再利用が重要な課題となっている。そのた
め、廃棄されたプラスチックをガス化して再利用するす
る方法が種々提案されている。ガス化の方法の一つとし
てプラスチックを反応容器内で超臨界水を含む高温熱水
と接触、反応せしめ、ガス化する方法が知られており、
この方法ではNaOH(アルカリ)、アルキルベンゼン
スルホン酸ナトリウム(界面活性剤)、CH3OH(ア
ルコール類)等が反応触媒として使用されている(特開
平6−299169)。
2. Description of the Related Art Conventionally, plastics, for example, thermoplastic resins such as polyethylene, polypropylene, polyvinyl chloride and polystyrene, and thermosetting resins such as polyurethane, melamine and PET (polyethylene terephthalate) have been enormous as domestic and industrial wastes. A large amount is discharged, and its disposal or reuse is an important issue. Therefore, various methods of gasifying and recycling the discarded plastic have been proposed. As one of the gasification methods, a method is known in which a plastic is contacted with high-temperature hot water containing supercritical water in a reaction vessel to cause a reaction, and gasified,
In this method, NaOH (alkali), sodium alkylbenzenesulfonate (surfactant), CH 3 OH (alcohols) and the like are used as reaction catalysts (JP-A-6-299169).

【0003】[0003]

【発明が解決しようとする課題】しかし、上記従来方法
ではプラスチックの分解で生成するガス中の水素ガスの
割合は低く、また水素ガス自体の生成量も実用上十分で
はない問題がある。本発明の目的は、プラスチックを効
率よく水素ガスに分解することのできるプラスチックの
ガス化方法を提供することにある。
However, in the above-mentioned conventional method, there is a problem that the ratio of hydrogen gas in the gas generated by the decomposition of plastic is low and the amount of hydrogen gas itself generated is not practically sufficient. An object of the present invention is to provide a method for gasifying a plastic, which can efficiently decompose the plastic into hydrogen gas.

【0004】[0004]

【課題を解決するための手段】請求項1に係る発明は、
プラスチックを水と所定の温度で反応させて主に水素ガ
ス等の有用なガスにガス化する方法であって、反応時に
ハロゲンを放出する化合物を反応促進物質として使用
し、反応温度が250〜500℃であり、反応圧力が5
〜305.9kg/cm 2 であることを特徴とするプラ
スチックのガス化方法である。上記反応温度及び反応圧
力の範囲内で反応時にハロゲンを放出する化合物が反応
促進物質として効果的に働くため、プラスチックを効率
よく水素ガスに分解することができる。請求項2に係る
発明は、請求項1に係る発明であって、反応促進物質
塩素を含むプラスチック又はハロゲン化合物であるガス
化方法である。ガス化されるプラスチックが塩素を含む
プラスチックである場合、このプラスチック自体から反
応時に塩素が放出されるため、特に反応促進物質更に
添加しなくてもプラスチックをガス化できる。
The invention according to claim 1 is
Mainly hydrogen gas is generated by reacting plastic with water at a specified temperature.
It is a method of gasifying useful gases such as hydrogen, and uses a compound that releases halogen during the reaction as a reaction accelerator.
The reaction temperature is 250 to 500 ° C. and the reaction pressure is 5
It is a gasification method for plastics, which is characterized in that it is about 305.9 kg / cm 2 . Reaction temperature and reaction pressure
Compounds that release halogen during reaction within the range of force react
Since it works effectively as a promoter , the plastic can be efficiently decomposed into hydrogen gas. The invention according to claim 2 is the invention according to claim 1, wherein the reaction promoting substance is a plastic containing chlorine or a halogen compound. When the plastic to be gasified is a chlorine-containing plastic, chlorine is released from the plastic itself during the reaction, so that a reaction- promoting substance is further added.
The plastic can be gasified without addition .

