JP2010155231A6 - Method and apparatus for low-temperature decomposition treatment of processed material - Google Patents

Method and apparatus for low-temperature decomposition treatment of processed material Download PDF

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JP2010155231A6
JP2010155231A6 JP2009176395A JP2009176395A JP2010155231A6 JP 2010155231 A6 JP2010155231 A6 JP 2010155231A6 JP 2009176395 A JP2009176395 A JP 2009176395A JP 2009176395 A JP2009176395 A JP 2009176395A JP 2010155231 A6 JP2010155231 A6 JP 2010155231A6
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正一 山本
哲信 石濱
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Abstract

【課題】この発明は、処理物を低温分解処理させて灰化することにより、排気を無害化し、灰の排出を激減させることを目的としたものである。
【解決手段】この発明は、処理装置の上部から処理物を投入し、該処理物の下部を加温して、0.25テスラ〜1.0テスラの磁場を通過した磁化空気を処理物内に導き、前記処理物をその下部から順次分解処理することにより、炭化し、灰化すると共に、前記処理装置の一側上部の排気管からの自然排気に伴って、前記処理装置の下部内側に磁化空気を自然流入させ、前記処理物は磁化空気の流入付近からの処理の進行に伴い、前記処理物の上部の未分解部分の自重が加えられて順次下降してその空洞化が防止され、前記処理物の減少に伴い、新しい処理物を逐次投入することにより、処理物を連続処理することを特徴とした処理物の低温分解処理方法により、目的を達成した。
【選択図】図1
An object of the present invention is to detoxify exhaust gas by ashing by subjecting a treated product to low-temperature decomposition treatment to drastically reduce ash emission.
According to the present invention, a processing object is introduced from the upper part of a processing apparatus, the lower part of the processing object is heated, and magnetized air that has passed a magnetic field of 0.25 Tesla to 1.0 Tesla is contained in the processing object. In order to carbonize and incinerate by sequentially decomposing the processed material from the lower part thereof, along with the natural exhaust from the exhaust pipe on the one side upper part of the processing apparatus, The magnetized air is allowed to naturally flow in, and with the progress of the process from the vicinity of the inflow of magnetized air, the weight of the undecomposed portion on the upper part of the treated object is added and the cavities are prevented from being hollowed out. The object was achieved by a low-temperature decomposition treatment method for a treated product characterized in that the treated product is continuously treated by sequentially adding new treated products as the treated product decreases.
[Selection] Figure 1

Description

この発明は、有機物を含む処理物(産業廃棄物、家庭廃棄物、その他の一切の廃棄物)を、低温(250℃〜400℃)、低酸素で、強磁場を通過した空気(以下「磁化空気」という、0.25テスラ(2500ガウス)〜0.5テスラ(5000ガウス)で磁場)を用いて分解処理し、金属、ガラス、石類、コンクリート(以下、金属等という)以外を悉く灰化し、前記金属等以外の残渣を極めて少なくする(例えば90000分の1)ことを可能とした処理物の低温分解処理方法及び装置に関する。   In the present invention, treated materials containing organic matter (industrial waste, household waste, all other waste) are passed through a strong magnetic field at a low temperature (250 ° C. to 400 ° C.), low oxygen (hereinafter “magnetization”). Ashes that are decomposed using 0.25 Tesla (2500 gauss) to 0.5 Tesla (5000 gauss), called “air”, and splatters other than metal, glass, stones, and concrete (hereinafter referred to as metal) The present invention relates to a method and an apparatus for low-temperature decomposition treatment of a processed product that can reduce the residue other than the metal or the like extremely (eg, 1/90000).

従来廃棄物を強磁場のもとに分解させて、ダイオキシンを発生することなく、廃棄物を低温分解処理する装置の提案があり、夫々の特徴のもとに実用化を図っている。前記空気の磁化には、0.4テスラ(4000ガウス)〜0.45テスラ(4500ガウス)の永久磁石を用いること、加熱温度として350℃〜400℃を用いることも知られている。   Conventionally, there has been proposed a device for decomposing waste under a strong magnetic field to decompose the waste at a low temperature without generating dioxin, which has been put into practical use based on each feature. For the magnetization of the air, it is also known to use a permanent magnet of 0.4 Tesla (4000 Gauss) to 0.45 Tesla (4500 Gauss) and a heating temperature of 350 ° C. to 400 ° C.

実用新案登録第3122682号公報Utility Model Registration No. 312682 特開2006−289296号公報JP 2006-289296 A 特開2006−150295号公報JP 2006-150295 A 特開2004−33966号公報JP 2004-33966 A

従来灰の低温加熱の熱(例えば350℃)と、磁化空気(例えば磁力0.45テスラ(4500ガウス))とによって、廃棄物を乾燥し、炭化し、ついで灰化する技術が開示されているが(特許文献1)、処理時間が長くかかる(例えば処理時間10時間以上)のみならず、往々処理不良になる問題点があった。また廃棄物の材質によっては、排煙中に臭気の強いものがあり、これについて撒水等による脱臭を行っているが未だ改良すべき点があった。   Conventionally, a technique for drying, carbonizing, and then ashing waste by heat of low-temperature heating of ash (for example, 350 ° C.) and magnetized air (for example, magnetic force of 0.45 Tesla (4500 gauss)) is disclosed. (Patent Document 1), however, there is a problem that not only processing time is long (for example, processing time of 10 hours or more), but processing defects often occur. Also, depending on the material of the waste, there is a strong odor in the flue gas, and this has been deodorized by flooding etc., but there was still a point to be improved.

