JP2006247437A - Thermal decomposition, carbonization and gasification treatment method for organic waste with no use of fuel - Google Patents

Thermal decomposition, carbonization and gasification treatment method for organic waste with no use of fuel Download PDF

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JP2006247437A
JP2006247437A JP2005054568A JP2005054568A JP2006247437A JP 2006247437 A JP2006247437 A JP 2006247437A JP 2005054568 A JP2005054568 A JP 2005054568A JP 2005054568 A JP2005054568 A JP 2005054568A JP 2006247437 A JP2006247437 A JP 2006247437A
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organic waste
oxygen
pyrolysis reactor
ash
heat
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Masato Nakajima
正人 中島
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OKINAWA NOREN KANKYO CENTER
OKINAWA NOREN KANKYO CT
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OKINAWA NOREN KANKYO CENTER
OKINAWA NOREN KANKYO CT
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a thermal decomposition method for an organic waste in which an energy of a heavy oil or the like is not used and a harmful compound such as dioxin is not by-produced, and an apparatus. <P>SOLUTION: In the organic waste treatment method, oxygen is diffused to the whole of a bottom surface of a thermal decomposition reactor 1 and a part of the organic waste product having calorific power and moisture content adjusted to the optimum is partially oxidized. Since an amount of oxygen is controlled by a valve at a distal end of an introduction pipe, the inside of the thermal decomposition reactor 1 in the non-oxygen state and by-production of the harmful compound such as dioxin is not totally generated. The partially oxidized organic waste product becomes ash and heat is generated. The peripheral organic waste product is thermally decomposed, carbonized, gasified and incinerated by the heat. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

要約wrap up

燃料を使用せずに、有機系廃棄物の一部を部分酸化して、その熱によってダイオキシン等の有害化合物を発生させること無く、有機系廃棄物を熱分解・炭化、ガス化、そして灰化処理する小型分散型の方法並びに装置に関するものである。Without using fuel, a part of organic waste is partially oxidized and the organic waste is pyrolyzed, carbonized, gasified, and incinerated without generating harmful compounds such as dioxin by the heat. The present invention relates to a small distributed method and apparatus for processing.

発明の詳細なる説明Detailed Description of the Invention

本発明は燃料を使用せずにダイオキシン等の有害化合物を副生することなく、有機系廃棄物を熱分解処理し、生成した炭化物およびアッシュを非常に効果的な肥料や土壌改良剤にし、一切の廃棄物を出さない小型分散型の資源循環型の方法並びに装置に関するものである。The present invention does not use fuel and does not produce harmful compounds such as dioxins, by pyrolysis of organic waste, and the resulting carbide and ash are made into very effective fertilizers and soil conditioners. The present invention relates to a small and distributed resource recycling method and apparatus that does not generate any waste.

有機系廃棄物は一般に埋め立てや焼却処理される。しかし、塩素化合物が含まれる有機系廃棄物を燃焼した場合にはダイオキシンが副生するので大量の重油を使用して高温で燃焼し無ければならない。日本は京都議定書において1990年をベースに2012年まで温室効果ガスを6%削減する事を義務付けられており、生産性の低い有機系廃棄物の処理に大量の重油を使用する現在のシステムは非常な問題がある。Organic waste is generally landfilled or incinerated. However, when organic waste containing chlorine compounds is combusted, dioxins are by-produced and must be burned at a high temperature using a large amount of heavy oil. Japan is obliged to reduce greenhouse gases by 6% based on 1990 in the Kyoto Protocol until 2012, and the current system that uses a large amount of heavy oil for the treatment of organic waste with low productivity is very There is a problem.

発明が解決しようとする課題Problems to be solved by the invention

本発明は従来技術の欠点を克服し、重油等のエネルギーを使用せずに有機系廃棄物の持つ内部エネルギーの一部を利用して、ダイオキシンなどの有害化合物を副生させずに有機系廃棄物を熱分解して、生成した炭化物およびアッシュを非常に効果的な肥料や土壌改良剤にし、一切の廃棄物を出さない資源循環型の方法並びに装置を開発することであるThe present invention overcomes the disadvantages of the prior art and uses part of the internal energy of organic waste without using energy such as heavy oil, so that organic waste can be disposed without by-producting harmful compounds such as dioxin. The purpose is to develop a resource recycling method and equipment that pyrolyzes the product, turns the generated carbide and ash into a highly effective fertilizer and soil conditioner, and does not emit any waste.

