JP2004269811A - Method for recycling waste product mainly comprising plastic resin - Google Patents

Method for recycling waste product mainly comprising plastic resin Download PDF

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Publication number
JP2004269811A
JP2004269811A JP2003066030A JP2003066030A JP2004269811A JP 2004269811 A JP2004269811 A JP 2004269811A JP 2003066030 A JP2003066030 A JP 2003066030A JP 2003066030 A JP2003066030 A JP 2003066030A JP 2004269811 A JP2004269811 A JP 2004269811A
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Japan
Prior art keywords
oil
waste
gas
steam
pyrolysis
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JP2003066030A
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Japanese (ja)
Inventor
Kazuo Onuki
一雄 大貫
Tadashi Manabe
忠司 真鍋
Kazuhisa Fukuda
和久 福田
Takahiko Oguro
隆彦 大黒
Hideo Nishimura
秀生 西村
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Nippon Steel Corp
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Nippon Steel Corp
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    • 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
    • Y02W30/20Waste processing or separation
    • 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

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for recycling waste products mainly comprising plastic resin that can recover thermally cracked gas and oil of high addition value in high recovery percentage by using inexpensive installation. <P>SOLUTION: In the method for recycling waste products mainly comprising plastic resin, the waste products mainly comprising plastic resin is subjected to the thermal cracking to recover cracked gas and/or oil and they are recycled. In this case, steam is fed into the thermally cracked reaction mixture thereby controlling the cracking process and/or the recovery percentage of the gas and/or oil. <P>COPYRIGHT: (C)2004,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、樹脂を主体とする廃棄物を熱分解してガスおよび/または油を回収する廃棄物の再資源化方法に関し、マテリアルリサイクル比率を高め、資源の有効活用を高める改善、特に、熱分解後に得られるガスや油の組成や回収率を制御する処理方法に関する。
【0002】
【従来の技術】
廃タイヤや廃プラスチックといった樹脂を主体とする廃棄物を乾留して乾留ガス、回収油および炭化物を得る単独のシステムとしては、特開昭49−111986号公報、特開昭51−135983号公報など、多数ある。
例えば、特開2000−296378号公報には、廃棄物のガス化において、油を形成することなく、高ガス化ガスの発熱量の低下を防止し、廃棄物の焼却において、排ガス又は焼却灰中の有害物質の量を少なくすることを可能とする廃棄物の処理方法が開示されている。その手段は、有機系廃棄物のガス化に際し、ガス化炉内にガス化促進剤として、有機系廃棄物の焼却に際し、燃焼場に燃焼促進剤として、焼却灰に有害物質分解剤として、排ガスに有害物質分解剤として、それぞれ600℃以上の高温水蒸気を導入する方法である。