【0005】[0005]

【0006】[0006]

【発明の実施の形態】本発明で使用される反応促進物質
は反応時にハロゲンを放出する化合物であって、その具
体例としては塩素を含むプラスチック又は塩酸、HB
のハロゲン化合物が挙げられる。塩素を含む熱可塑性
プラスチックとしてはポリ塩化ビニル(PVC)、塩化
ビニル・酢酸ビニル共重合体等が挙げられる。ガス化反
応の終了後に残留した反応促進物質を含む水溶液はこれ
を再度循環させて再利用することができる。この場合、
新たな促進物質更に添加する必要はない。
BEST MODE FOR CARRYING OUT THE INVENTION The reaction accelerator used in the present invention is a compound which releases halogen during the reaction, and specific examples thereof include plastic containing chlorine or hydrochloric acid, HBr .
And other halogen compounds. Examples of the chlorine-containing thermoplastics include polyvinyl chloride (PVC) and vinyl chloride / vinyl acetate copolymers. The aqueous solution containing the reaction promoting substance remaining after the completion of the gasification reaction can be recycled by recycling it. in this case,
It is not necessary to add new accelerating substances .

【0007】次に本発明において、反応時にハロゲンを
放出する化合物が反応促進物質として働く反応の機構に
ついて説明する。例えばプラスチックがポリ塩化ビニル
の場合にはこれ自体が反応促進物質として作用するた
め、特に反応促進物質添加する必要ない。先ずポリ
塩化ビニルが水と250〜500℃の温度、5〜30
5.9kg/cm 2 の圧力で反応することによりポリ塩
化ビニルから塩素が脱離してポリマー内部に炭素ラジカ
ルを生じ、外部に活性な塩素を生じる。雰囲気が250
〜500℃、5〜305.9kg/cm 2 の水であるた
め、この水が上記炭素ラジカルに隣接する炭素原子に結
合する水素原子を攻撃して水素原子を脱離させ、上記炭
素ラジカルは上記炭素原子と二重結合を作る。また外部
に脱離した上記活性な塩素は上記炭素ラジカルに隣接す
る炭素原子に結合する水素原子を攻撃して水素原子を脱
離させ、上記炭素ラジカルは上記炭素原子と二重結合を
作る。活性な塩素は消費されずに残存し、ポリマーの残
りの水素原子を攻撃して水素原子を脱離させ、最終的に
は水と反応して塩酸溶液となる。このようにして脱離し
た水素原子は目的とする水素ガスとなり、捕集され、残
渣は主にカーボンとなる。また、例えばプラスチックと
してポリプロピレンを使用し、反応促進物質として塩酸
を使用した場合には、先ず塩酸が水と250〜500℃
の温度、5〜305.9kg/cm 2 の圧力で反応する
ことにより塩酸が分解して活性な塩素を生じ、この活性
な塩素がポリマーを構成する炭素原子に結合する水素原
子を攻撃して水素原子を脱離させる。活性な塩素は消費
されずに残存し、ポリマーの残りの水素原子を攻撃して
水素原子を脱離させ、最終的には水と反応して塩酸溶液
となる。このようにして脱離した水素原子は目的とする
水素ガスとなり、捕集され、残渣はカーボンとなる。
Next, in the present invention, the mechanism of the reaction in which the compound that releases halogen during the reaction acts as a reaction promoting substance will be described. For example, when the plastic is polyvinyl chloride, it acts as a reaction promoting substance by itself, so that it is not necessary to add a reaction promoting substance . First, polyvinyl chloride is mixed with water at a temperature of 250 to 500 ° C. for 5 to 30
By reacting at a pressure of 5.9 kg / cm 2 , chlorine is desorbed from polyvinyl chloride to generate carbon radicals inside the polymer, and active chlorine is generated outside. Atmosphere is 250
Since it is water at ˜500 ° C. and 5-305.9 kg / cm 2 , this water attacks a hydrogen atom bonded to a carbon atom adjacent to the carbon radical to desorb the hydrogen atom, and the carbon radical is Make a double bond with a carbon atom. Further, the active chlorine released to the outside attacks a hydrogen atom bonded to a carbon atom adjacent to the carbon radical to release the hydrogen atom, and the carbon radical forms a double bond with the carbon atom. The active chlorine remains without being consumed, attacks the remaining hydrogen atoms of the polymer to desorb the hydrogen atoms, and finally reacts with water to form a hydrochloric acid solution. The hydrogen atoms desorbed in this way become the desired hydrogen gas and are collected, and the residue mainly becomes carbon. Also, for example, when polypropylene is used as the plastic and hydrochloric acid is used as the reaction accelerating substance , the hydrochloric acid is first mixed with water at 250 to 500 ° C.
At a temperature of 5 to 305.9 kg / cm 2, the hydrochloric acid decomposes to generate active chlorine, and this active chlorine attacks the hydrogen atoms bonded to the carbon atoms constituting the polymer to generate hydrogen. Detach an atom. Active chlorine remains without being consumed, attacks the remaining hydrogen atoms of the polymer to desorb the hydrogen atoms, and finally reacts with water to form a hydrochloric acid solution. The hydrogen atoms desorbed in this way become the target hydrogen gas, are collected, and the residue becomes carbon.