課題を解決するための手段Means for solving the problem

上記課題を解決するための発明の要件は次の通りである。
(a)底部に酸素を制御しながら導入する導入管を有する熱分解反応器と(b)熱分解反応器内部の導入管の長さが、一部は中心部、一部は中間部、一部は端部に酸素が拡散するように作られていることと(c)熱分解によって得られたアッシュを導入管が埋まるように敷き詰め、酸素の拡散速度の制御、生成した塩酸などの中和、ガス化反応の触媒、水分や生成した高沸点有機物の捕集剤として使用することと(d)発熱量と水分含量を計算して調製した有機系廃棄物を熱分解反応器に隙間無く充填し、熱分解によって発生した水分や有機物と熱交換させて、再び反応系に戻す事と(e)酸素が逆流しないような構造を持つ冷却器と排出口を有する有機系廃棄物の熱分解方法並びに装置である。
The requirements of the invention for solving the above-mentioned problems are as follows.
(A) a pyrolysis reactor having an introduction pipe for introducing oxygen to the bottom while controlling oxygen; and (b) the length of the introduction pipe inside the pyrolysis reactor is partly in the center, part in the middle, The part is made so that oxygen diffuses at the end, and (c) the ash obtained by thermal decomposition is laid down so that the introduction pipe is buried, the oxygen diffusion rate is controlled, and the generated hydrochloric acid is neutralized Used as a catalyst for gasification reaction, trapping agent for water and high-boiling organic matter produced, and (d) filling organic pyrolysis reactors prepared by calculating calorific value and water content without any gaps And heat exchange with moisture and organic matter generated by pyrolysis and returning it to the reaction system again; and (e) a pyrolysis method of organic waste having a cooler with a structure that prevents backflow of oxygen and an outlet. As well as a device.

ダイオキシンが発生する機構は塩素を含む有機廃棄物が分解して発生した塩酸(HCl)と酸素(O)と前駆体と反応する。従って、酸素をできるだけ抑えてやればダイオキシンの生成は防ぐ事ができる。炭焼き釜のような乾留・炭化炉はダイオキシンの生成量が非常に低いのはこのためである。我々は種々調査・検討した結果、密閉した熱分解反応器内に少量の酸素を送り込み、ほんの一部の有機系廃棄物を部分酸化してやれば、外部から熱を供給することなく、ダイオキシン等の副生も無く、全体を乾留・炭化・ガス化・灰化できることを、見出し本発明を完成した。The mechanism for generating dioxin is a reaction between hydrochloric acid (HCl), oxygen (O 2 ) and a precursor generated by decomposition of organic waste containing chlorine. Therefore, if oxygen is suppressed as much as possible, the production of dioxins can be prevented. This is why the amount of dioxins produced in carbonization furnaces such as charcoal pots is very low. As a result of various investigations and examinations, if a small amount of oxygen is sent into a sealed pyrolysis reactor and only a small portion of organic waste is partially oxidized, heat is not supplied from the outside. The present invention was completed by finding out that the whole can be distilled, carbonized, gasified and incinerated without any raw material.