しかしながら、600℃以上の過熱水蒸気を工業的に得るにはコストが高く、また、回収ガスの発熱量も低下してくるという問題点があった。
【0003】
一方、特開2002−336673号公報には、有機廃棄物の高速分解方法について、550℃以下の過熱水蒸気によって分解する方法が開示されている。
しかし、この従来技術は、空気中の酸素による酸化反応と過熱水蒸気による乾燥、加水分解反応、熱分解反応の全てまたはいずれかの組み合わせにより、有機廃棄物を酸化分解する方法であって、水蒸気を熱源とするため、本発明が課題とする熱分解により回収するガスや油の組成や回収率の制御に関して何ら示されていない。
また、特開2002−322481号公報には、有機性廃棄物を過熱水蒸気の雰囲気下で炭化する方法が開示されている。
しかし、この従来技術は、炉内中の空気を過熱水蒸気で置換することによって、炉中の酸素濃度を極めて低い状態にして有機物の良好な炭化雰囲気を形成するものであって、本発明が課題とする熱分解により回収するガスや油の組成や回収率の制御に関して何ら示されていない。
【0004】
【特許文献1】特開昭49−111986号公報
【特許文献2】特開昭51−135983号公報
【特許文献3】特開2000−296378号公報
【特許文献4】特開2002−336673号公報
【特許文献5】特開2002−322481号公報
【0005】
【発明が解決しようとする課題】
前述のように、循環型社会の構築に向けて、樹脂を主体とする廃棄物の再資源化に関する従来から種々の提案がなされているが、いずれも処理コストが高価な方式を前提としており、また、回収ガスや油の品位や回収率を高く維持する必要があるなど、解決されていない課題も多かった。
そこで本発明は、樹脂を主体とする廃棄物の再資源化において、より安価な設備で高付加価値のガスや油を高い回収率で再資源化することができる、樹脂を主体とする廃棄物の再資源化方法を提供することを課題とする。
【0006】
【課題を解決するための手段】
本発明は、前述のような従来技術の問題点を解決し、熱分解中に水蒸気を供給し、回収される前記ガスおよび/または油の組成および/または回収率を制御することによって、より安価な設備で高付加価値のガスや油を高い回収率で再資源化することができる、樹脂を主体とする廃棄物の再資源化方法を提供するものであり、その要旨とするところは特許請求の範囲に記載した通りの下記内容である。
(1) 樹脂を主体とする廃棄物を熱分解してガスおよび/または油を回収する廃棄物の再資源化方法において、前記熱分解中に水蒸気を供給し、回収される前記ガスおよび/または油の組成および/または回収率を制御することを特徴とする樹脂を主体とする廃棄物の再資源化方法。
(2)前記熱分解中に供給する水蒸気が600℃未満の過熱水蒸気であることを特徴とする(1)に記載の廃棄物の再資源化方法。
(3)前記熱分解中に供給する水蒸気は、該熱分解で発生する高温のガスと水とを熱交換して発生する水蒸気を用いることを特徴とする(1)または(2)に記載の廃棄物の再資源化方法。
(4)前記樹脂を主体とする廃棄物が、廃タイヤ、廃プラスチック、シュレッダーダストの1種または2種以上を含むことを特徴とする(1)乃至(3)に記載の廃棄物の再資源化方法。
【0007】
【発明の実施の形態】
本発明の実施形態について図1および図2を用いて詳細に説明する。
図1は、本発明における樹脂を主体とする廃棄物の再資源化方法の実施形態を例示するプロセスフロー図である。
本発明においては、廃タイヤ、廃プラスチック、シュレッダーダストなどの樹脂を主体とする樹脂含有廃棄物は熱分解されてガスおよび/または油を回収する際に、熱分解中に水蒸気を供給する。水蒸気を供給することによって、炉内の見かけのガス体積が大きくなり、熱分解されたガスの炉内滞留時間が短くなるので、反応時間が変化するためガスや油の回収率や組成を制御することができ、より付加価値の高いガスや油を提供することができる。
特に、熱分解により回収されたガスと水とを熱交換することによって、水成ガス化反応により水蒸気を製造して熱分解時に供給することによって、熱分解時の廃熱を利用して安価に水蒸気を供給することができる。
【0008】
また、水蒸気の温度を高めて600℃未満の過熱水蒸気とし、これを熱分解中に供給することによって、ガスの回収率を著しく高めることができる。
600℃未満とするのは、これ以上の温度になると過熱水蒸気の製造コストが高まるからである。また、加熱水蒸気の温度は、400℃以上が好ましい。400℃未満では、炉内の雰囲気温度が低下し熱分解反応が進行しにくくなるからである。
また、本発明においては熱分解の方法は問わないが、ガスや油を回収するためには、外熱式のロータリーキルンなどの間接加熱方法が好ましく、さらに、高温のガスや油が有する熱エネルギーを熱分解処理の熱源として利用することによってエネルギーコストを低減することができる。
【0009】
図2は、本発明に用いる水蒸気が油の品質に及ぼす影響を示す図である。
図2において、横軸は水蒸気を供給する場合の見かけのガス体積の増加分を見込んだ熱分解ガス炉内滞留時間指標(min)を示し、縦軸は熱天秤100℃での重量減少率(%)であって油品質指標を示し、この値が低い程、軽油などの軽質分の割合が少なく、重油の収率が大きいことを示す。
図2の○印は熱分解温度600℃、廃棄物処理速度170kg/hrで水蒸気を供給しない場合、△印は、熱分解温度650℃、廃棄物処理速度240kg/hrで水蒸気を供給しない場合、●印は熱分解温度600℃、廃棄物処理速度170kg/hrで水蒸気を供給する場合を示す。
