JP2021006747A - Thermal decomposition treatment method of refuse using organic substance thermal decomposition furnace - Google Patents

Thermal decomposition treatment method of refuse using organic substance thermal decomposition furnace Download PDF

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JP2021006747A
JP2021006747A JP2018249006A JP2018249006A JP2021006747A JP 2021006747 A JP2021006747 A JP 2021006747A JP 2018249006 A JP2018249006 A JP 2018249006A JP 2018249006 A JP2018249006 A JP 2018249006A JP 2021006747 A JP2021006747 A JP 2021006747A
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勉 勅使河原
Tsutomu Teshigawara
勉 勅使河原
正憲 藤島
Masanori Fujishima
正憲 藤島
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Abstract

To provide a thermal decomposition treatment method of refuse using an organic substance thermal decomposition furnace capable of removing residual organic substances from inorganic substances by surely self-heating, when treating a large amount of flue gas (self-sustained combustion gas) by circulating self-sustained combustion gas generated in an incineration treating chamber of the organic substance thermal decomposition furnace back to the incineration treating chamber, without discharging the gas outside an incineration treating furnace.SOLUTION: Self-sustained combustion gas induced and discharged outside the heat treating part of an organic substance thermal decomposition furnace is cooled, and the treated self-sustained combustion gas with tar and odor removed therefrom is mixed with a predetermined amount of air and agitated to form mixed gases. The mixed gas is passed through a magnetic field and excited, and led into the heat treating part of the organic substance thermal decomposition furnace.SELECTED DRAWING: None

Description

本発明は、廃棄物の熱分解処理方法に関し、更に詳しくは廃棄物を予め定めた温度の範囲内の雰囲気下に所定時間維持しつつ該廃棄物を不完全燃焼雰囲気下に置くことで廃棄物の可燃性部材を自燃させて取り出し可能に処理することが出来る極めて優れた有機物熱分解炉を用いた廃棄物の熱分解処理方法に関するものである。 The present invention relates to a method for thermally decomposing waste, and more specifically, by placing the waste in an incomplete combustion atmosphere while maintaining the waste in an atmosphere within a predetermined temperature range for a predetermined time. The present invention relates to a method for thermally decomposing waste using an extremely excellent organic pyrolysis furnace capable of self-combusting the flammable member of the above.

従来、可燃性部材を有した廃棄物を処理する炉としては、例えば、特開2001−304520号公報所載のものや特開2012−2386号公報所載のもの、更に特開2016−144776号公報所載のものが存在する。
特開2001−304520号公報 特開2012− 2386号公報 特開2016−144776号公報
Conventionally, as a furnace for treating waste having a flammable member, for example, a furnace published in JP-A-2001-304520, a furnace published in JP-A-2012-2386, and a furnace published in JP-A-2016-1474776. Some are published in the gazette.
Japanese Unexamined Patent Publication No. 2001-304520 Japanese Unexamined Patent Publication No. 2012-2386 JP-A-2016-144776

即ち、上記特開2001−304520号公報に記載のものは、耐熱容器(焼却炉)の焼却処理室(炉)内に取り入れられる燃焼用空気の流入量を制限する流入空気制限手段と、前記燃焼用空気の空気通路上に磁場を形成して、該燃焼用空気を磁気処理する磁石手段と、前記焼却処理室の壁部に燃焼ガスの排出口を有した焼却炉であり、かかる構成にしてなる焼却炉においては、使用時に磁石手段を介して活性化された燃焼用空気により、僅かな流入量の空気によっても燃焼状態を継続して維持することが出来るだけでなく、流入空気制限手段を介して燃焼用空気量をも制限することで焼却処理室内の温度を700℃以下の低温燃焼状態に維持し、その結果として廃棄物の燃焼により生じるダイオキシン類の生成を抑えることが出来るというものである。 That is, the ones described in JP-A-2001-304520 are an inflow air limiting means for limiting the inflow amount of combustion air taken into the incineration chamber (incinerator) of a heat-resistant container (incinerator) and the combustion. An incinerator having a magnet means for magnetically treating the combustion air by forming a magnetic field on the air passage of the combustion air and an incinerator having a combustion gas discharge port on the wall of the incineration chamber. In the incinerator, the combustion air activated via the magnet means during use not only allows the combustion state to be continuously maintained even with a small amount of inflow of air, but also provides inflow air limiting means. By limiting the amount of combustion air through the incineration chamber, the temperature in the incineration chamber can be maintained at a low temperature of 700 ° C or less, and as a result, the production of dioxin generated by the combustion of waste can be suppressed. is there.

一方、廃棄物の中には、各種電子基板(例えば、パソコン、携帯電話、ゲーム機等)が含まれることもある。 On the other hand, the waste may include various electronic boards (for example, personal computers, mobile phones, game machines, etc.).