次に本発明の詳細な内容について述べる。密閉した上記熱分解反応器の底部に導入管が埋まるようにアッシュを敷き詰め、発熱量と水分量を調製した有機系廃棄物を隙間無く充填し、中央部のアッシュと有機系廃棄物の境目を電熱ヒータなどで加熱する。温度が上がり有機系廃棄物の一部が着火したらすぐに電熱ヒータを切る。熱分解反応器内の酸素は直ぐに消費されて無酸素状態になり、導入管とアッシュを拡散してきた酸素はアッシュとの境目にある有機系廃棄物のみを部分酸化し、自らはアッシュとなって発熱する。この熱は熱伝導のあまり良くない有機系廃棄物で覆われているために蓄熱し、周囲の有機系廃棄物を熱分解して、ガスやピッチ、炭化物などを生成する。このために、アッシュとの境界面は常に分解ガスやピッチ、炭化物など酸化され易い物質になっている。導入管とアッシュを通って濃度拡散によって運ばれる酸素はアッシュとの境界面にあるガスやピッチ、炭化物などの部分酸化に消費されるために部分酸化が起こっている層の上側にある有機系廃棄物の熱分解は無酸素状態で行われるために、ダイオキシンなどの有害化合物の副生は殆ど起こらない。部分酸化層の厚さは温度を測定できないほど薄く、アッシュの状態で判断するしかないが、熱が蓄積されやすく、高カロリーの炭化物、ガス、ピッチなどが酸化されるために800℃以上の高温になっていると推定している。熱分解によって発生したガスや蒸発した水分はびっしりと充填された有機系廃棄物の中を熱交換しながら上昇するが、沸点の高いピッチやダイオキシン前駆体などは殆どすべて有機系廃棄物の中に捕集されて外部には出てこない。これらはやがてアッシュ層の境界面に達し、部分酸化によってアッシュとなる。有機系廃棄物の水分含有率は60%程度まで問題ないが水分の役割は次のよう考えている。潜熱が大きく、沸点の低い水分は部分酸化層で蒸気となって有機系廃棄物の中を上昇し、熱交換によって有機系廃棄物全体の温度をあげる。また、熱交換によって水滴となってダイオキシン発生の原因物質である塩酸を溶解し壁を伝わってアッシュ層に入り、塩基性物質を含むアッシュと塩酸を反応させて固定する。アッシュに入った水分は毛細管現象によって部分酸化層に達し、有機系廃棄物の中から落下する水滴と共に部分酸化層のガス化を促進させる。その時、アッシュはその成分から推定するとガス化触媒として作用すると考えている。Next, the detailed contents of the present invention will be described. Fill the bottom of the sealed pyrolysis reactor with ash so that the introduction pipe is buried, and fill the organic waste with adjusted calorific value and moisture without gaps, and the boundary between the central ash and organic waste Heat with an electric heater. Turn off the electric heater as soon as the temperature rises and some of the organic waste is ignited. Oxygen in the pyrolysis reactor is immediately consumed and becomes oxygen-free, and oxygen that has diffused through the introduction pipe and ash partially oxidizes only organic waste at the boundary with ash and becomes ash itself. Fever. Since this heat is covered with organic waste that does not conduct heat well, heat is stored, and the surrounding organic waste is thermally decomposed to generate gas, pitch, carbide, and the like. For this reason, the interface with ash is always a substance that is easily oxidized, such as cracked gas, pitch, and carbide. Oxygen transported by concentration diffusion through the inlet pipe and ash is consumed by partial oxidation of gas, pitch, carbide, etc. at the interface with ash, so organic waste above the layer where partial oxidation occurs Since thermal decomposition of the product is performed in an anoxic state, almost no byproduct of harmful compounds such as dioxin occurs. The thickness of the partially oxidized layer is so thin that the temperature cannot be measured and can only be judged in the ash state. However, heat is likely to accumulate, and high-calorie carbides, gases, pitches, etc. are oxidized, resulting in high temperatures of 800 ° C or higher. It is estimated that Gas generated by pyrolysis and evaporated water rise while exchanging heat in the organic waste that is packed, but almost all of the high boiling point pitch and dioxin precursors are in the organic waste. It is collected and does not come out. These eventually reach the interface of the ash layer and become ash by partial oxidation. There is no problem with the water content of organic waste up to about 60%, but the role of water is considered as follows. Moisture with large latent heat and low boiling point becomes vapor in the partial oxidation layer and rises in the organic waste, and the temperature of the entire organic waste is raised by heat exchange. In addition, hydrochloric acid, which is a causative substance of dioxin generation, is dissolved by heat exchange and dissolved in hydrochloric acid, enters the ash layer through the wall, and reacts and fixes ash containing a basic substance and hydrochloric acid. Moisture entering the ash reaches the partially oxidized layer by capillary action, and promotes gasification of the partially oxidized layer together with water droplets falling from the organic waste. At that time, ash is considered to act as a gasification catalyst when estimated from its components.