図2の右側の点線で示すように、水蒸気を供給することによって、見かけのガス体積が増加するため熱分解ガス炉内滞留時間指標(min)が低くなり、それに伴って油品質指標も低下しており、油中の軽油などの軽質分の割合が少なく、重油の比率が高いので、引火しにくく設備の安全対策を簡素化できる油を供給することができる。
【0010】
同様に、図2の□印は熱分解温度700℃、廃棄物処理速度420kg/hrで水蒸気を供給しない場合、■印は、熱分解温度700℃、廃棄物処理速度420kg/hrで水蒸気を供給する場合、※印は熱分解温度720℃、廃棄物処理速度170kg/hrで過剰熱分解した場合を示す。
図2の左側の点線で示すように、水蒸気を供給することによって、見かけのガス体積が増加して熱分解ガス炉内滞留時間指標(min)が低くなり、それに伴って油品質指標も低下しており、油中の軽油などの軽質分の割合が少なく、重油の比率が高いので、引火しにくく設備の安全対策を簡素化できる油を供給することができる。
また、従来は、重油の比率を高くするために、回収した油を再度蒸留処理する場合もあったが、本発明によれば、回収時点で重油比率を高くすることができるので、このような再蒸留処理も不要となる。
【0011】
【実施例】
内径800mm長さ6000mmの外熱式ロータリーキルンを用いて、表1の条件にて、平均粒径30mmのカットタイヤの熱分解実験を行った。
<実施例−1>
熱分解時に水蒸気を80kg/hr供給した本発明例であり、水蒸気を供給することにより見かけのガス体積が大きいため熱分解ガスの炉内滞留時間が短く、油軽質分比率が20%となったが、供給する水蒸気温度が150℃と比較的低いため、ガス回収率は18%だった。
<実施例−2>
熱分解時に水蒸気を80kg/hr供給した本発明例であり、水蒸気を供給することにより見かけのガス体積が大きいため熱分解ガスの炉内滞留時間が短く、油軽質分比率が15%となったうえ、熱分解時に400℃の過熱水蒸気を供給したため、ガス回収率が46%と高まった。
<実施例−3>
熱分解時に水蒸気を80kg/hr供給した本発明例であり、水蒸気を供給することにより見かけのガス体積が大きいため熱分解ガスの炉内滞留時間が短く、油軽質分が10%となったうえ、熱分解時に580℃の過熱水蒸気を供給したため、ガス回収率が51%とさらに高まった。
【0012】
<比較例−1>
熱分解時に水蒸気80kg/hrと酸素24Nm3/hrを供給した比較例であり、酸素を供給することによってガス回収率は42%となったが、酸素によってガスが燃焼してガス発熱量が本発明例の半分近くまで低下したうえ、油軽質分比率が80%と高くなった。
<比較例−2>
熱分解時に水蒸気も酸素も供給しなかった比較例であり、ガス回収率は18%と低いうえ、油軽質分比率も28%と比較的高かった。
<実験結果>
この実験の結果、熱分解時に水蒸気もしくは過熱水蒸気を供給することによって、ガス回収率を高めることができるうえ、油軽質分比率を低下させることができるので必要に応じてガス回収率や油軽質分比率を制御することができ、付加価値の高いガスや油を安価な設備で提供することができることが確認された。
【表1】

Figure 2004269811
【0013】
【発明の効果】
本発明によれば、熱分解中に水蒸気を供給し、回収される前記ガスおよび/または油の組成および/または回収率を制御することによって、より安価な設備で高付加価値のガスや油を高い回収率で再資源化することができる、樹脂を主体とする廃棄物の再資源化方法を提供することができるなど、産業上有用な著しい効果を奏する。
【図面の簡単な説明】
【図1】本発明における樹脂を主体とする廃棄物の再資源化方法の実施形態を例示するプロセスフロー図である。
【図2】本発明に用いる水蒸気が油の品質に及ぼす影響を示す図である。[0001]
TECHNICAL FIELD OF THE INVENTION
TECHNICAL FIELD The present invention relates to a method for recycling waste, which is a method of recovering gas and / or oil by pyrolyzing waste mainly composed of resin, and improving the material recycling ratio and improving the effective use of resources. The present invention relates to a processing method for controlling the composition and recovery of gas and oil obtained after decomposition.
[0002]
[Prior art]
JP-A-49-111986, JP-A-51-135983, and the like are examples of a single system for dry-distilling waste mainly composed of resin such as waste tires and waste plastics to obtain a dry-distilled gas, recovered oil and carbide. , There are many.