尚、かかる各種電子基板には、金、銀、パラジウム等の有用貴金属類のみならずセラミック類が大量の樹脂等の可燃性部材に囲まれて存在しており、よって近年かかる各種電子基板から有用貴金属類やセラミック類を回収するリサイクル事業が行われてはいるが可燃性部材に囲まれた中から有用貴金属類やセラミック類を回収するには多額のコストがかかることとなり、費用対効果が高いとは決して言えないのが現状である。 In such various electronic substrates, not only useful precious metals such as gold, silver, and palladium but also ceramics are surrounded by a large amount of flammable members such as resin, which is useful from various electronic substrates in recent years. Although there is a recycling business to collect precious metals and ceramics, it is cost-effective to recover useful precious metals and ceramics from being surrounded by flammable materials. The current situation is that it cannot be said at all.

よって、昨今、各種電子基板を上記構成の焼却処理炉で焼却することで可燃性部材から有用貴金属類やセラミック類を回収する試みがなされ、上記特開2012−2386号公報に記載の様に、熱源収容室内に発熱と吸熱とが可能な練炭を保熱材として配置するものがある。
かかる保熱材によれば炉内の温度が上昇すると周囲の雰囲気から吸熱し、炉内の温度が低下すると周囲へ放熱を行うことで炉内の温度変化を緩衝して炉内が所定の温度範囲内に維持するというものである。
Therefore, in recent years, an attempt has been made to recover useful precious metals and ceramics from combustible members by incinerating various electronic substrates in an incinerator having the above configuration, and as described in JP2012-2386. In some heat source storage chambers, briquettes capable of generating heat and absorbing heat are placed as heat insulating materials.
According to such a heat insulating material, when the temperature inside the furnace rises, heat is absorbed from the surrounding atmosphere, and when the temperature inside the furnace drops, heat is dissipated to the surroundings to buffer the temperature change in the furnace and the temperature inside the furnace becomes a predetermined temperature. It is to keep it within the range.

即ち、炉内の温度を可燃性部材が燃焼、熱分解若しくは流動化する温度に保つことで、可燃性部材からの有用貴金属類やセラミック類の分離を容易にして回収する手間を簡易ならしめんとするものであるが、処理する各種電子基板に使用されている樹脂等の可燃性部材の量も処理ロット等により一定ではなく、よって炉内の瞬間的な温度変化に即対応して吸熱、放熱を瞬間的に行うことが出来ず、所謂タイムロスが生じることとなり、特にある容積を有した炉内全体の温度(特に炉内の鉛直方向での温度ムラ)を即均一化することが極めて難しく、よって各種電子基板から回収する有用貴金属類が高温融着したり酸化したりする等リサイクルという目的にとって致命的とも言える問題が生じていた。 That is, by keeping the temperature inside the furnace at a temperature at which the flammable members burn, thermally decompose, or fluidize, it is easy to separate useful precious metals and ceramics from the combustible members and recover them easily. However, the amount of flammable members such as resin used in various electronic substrates to be processed is not constant depending on the processing lot, etc. Therefore, heat is absorbed immediately in response to the instantaneous temperature change in the furnace. It is not possible to dissipate heat instantaneously, so-called time loss occurs, and it is extremely difficult to immediately equalize the temperature of the entire furnace with a certain volume (especially temperature unevenness in the vertical direction inside the furnace). Therefore, there has been a problem that can be said to be fatal for the purpose of recycling, such as useful noble metals recovered from various electronic substrates being fused at high temperature or oxidized.

更に、上記練炭は、石炭を粉末成型したものであり、よって石炭の種類によっては、硫黄臭や鉱物臭が発生する場合のみならず、燃焼後の練炭殻には、微量ではあるが石炭由来の各種有害物質や重金属が含まれており、使用済の練炭を捨てる場所、所謂廃棄処理にコストがかかるいう問題のみならず排煙に含まれる炭化粒子の処理も必要であるという問題が生じていた。 Further, the briquette is obtained by powder-molding coal, and therefore, depending on the type of coal, not only when a sulfur odor or a mineral odor is generated, but also in the briquette shell after combustion, a small amount is derived from coal. It contains various harmful substances and heavy metals, and there has been a problem that it is necessary to dispose of carbonized particles contained in smoke exhaust as well as a place to dispose of used briquettes, so-called disposal cost. ..

よって、前記両公報所載の問題点を解決すべく諸々の焼却処理炉が開発されているが、前記特開2001−304520号公報所載のもの、前記特開2012−2386号公報所載のもの何れの場合であっても廃棄物を不完全燃焼下におくことで廃棄物に含まれる有機物を自燃させて処理するものであることからその自燃ガス自体が極めて多量の煙を伴うのであり、しいては排煙処理に極めて高額な設備費が必要であるという最大の問題点があった。 Therefore, various incineration furnaces have been developed in order to solve the problems described in both of the publications, but those published in JP-A-2001-304520 and those published in JP-A-2012-2386. In any case, the self-burning gas itself is accompanied by an extremely large amount of smoke because the organic substances contained in the waste are self-burned and treated by putting the waste under incomplete combustion. As a result, there was the biggest problem that the smoke exhaust treatment required an extremely high equipment cost.