【0008】本発明のプラスチックのガス化方法を実施
する場合には、例えば図1に示すような装置が用いられ
る。図1に示すように、ガス化装置はプラスチック原
料、水及び反応促進物質が供給される反応器10と水及
び反応促進物質を収納する反応促進物質水溶液槽11と
反応器10で発生したガスを含む流体を冷却する冷却器
12と冷却器12からのガスを含む流体を収納してガス
の容量を測定するガス容量測定器13とガス容量測定器
13からのガスを回収して貯えるガスバッグ14とを備
える。反応器10と反応促進物質水溶液槽11との間に
は予熱器16と高圧無脈流ポンプ17が設けられる。
11内の水及び反応促進物質はポンプ17により吸引加
圧されて予熱器16に送られた後、反応器10に入る。
反応器10内の圧力が所定の値に達した後、反応器10
と予熱器16を図の破線で示す流動層サンドバス18内
に入れて急速に所定の温度まで加熱する。反応器10の
反応温度はその出口に挿入した図示しない熱電対により
直接測定できるように構成される。反応器10には反応
前に矢印Aで示すプラスチック原料が充填され、反応後
に矢印Bで示す反応残渣が取出される。冷却器12とガ
ス容量測定器13との間には減圧弁19及びバルブ20
が設けらる。冷却器12と11との間には減圧弁1
9及びバルブ21が設けられ、ガス容量測定器13と
11との間にはバルブ20及びバルブ21が設けられ
る。またガス容量測定器13とガスバッグ14との間に
はバルブ22が設けられる。
When carrying out the plastic gasification method of the present invention, for example, an apparatus as shown in FIG. 1 is used. As shown in FIG. 1, the gasifier comprises a reactor 10 to which a plastic material, water and a reaction promoting substance are supplied, a reaction promoting substance aqueous solution tank 11 containing water and a reaction promoting substance , and a gas generated in the reactor 10. A cooler 12 for cooling the fluid containing the gas, a gas capacity measuring instrument 13 for storing the fluid containing the gas from the cooler 12 and measuring the capacity of the gas, and a gas bag 14 for collecting and storing the gas from the gas capacity measuring instrument 13. With. A preheater 16 and a high-pressure pulseless flow pump 17 are provided between the reactor 10 and the reaction promoting substance aqueous solution tank 11. The water and the reaction promoting substance in the tank 11 are sucked and pressurized by the pump 17 and sent to the preheater 16 and then enter the reactor 10.
After the pressure in the reactor 10 reaches a predetermined value, the reactor 10
Then, the preheater 16 is put in a fluidized bed sand bath 18 shown by a broken line in the figure to rapidly heat it to a predetermined temperature. The reaction temperature of the reactor 10 can be directly measured by a thermocouple (not shown) inserted in the outlet of the reactor. The reactor 10 is filled with the plastic raw material shown by the arrow A before the reaction, and the reaction residue shown by the arrow B is taken out after the reaction. A pressure reducing valve 19 and a valve 20 are provided between the cooler 12 and the gas capacity measuring device 13.
Is provided et al is Ru. A pressure reducing valve 1 is provided between the cooler 12 and the tank 11.
9 and a valve 21 are provided, and a valve 20 and a valve 21 are provided between the gas capacity measuring device 13 and the tank 11. A valve 22 is provided between the gas capacity measuring device 13 and the gas bag 14.