For example, Japanese Patent Application Laid-Open No. 2000-296378 discloses that in the gasification of waste, a decrease in the calorific value of the highly gasified gas is prevented without forming oil, and in the incineration of waste, the waste gas or incinerated ash There is disclosed a waste treatment method which enables the amount of harmful substances to be reduced. The measures are as follows: gasification of organic waste, gasification accelerator in gasification furnace, combustion incineration of organic waste, combustion promoter in combustion field, hazardous substance decomposer in incineration ash, exhaust gas In this method, high-temperature steam of 600 ° C. or more is introduced as a harmful substance decomposing agent.
However, there is a problem that it is costly to industrially obtain superheated steam of 600 ° C. or higher, and that the calorific value of the recovered gas also decreases.
[0003]
On the other hand, Japanese Patent Application Laid-Open No. 2002-336673 discloses a method of decomposing organic waste by using superheated steam at 550 ° C. or lower as a high-speed decomposition method.
However, this conventional technique is a method of oxidatively decomposing organic waste by all or any combination of an oxidation reaction with oxygen in air and drying with superheated steam, a hydrolysis reaction, and a pyrolysis reaction. There is no description on the composition of the gas or oil to be recovered by pyrolysis, which is the subject of the present invention, and on the control of the recovery rate because it is a heat source.
Japanese Patent Application Laid-Open No. 2002-322481 discloses a method of carbonizing organic waste under an atmosphere of superheated steam.
However, in this conventional technique, the air in the furnace is replaced with superheated steam, thereby making the oxygen concentration in the furnace extremely low to form a good carbonized atmosphere of organic substances. No mention is made of the composition of the gas or oil to be recovered by thermal decomposition or the control of the recovery.
[0004]
[Patent Document 1] JP-A-49-111986 [Patent Document 2] JP-A-51-135983 [Patent Document 3] JP-A-2000-296378 [Patent Document 4] JP-A-2002-333673 [Patent Document 5] Japanese Patent Application Laid-Open No. 2002-322481
[Problems to be solved by the invention]
As mentioned above, various proposals have been made regarding the recycling of waste mainly composed of resin for the construction of a recycling-based society, but all of them are based on the premise that the processing cost is expensive. There were also many unresolved issues such as the need to maintain high quality and recovery rates of recovered gas and oil.
Therefore, the present invention relates to a resin-based waste that can be used to recycle high value-added gas and oil at a high recovery rate with less expensive equipment in the recycling of resin-based waste. An object of the present invention is to provide a method for recycling resources.
[0006]
[Means for Solving the Problems]
The present invention solves the above-mentioned problems of the prior art, and supplies steam during pyrolysis to control the composition and / or recovery rate of the recovered gas and / or oil, thereby reducing the cost. The present invention provides a method for recycling resin-based waste, which can recycle high value-added gas and oil with a high recovery rate using simple equipment. The following contents are described as described in the range.
(1) In a waste recycling method for recovering gas and / or oil by thermally decomposing waste mainly composed of resin, steam is supplied during the pyrolysis to recover the gas and / or oil recovered. A method of recycling resin-based waste, characterized by controlling the composition and / or recovery of oil.
(2) The method for recycling waste as described in (1), wherein the steam supplied during the pyrolysis is superheated steam of less than 600 ° C.
(3) The steam according to (1) or (2), wherein steam supplied during the thermal decomposition uses steam generated by heat exchange between high-temperature gas generated by the thermal decomposition and water. How to recycle waste.
(4) The recycling of waste according to (1) to (3), wherein the resin-based waste contains one or more of waste tire, waste plastic, and shredder dust. Method.
[0007]
BEST MODE FOR CARRYING OUT THE INVENTION
An embodiment of the present invention will be described in detail with reference to FIGS.
FIG. 1 is a process flow diagram illustrating an embodiment of a method for recycling waste mainly composed of resin according to the present invention.
In the present invention, resin-containing waste mainly composed of resin such as waste tires, waste plastics, and shredder dust is supplied with steam during the thermal decomposition when the gas and / or oil is recovered by pyrolysis. By supplying steam, the apparent gas volume in the furnace is increased, and the residence time of the pyrolyzed gas in the furnace is shortened, so that the reaction time changes, so the recovery rate and composition of the gas and oil are controlled. Gas and oil with higher added value can be provided.