特許文献2には、密閉容器内に投入された廃棄物に、磁場内を通過させて活性化した微量空気を照射することにより、前記廃棄物を燃焼させることなく、分解して減容処理する廃棄物処理炉が開示されている。   In Patent Document 2, the waste introduced into the sealed container is irradiated with a minute amount of air that has been activated by passing through a magnetic field, whereby the waste is decomposed and reduced in volume without burning. A waste treatment furnace is disclosed.

また強磁性体で形成された反応容器内に有機物を収容し、該反応容器の内部と連通する外部管路を挟んでN極とS極とを互いに対向させて配置された1対の磁石により、有機物に磁場振動を起こさせてこれを分解する技術の提案がある(特許文献3)。前記特許文献3によれば、有機物の分解過程については一応説明されており、生ゴミ100kg、古紙類100kg、石膏ボード100kg及び木材屑150kgを投入処理し、周壁温度50℃〜60℃で24時間で灰になったと記載されている。前記における中心部の温度は何度か、化学変化のみなのか、何れも不明であるが、タイヤとか、プラスチックとかの固形物単独でも処理できるのか、他の可燃物との混合使用でなければならないか全く不明であり、安定して使用できる新規技術が見当たらない。   Further, an organic substance is accommodated in a reaction vessel formed of a ferromagnetic material, and a pair of magnets arranged so that the N pole and the S pole are opposed to each other with an external conduit communicating with the inside of the reaction vessel interposed therebetween. There is a proposal of a technique for causing a magnetic field vibration in an organic substance and decomposing it (Patent Document 3). According to Patent Document 3, the decomposition process of organic matter is described for the time being, and 100 kg of raw garbage, 100 kg of waste paper, 100 kg of gypsum board and 150 kg of wood waste are charged and processed at a peripheral wall temperature of 50 ° C. to 60 ° C. for 24 hours. It is stated that it became ash. It is unclear whether the temperature of the central part is several times or only a chemical change in the above, but it can be treated with a solid material such as a tire or plastic alone, or it must be mixed with other combustible materials This is completely unknown, and there is no new technology that can be used stably.

特許文献4は、廃棄物を、マイナスイオンを含む気体雰囲気中で熱分解させる処理方式であって、焼却炉と、この焼却炉に連通する吸気通路と、前記焼却炉の上部に開口して、排気通路と前記吸気通路に設置された磁石を備えた廃棄物処理装置により、前記方法を実施している。   Patent Document 4 is a treatment method in which waste is thermally decomposed in a gas atmosphere containing negative ions, and is opened to an incinerator, an intake passage communicating with the incinerator, and an upper portion of the incinerator. The method is carried out by a waste treatment apparatus including a magnet installed in an exhaust passage and the intake passage.

この発明は、処理物(廃棄物)の処理中に、処理室の下部に収容された処理物を撹拌することにより、該部における熱分解処理が合理化され、均等化して、その処理時間を20%〜40%短縮し(例えば10時間かかったのを8時間〜6時間にする)、かつ安定処理が認められた。その理由は、撹拌によって処理に磁化空気が均一に接触すると共に、磁化空気の供給が合理化され、その結果全体の処理能力を向上させたものと考えられる。撹拌は2〜4時間に1〜2回であり、1回の撹拌時間は5〜10分で十分である(例えば回転軸は毎分5〜10回回転)。   In the present invention, during the treatment of the treatment product (waste), the treatment product accommodated in the lower part of the treatment chamber is agitated so that the thermal decomposition treatment in the part is rationalized and equalized, and the treatment time is reduced to 20 times. % To 40% (for example, 10 hours was changed to 8 to 6 hours), and a stable treatment was observed. The reason is considered to be that the magnetized air uniformly comes into contact with the treatment by agitation, and the supply of magnetized air is rationalized, and as a result, the overall processing capacity is improved. Stirring is 1 to 2 times in 2 to 4 hours, and 5 to 10 minutes is sufficient for one stirring time (for example, the rotating shaft rotates 5 to 10 times per minute).

前記のように、分解過程において、架橋が生じ易い処理物を処理する場合には撹拌が必要であるが、架橋が出来ない処理物の場合には撹拌の必要がない。例えば、分解物が予め小さく破砕(例えば5cm程度)されていて架橋しない場合には、撹拌装置が不必要になる。元来分解処理は、処理室の下部から順次進行するので、仮に架橋が出来てもその支持力は弱いと思われる。そこで次期処理物をまとめて投入すれば、処理物の自重により処理室の半処理物付近へ加圧力がかかるので、架橋ができない。従って特定の処理物を除き撹拌をしなくても良いことが判る。例えばまとめて投入する処理物は、1mでおよそ150kg〜700kgあるので、これを処理槽の上部へ収容すると、処理槽の未処理物の上部に前記150kg〜700kgの重量が掛かるので、通常架橋を生じるおそれがないことになる。 As described above, in the decomposition process, stirring is required when processing a product that is likely to be crosslinked, but stirring is not required when processing a product that cannot be crosslinked. For example, when the decomposition product is crushed small in advance (for example, about 5 cm) and does not crosslink, a stirring device is unnecessary. Originally, the decomposition process proceeds sequentially from the lower part of the processing chamber, so even if crosslinking is possible, it seems that the supporting force is weak. Therefore, if the next processed materials are put together, the pressure is applied to the vicinity of the semi-processed material in the processing chamber due to the weight of the processed material, so that crosslinking cannot be performed. Therefore, it can be seen that stirring is not required except for a specific processed product. For example, since the processed materials to be put together are approximately 150 kg to 700 kg at 1 m 3 , if this is accommodated in the upper portion of the processing tank, the weight of 150 kg to 700 kg is applied to the upper portion of the untreated material in the processing tank. There will be no risk of occurrence.

