JP4441364B2 - Resin-based waste recycling method - Google Patents
Resin-based waste recycling method Download PDFInfo
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- JP4441364B2 JP4441364B2 JP2004270601A JP2004270601A JP4441364B2 JP 4441364 B2 JP4441364 B2 JP 4441364B2 JP 2004270601 A JP2004270601 A JP 2004270601A JP 2004270601 A JP2004270601 A JP 2004270601A JP 4441364 B2 JP4441364 B2 JP 4441364B2
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- Y—GENERAL 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
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Description
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。 The present invention relates to a waste recycling method for recovering gas and / or oil by thermally decomposing waste mainly composed of resin, and relates to an improvement in increasing a material recycling ratio and effective use of resources, in particular, heat. The present invention relates to a processing method for controlling the composition and recovery rate of gas and oil obtained after decomposition.
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。
Examples of a single system for carbonizing waste such as waste tires and plastics to obtain carbonization gas, recovered oil, and carbides are disclosed in JP-A-49-111986, JP-A-51-135983, and the like. There are many.
For example, in Japanese Patent Laid-Open No. 2000-296378, in the gasification of waste, the reduction in the calorific value of the high gasification gas is prevented without forming oil, and in the incineration of waste, Disclosed is a waste treatment method that can reduce the amount of harmful substances. When gasifying organic waste, it is used as a gasification accelerator in the gasification furnace, when incinerating organic waste, as a combustion accelerator in the combustion field, as a hazardous substance decomposition agent in incineration ash, and as an exhaust gas. In this method, high-temperature steam at 600 ° C. or higher is introduced as a harmful substance decomposing agent.
However, there are problems in that it is expensive to industrially obtain superheated steam at 600 ° C. or higher, and the amount of heat generated from the recovered gas also decreases.
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。
However, this prior art is a method of oxidizing and decomposing organic waste by all or any combination of oxidation reaction with oxygen in the air and drying, hydrolysis reaction and thermal decomposition reaction with superheated steam. In order to make it a heat source, nothing is shown regarding the control of the composition and recovery rate of the gas and oil recovered by the thermal decomposition which is the subject of the present invention.
Japanese Patent Application Laid-Open No. 2002-322481 discloses a method of carbonizing organic waste in an atmosphere of superheated steam.
However, this prior art replaces the air in the furnace with superheated steam, thereby forming a good carbonized atmosphere of organic matter with a very low oxygen concentration in the furnace. Nothing is shown regarding the control of the composition and recovery rate of gas and oil recovered by thermal decomposition.
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バラツキ無く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。
As mentioned above, various proposals for the recycling of waste mainly consisting of resin have been made for the establishment of a recycling-oriented society. There were also many unresolved issues such as the need to maintain high quality and recovery rate of recovered gas and oil.
Therefore, the present invention can recycle wastes mainly made of resin, which can recycle high-value-added gas and oil without variation in cheaper equipment. It is an object to provide a resource recycling method.
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安定して回収し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、前記熱分解温度を600〜700℃とし、前記熱分解中に3 0 0 ℃ 未満の水蒸気を供給し、回収される前記油の組成および/ 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)に記載の廃棄物の再資源化方法。
(3)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)または(2)に記載の廃棄物の再資源化方法。
(4)前記水蒸気の導入量を熱分解ガス組成の変化に応じて制御することを特徴とする(1)乃至(3)のいずれか1項に記載の廃棄物の再資源化方法。
The present invention solves the problems of the prior art as described above, supplies steam during thermal decomposition, and controls the composition and / or recovery rate of the recovered gas and / or oil, thereby reducing the cost. It provides a method for recycling waste mainly consisting of resin, which can stably recover and recycle high value-added gas and oil in a simple facility. It is the following contents as described in the claims.
(1) In a waste recycling method in which waste mainly composed of resin is thermally decomposed to recover gas and oil , the thermal decomposition temperature is set to 600 to 700 ° C., and 300 ° C. during the thermal decomposition. A method for recycling waste mainly composed of resin, characterized by supplying less than water vapor and controlling the composition and / or recovery rate of the recovered oil .
(2) The steam supplied during the pyrolysis is steam generated by exchanging heat between the high-temperature gas generated by the pyrolysis and water. Recycling method.
(3) The waste recycling material according to (1) or (2), wherein the waste mainly composed of the resin includes one or more of waste tire, waste plastic, and shredder dust. Method.
(4) The waste recycling method according to any one of (1) to (3) , wherein the amount of water vapor introduced is controlled in accordance with a change in the pyrolysis gas composition.