In particular, by exchanging heat between gas and water recovered by pyrolysis, water vapor is produced by the hydrogasification reaction and supplied during pyrolysis, making it possible to use waste heat from pyrolysis at low cost. Steam can be supplied.
[0008]
Further, by increasing the temperature of the steam to form superheated steam of less than 600 ° C. and supplying it during pyrolysis, the gas recovery rate can be significantly increased.
The reason why the temperature is lower than 600 ° C. is that if the temperature is higher than this, the production cost of superheated steam increases. The temperature of the heated steam is preferably 400 ° C. or higher. If the temperature is lower than 400 ° C., the temperature of the atmosphere in the furnace decreases, and the thermal decomposition reaction does not easily proceed.
In addition, in the present invention, the method of thermal decomposition is not limited, but in order to recover gas and oil, an indirect heating method such as an externally heated rotary kiln is preferable. Energy cost can be reduced by using it as a heat source for the thermal decomposition treatment.
[0009]
FIG. 2 is a diagram showing the effect of steam used in the present invention on oil quality.
In FIG. 2, the horizontal axis indicates the residence time index (min) in the pyrolysis gas furnace in consideration of the apparent increase in gas volume when steam is supplied, and the vertical axis indicates the weight loss rate at 100 ° C. of the thermobalance ( %), Which indicates an oil quality index. The lower this value is, the smaller the ratio of light components such as light oil is, and the higher the yield of heavy oil is.
In FIG. 2, a circle indicates a case where steam is not supplied at a pyrolysis temperature of 600 ° C. and a waste processing speed of 170 kg / hr, and a triangle indicates a case where steam is not supplied at a pyrolysis temperature of 650 ° C. and a waste processing speed of 240 kg / hr. The mark ● indicates the case where steam is supplied at a thermal decomposition temperature of 600 ° C. and a waste treatment rate of 170 kg / hr.
As shown by the dotted line on the right side of FIG. 2, by supplying steam, the apparent gas volume increases, so that the residence time index (min) in the pyrolysis gas furnace decreases, and the oil quality index decreases accordingly. Since the ratio of light components such as light oil in oil is low and the ratio of heavy oil is high, it is possible to supply oil that is difficult to catch fire and that can simplify equipment safety measures.
[0010]
Similarly, in FIG. 2, the symbol □ indicates that the steam is not supplied at the thermal decomposition temperature of 700 ° C. and the waste processing speed of 420 kg / hr, and the symbol Δ indicates that the steam is supplied at the thermal decomposition temperature of 700 ° C. and the waste processing speed of 420 kg / hr. In this case, the * mark indicates a case where excessive pyrolysis was performed at a thermal decomposition temperature of 720 ° C. and a waste disposal rate of 170 kg / hr.
As shown by the dotted line on the left side of FIG. 2, by supplying steam, the apparent gas volume increases, the residence time index (min) in the pyrolysis gas furnace decreases, and the oil quality index decreases accordingly. Since the ratio of light components such as light oil in oil is low and the ratio of heavy oil is high, it is possible to supply oil that is difficult to catch fire and that can simplify equipment safety measures.
In addition, conventionally, in order to increase the ratio of heavy oil, the recovered oil may be subjected to distillation again in some cases. However, according to the present invention, the ratio of heavy oil can be increased at the time of collection. The need for a redistillation process is eliminated.
[0011]
【Example】
Using an externally heated rotary kiln having an inner diameter of 800 mm and a length of 6000 mm, a thermal decomposition experiment was performed on cut tires having an average particle size of 30 mm under the conditions shown in Table 1.
<Example-1>
This is an example of the present invention in which steam was supplied at a rate of 80 kg / hr during pyrolysis. By supplying steam, the apparent gas volume was large, so that the residence time of the pyrolysis gas in the furnace was short, and the oil light fraction was 20%. However, since the supplied steam temperature was relatively low at 150 ° C., the gas recovery rate was 18%.
<Example-2>
This is an example of the present invention in which steam was supplied at a rate of 80 kg / hr during the pyrolysis. The apparent gas volume was large due to the supply of the steam, so the residence time of the pyrolysis gas in the furnace was short, and the oil light fraction was 15%. In addition, the supply of superheated steam at 400 ° C. during the pyrolysis increased the gas recovery rate to 46%.