前記撹拌によって、処理物の下端部と、灰(例えば、セラミックス灰)の赤熱部とは、常時近接かつ正対関係にあって、セラミックス灰の輻射熱と磁化空気とにより、処理物を急速に乾燥し、炭化し、ついで灰化を促進させることができる。   By the agitation, the lower end of the processed product and the red hot part of ash (for example, ceramic ash) are always in close proximity and facing each other, and the processed product is rapidly dried by the radiant heat of the ceramic ash and magnetized air. And carbonized, and then promote ashing.

従来処理物の処理には10時間以上を要し、かつ不安定であったが、この発明によれば、処理時間は数時間(4〜7時間/1m)であって、連続運転により効率の向上が見受けられ、かつ安定した処理ができることが判明した。また処理物の材質によっては、排気の臭気が大きくなるおそれがあるが、この発明は排気を処理槽に導き、撒水及び磁化によって消臭・脱臭と異物を除去することに成功したのである。 Conventionally, the treatment of the processed product takes 10 hours or more and is unstable. However, according to the present invention, the treatment time is several hours (4 to 7 hours / 1 m 3 ), and the efficiency is improved by continuous operation. As a result, it was found that stable treatment was possible. Further, depending on the material of the treated material, the odor of the exhaust gas may increase. However, the present invention has succeeded in removing the odor and deodorizing and removing foreign matter by flooding and magnetization by introducing the exhaust gas into the treatment tank.

前記において臭気を発生するものは、例えば処理物がタイヤその他のように硫黄酸化物又は窒素酸化物などを多く含んだ処理物の処理の場合であるが、家庭廃棄物の処理では臭気が少ないのが普通である。   In the above, what generates odor is, for example, in the case of treatment of a treated product containing a large amount of sulfur oxides or nitrogen oxides such as tires, etc., but there is little odor in the treatment of household waste. Is normal.

また、処理室内へ投入した処理物の下端が往々架橋を形成して、効率のよい処理を困難にするのに鑑み、この発明は前記架橋を時々崩すことによって、処理物と、セラミックス灰との対峙関係を最良とすると共に、空気量を制御した磁化空気を均一に流入接触させることにより、セラミックス灰の熱輻射と、イオン化した酸素(強磁場通過によるイオン化)その他活性化した空気との複合処理により、前記従来の問題点を解決したのである。前記における酸素量は、燃焼に必要な酸素量より少なくするが、その割合は廃棄物の材質により異なる。従って最良値は実験的に定める。   Further, in view of the fact that the lower end of the processed material thrown into the processing chamber often forms a bridge, making it difficult to perform efficient treatment, the present invention sometimes breaks the cross-linking so that the processed material and the ceramic ash Combined treatment of thermal radiation of ceramic ash with ionized oxygen (ionization by passing through a strong magnetic field) and other activated air by optimizing the relationship and bringing in uniform contact with magnetized air with controlled air volume. Thus, the conventional problems are solved. The amount of oxygen in the above is less than the amount of oxygen necessary for combustion, but the proportion varies depending on the material of the waste. Therefore, the best value is determined experimentally.

前記における磁化空気は、通常排気に伴い自然流入するようになっているが、磁化空気の通路へファンを介装し、磁化空気の流入量をコントロールすることもできる。   The magnetized air in the above is normally naturally flowed along with the exhaust, but a fan can be interposed in the magnetized air passage to control the inflow of magnetized air.

更に前記処理状態の条件を最良にして定常的に処理することにより灰の増加を低減させることができる。前記のように、良好な状態で継続運転することにより、灰の増加が認められないという結果がある。   Furthermore, the increase in ash can be reduced by carrying out steady treatment with the best treatment condition. As described above, there is a result that no increase in ash is observed by continuously operating in a good state.

即ちこの発明は、処理装置の上部から処理物を投入し、該処理物の下部を加温して、0.3テスラ(3000ガウス)〜1.0テスラ(10000ガウス)の磁場を通過した磁化空気を処理物内に導き、前記処理物をその下部から順次分解処理することにより、炭化し、灰化すると共に、前記処理装置の一側上部の排気管からの自然排気に伴って、前記処理装置の下部内側に磁化空気を自然流入させ、前記処理物は磁化空気の流入付近からの処理の進行に伴い、前記処理物の上部の未分解部分の自重が加えられて順次下降してその空洞化が防止され、前記処理物の減少に伴い、新しい処理物を逐次投入することにより、処理物を連続処理することを特徴とした処理物の低温分解処理方法であり、処理装置の排気管からの自然排気に伴って、磁化空気を自然流入させると共に、該流入空気量を調節するものであり、磁化空気は、処理装置の下部側壁から、中央部にかけて装置内へ突出設置した給気管から自然流出させると共に前記磁化空気は処理装置の周縁部内側を下降させ、中央部は上昇させて上下対流させるものである。   That is, according to the present invention, the processed material is charged from the upper part of the processing apparatus, the lower part of the processed material is heated, and the magnetization passes through a magnetic field of 0.3 Tesla (3000 Gauss) to 1.0 Tesla (10000 Gauss). Air is introduced into the processed material, and the processed material is sequentially decomposed from the lower portion thereof to carbonize and ash, and with the natural exhaust from the exhaust pipe on one side upper portion of the processing device, the processing is performed. Magnetized air naturally flows into the lower inner side of the apparatus, and the processed object gradually descends due to the weight of the undecomposed portion at the upper part of the processed object as the process proceeds from the vicinity of the inflow of the magnetized air. Is a low-temperature decomposition treatment method for a treated product, characterized by continuously treating a treated product by sequentially adding a new treated product as the treated product decreases, from the exhaust pipe of the processing device. With the natural exhaust of While allowing natural air to flow in and adjusting the amount of air flowing in, the magnetized air naturally flows out from a supply pipe projecting into the apparatus from the lower side wall of the processing apparatus to the center, and the magnetized air is processed. The inside of the peripheral part of the device is lowered, and the central part is raised to cause convection up and down.