従って、上記特開2016−144776号公報所載のように、焼却処理室(炉)内で生じた自燃ガスを焼却処理炉から屋外に排出することなく焼却処理室(炉)内に戻す様に循環させて取り入れることで多量に発生する排煙(自燃ガス)を処理出来る分解装置が近年開発されてはいるものの、如何せん、排煙(自燃ガス)の処理を優先すると自燃ガスの酸素濃度が極端に低下することとなり、その結果不完全燃焼下に置かれることで廃棄物に含まれる有機物を自燃させて処理する工程において、有機物の自燃箇所にムラが発生することとなり、特に廃棄物が有機物と無機物との混合である場合に、自燃せずに残存する有機物が無機物から除去することが出来なくなるという廃棄物の処理において致命的な問題が生じることになった。 Therefore, as described in JP-A-2016-144776, the self-combustion gas generated in the incineration chamber (furnace) is returned to the incineration chamber (furnace) without being discharged to the outside from the incineration furnace. Although a decomposition device capable of treating a large amount of flue gas (self-combustion gas) generated by circulating and taking in it has been developed in recent years, the oxygen concentration of the self-combustion gas is extremely high if the treatment of flue gas (self-combustion gas) is prioritized. As a result, in the process of self-combusting and treating the organic matter contained in the waste by being placed under incomplete combustion, unevenness will occur in the self-combustion part of the organic matter, and in particular, the waste will be regarded as an organic matter. In the case of mixing with an inorganic substance, a fatal problem arises in the treatment of waste that the organic substance remaining without self-combustion cannot be removed from the inorganic substance.

然して、本発明は、上記課題を解決するためのものであり、請求項1記載の発明は、熱源を介して有機物熱分解炉内の熱処理部の温度を所定の温度まで上昇させる工程と、該有機物熱分解炉内の熱処理部に導入される空気の量を調整することで熱処理部に収納された廃棄物を予め定めた温度の範囲内の雰囲気下に所定時間維持しつつ該廃棄物を不完全燃焼雰囲気下に置くことで廃棄物の可燃性部材を自燃させて取り出し可能とする工程と、廃棄物の可燃性部材が自燃する際に発生した高温多湿の自燃ガスを誘引手段を介して有機物熱分解炉の熱処理部外に誘引排出する工程と、有機物熱分解炉の熱処理部外に誘引排出された自燃ガスを冷却すると共にタールや臭い等を取り除くフィルタ工程と、該フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスを磁界内に通過させて励起し再び有機物熱分解炉内の熱処理部に導入する工程とを備えることで自燃ガスの煙を外部に排出しない廃棄物の熱分解処理方法であって、前記フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスが磁界内を通過して励起される前に所定量の空気を自燃ガスと混合攪拌する混合気体製造工程を有してなることを特徴とする有機物熱分解炉を用いた廃棄物の熱分解処理方法である。 However, the present invention is for solving the above problems, and the invention according to claim 1 is a step of raising the temperature of the heat treatment section in the organic pyrolysis pyrolysis furnace to a predetermined temperature via a heat source, and the above-mentioned step. By adjusting the amount of air introduced into the heat treatment section in the organic pyrolysis furnace, the waste stored in the heat treatment section is maintained in an atmosphere within a predetermined temperature range for a predetermined time, and the waste is not removed. The process of making the combustible members of waste self-combustible and taking out by placing them in a complete combustion atmosphere, and the hot and humid self-combustible gas generated when the combustible members of waste self-combustion are organic substances via an attracting means. A step of attracting and discharging to the outside of the heat treatment part of the pyrolysis furnace, a filter step of cooling the self-combustion gas attracted and discharged to the outside of the heat treatment part of the organic pyrolysis furnace and removing tar and odor, and tar through the filter step. Waste that does not emit the smoke of the self-combustion gas to the outside by providing a step of passing the treated self-combustion gas from which the odor and the like have been removed into a magnetic field, exciting it, and introducing it into the heat treatment section in the organic pyrolysis pyrolysis furnace again. A pyrolysis method, in which a predetermined amount of air is mixed and stirred with the self-combustible gas before the treated self-combustible gas from which tar, odor, etc. have been removed through the filter step is excited by passing through the magnetic field. It is a method for pyrolyzing waste using an organic pyrolysis furnace, which comprises a gas production process.

更に、請求項2記載の発明は、有機物熱分解炉内の熱処理部外に誘引排出された自燃ガスの有機物熱分解炉からフィルタ工程までの間に自燃ガスの酸素濃度を計測する第1測定部が設けられ、且つ前記混合気体製造工程から磁界までの間には、処理済自燃ガスと空気とが混合された混合気体の酸素濃度を計測する第2測定部が設けられてなり、しかも第1測定部と第2測定部から得られた各々の計測データを演算処理することで処理済自燃ガスと混合攪拌される空気の量を常時変化させることを特徴する有機物熱分解炉を用いた廃棄物の熱分解処理方法である。 Further, the invention according to claim 2 is a first measuring unit for measuring the oxygen concentration of the self-combustible gas between the organic pyrolysis furnace and the filter step of the self-combustible gas attracted and discharged to the outside of the heat treatment unit in the organic pyrolysis furnace. Is provided, and a second measuring unit for measuring the oxygen concentration of the mixed gas in which the treated self-burning gas and air are mixed is provided between the mixed gas manufacturing process and the magnetic field. Waste using an organic pyrolysis furnace, which is characterized in that the amount of air mixed and stirred with the processed self-burning gas is constantly changed by arithmetically processing each measurement data obtained from the measuring unit and the second measuring unit. It is a thermal decomposition treatment method of.