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安定して回収し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。 According to the present invention, high value-added gas and oil can be produced with less expensive equipment by supplying steam during thermal decomposition and controlling the composition and / or recovery rate of the recovered gas and / or oil. There are significant industrially useful effects, such as a method for stably recovering and recycling resources, and a method for recycling waste mainly composed of resin.
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。
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 waste recycling method mainly composed of resin in the present invention.
In the present invention, when resin-containing waste mainly composed of resin such as waste tire, waste plastic, and shredder dust is thermally decomposed to recover gas and / or oil, water vapor is supplied during the thermal decomposition. Supplying water vapor increases the apparent gas volume in the furnace and shortens the residence time of the pyrolyzed gas in the furnace, thereby controlling the recovery rate and composition of gas and oil because the reaction time changes. It is possible to provide gas and oil with higher added value.
In particular, by exchanging heat between the gas recovered by pyrolysis and water, water vapor is produced by an aquatic gasification reaction and supplied at the time of pyrolysis. Steam can be supplied.
また、対象とする廃棄物の組成バラツキに応じて熱分解生成物であるガスならにび油の組成が変化してくる。そこで、この状況をガスクロやFT-IR法等のガス組成分析法等の製品性状を把握する手段を用いて観測しながら、熱分解炉内へ導入する水蒸気を供給することが好ましい。なお、水蒸気の温度を300℃未満とすることで、ガスならびに油の回収比率を大幅に変化させることなく、ガスならにび油の組成を一定値に制御できる。ガスや油の組成を一定値に制御することにより、ガスや油を使用する次工程との間で、ガス不足による次工程の稼働率低下等の生産調整をする必要が無くなる。
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。
In addition, the composition of the oil and the oil, which is a pyrolysis product, changes according to the compositional variation of the target waste. Therefore, it is preferable to supply water vapor to be introduced into the pyrolysis furnace while observing this situation using means for grasping product properties such as gas composition analysis methods such as gas chromatography and FT-IR. In addition, by setting the temperature of water vapor to less than 300 ° C., the composition of gas and oil can be controlled to a constant value without significantly changing the recovery ratio of gas and oil. By controlling the composition of the gas or oil to a constant value, it is not necessary to make production adjustments such as a reduction in the operation rate of the next process due to gas shortage with the next process using the gas or oil.
In the present invention, the thermal decomposition method is not limited, but in order to recover the gas or oil, an indirect heating method such as an external heating type rotary kiln is preferable, and the thermal energy of the high temperature gas or oil is further increased. By using it as a heat source for the thermal decomposition treatment, the energy cost can be reduced.
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。なお、いずれの場合も、水蒸気温度は300℃未満のものを使用している。
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。
FIG. 2 is a diagram showing the influence of water vapor used in the present invention on the quality of oil.
In FIG. 2, the horizontal axis represents the residence time index (min) in the pyrolysis gas furnace in consideration of the increase in the apparent gas volume when water vapor is supplied, and the vertical axis represents the weight loss rate at a thermobalance of 100 ° C. %) Indicates an oil quality index, and the lower this value, the smaller the ratio of light components such as light oil and the greater the yield of heavy oil. In FIG. 2, a circle indicates a case where no steam is supplied at a thermal decomposition temperature of 600 ° C. and a waste treatment rate of 170 kg / hr, and a triangle indicates a case where water vapor is not supplied at a thermal decomposition temperature of 650 ° C. and a waste treatment rate of 240 kg / hr. The symbol ● indicates the case where water vapor is supplied at a thermal decomposition temperature of 600 ° C. and a waste treatment rate of 170 kg / hr. In either case, the water vapor temperature is less than 300 ° C.
As shown by the dotted line on the right side of FIG. 2, by supplying water vapor, the apparent gas volume increases, so the residence time index (min) in the pyrolysis gas furnace decreases, and the oil quality index also decreases accordingly. Because the ratio of light components such as light oil in the oil is small and the ratio of heavy oil is high, it is possible to supply oil that is difficult to ignite and that can simplify the safety measures of the equipment.
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。
Similarly, □ in FIG. 2 indicates that steam is not supplied at a pyrolysis temperature of 700 ° C. and a waste treatment rate of 420 kg / hr, and ■ indicates that steam is supplied at a pyrolysis temperature of 700 ° C. and a waste treatment rate of 420 kg / hr. In this case, an asterisk (*) indicates a case where excessive thermal decomposition is performed at a thermal decomposition temperature of 720 ° C. and a waste treatment rate of 170 kg / hr.