【0009】このように構成されたガス化装置におい
て、先ずプラスチック原料として塊状の廃プラスチック
を用意し、これを反応器10に充填した後、ポンプ17
を作動させて11内の水及び反応促進物質を反応器1
0及び予熱器16を含む反応系に供給し、減圧弁19を
調整して所定圧力まで加圧する。反応促進物質を含有す
る水の圧力と流量が安定した後、反応器10と予熱器1
6を流動層サンドバス18内に入れて急速に所定の温度
まで昇温する。反応器10から発生するガスを含む流体
は冷却器12で急冷され、減圧弁19により減圧させ、
バルブ20を通過してガス容量測定器13に流入し、こ
こでガスの体積が測定される。ガス容量測定器13内の
ガスはバルブ22を介してガスバッグ14に送られて分
析される。ガス容量測定器13内の水及び反応促進物質
を含む液体はバルブ20,21を介して11に送られ
て再びガス化反応に使用される。このように反応系の温
度及び圧力を所定の値に保ちながら冷却器12の出口か
らガスがほぼ発生しなくなるまで反応を続行させた後、
反応器10と予熱器16を流動層サンドバス18内から
引上げて水で急冷して反応を停止させる。
In the gasifier constructed as described above, a lump of waste plastic is first prepared as a plastic raw material, the reactor 10 is filled with the waste plastic, and then the pump 17 is used.
To activate the water in the tank 11 and the reaction promoting substance in the reactor 1
0 and the reaction system including the preheater 16, and the pressure reducing valve 19 is adjusted to pressurize to a predetermined pressure. After the pressure and the flow rate of the water containing the reaction promoting substance are stabilized, the reactor 10 and the preheater 1
6 is put in the fluidized bed sand bath 18 and rapidly heated to a predetermined temperature. The fluid containing the gas generated from the reactor 10 is rapidly cooled by the cooler 12, and the pressure is reduced by the pressure reducing valve 19.
It passes through the valve 20 and flows into the gas volume measuring device 13, where the volume of gas is measured. The gas in the gas capacity measuring device 13 is sent to the gas bag 14 via the valve 22 and analyzed. The water and the liquid containing the reaction promoting substance in the gas capacity measuring device 13 are sent to the tank 11 via the valves 20 and 21 and used again for the gasification reaction. After continuing the reaction until the gas is substantially not generated from the outlet of the cooler 12 while keeping the temperature and pressure of the reaction system at predetermined values in this way,
The reactor 10 and the preheater 16 are pulled up from the fluidized bed sand bath 18 and quenched with water to stop the reaction.

【0010】[0010]

【実施例】次に本発明の具体的態様を示すために、本発
明の実施例を比較例とともに説明する。 <実施例1> 図1に示した装置により、表1に示す反応条件、即ち、
原料の廃プラスチックとしてポリプロピレン(PP)を
使用し、反応促進物質として塩酸(HCl)を使用し、
400℃の反応温度、305.9kg/cm2(30M
Pa)の反応圧力、120分の反応時間及び塩酸を含む
水の流量を4ml/分としてプラスチックをガス化し
た。この例では反応器10の内容積は約11cm3であ
った。その結果を表1に示す。表1において、発生ガス
量(ml/g)は廃プラスチック1g当りで得られた水
素ガスを含むガスの量を示し、水素含量(%)はガスの
総量に占める水素ガスの割合を示す。
EXAMPLES Next, examples of the present invention will be described together with comparative examples in order to show specific embodiments of the present invention. <Example 1> Using the apparatus shown in FIG. 1, the reaction conditions shown in Table 1, that is,
Polypropylene (PP) is used as the waste plastic of the raw material , hydrochloric acid (HCl) is used as the reaction promoting substance ,
Reaction temperature of 400 ° C, 305.9 kg / cm 2 (30 M
The plastic was gasified with the reaction pressure of Pa), the reaction time of 120 minutes and the flow rate of water containing hydrochloric acid of 4 ml / min. In this example, the internal volume of the reactor 10 was about 11 cm 3 . The results are shown in Table 1. In Table 1, the amount of generated gas (ml / g) shows the amount of gas containing hydrogen gas obtained per 1 g of waste plastic, and the hydrogen content (%) shows the ratio of hydrogen gas to the total amount of gas.

【0011】<実施例2>廃プラスチックとしてポリエ
チレン(PE)を使用したことを除いては実施例1の方
法を繰返してプラスチックをガス化した。その結果を表
1に示す。
Example 2 The method of Example 1 was repeated except that polyethylene (PE) was used as the waste plastic, and the plastic was gasified. The results are shown in Table 1.