更に、請求項3記載の発明は、フィルタ工程には、高温多湿の自燃ガスを冷却することで生じた水分を水切りを介して集水して貯溜槽に貯溜する工程と、該貯溜槽から生じる水蒸気と前記冷却時に残存する高温多湿の処理済自燃ガスとを混合した後再び除湿冷却する二次除湿冷却工程が設けられてなることを特徴とする有機物熱分解炉を用いた廃棄物の熱分解処理方法である。 Further, the invention according to claim 3 occurs in the filter step, that is, a step of collecting water generated by cooling a hot and humid self-combustion gas through a drain and storing it in a storage tank, and a step of storing the water in the storage tank. A secondary dehumidifying / cooling step is provided in which steam and the treated self-combustion gas having a high temperature and humidity remaining at the time of cooling are mixed and then dehumidified and cooled again. It is a processing method.

更に、請求項4記載の発明は、フィルタ工程において、高温多湿の自燃ガスは水を介して冷却されてなり、しかも該自燃ガスを冷却する水が、水切りを介して集水されて貯溜槽に貯溜された水を循環させる工程とから得られることを特徴とする有機物熱分解炉を用いた廃棄物の熱分解処理方法である。 Further, according to the invention of claim 4, in the filter step, the hot and humid self-combustion gas is cooled through water, and the water for cooling the self-combustion gas is collected through a drain and collected in a storage tank. It is a method for thermally decomposing waste using an organic material pyrolysis furnace, which is characterized by being obtained from a step of circulating the stored water.

本発明における請求項1記載の有機物熱分解炉を用いた廃棄物の熱分解処理方法は、熱源を介して有機物熱分解炉内の熱処理部の温度を所定の温度まで上昇させる工程と、該有機物熱分解炉内の熱処理部に導入される空気の量を調整することで熱処理部に収納された廃棄物を予め定めた温度の範囲内の雰囲気下に所定時間維持しつつ該廃棄物を不完全燃焼雰囲気下に置くことで廃棄物の可燃性部材を自燃させて取り出し可能とする工程と、廃棄物の可燃性部材が自燃する際に発生した高温多湿の自燃ガスを誘引手段を介して有機物熱分解炉の熱処理部外に誘引排出する工程と、有機物熱分解炉の熱処理部外に誘引排出された自燃ガスを冷却すると共にタールや臭い等を取り除くフィルタ工程と、該フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスを磁界内に通過させて励起し再び有機物熱分解炉内の熱処理部に導入する工程とを備えることで自燃ガスの煙を外部に排出しない廃棄物の熱分解処理方法であって、前記フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスが磁界内を通過して励起される前に所定量の空気を自燃ガスと混合攪拌する混合気体製造工程を有してなるものである。 The method for thermally decomposing waste using the organic pyrolysis furnace according to claim 1 of the present invention includes a step of raising the temperature of the heat treatment section in the organic pyrolysis furnace to a predetermined temperature via a heat source, and the organic substance. By adjusting the amount of air introduced into the heat treatment section in the pyrolysis furnace, the waste stored in the heat treatment section is kept in an atmosphere within a predetermined temperature range for a predetermined time, and the waste is incomplete. By placing it in a combustion atmosphere, the combustible member of the waste can be self-combusted and taken out, and the hot and humid self-combustible gas generated when the combustible member of the waste self-combustes is attracted to organic heat. A step of attracting and discharging to the outside of the heat treatment part of the decomposition furnace, a filter step of cooling the self-combustion gas attracted and discharged to the outside of the heat treatment part of the organic pyrolysis furnace and removing tar and odor, and a step of removing tar and odor through the filter step. The heat of waste that does not emit the smoke of the self-combustion gas to the outside by providing a step of passing the treated self-combustion gas from which odors have been removed into a magnetic field, exciting it, and introducing it into the heat treatment section in the organic pyrolysis pyrolysis furnace again. A pyrolysis method, which is a mixed gas in which a predetermined amount of air is mixed and stirred with the self-combustion gas before the treated self-combustion gas from which tar, odor, etc. have been removed through the filter step is excited by passing through a magnetic field. It has a manufacturing process.