As shown by the dotted line on the left side of FIG. 2, by supplying water vapor, the apparent gas volume increases and the residence time index (min) in the pyrolysis gas furnace decreases, and the oil quality index also decreases accordingly. Because the ratio of light components such as light oil in the oil is small and the ratio of heavy oil is high, it is possible to supply oil that is difficult to ignite and that can simplify the safety measures of the equipment.
In addition, conventionally, in order to increase the ratio of heavy oil, the recovered oil may be distilled again, but according to the present invention, the ratio of heavy oil can be increased at the time of recovery. A re-distillation process is also unnecessary.
内径800mm長さ6000mmの外熱式ロータリーキルンを用いて、表1の条件にて樹脂を主体とする廃棄物の熱分解実験を行った。
<実施例−1および比較例−1>
タイヤ420kg/hで熱分解時に水蒸気を80kg/hr供給した本発明例が実施例−1であり、同じ条件で水蒸気を供給しなかった場合が比較例−1である。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、ガスの発熱量は11000kcal/Nm3と高く、油軽質分比率は20%となった。一方、比較例−1では、実施例−1に比べて、ガス発熱量の低下と油軽質分の増加が認められた。
<実施例−2および比較例−2>
熱分解温度が700℃で、実施例−1よりもタイヤ供給量が下がり、260kg/hで熱分解時に水蒸気を120kg/hr供給した場合が実施例−2であり、同じ条件で水蒸気を供給しなかった場合が比較例−2である。実施例−1と比べると、比較例−2では、ガス回収率ならびに油軽質分比率が高まるとともにガス発熱量は低下している。一方、実施例−2では、ガス回収率、油軽質分比率ならびにガス発熱量は実施例−1同様であった。
Using an externally heated rotary kiln having an inner diameter of 800 mm and a length of 6000 mm, a thermal decomposition experiment of waste mainly composed of resin was performed under the conditions shown in Table 1.
<Example-1 and Comparative Example-1>
An example of the present invention in which water vapor was supplied at a rate of 420 kg / h at the time of thermal decomposition at 80 kg / hr is Example-1, and a case in which water vapor was not supplied under the same conditions is Comparative Example-1. Since the apparent gas volume was increased by supplying water vapor, the residence time of the pyrolysis gas in the furnace was short, the calorific value of the gas was as high as 11000 kcal / Nm3, and the oil-light fraction was 20%. On the other hand, in Comparative Example-1, a decrease in the calorific value of gas and an increase in light oil were observed as compared to Example-1.
<Example-2 and Comparative Example-2>
Example 2 shows a case where the thermal decomposition temperature is 700 ° C., the tire supply amount is lower than that in Example 1, and water vapor is supplied at 120 kg / hr at the time of thermal decomposition at 260 kg / h. The case where there was no is Comparative Example-2. Compared with Example-1, in Comparative Example-2, the gas recovery rate and the oil / light fraction increase and the gas calorific value decreases. On the other hand, in Example-2, the gas recovery rate, the oil / light fraction, and the gas heating value were the same as in Example-1.
<実施例−3および比較例−3>
熱分解温度が700℃で、実施例−1の原料条件が変化し、タイヤ80%と廃プラ20%の混合廃棄物を300kg/hで熱分解時に水蒸気を100kg/hr供給した場合が実施例−3であり、同じ条件で水蒸気を供給しなかった場合が比較例−3である。比較例−3では、ガス回収率ならびに油軽質分比率が高まるとともにガス発熱量は低下している。一方、実施例−3では、ガス回収率、油軽質分比率ならびにガス発熱量は実施例−1同様であった。
<実験結果>
この実験の結果、熱分解の原料や供給速度が変化した場合でも、熱分解時に水蒸気を供給することによって、ガス発熱量、油軽質分比率を変化させることなくガスや油を回収できるため、付加価値の高いガスや油を安価な設備で提供できることが確認された。
Example in which the pyrolysis temperature is 700 ° C., the raw material conditions in Example-1 are changed, and mixed waste of 80% tire and 20% waste plastic is supplied at 300 kg / h and steam is supplied at 100 kg / hr during pyrolysis. -3, and the case where water vapor was not supplied under the same conditions is Comparative Example-3. In Comparative Example-3, the gas recovery rate and the oil / light fraction increase and the gas heating value decreases. On the other hand, in Example-3, the gas recovery rate, the oil / light fraction, and the gas heating value were the same as in Example-1.
<Experimental result>
As a result of this experiment, gas and oil can be recovered without changing the gas heating value and oil / light fraction by supplying water vapor during pyrolysis even when the pyrolysis raw material and feed rate change. It was confirmed that high-value gas and oil can be provided with inexpensive equipment.
Claims (4)
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