<Example-3>
This is an example of the present invention in which steam was supplied at a rate of 80 kg / hr during the pyrolysis. By supplying the steam, the apparent gas volume was large, so that the residence time of the pyrolysis gas in the furnace was short, and the light oil content became 10%. Since 580 ° C. superheated steam was supplied during the thermal decomposition, the gas recovery rate was further increased to 51%.
[0012]
<Comparative Example-1>
This is a comparative example in which water vapor of 80 kg / hr and oxygen of 24 Nm3 / hr were supplied during pyrolysis. The gas recovery rate was 42% by supplying oxygen. In addition to falling to nearly half of the cases, the oil light fraction increased to 80%.
<Comparative Example-2>
This is a comparative example in which neither steam nor oxygen was supplied at the time of pyrolysis. The gas recovery rate was as low as 18%, and the ratio of light oil components was relatively high as 28%.
<Experimental results>
As a result of this experiment, by supplying steam or superheated steam during pyrolysis, the gas recovery rate can be increased and the oil light fraction can be reduced. It has been confirmed that the ratio can be controlled and high value-added gas and oil can be provided with inexpensive equipment.
[Table 1]
Figure 2004269811
[0013]
【The invention's effect】
According to the present invention, by supplying steam during pyrolysis and controlling the composition and / or recovery rate of the gas and / or oil to be recovered, high-value-added gas and oil can be produced with less expensive equipment. It has remarkable industrially useful effects, such as being able to recycle at a high recovery rate and providing a method of recycling waste mainly composed of resin.
[Brief description of the drawings]
FIG. 1 is a process flow diagram illustrating an embodiment of a resin-based waste recycling method according to the present invention.
FIG. 2 is a diagram showing the effect of steam used in the present invention on oil quality.

Claims (4)

樹脂を主体とする廃棄物を熱分解してガスおよび/または油を回収する廃棄物の再資源化方法において、前記熱分解中に水蒸気を供給し、回収される前記ガスおよび/または油の組成および/または回収率を制御することを特徴とする樹脂を主体とする廃棄物の再資源化方法。In a waste recycling method for recovering gas and / or oil by thermally decomposing waste mainly composed of resin, the composition of the recovered gas and / or oil is supplied by supplying steam during the pyrolysis. And / or controlling the recovery rate. A method for recycling waste mainly composed of resin. 前記熱分解中に供給する水蒸気が600℃未満の過熱水蒸気であることを特徴とする請求項1に記載の廃棄物の再資源化方法。The method according to claim 1, wherein steam supplied during the pyrolysis is superheated steam having a temperature of less than 600C. 前記熱分解中に供給する水蒸気は、該熱分解で発生する高温のガスと水とを熱交換して発生する水蒸気を用いることを特徴とする請求項1または請求項2に記載の廃棄物の再資源化方法。The wastewater according to claim 1 or 2, wherein steam supplied during the pyrolysis uses steam generated by exchanging heat between high-temperature gas and water generated by the pyrolysis. Recycling method. 前記樹脂を主体とする廃棄物が、廃タイヤ、廃プラスチック、シュレッダーダストの1種または2種以上を含むことを特徴とする請求項1乃至請求項3に記載の廃棄物の再資源化方法。4. The method according to claim 1, wherein the resin-based waste contains one or more of waste tire, waste plastic, and shredder dust. 5.
JP2003066030A 2003-03-12 2003-03-12 Method for recycling waste product mainly comprising plastic resin Pending JP2004269811A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007105628A (en) * 2005-10-13 2007-04-26 Nippon Steel Corp Method and apparatus for estimating progress of pyrolysis of waste, and method and apparatus for pyrolyzing waste
CN102335668A (en) * 2010-07-19 2012-02-01 车磊 Method for treating industrial hazardous wastes containing organic solvent
JP2021133597A (en) * 2020-02-27 2021-09-13 株式会社セレア Separation method and separation device

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007105628A (en) * 2005-10-13 2007-04-26 Nippon Steel Corp Method and apparatus for estimating progress of pyrolysis of waste, and method and apparatus for pyrolyzing waste
CN102335668A (en) * 2010-07-19 2012-02-01 车磊 Method for treating industrial hazardous wastes containing organic solvent
JP2021133597A (en) * 2020-02-27 2021-09-13 株式会社セレア Separation method and separation device

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