よって、熱処理部(焼却処理室)内で生じた自燃ガスを有機物熱分解炉の熱処理部から屋外に排出することなく熱処理部内に戻す様に循環させて取り入れることで多量に発生する排煙(自燃ガス)を処理出来るだけでなく、タールや臭い等が除去された処理済自燃ガスが磁界内を通過して励起される前に所定量の空気と混合攪拌することで不完全燃焼雰囲気下に廃棄物が置かれた場合でも自燃の燃焼バランスを保持するために必要最少限の酸素を取り入れて有機物の隅々までムラなく自燃させることが出来るという効果を奏する。 Therefore, a large amount of smoke (self-combustion) is generated by circulating and taking in the self-combustion gas generated in the heat treatment section (incineration chamber) so as to return it to the heat treatment section without discharging it from the heat treatment section of the organic pyrolysis furnace to the outside. Not only can the gas) be treated, but the treated self-combustion gas from which tar and odors have been removed passes through the magnetic field and is discarded in an incomplete combustion atmosphere by mixing and stirring with a predetermined amount of air before being excited. Even when an object is placed, it has the effect of being able to take in the minimum amount of oxygen necessary to maintain the combustion balance of self-combustion and evenly self-combust every corner of the organic substance.

更に、有機物熱分解炉内の熱処理部外に誘引排出された自燃ガスの有機物熱分解炉からフィルタ工程までの間に自燃ガスの酸素濃度を計測する第1測定部が設けられ、且つ前記混合気体製造工程から磁界までの間には、処理済自燃ガスと空気とが混合された混合気体の酸素濃度を計測する第2測定部が設けられてなり、しかも第1測定部と第2測定部から得られた各々の計測データを演算処理することで処理済自燃ガスと混合攪拌される空気の量を常時変化させることにより、有機物熱分解炉内の熱処理部内の温度が、収納された廃棄物に用いられる有機物(可燃性部材)の材質や量で不安定となった場合でも、熱処理部内の温度変化から本来必要とする温度まで回復させるまでに至るタイムロスを最少限にとどめることが可能となるばかりか、特にある容積を有した熱処理部内の各箇所(例えば、上下等)における温度を即均一化することが可能になるという効果を奏する。 Further, a first measuring unit for measuring the oxygen concentration of the self-combustible gas is provided between the organic thermal decomposition furnace and the filter step of the self-combustible gas attracted and discharged to the outside of the heat treatment unit in the organic thermal decomposition furnace, and the mixed gas Between the manufacturing process and the magnetic field, a second measuring unit for measuring the oxygen concentration of the mixed gas in which the treated self-burning gas and air are mixed is provided, and from the first measuring unit and the second measuring unit. By constantly changing the amount of air that is mixed and agitated with the processed self-burning gas by arithmetically processing each of the obtained measurement data, the temperature inside the heat treatment section in the organic thermal decomposition furnace is converted to the stored waste. Even if the material and amount of the organic substance (flammable member) used becomes unstable, it is only possible to minimize the time loss from the temperature change in the heat treatment section to the recovery to the originally required temperature. In particular, it has the effect of making it possible to immediately equalize the temperature at each location (for example, upper and lower) in the heat treatment section having a certain volume.

更に、フィルタ工程には、高温多湿の自燃ガスを冷却することで生じた水分を水切りを介して集水して貯溜槽に貯溜する工程と、該貯溜槽から生じる水蒸気と前記冷却時に残存する高温多湿の処理済自燃ガスとを混合した後再び除湿冷却する二次除湿冷却工程が設けられてなることにより、磁界内を通過して励起される前に空気と攪拌混合する処理済自燃ガスに含まれる水分量を極少とすることでより正確な酸素量を計測可能となり、廃棄物の有機物の自燃の燃焼バランスを高効率で維持することが出来るという効果を奏する。 Further, the filter step includes a step of collecting water generated by cooling the hot and humid self-combustion gas through a drain and storing it in a storage tank, and a step of storing water vapor generated from the storage tank and the high temperature remaining at the time of cooling. By providing a secondary dehumidifying / cooling step of mixing with the humid treated self-combustion gas and then dehumidifying and cooling it again, it is included in the treated self-combustion gas that is stirred and mixed with air before being excited by passing through the magnetic field. By minimizing the amount of water vapor, it becomes possible to measure the amount of oxygen more accurately, and it is possible to maintain the self-combustion combustion balance of organic waste with high efficiency.

更に、フィルタ工程において、高温多湿の自燃ガスは水を介して冷却されてなり、しかも該自燃ガスを冷却する水が、水切りを介して集水されて貯溜槽に貯溜された水を循環させる工程とから得られることから、有機物熱分解炉のランニングコストを必要最小限にとどめることが可能になるという効果を奏する。 Further, in the filter step, the hot and humid self-combustion gas is cooled through water, and the water for cooling the self-combustion gas is collected through a drain and circulates the water stored in the storage tank. Since it is obtained from the above, it has the effect that the running cost of the organic pyrolysis furnace can be kept to the minimum necessary.