前記において、灰の温度は分解熱により維持される。分解熱は排気の熱処理物の乾燥熱などに使用されるので、発生と消費のバランスを保ち、400℃以上に上昇するおそれはない。また当初灰を加熱しなくても分解進行と共に灰は加熱されるが、最初の時間が長く掛かるので灰を加熱して出発するのが好ましい。   In the above, the temperature of ash is maintained by the heat of decomposition. Since the decomposition heat is used for drying heat of the heat-treated product of the exhaust, the balance between generation and consumption is maintained, and there is no possibility of increasing to 400 ° C. or higher. Even if the ash is not initially heated, the ash is heated with the progress of decomposition. However, since it takes a long time for the first time, it is preferable to start by heating the ash.

また他の発明は、排気管からの排気は、消煙、消臭処理槽内で撒水処理されて消煙、消臭処理されるものであり、処理物の処理が進行し、処理装置の上部に空隙が生じた際に新しい処理物を投入する間欠投入方式とするものであり、処理物を、産業廃棄物、家庭廃棄物、その他有機物を含む廃棄物とするものである。また空洞化防止は、投入処理物の下部付近を定期的に撹拌したり、新しい処理物の投入による重さで解消し、実に処理装置の上部内側を減圧して、開蓋時に内部気体が外に排出されるのを防止するものである。   In another aspect of the invention, the exhaust from the exhaust pipe is smoked and deodorized in a deodorizing and deodorizing treatment tank to be deodorized and deodorized. In this case, an intermittent charging method is employed in which a new treated material is introduced when a void is generated in the material, and the treated material is industrial waste, household waste, or other waste containing organic matter. To prevent cavitation, the vicinity of the lower part of the processed material is periodically stirred, or the weight of the new processed material is eliminated, and the inside of the upper part of the processing device is actually decompressed so that the internal gas is removed when the lid is opened. It prevents it from being discharged.

次にこの発明は、処理装置の上部から処理物を投入し、該処理物の中央下部を加温し上昇気流を生起し、処理装置の内側壁部に下降気流を生起して磁化空気を上下対流させて、0.25テスラ(2500ガウス)〜1.0テスラ(10000ガウス)の磁場を通過した磁化空気を処理物内に導き、前記処理物をその下部から順次分解処理することにより、前記処理物を炭化し、次いで灰化させると共に、前記処理装置の一側上部の排気管からの排気に伴って、前記処理装置の下部内側に磁化空気を自然流入させ、前記処理物の処理の進行に伴い、前記処理物はその上部の未分解部分の自重が加えられて順次下降してその空洞化が防止され、前記処理物の減少に伴い、新しい処理物を逐次投入することにより、処理物を自動連続処理することを特徴とした処理物の低温分解処理方法であり、処理装置の排気管からの排気に伴って、磁化空気を自動流入させると共に、該流入空気量を調節できるようにすることを特徴とした請求項1記載の処理物の低温分解処理方法である。   Next, according to the present invention, a processing object is introduced from the upper part of the processing apparatus, the central lower part of the processing object is heated to generate an updraft, and a downward airflow is generated on the inner wall portion of the processing apparatus to move the magnetized air up and down. By conducting convection and guiding magnetized air that has passed through a magnetic field of 0.25 Tesla (2500 Gauss) to 1.0 Tesla (10000 Gauss) into the treatment object, the treatment object is sequentially decomposed from the lower part thereof, The treated material is carbonized and then incinerated, and magnetized air is naturally introduced into the lower inside of the processing device along with exhaust from the exhaust pipe on one side of the processing device, and the processing of the processed material proceeds. Accordingly, the processed material is gradually lowered by adding the weight of the undecomposed portion at the upper part thereof to prevent its hollowing, and as the processed material decreases, a new processed material is sequentially added to the processed material. Automatic continuous processing A method for low-temperature decomposition treatment of a treated product, characterized in that magnetized air is automatically introduced and the amount of inflow air can be adjusted with exhaust from an exhaust pipe of a processing apparatus. 1 is a method for low-temperature decomposition treatment of a treated product.