本発明は焼却装置とは明らかに違う。燃焼においては燃料の10倍以上の空気を強制的に吹き込み、排ガス流量が大きいために沸点の高いダイオキシンを付着した大量の粉塵や排ガスの冷却過程で再合成されたダイオキシンを付着した飛灰を外部にもたらすため、非常に高価な集塵装置やフィルターなどを設置する必要がある。しかし、本発明装置においては酸素の濃度拡散で熱分解反応器内に酸素を供給するために、導入管の先に薄い麈紙やタバコの煙をかざしても殆ど動かないくらいの少流量しか供給されない。熱分解が始まると熱分解反応器内の圧力は高くなり、バルブを僅かしか開放していない導入管からは空気は殆ど流入しない。しかし、熱分解反応器内の酸素は部分酸化によって直ぐ消費されてしまうので酸素濃度はゼロに近い。従って、酸素分圧のたかい外気から酸素が濃度拡散によって流入すると考えている。
排ガス量は非常に少なく、分厚く積層された有機系廃棄物の中を熱交換しながら排出口に向かうので粉塵は全く発生しない。従って、ダイオキシンが発生したとしても有機系廃棄物中に捕集されて、やがて部分酸化層に達して分解してしまう。
The present invention is clearly different from the incinerator. In combustion, air more than 10 times the fuel is forcibly blown, and because the exhaust gas flow rate is large, a large amount of dust attached with high boiling point dioxin and fly ash attached with dioxin recombined in the exhaust gas cooling process Therefore, it is necessary to install very expensive dust collectors and filters. However, in the apparatus of the present invention, in order to supply oxygen into the pyrolysis reactor by oxygen concentration diffusion, supply a small flow rate that does not move even if a thin paper or cigarette smoke is put over the tip of the introduction pipe. Not. When pyrolysis begins, the pressure in the pyrolysis reactor increases, and almost no air flows from the inlet pipe with the valve only slightly open. However, oxygen in the pyrolysis reactor is consumed immediately by partial oxidation, so the oxygen concentration is close to zero. Therefore, it is considered that oxygen flows from outside air having a high oxygen partial pressure by concentration diffusion.
The amount of exhaust gas is very small, and dust is not generated at all because it goes to the discharge port while exchanging heat in thick organic waste. Therefore, even if dioxin is generated, it is collected in the organic waste, and eventually reaches the partially oxidized layer and decomposes.

有機系廃棄物の熱分解反応の過程を図1に模式的に示した。アッシュを通って拡散してきた酸素はアッシュとの境界面に生成している炭化物、ピッチ、ガスを酸化して発熱する。この層は高カロリーの物質をサンカスルために800℃以上の高温になる。アッシュから上がってきた水分や上から落ちてきた水滴は高温の水蒸気となり、ガス化や有機系廃棄物の炭化を促す。高温層の上に無酸素状態で熱分解された炭化層がやや厚めに存在する。この層はやがてアッシュと接触して高温層になる。その上には熱変化を受けていない有機系廃棄物の層がある.この層は水蒸気と熱交換して温度は上昇するが50℃〜70℃程であるので水滴によって濡らされ下部のガスや有機性蒸気を密閉する。このようにして大部分の有機系廃棄物が無酸素状態で熱分解が進行するためにダイオキシンなどの有害物は副性しない。熱分解反応器の側壁や上部は手で触れるほどの暖かさでダイオキシン発生の原因となる前駆体は冷やされて熱分解反応器内に戻ってしまい外部には殆ど出てこない。The process of the thermal decomposition reaction of organic waste is schematically shown in FIG. Oxygen diffused through the ash generates heat by oxidizing carbides, pitch, and gas generated at the interface with the ash. This layer is heated to a high temperature of 800 ° C. or higher because of high-calorie substances. Moisture rising from the ash and water droplets falling from the top become high-temperature water vapor, which promotes gasification and carbonization of organic waste. There is a slightly thick carbonized layer thermally decomposed in the absence of oxygen on the high temperature layer. This layer eventually comes into contact with the ash and becomes a high temperature layer. Above that there is a layer of organic waste that has not undergone thermal changes. This layer heat-exchanges with water vapor and the temperature rises, but it is about 50 ° C. to 70 ° C., so it is wetted by water droplets and seals the gas and organic vapor below. In this way, since most organic wastes undergo thermal decomposition in the absence of oxygen, harmful substances such as dioxins are not secondary. The precursor that causes the generation of dioxins is cooled to the extent that it is warm enough to touch the side wall and upper part of the pyrolysis reactor, and returns to the pyrolysis reactor and hardly goes outside.

熱分解反応器の内部には断熱と過剰な水分を除くための多数の穴を持つ内部壁を設ける。穴の形状はガスを通し、凝縮液をアッシュ層に流せるものならどのような形状でも良いが、例えば、外からうちへ向かって上が開くように打ち抜く。そうすれば、熱分解反応器内部から発生した蒸気や有機性のガスが外壁と内壁の間に入り込み、外壁によって冷やされて凝縮液となって流下するときにも熱分解反応器内部に戻らずにアッシュ層に流す事ができる。Inside the pyrolysis reactor is an internal wall with a number of holes to insulate and remove excess moisture. The shape of the hole may be any shape as long as it allows gas to pass and the condensate to flow into the ash layer. For example, the hole is punched so that the top opens from the outside to the inside. Then, when the vapor or organic gas generated from the inside of the pyrolysis reactor enters between the outer wall and the inner wall and is cooled by the outer wall and flows down as a condensate, it does not return to the inside of the pyrolysis reactor. It can flow to the ash layer.