本発明における有機物熱分解炉を用いた廃棄物の熱分解処理方法によれば、熱源を介して有機物熱分解炉内の熱処理部の温度を所定の温度まで上昇させる工程と、該有機物熱分解炉内の熱処理部に導入される空気の量を調整することで熱処理部に収納された廃棄物を予め定めた温度の範囲内の雰囲気下に所定時間維持しつつ該廃棄物を不完全燃焼雰囲気下に置くことで廃棄物の可燃性部材を自燃させて取り出し可能とする工程と、廃棄物の可燃性部材が自燃する際に発生した高温多湿の自燃ガスを誘引手段を介して有機物熱分解炉の熱処理部外に誘引排出する工程と、有機物熱分解炉の熱処理部外に誘引排出された自燃ガスを冷却すると共にタールや臭い等を取り除くフィルタ工程と、該フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスを磁界内に通過させて励起し再び有機物熱分解炉内の熱処理部に導入する工程とを備えることで自燃ガスの煙を外部に排出しない廃棄物の熱分解処理方法であって、前記フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスが磁界内を通過して励起される前に所定量の空気を自燃ガスと混合攪拌する混合気体製造工程を有してなるものである。 According to the method for thermally decomposing waste using an organic pyrolysis furnace in the present invention, a step of raising the temperature of the heat treatment section in the organic pyrolysis furnace to a predetermined temperature via a heat source and the organic pyrolysis furnace By adjusting the amount of air introduced into the heat treatment section, the waste stored in the heat treatment section is maintained in an atmosphere within a predetermined temperature range for a predetermined time, and the waste is kept in an incomplete combustion atmosphere. The process of making the combustible members of waste self-combustible and taking them out by placing them in the oven, and the hot and humid self-combustible gas generated when the combustible members of waste self-combustion are attracted to the organic pyrolysis furnace. A step of attracting and discharging to the outside of the heat treatment part, a filter step of cooling the self-combustion gas attracted and discharged to the outside of the heat treatment part of the organic pyrolysis furnace and removing tar and odor, and a filter step of removing tar and odor, etc. A method for thermally decomposing waste that does not emit the smoke of the self-combustion gas to the outside by providing a step of passing the removed treated self-combustion gas through a magnetic field, exciting it, and introducing it into the heat treatment section in the organic pyrolysis furnace again. A mixed gas manufacturing step of mixing and stirring a predetermined amount of air with the self-combustible gas before the treated self-combustible gas from which tar, odor, etc. have been removed through the filter step passes through the magnetic field and is excited. It is something that you have.

従って、熱処理部(焼却処理室)内で生じた自燃ガスを有機物熱分解炉の熱処理部から屋外に排出することなく熱処理部内に戻す様に循環させて取り入れることで多量に発生する排煙(自燃ガス)を処理出来るだけでなく、タールや臭い等が除去された処理済自燃ガスが磁界内を通過して励起される前に所定量の空気と混合攪拌することで不完全燃焼雰囲気下に廃棄物が置かれた場合でも自燃の燃焼バランスを保持するために必要最少限の酸素を取り入れて有機物の隅々までムラなく自燃させることが出来るという利点がある。 Therefore, a large amount of smoke (self-combustion) is generated by circulating and taking in the self-combustion gas generated in the heat treatment section (incineration chamber) so as to return it to the heat treatment section without discharging it from the heat treatment section of the organic pyrolysis furnace to the outside. Not only can the gas) be treated, but the treated self-combustion gas from which tar and odors have been removed passes through the magnetic field and is discarded in an incomplete combustion atmosphere by mixing and stirring with a predetermined amount of air before being excited. Even when an object is placed, it has the advantage of being able to take in the minimum amount of oxygen necessary to maintain the combustion balance of self-combustion and evenly self-combust every corner of the organic substance.

更に、有機物熱分解炉内の熱処理部外に誘引排出された自燃ガスの有機物熱分解炉からフィルタ工程までの間に自燃ガスの酸素濃度を計測する第1測定部が設けられ、且つ前記混合気体製造工程から磁界までの間には、処理済自燃ガスと空気とが混合された混合気体の酸素濃度を計測する第2測定部が設けられてなり、しかも第1測定部と第2測定部から得られた各々の計測データを演算処理することで処理済自燃ガスと混合攪拌される空気の量を常時変化させることにより、有機物熱分解炉内の熱処理部内の温度が、収納された廃棄物に用いられる有機物(可燃性部材)の材質や量で不安定となった場合でも、熱処理部内の温度変化から本来必要とする温度まで回復させるまでに至るタイムロスを最少限にとどめることが可能となるばかりか、特にある容積を有した熱処理部内の各箇所(例えば、上下等)における温度を即均一化することが可能になるという利点がある。 Further, a first measuring unit for measuring the oxygen concentration of the self-combustible gas is provided between the organic thermal decomposition furnace and the filter step of the self-combustible gas attracted and discharged to the outside of the heat treatment unit in the organic thermal decomposition furnace, and the mixed gas Between the manufacturing process and the magnetic field, a second measuring unit for measuring the oxygen concentration of the mixed gas in which the treated self-burning gas and air are mixed is provided, and from the first measuring unit and the second measuring unit. By constantly changing the amount of air that is mixed and agitated with the processed self-burning gas by arithmetically processing each of the obtained measurement data, the temperature inside the heat treatment section in the organic thermal decomposition furnace can be converted to the stored waste. Even if the material and amount of the organic material (flammable member) used becomes unstable, it is only possible to minimize the time loss from the temperature change in the heat treatment section to the recovery to the originally required temperature. In particular, there is an advantage that it is possible to immediately make the temperature uniform at each location (for example, upper and lower) in the heat treatment section having a certain volume.