また、有底筒状の処理装置の下部に、加熱室を設け、該加熱室の上部に処理物を収容し、磁化空気を給気して、処理する2重壁の処理室を連設し、前記加熱室と処理室の下部に、磁化空気の給気管を側壁から中央部に向けて上下多段に複数水平方向に設置し、前記給気管は、流入空気を磁化する磁化筒に連設し、前記処理室の上部に処理物の投入口を設けると共に、排気管を連設し、前記投入口へ開閉蓋を被冠し、前記排気管に処理槽を連結し、前記処理室内の上下対流の為に2重壁の上下部へ通気口を設け、前記処理室の下部へ、処理装置外から操作できる処理物の撹拌装置を架設し、前記加熱室の側壁下部に、残渣取り出し口を設け、該残渣取り出し口に開閉蓋を被冠したことを特徴とする処理物の低温分解処理装置であり、処理槽は、撒水により消煙、消臭するものであり、磁化筒内には、一端に磁化空気の給気管を連結し、他端を外界に開口し、中央部に高磁化用の永久磁石を介装した通気管を内装したものであり、撹拌装置は、処理室の下部へ複数の撹拌杆を突設した1本又は複数本の回転軸を水平方向に架設し、該回転軸の一端を処理装置の壁外へ突出して突出部とし、該突出部にハンドルを取り付けたものである。   In addition, a heating chamber is provided in the lower part of the bottomed cylindrical processing apparatus, a processing object is accommodated in the upper part of the heating chamber, magnetized air is supplied, and a double-walled processing chamber for processing is continuously provided. In the lower part of the heating chamber and the processing chamber, a plurality of air supply pipes of magnetized air are installed in a plurality of horizontal directions vertically from the side wall toward the center, and the air supply pipes are connected to a magnetizing cylinder for magnetizing the inflowing air. A processing material inlet is provided at the upper part of the processing chamber, an exhaust pipe is continuously provided, an opening / closing lid is covered with the input port, a processing tank is connected to the exhaust pipe, and a vertical convection in the processing chamber is provided. For this purpose, vents are provided in the upper and lower parts of the double wall, a stirring device for the processed material that can be operated from outside the processing apparatus is installed in the lower part of the processing chamber, and a residue outlet is provided in the lower part of the side wall of the heating chamber. , A low-temperature decomposition treatment apparatus for the treated product, characterized in that the residue outlet is covered with an open / close lid, Smoke and deodorize with water. Inside the magnetized cylinder, one end of the magnetized air supply pipe is connected, the other end is opened to the outside, and a permanent magnet for high magnetization is inserted in the center. The agitator is equipped with a ventilation pipe, and the agitation device is constructed by horizontally laying one or a plurality of rotating shafts with a plurality of stirring rods projecting from the lower part of the processing chamber, and one end of the rotating shaft is connected to the processing device. It protrudes out of the wall to form a protrusion, and a handle is attached to the protrusion.

また、撹拌装置を設けた場合には回転軸は3本とし、上部に2本の回転軸を並列架設し、前記2本の回転軸の中間下部へ他の1本の回転軸を、前記2本の回転軸と並列架設したものであり、開閉蓋又は処理室の上部に排気ホースの一端を連結し、該排気ホースの他端を排気ポンプに連結し、該排気ポンプの吐出側を処理槽に連結したものであり、消煙、消臭する処理槽は、筒状の槽内を複数の仕切板により縦に仕切り、上下に屈曲した流路を形成すると共に、前記筒状の槽の上部に撒水管を架設し、前記流路の上部に撒水できるように配管したものである。   Further, when the stirring device is provided, the number of rotation shafts is three, two rotation shafts are installed in parallel on the upper part, and the other one rotation shaft is connected to the lower part of the middle of the two rotation shafts. One end of the exhaust hose is connected to the upper part of the opening / closing lid or the processing chamber, the other end of the exhaust hose is connected to the exhaust pump, and the discharge side of the exhaust pump is connected to the processing tank. The treatment tank for smoking and deodorizing is connected vertically to the inside of the cylindrical tank by a plurality of partition plates to form a vertically bent channel, and the upper part of the cylindrical tank. A water pipe is installed in the pipe and piped so that it can be watered in the upper part of the flow path.

前記における処理物には、産業廃棄物、家庭廃棄物、その他有機物を含んだ処理物であって、石、硝子、コンクリート、陶器などの他の不用物は総て含むものとする。   The treated materials mentioned above are industrial waste, household waste, and other treated materials containing organic matter, and all other unnecessary materials such as stone, glass, concrete, and ceramics are included.

この発明におけるセラミックス灰とは、処理物を処理させて残った残灰(無機質)、泥土又は石の粉末であるが、その他に通常の処理物を処理させて得た灰も含まれる。処理装置販売時に付属させることもできる。処理装置の最初の使用に際しては、処理室内へ5kg〜10kgのセラミックス灰を収容し、該セラミックス灰をガスバーナーその他で350℃〜400℃に加熱してから、処理物を投入することにより(又は処理物を投入後セラミックス灰を加熱してもよい)、爾後継続して処理物を分解処理することができる。処理物の投入を中止した場合には、前記セラミックス灰は埋め火となり、100時間〜120時間その機能が保存される。この間に処理物を投入すれば、早急に再び処理を開始することが認められた。従って、生産工場などにおいて夕方仕事終了時に、当日の処理物を全部処理装置に投入し、翌朝セラミックス灰のみ残っている場合であっても、その日の夕方当日の処理物を投入すれば、翌朝までにセラミックス灰になるという処理と、中断との繰り返しでも使用することができる。前記において最初の使用の際セラミックス灰を加熱すると説明したが、前記ガスバーナーに代えて紙などの可燃物若干量(例えば1kg)を燃やして上昇流を作り、磁化空気を入れるようにしてもよい。   The ceramic ash in the present invention is residual ash (inorganic), mud or stone powder left after processing the processed product, but also includes ash obtained by processing a normal processed product. It can be attached at the time of processing equipment sale. When the processing apparatus is used for the first time, 5 kg to 10 kg of ceramic ash is accommodated in the processing chamber, the ceramic ash is heated to 350 ° C. to 400 ° C. with a gas burner or the like, and then the processed material is charged (or The ceramic ash may be heated after adding the treated product), and the treated product can be decomposed continuously after the soaking. When the processing is stopped, the ceramic ash is buried and its function is preserved for 100 to 120 hours. It was recognized that if the processed material was introduced during this period, the processing was started again immediately. Therefore, at the end of work in the evening in a production plant, etc., even if all the processed material for the day is put into the processing equipment and only the ceramic ash remains the next morning, if the processed material for the evening of that day is input, the next morning It can also be used by repeating the process of becoming ceramic ash and interruption. In the above description, the ceramic ash is heated in the first use. However, instead of the gas burner, a slight amount of combustible material such as paper (for example, 1 kg) is burned to create an upward flow, and magnetized air may be introduced. .