【0012】<実施例3> 廃プラスチックとしてポリ塩化ビニル(PVC)を使用
し、反応促進物質を使用しなかったことを除いては実施
例1の方法を繰返してプラスチックをガス化した。その
結果を表1に示す。
Example 3 The method of Example 1 was repeated except that polyvinyl chloride (PVC) was used as the waste plastic and no reaction accelerator was used, and the plastic was gasified. The results are shown in Table 1.

【0013】<実施例4> 廃プラスチックとしてポリ塩化ビニル(PVC)を使用
し、102kg/cm2(10MPa)の反応圧力及び
10分の反応時間で、反応促進物質を使用しなかったこ
とを除いては実施例1の方法を繰返してプラスチックを
ガス化した。その結果を表1に示す。
Example 4 Polyvinyl chloride (PVC) was used as the waste plastic, except that a reaction accelerating substance was not used at a reaction pressure of 102 kg / cm 2 (10 MPa) and a reaction time of 10 minutes. For example, the method of Example 1 was repeated to gasify the plastic. The results are shown in Table 1.

【0014】<実施例5>廃プラスチックとして ポリ
塩化ビニル(PVC)50%とポリプロピレン(PP)
50%とからなる混合物を使用したことを除いては実施
例1の方法を繰返してプラスチックをガス化した。その
結果を表1に示す。
<Example 5> As waste plastics, polyvinyl chloride (PVC) 50% and polypropylene (PP)
The method of Example 1 was repeated except that a mixture consisting of 50% was used to gasify the plastic. The results are shown in Table 1.

【0015】<比較例1> 廃プラスチックとしてポリプロピレン(PP)を使用
し、反応促進物質を使用しなかったことを除いては実施
例1の方法を繰返してプラスチックをガス化した。その
結果を表1に示す。
Comparative Example 1 The method of Example 1 was repeated except that polypropylene (PP) was used as the waste plastic and no reaction accelerator was used, and the plastic was gasified. The results are shown in Table 1.

【0016】<比較例2> 廃プラスチックとしてポリエチレン(PE)を使用し、
反応促進物質を使用しなかったことを除いては実施例1
の方法を繰返してプラスチックをガス化した。その結果
を表1に示す。
Comparative Example 2 Polyethylene (PE) was used as waste plastic,
Example 1 except that no reaction promoter was used
The above method was repeated to gasify the plastic. The results are shown in Table 1.

【0017】[0017]

【表1】 [Table 1]

【0018】表1において、*印は発生ガス量が少ない
ため、水素含量の分析ができなかったことを示す。
In Table 1, the mark * indicates that the hydrogen content could not be analyzed because the amount of generated gas was small.

【0019】<比較評価> 表1から明らかなように、実施例1〜5ではいずれも水
素含量が90%を超えており、プラスチックを効率よく
水素ガスに分解できることが判る。また実施例3〜5に
示すようにプラスチックが塩素を含むプラスチックであ
る場合、反応促進物質更に添加しなくてもプラスチッ
クを効率よくガス化できることが判る。これに対し塩素
を含まないプラスチックであるPP及びPEを使用し、
かつ反応促進物質添加しない比較例1及び2の場合に
は、プラスチックを効率よく水素ガスに分解できないこ
とが判る。
<Comparative Evaluation> As is clear from Table 1, in each of Examples 1 to 5, the hydrogen content exceeds 90%, which shows that the plastic can be efficiently decomposed into hydrogen gas. Further, as shown in Examples 3 to 5, when the plastic is a chlorine-containing plastic, it can be understood that the plastic can be efficiently gasified without further adding a reaction promoting substance . On the other hand, using chlorine-free plastics PP and PE,
In addition, in Comparative Examples 1 and 2 in which the reaction promoting substance is not added, it is understood that the plastic cannot be efficiently decomposed into hydrogen gas.

【0020】[0020]

【発明の効果】以上述べたように、本発明によれば、反
応時にハロゲンを放出する化合物を反応促進物質として
使用して、プラスチックを水と250〜500℃の温度
及び5〜305.9kg/cm 2 の圧力範囲内で反応さ
せてガス化するようにしたので、プラスチックを効率よ
く水素ガスに分解できる。
As described above, according to the present invention, a compound that releases a halogen during the reaction is used as a reaction promoting substance , and the plastic is treated with water at a temperature of 250 to 500 ° C.
And 5 to 305.9 kg / cm 2 within the pressure range of the reaction to cause gasification, so that the plastic can be efficiently decomposed into hydrogen gas.