発明の実施形態Embodiments of the Invention

本発明の実施形態を図面に基づいて具体的に説明する。
図2に熱分解反応器の正面図を示した。これは製作した熱分解反応器の1例でこれに限定されるものではない。熱分解反応器1は鉄製で直径1000、高さ1200の円筒形である。図3に上から見た熱分解反応器の断面図を示した。熱分解反応器の底部に中心部に向かって内壁から400の導入管を4本、200の導入管を4本、100の導入管を8本取り付けてある。導入管にはそれぞれ酸素の拡散速度を制御するためのバルブを取り付けてある。酸素供給量が多すぎる場合はいくつかのバルブを閉じる。熱分解反応器底部はアッシュを取り出しやすいように勾配がつけ、先端にロータリーバルブなどを取り付け、アッシュを取り出す作業がしやすいような高さに調製する足が付けられている。熱分解反応器の底部側壁に点検や誤って投入された金属類などを取り出す開口部を設けてある。この扉は耐熱性のパッキンによって通常は完全に密閉される。熱分解反応器の内側には適度な隙間を空けて多数の穴の開いた内壁が設けられている。過剰な水分や有機性蒸気はこの穴を抜けて外壁と接触して冷やされ流下して有機系廃棄物に付着して熱分解されるので外部にはほんの僅かしか排出されない。水分はアッシュ層に浸透していき一部は毛細管現象によって上昇し有機系廃棄物のガス化反応に使われる。排出ガスはコンデンサーの冷却水をバブリングして排出され、外気からも遮断されている。
Embodiments of the present invention will be specifically described with reference to the drawings.
FIG. 2 shows a front view of the pyrolysis reactor. This is an example of the manufactured pyrolysis reactor, and is not limited thereto. The pyrolysis reactor 1 is made of iron and has a cylindrical shape with a diameter of 1000 and a height of 1200. FIG. 3 shows a sectional view of the pyrolysis reactor as seen from above. Four 400 introduction pipes, 4 200 introduction pipes, and 8 100 introduction pipes are attached to the bottom of the pyrolysis reactor from the inner wall toward the center. Each inlet pipe is provided with a valve for controlling the oxygen diffusion rate. If the oxygen supply is too high, close some valves. The bottom of the pyrolysis reactor is sloped so that the ash can be easily taken out, and a rotary valve or the like is attached to the tip of the pyrolysis reactor so that the feet can be adjusted to a height that makes it easy to take out the ash. An opening is provided in the bottom side wall of the pyrolysis reactor to take out metal that has been inspected or misplaced. This door is usually completely sealed by heat-resistant packing. An inner wall with a large number of holes is provided inside the pyrolysis reactor with an appropriate gap. Excess water and organic vapor pass through this hole, come into contact with the outer wall, cool down, flow down, adhere to organic waste, and are thermally decomposed, so that only a little is discharged to the outside. Moisture penetrates into the ash layer and partly rises by capillary action and is used for gasification reaction of organic waste. Exhaust gas is discharged by bubbling condenser cooling water, and is also cut off from outside air.

発明の効果The invention's effect

アッシュ層に接触する有機系廃棄物の一部を部分酸化して、その発熱によって無酸素状態で他の大部分の有機系廃棄物を熱分解、炭化、ガス化反応を起させて、ダイオキシンなどの有害化合物を副生することなく、有機系廃棄物を無燃料で処理する方法である。Part of organic waste that comes into contact with the ash layer is partially oxidized, and the exothermic heat causes pyrolysis, carbonization, and gasification of most other organic waste in the absence of oxygen. This is a method of treating organic waste without fuel without the by-product of harmful compounds.