前記において、セラミックス灰は、分解処理を継続しても一定量(当初供給した量、例えば10kg〜30kg)を保ち、増加しないので、処理継続に際し、処理物の追加投入以外は人力を要しない。また最高温度400℃であるから、処理装置の外壁は60℃以下であり、素手で触れても火傷を生じるおそれは殆どない。また、処理室の外壁が2重にしてあるので、他物に引火、損傷を与えるおそれは皆無である。更に処理室内へ熱交換器を設置すれば、処理室内の気体との熱交換により温水を得ることができる。   In the above, the ceramic ash maintains a constant amount (amount initially supplied, for example, 10 kg to 30 kg) and does not increase even if the decomposition process is continued. Further, since the maximum temperature is 400 ° C., the outer wall of the processing apparatus is 60 ° C. or less, and there is almost no possibility of causing burns even if it is touched with bare hands. In addition, since the outer wall of the processing chamber is doubled, there is no possibility of igniting or damaging other objects. Furthermore, if a heat exchanger is installed in the processing chamber, hot water can be obtained by heat exchange with the gas in the processing chamber.

前記において処理室の容量1mの実験処理装置に、牧場廃棄物(籾殻、藁、牛糞など)を8時間毎に1m宛投入し、200時間以上継続処理したが、セラミックス灰は当初(20kg)より若干増加(20%〜30%増)の状態で安定し、爾後増加は認められなかった。 In the above experiment, ranch waste (rice husk, straw, cow dung, etc.) was put into 1 m 3 every 8 hours in an experimental processing apparatus with a capacity of 1 m 3 in the processing chamber and continuously treated for 200 hours or more. ) Was stabilized at a slight increase (20% to 30% increase), and no increase was observed after the eyelid.

前記発明における処理物の継続投入は、前投入の処理物の処理が進行し、その容積が半減した時に行う。例えば、処理室の容量2.0mに対し、当初処理物2.0m入れ、3〜4時間経過後1mの空間ができたならば、1mの処理物を補充し、爾後3〜4時間毎に1mの処理物を追加投入すれば、この処理装置を最も効率よく使用することができる。 In the present invention, the continuous supply of the processed material is performed when the processing of the previously input processed material has progressed and the volume has been reduced by half. For example, if a space of 1 m 3 is formed after 3 to 4 hours have passed after the initial treatment product of 2.0 m 3 is added to the processing chamber capacity of 2.0 m 3 , 1 m 3 of treatment material is replenished, If an additional 1 m 3 of processed material is added every 4 hours, this processing apparatus can be used most efficiently.

前記において、撹拌装置は、1時間〜2時間毎に5分間位使用する。前記撹拌装置はタイマー付電気回路を用いて撹拌軸の回転を自動化すれば、定期的撹拌を全自動化することができる。送配電設備のない地域においては、例えば太陽光による発電と、電池との組み合わせによって、前記自動化に必要な電源を得ることができる。   In the above, the stirring device is used for about 5 minutes every 1 to 2 hours. If the stirring device automates the rotation of the stirring shaft using an electric circuit with a timer, the periodic stirring can be fully automated. In an area where there is no power transmission / distribution facility, a power source necessary for the automation can be obtained by, for example, a combination of power generation using sunlight and a battery.

前記における処理物の投入は、人力を介在するけれども、前記分解処理装置の投入口へ、自動投入装置を連設すれば、処理物投入を全自動化することができる。例えば、4時間毎に処理物1mを投入する装置であれば、1日の投入量は6mであるから、前記処理装置の上部へ処理物6mを収容できるホッパーの下部を連設し、該ホッパーの下部へ、定量投入装置を付属させ、この投入装置を自動化すれば、処理物の全自動投入ができる。そこで作業者は、1日1回6mの処理物を、前記ホッパーに供給すれば、後は全自動で1日分の処理物が処理される。 Although the introduction of the processed material in the above-described manner involves human power, the automatic operation of the introduction of the processed material can be achieved by connecting an automatic input device to the input port of the decomposition processing device. For example, in the case of an apparatus that inputs 1 m 3 of processed material every 4 hours, the input amount per day is 6 m 3 , so that a lower portion of a hopper that can store the processed material 6 m 3 is connected to the upper part of the processing apparatus. If a fixed amount charging device is attached to the lower part of the hopper and this charging device is automated, the processing object can be fully automatically charged. Therefore, if the worker supplies a processed product of 6 m 3 once a day to the hopper, the processed product for one day is processed fully automatically thereafter.