更に、フィルタ工程には、高温多湿の自燃ガスを冷却することで生じた水分を水切りを介して集水して貯溜槽に貯溜する工程と、該貯溜槽から生じる水蒸気と前記冷却時に残存する高温多湿の処理済自燃ガスとを混合した後再び除湿冷却する二次除湿冷却工程が設けられてなることにより、磁界内を通過して励起される前に空気と攪拌混合する処理済自燃ガスに含まれる水分量を極少とすることでより正確な酸素量を計測可能となり、廃棄物の有機物の自燃の燃焼バランスを高効率で維持することが出来るという利点がある。 Further, the filter step includes a step of collecting water generated by cooling the hot and humid self-combustion gas through a drain and storing it in a storage tank, and a step of storing water vapor generated from the storage tank and the high temperature remaining at the time of cooling. By providing a secondary dehumidifying / cooling step of mixing with the humid treated self-combustion gas and then dehumidifying and cooling it again, it is included in the treated self-combustion gas that is stirred and mixed with air before being excited by passing through the magnetic field. By minimizing the amount of water vapor, it is possible to measure the amount of oxygen more accurately, and there is an advantage that the self-combustion combustion balance of organic waste can be maintained with high efficiency.

更に、フィルタ工程において、高温多湿の自燃ガスは水を介して冷却されてなり、しかも該自燃ガスを冷却する水が、水切りを介して集水されて貯溜槽に貯溜された水を循環させる工程とから得られることから、有機物熱分解炉のランニングコストを必要最小限にとどめることが可能になるという利点がある。 Further, in the filter step, the hot and humid self-combustion gas is cooled through water, and the water for cooling the self-combustion gas is collected through a drain and circulates the water stored in the storage tank. Since it is obtained from the above, there is an advantage that the running cost of the organic pyrolysis furnace can be kept to the minimum necessary.

而して、本発明の有機物熱分解炉を用いた廃棄物の熱分解処理方法を実施するための有機物熱分解炉、熱処理部、高温多湿の自燃ガスを誘引手段を介して有機物熱分解炉の熱処理部外に誘引排出する工程、有機物熱分解炉の熱処理部外に誘引排出された自燃ガスを冷却すると共にタールや臭い等を取り除くフィルタ工程、フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスを磁界内に通過させて励起し再び有機物熱分解炉内の熱処理部に導入する工程に用いる具体的な部材、材質、構造、装置等も本発明の意図する範囲内で任意に設計変更自在であるのは言うまでもない。 Thus, the organic pyrolysis furnace for carrying out the method for thermally decomposing waste using the organic pyrolysis furnace of the present invention, the heat treatment section, and the hot and humid self-combustible gas of the organic pyrolysis furnace via an attracting means. The tar and odor were removed through the process of attracting and discharging to the outside of the heat treatment part, the filter step of cooling the self-burning gas attracted and discharged to the outside of the heat treatment part of the organic pyrolysis furnace and removing tar and odor, etc. Specific members, materials, structures, devices, etc. used in the process of passing the treated self-burning gas through a magnetic field, exciting it, and introducing it into the heat treatment section in the organic pyrolysis pyrolysis furnace are also arbitrarily specified within the scope of the present invention. Needless to say, the design can be changed freely.

本発明は、廃棄物の熱分解処理方法に関し、更に詳しくは廃棄物を予め定めた温度の範囲内の雰囲気下に所定時間維持しつつ該廃棄物を不完全燃焼雰囲気下に置くことで廃棄物の可燃性部材を自燃させて取り出し可能に処理することが出来る極めて優れた有機物熱分解炉を用いた廃棄物の熱分解処理方法に関するものである。 The present invention relates to a method for thermally decomposing waste, and more specifically, by placing the waste in an incomplete combustion atmosphere while maintaining the waste in an atmosphere within a predetermined temperature range for a predetermined time. The present invention relates to a method for thermally decomposing waste using an extremely excellent organic thermal decomposition furnace capable of self-combustion and retrievably processing the flammable member of the above.