45Lのポリ袋に詰め込まれた生ゴミ5袋、電話帳や雑誌、新聞など紙類200kg、梱包用のポリスチレン等を熱分解反応器に入れ、隙間と上部を100Lの籾殻で埋めて投入口を閉じた。全体の容量は約1000L(重量250kg)である。着火ヒータで加熱し、煙突から煙が出始めたら直ぐにヒータを切った。バルブは始めのうちはやや開放にし、熱分解が順調に開始されてからは僅かに開放にした。熱分解反応器の外壁温度は初期には室温であるが次第に暖まり、全体の外壁の温度は50℃〜60℃ほどの定常状態になった。そのまま、無人で24時間放置して熱分解を行った。投入口を開けて中を点検した結果、有機系廃棄物は表面の1cmが黒い炭化物であったがその下は全て白っぽいアッシュとなっていた。乾留液は約10Lほどであった。排出口から排出されたガス、乾留液及びアッシュなどを採取し、ダイオキシン、コプラナPCBsを分析した結果は毒性等量換算で排ガス0.2pg−TEQ/Nm、乾留液で0.009ng−TEQ/g、アッシュで0.008ng−TEQ/gで排ガスの国の環境基準値5.0ng−TEQ/Nm、処理灰の環境基準値3.0ng−TEQ/mの大幅に下回る結果であった。Place 5 bags of garbage in a 45L plastic bag, 200kg of paper such as phonebooks, magazines and newspapers, polystyrene for packing, etc. into a pyrolysis reactor, fill the gap and the top with 100L of rice husk, and fill the inlet Closed. The total capacity is about 1000 L (weight 250 kg). The heater was heated with an ignition heater, and the heater was turned off as soon as smoke began to come out of the chimney. The valve was opened a little at the beginning, and slightly opened after the thermal decomposition started smoothly. The outer wall temperature of the pyrolysis reactor was initially room temperature but gradually warmed, and the temperature of the entire outer wall became a steady state of about 50 ° C to 60 ° C. As it was, it was left unattended for 24 hours for thermal decomposition. As a result of opening the inlet and inspecting the inside, the organic waste was a black carbide with 1 cm on the surface, but the bottom was all whitish ash. The dry distillation liquid was about 10L. The gas, dry distillation liquid, and ash discharged from the discharge port were collected and analyzed for dioxins and coplanar PCBs. The result was 0.2 pg-TEQ / Nm 3 of exhaust gas in terms of toxic equivalent, 0.009 ng-TEQ / in dry distillation liquid. g, Ash was 0.008 ng-TEQ / g, and the environmental standard value of the exhaust gas country was 5.0 ng-TEQ / Nm 3 , and the treated ash environmental standard value was 3.0 ng-TEQ / m 3 . .

Claims (5)

酸素を制御して熱分解反応器内に導入し、発熱量と水分量を最適に調整して熱分解反応器内に充填した有機系廃棄物の一部を部分酸化して、その熱を熱分解反応容器内に蓄熱し、他の大部分の有機系廃棄物を熱分解・炭化、ガス化、灰化して、ダイオキシン等の有害化合物を副生することなく、外部からエネルギーを供給せずに有機系廃棄物を処理する方法。Oxygen is controlled and introduced into the pyrolysis reactor, and the amount of heat generated and moisture are adjusted optimally to partially oxidize part of the organic waste filled in the pyrolysis reactor to heat the heat. Stores heat in the decomposition reaction vessel, pyrolyzes, carbonizes, gasifies, and incinerates most other organic waste without generating by-products such as dioxins and without supplying energy from the outside A method of treating organic waste. 熱分解反応器の底部に複数の開口部を設け、酸素を熱分解反応器内に導入するための導入管を取り付け先端に酸素量を制御するためのバルブを取り付ける。熱分解反応器内部の導入管の長さは、一部は中心部、一部は中間部、一部は端部に酸素が拡散するように長さを調製することを特徴とする請求項1記載の方法。A plurality of openings are provided at the bottom of the pyrolysis reactor, an introduction pipe for introducing oxygen into the pyrolysis reactor is attached, and a valve for controlling the amount of oxygen is attached to the tip. The length of the introduction pipe inside the pyrolysis reactor is adjusted so that oxygen diffuses partially in the center, partially in the middle, and partially in the end. The method described. 導入管が埋まる程度に熱分解反応によって生成したアッシュを敷き詰め酸素の拡散速度を制御すると共に、アッシュの触媒作用によって有機系廃棄物のガス化を促進することを特徴とする請求項1記載の方法。2. The method according to claim 1, wherein the ash produced by the pyrolysis reaction is spread to such an extent that the introduction pipe is filled, the oxygen diffusion rate is controlled, and the gasification of organic waste is promoted by the catalytic action of ash. . 熱分解反応器の内部に多数の穴の開いた内部壁を設け過剰な水分や有機性蒸気を除くことを特徴とする請求項1記載の方法。2. The method according to claim 1, wherein an excess of water and organic vapor are removed by providing an inner wall with a large number of holes inside the pyrolysis reactor. バルブの先端に2000ガウス以上の磁石を取り付けることを特徴とする請求項1記載の方法。2. A method according to claim 1, wherein a magnet of 2000 gauss or more is attached to the tip of the valve.
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