前記処理物の分解熱の温度は、最高温度が400℃(通常250℃〜350℃)であるから、何等かの故障により、処理能力が低下したり、中断したとしても、外部に熱的危害が及ぶおそれはない。但し処理装置の処理物投入口を開け放しておくと、酸素の供給によって、処理物が通常温度で燃焼するおそれがあるが、処理装置の構造上、自動的に蓋が開くおそれがないので、前記のようなおそれがなく安全である。唯一作業者が蓋を閉め忘れる不慮の場合があるとしても、開蓋により突如白煙を上げて燃焼を開始するので、作業者が気付く筈である。万一気付かぬ場合があっても、前記設例によれば、2mの処理物が燃焼すれば燃焼は総て終了するので、他に危害が及ぶおそれはない。また処理装置は閉蓋していれば、排気量だけ吸気される(厳密には、水蒸気分だけ吸気量が少ない)ので、気圧上昇による爆発のおそれはない。仮に排気口が閉ざされると、吸気がなくなり、前記処理物の処理は自動的に中断されることになる。 Since the maximum temperature of decomposition heat of the processed product is 400 ° C. (usually 250 ° C. to 350 ° C.), even if the processing capacity decreases or is interrupted due to any failure, there is a thermal hazard to the outside. There is no fear of reaching. However, if the processing material inlet of the processing apparatus is left open, the processing object may burn at normal temperature due to the supply of oxygen, but because of the structure of the processing apparatus, there is no risk that the lid will automatically open. It is safe without fear. Even if there is a case where it is unintentional that the operator forgets to close the lid, the operator should notice that the white smoke is suddenly raised by the lid and combustion starts. Even if it may not be noticed, according to the above example, if the processed material of 2 m 3 is combusted, the combustion is completed, so there is no risk of other harm. Further, if the processing device is closed, intake is performed by the amount of exhaust (strictly speaking, the amount of intake is small by the amount of water vapor), so there is no risk of explosion due to an increase in atmospheric pressure. If the exhaust port is closed, the intake air is lost and the processing of the processed material is automatically interrupted.

前記発明における磁化空気の流入は、排気の排出量により定まる。従ってセラミックス灰の加熱により、処理物の水分が蒸発すれば、蒸発量が増加するに伴って一時的に磁化空気の吸入量が低下することになる。また磁化空気の吸入量と、処理物処理の効率化について、更なる比較試験を要するが、水分20%〜80%の現廃棄物の処理においては、自然排気に伴う自動流入(磁化空気)が良いと認められているが、吸入側に手動バルブを介装してあり、処理物により磁化空気の吸入量を制御することができる。更にセラミックス灰による効率のよい加熱と、これに見合う磁化空気量の流入設定には、各種条件(廃棄物の水分量、材質、装置の形状、寸法及び磁気強度)が影響するので、最良の条件を得る為には幾多の実験を経なければならない。   The inflow of magnetized air in the invention is determined by the exhaust amount. Therefore, if the moisture of the processed product evaporates due to the heating of the ceramic ash, the amount of suction of magnetized air temporarily decreases as the amount of evaporation increases. Moreover, further comparison tests are required for the amount of magnetized air inhaled and the efficiency of the treatment of the treated material. However, in the treatment of current waste with 20% to 80% moisture, automatic inflow (magnetized air) due to natural exhaust is not possible. Although it is recognized as good, a manual valve is provided on the suction side, and the amount of magnetized air sucked can be controlled by the processed material. In addition, various conditions (water content of waste, material, shape of equipment, dimensions, and magnetic strength) affect the efficient heating with ceramic ash and the setting of inflow of magnetized air corresponding to this, so the best conditions In order to obtain, you have to go through many experiments.

前記空気の磁化については、理論的に解明されていないけれども、前記公知例(例えば特開2006−150295)においても磁化空気を使用して有機物を分解したとされている。またこの発明を完成するに当たっても数年間の実験、研究を繰り返している。例えば、磁気の強さにしても、0.3テスラ(3000ガウス)より1.0テスラ(10000ガウス)の方が分解効率がよく、かつ均等分解できることが判明している。この場合に吸入空気量が関係することは確認しているが、処理物の材質と湿度により最良の磁気強さは今後の研究に待たなければならない。前記事情により磁化空気としているが、実情は強磁場によって空気の活性化が行われ、有機物の分解を促進するとも考えられる。また筒状装置が強磁性材質だから分解を促進するとの説もある。尚、磁気の強さは0.4テスラ(4000ガウス)を越えて1.0テスラ(10000ガウス)まで実験しているが、0.5テスラ(5000ガウス)以上の方が処理状態が安定している。   Although the magnetization of the air is not theoretically clarified, it is said that the organic matter is decomposed using the magnetized air in the known example (for example, JP-A-2006-150295). In addition, several years of experimentation and research have been repeated to complete this invention. For example, it has been proved that 1.0 Tesla (10000 Gauss) has higher decomposition efficiency and can be equally decomposed than 0.3 Tesla (3000 Gauss) even in terms of magnetic strength. Although it has been confirmed that the amount of intake air is related to this case, the best magnetic strength must be awaited for future research due to the material and humidity of the treated material. Although magnetized air is used for the above circumstances, it is considered that air is activated by a strong magnetic field and promotes decomposition of organic matter. There is also a theory that the cylindrical device is a ferromagnetic material, so that the decomposition is accelerated. In addition, although the magnetic strength exceeded 0.4 Tesla (4000 Gauss) and experimented to 1.0 Tesla (10000 Gauss), the treatment state is more stable at 0.5 Tesla (5000 Gauss) or more. ing.

この発明の装置としては、加熱室から、処理室の下部にかけて、上下多段に磁化空気の給気パイプを突設したので、処理すべき処理物の内部まで磁化空気を供給することが可能となり、処理条件が均一化されて、処理状態を良好にし、処理時間を短縮し、処理物の材質に拘わらず、最良の処理状態で連続処理させることができた。   As the apparatus of the present invention, since the air supply pipe of the magnetized air protrudes from the heating chamber to the lower part of the processing chamber in multiple stages, it becomes possible to supply the magnetized air to the inside of the processing object to be processed, The processing conditions were made uniform, the processing state was improved, the processing time was shortened, and continuous processing was possible in the best processing state regardless of the material of the processed material.