Claims (4)

熱源を介して有機物熱分解炉内の熱処理部の温度を所定の温度まで上昇させる工程と、該有機物熱分解炉内の熱処理部に導入される空気の量を調整することで熱処理部に収納された廃棄物を予め定めた温度の範囲内の雰囲気下に所定時間維持しつつ該廃棄物を不完全燃焼雰囲気下に置くことで廃棄物の可燃性部材を自燃させて取り出し可能とする工程と、廃棄物の可燃性部材が自燃する際に発生した高温多湿の自燃ガスを誘引手段を介して有機物熱分解炉の熱処理部外に誘引排出する工程と、有機物熱分解炉の熱処理部外に誘引排出された自燃ガスを冷却すると共にタールや臭い等を取り除くフィルタ工程と、該フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスを磁界内に通過させて励起し再び有機物熱分解炉内の熱処理部に導入する工程とを備えることで自燃ガスの煙を外部に排出しない廃棄物の熱分解処理方法であって、前記フィルタ工程を介してタールや臭い等が除去された処理済自燃ガスが磁界内を通過して励起される前に所定量の空気を自燃ガスと混合攪拌する混合気体製造工程を有してなることを特徴とする有機物熱分解炉を用いた廃棄物の熱分解処理方法。 It is stored in the heat treatment section by adjusting the step of raising the temperature of the heat treatment section in the organic pyrolysis furnace to a predetermined temperature via a heat source and adjusting the amount of air introduced into the heat treatment section in the organic pyrolysis furnace. A process of maintaining the waste in an atmosphere within a predetermined temperature range for a predetermined time and placing the waste in an incomplete combustion atmosphere so that the combustible member of the waste can be self-combusted and taken out. The process of attracting and discharging the hot and humid self-combustible gas generated when the combustible member of the waste burns to the outside of the heat treatment part of the organic pyrolysis furnace via an attracting means and the process of attracting and discharging it to the outside of the heat treatment part of the organic pyrolysis furnace. A filter step that cools the self-combustion gas and removes tar and odors, and a processed self-combustion gas from which tar and odors have been removed through the filter step is passed through a magnetic field to excite and re-excite the organic pyrolysis furnace. It is a method of pyrolyzing waste that does not emit the smoke of self-combustion gas to the outside by providing a step of introducing it into the heat treatment section inside, and the treated self-combustion from which tar, odor, etc. are removed through the filter process. Pyrolysis of waste using an organic pyrolysis furnace, which comprises a mixed gas production process in which a predetermined amount of air is mixed and stirred with a self-combustible gas before the gas passes through a magnetic field and is excited. Processing method. 前記有機物熱分解炉内の熱処理部外に誘引排出された自燃ガスの有機物熱分解炉からフィルタ工程までの間に自燃ガスの酸素濃度を計測する第1測定部が設けられ、且つ前記混合気体製造工程から磁界までの間には、処理済自燃ガスと空気とが混合された混合気体の酸素濃度を計測する第2測定部が設けられてなり、しかも第1測定部と第2測定部から得られた各々の計測データを演算処理することで処理済自燃ガスと混合攪拌される空気の量を常時変化させることを特徴する請求項1記載の有機物熱分解炉を用いた廃棄物の熱分解処理方法。 A first measuring unit for measuring the oxygen concentration of the self-combustible gas is provided between the organic thermal decomposition furnace of the self-combustible gas attracted and discharged to the outside of the heat treatment unit in the organic thermal decomposition furnace and the filter step, and the mixed gas production Between the step and the magnetic field, a second measuring unit for measuring the oxygen concentration of the mixed gas in which the treated self-burning gas and air are mixed is provided, and moreover, it is obtained from the first measuring unit and the second measuring unit. Thermal decomposition treatment of waste using the organic thermal decomposition furnace according to claim 1, wherein the amount of air mixed and stirred with the processed self-burning gas is constantly changed by arithmetically processing each of the measured measurement data. Method. 前記フィルタ工程には、高温多湿の自燃ガスを冷却することで生じた水分を水切りを介して集水して貯溜槽に貯溜する工程と、該貯溜槽から生じる水蒸気と前記冷却時に残存する高温多湿の処理済自燃ガスとを混合した後再び除湿冷却する二次除湿冷却工程が設けられてなることを特徴とする請求項1又は2記載の有機物熱分解炉を用いた廃棄物の熱分解処理方法。 The filter step includes a step of collecting water generated by cooling the hot and humid self-combustion gas through a drain and storing it in a storage tank, and a step of storing water vapor generated from the storage tank and the high temperature and humidity remaining during the cooling. The method for thermally decomposing waste using an organic thermal decomposition furnace according to claim 1 or 2, wherein a secondary dehumidifying and cooling step of mixing with the treated self-combustion gas and then dehumidifying and cooling is provided. .. 前記フィルタ工程には、高温多湿の自燃ガスは水を介して冷却されてなり、しかも該自燃ガスを冷却する水が、水切りを介して集水されて貯溜槽に貯溜された水を循環させる工程とから得られることを特徴とする請求項3記載の有機物熱分解炉を用いた廃棄物の熱分解処理方法。 In the filter step, the hot and humid self-combustion gas is cooled through water, and the water for cooling the self-combustion gas is collected through a drain and circulates the water stored in the storage tank. The method for thermally decomposing waste using the organic material pyrolysis furnace according to claim 3, wherein the method is obtained from
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