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

【図1】本発明のプラスチックのガス化方法の実施に用
いる装置の構成図。
FIG. 1 is a configuration diagram of an apparatus used for carrying out a plastic gasification method of the present invention.

【符号の説明】[Explanation of symbols]

10 反応器 11 反応促進物質水溶液槽 12 冷却器 13 ガス容量測定器 14 ガスバッグ 16 予熱器 17 高圧無脈流ポンプ 18 流動層サンドバス 19 減圧弁 20,21,22 バルブ10 Reactor 11 Reaction Accelerator Aqueous Solution Tank 12 Cooler 13 Gas Capacity Measuring Device 14 Gas Bag 16 Preheater 17 High-Pressure Pulse-Free Pump 18 Fluidized Bed Sand Bath 19 Pressure Reducing Valve 20, 21, 22 Valve

───────────────────────────────────────────────────── フロントページの続き (72)発明者 飯村 健 茨城県那珂郡那珂町大字向山字六人頭 1002番地の14 三菱マテリアル株式会社 那珂エネルギー研究所内 (72)発明者 西村 建二 茨城県那珂郡那珂町大字向山字六人頭 1002番地の14 三菱マテリアル株式会社 那珂エネルギー研究所内 (56)参考文献 特開 平6−126744(JP,A) (58)調査した分野(Int.Cl.7,DB名) C10J 3/00 C01B 3/02 - 3/48 C10B 57/00 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Ken Iimura Inventor Ken Iimura Naka-machi, Naka-gun, Ibaraki Prefecture 6-headed six Mukaiyama, Naka-machi, Japan 14 Mitsubishi Materials Corporation Naka Energy Laboratory (72) Inventor Kenji Nishimura Naka-gun, Ibaraki Prefecture Nakamachi, Oita, Mukaiyama, Rokujinzu, No. 1002 14 14 Mitsubishi Materials Corporation, Naka Energy Laboratory (56) Reference JP-A-6-126744 (JP, A) (58) Fields investigated (Int.Cl. 7 , DB) Name) C10J 3/00 C01B 3/02-3/48 C10B 57/00

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 プラスチックを水と所定の温度で反応さ
せて主に水素ガス等の有用なガスにガス化する方法であ
って、反応時にハロゲンを放出する化合物を反応促進物
として使用し、反応温度が250〜500℃であり、
反応圧力が5〜305.9kg/cm 2 であることを特
徴とするプラスチックのガス化方法。
1. A method for reacting plastic with water at a predetermined temperature to gasify mainly useful gas such as hydrogen gas, wherein a compound that releases halogen during the reaction is a reaction accelerator.
Used as a quality , the reaction temperature is 250 ~ 500 ℃,
Gasification method for a plastic, wherein the reaction pressure is 5~305.9kg / cm 2.
【請求項2】 反応促進物質が塩素を含むプラスチック
又はハロゲン化合物である請求項1記載のガス化方法。
2. The gasification method according to claim 1, wherein the reaction promoting substance is a chlorine-containing plastic or a halogen compound.
JP35451097A 1997-12-24 1997-12-24 Gasification method of plastic Expired - Fee Related JP3478324B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP35451097A JP3478324B2 (en) 1997-12-24 1997-12-24 Gasification method of plastic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP35451097A JP3478324B2 (en) 1997-12-24 1997-12-24 Gasification method of plastic

Publications (2)

Publication Number Publication Date
JPH11181449A JPH11181449A (en) 1999-07-06
JP3478324B2 true JP3478324B2 (en) 2003-12-15

Family

ID=18438052

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Application Number Title Priority Date Filing Date
JP35451097A Expired - Fee Related JP3478324B2 (en) 1997-12-24 1997-12-24 Gasification method of plastic

Country Status (1)

Country Link
JP (1) JP3478324B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114433139A (en) * 2020-10-30 2022-05-06 中国石油化工股份有限公司 Biological coke gasification catalyst and biological coke catalytic raw material
CN113122294A (en) * 2021-03-15 2021-07-16 北京大学深圳研究生院 Pyrolysis system and pyrolysis method for reducing discharge of chlorine-containing pollutants generated by pyrolysis of marine plastic wastes

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