また少なくとも処理室の側壁を2重壁とし、上下に通気口を設けて、磁化空気の循環流動を図っているので、磁化空気は上下対流を生じる。即ち、下部にある加熱室の加熱灰(250℃〜400℃)の温度により上昇流を生じる。従って磁化空気は内部で上昇流となり、周壁部(2重壁)で下降流となり、一部は排気となり、排気量だけ新しい磁化空気が吸入される。   In addition, since at least the side wall of the processing chamber is a double wall and vent holes are provided above and below to circulate and flow the magnetized air, the magnetized air generates up-down convection. That is, an upward flow is generated by the temperature of the heated ash (250 ° C. to 400 ° C.) in the heating chamber at the bottom. Accordingly, the magnetized air becomes an upward flow inside, becomes a downward flow at the peripheral wall portion (double wall), partially becomes exhaust, and new magnetized air is sucked in by the exhaust amount.

前記のように分解熱は分解に使用されると共に、残余は灰中に集まり、磁化空気を加温上昇させると共に、処理物の下側に赤外線を放射して、その乾燥と、分解を促進させる。前記加熱灰の存在により、分解効率と、分解の安定性及び確実性を確認することができた。   As described above, the heat of decomposition is used for decomposition, and the remainder gathers in the ash, warms and raises the magnetized air, and radiates infrared rays to the lower side of the processed material to accelerate its drying and decomposition. . Due to the presence of the heated ash, it was possible to confirm the decomposition efficiency and the stability and certainty of the decomposition.

前記発明によれば、開閉蓋又は処理室の上部へ排気ホースの一端を連結し、前記排気ホースの他端を排気ポンプに連結(直接又は間接)したので、ポンプを稼働すれば、前記処理室の上部が減圧される。従って処理室内の気体(臭気、排気)が外部へ出るのを未然に防止することができる。   According to the invention, one end of the exhaust hose is connected to the opening / closing lid or the upper part of the processing chamber, and the other end of the exhaust hose is connected (directly or indirectly) to the exhaust pump. The top of is depressurized. Therefore, it is possible to prevent the gas (odor and exhaust) in the processing chamber from coming out.

また、処理室の下部へ撹拌装置を設け、手動又は自動によって処理物を撹拌すれば、処理の進行に伴う処理物の架橋がなくなり、均等な処理が行われる。従って処理時間を大幅に短縮させると共に、処理物の材質に拘わらず、速やかな均質処理ができる。前記において処理物の大きさによっては架橋を作らないので、撹拌は不必要となる。   Moreover, if a stirring apparatus is provided in the lower part of a process chamber and a process thing is stirred manually or automatically, the bridge | crosslinking of the process object accompanying a progress of a process will lose | eliminate, and an equal process will be performed. Accordingly, the processing time can be greatly shortened, and a rapid homogeneous process can be performed regardless of the material of the processed material. In the above, since no cross-linking is made depending on the size of the treated product, stirring is unnecessary.

この発明によれば、250℃〜400℃に加熱したセラミックス灰と、0.3テスラ(3000ガウス)〜1.0テスラ(10000ガウス)の磁場を通過した磁化空気とによって処理物を加熱乾燥し、炭化し、ついで灰化処理したので、燃焼その他外部熱量に依存することなく、処理物を自動かつ継続して分解し、無害化処理できる効果がある。   According to the present invention, a processed product is heated and dried by ceramic ash heated to 250 ° C. to 400 ° C. and magnetized air that has passed a magnetic field of 0.3 Tesla (3000 Gauss) to 1.0 Tesla (10000 Gauss). Since it is carbonized and then ashed, it has the effect of automatically and continuously decomposing and detoxifying it without depending on combustion or other external heat.

特に加熱室と処理室の中央部に向けて給気パイプを横設すると共に、給気するので、処理物内へ磁化空気を均等に供給できる効果がある。   In particular, since the air supply pipe is provided laterally toward the central portion of the heating chamber and the processing chamber and the air is supplied, there is an effect that the magnetized air can be evenly supplied into the processing object.

また加熱室の上部、処理室の下部へ撹拌装置を設けた場合には、処理物の分解処理時に、その架橋を防止し、均等処理を容易にして、処理時間を短縮できる効果がある。   Further, when a stirring device is provided in the upper part of the heating chamber and the lower part of the processing chamber, it is possible to prevent the cross-linking during the decomposition treatment of the processed material, to facilitate the uniform processing, and to shorten the processing time.

更に残灰を処理して残留灰の増加を防止できるので、処理物の連続処理に際し、残灰の取り出し量は皆無か、又は少量の取り出しによって残灰が燃焼室に充満するのを未然に防止し得る効果がある。更に磁化空気量を調節して、分解処理の合理化を図ることができる効果がある。   Furthermore, since residual ash can be treated to prevent an increase in residual ash, there is no amount of residual ash taken out during continuous processing of processed products, or a small amount of residual ash is prevented from filling the combustion chamber in advance. There is a possible effect. Furthermore, there is an effect that the decomposition process can be rationalized by adjusting the amount of magnetized air.

(a)この発明の実施例のブロック図、(b)同じく排気処理における浄水の実施例のブロック図。(A) The block diagram of the Example of this invention, (b) The block diagram of the Example of the purified water in exhaust processing similarly. この発明の方法を実施する装置の実施例の正面図。The front view of the Example of the apparatus which implements the method of this invention. 同じく一部を省略した背面図。The rear view which abbreviate | omitted a part similarly. 同じく一部を省略した側面図。The side view which abbreviate | omitted a part similarly. 同じく一部を省略した平面図。The top view which abbreviate | omitted a part similarly. 同じく一部を省略した断面図。Sectional drawing which abbreviate | omitted one part. 同じく一部を省略した縦断側面図(断面線省略)。Similarly, a longitudinal side view with a part omitted (cross-sectional line omitted). 同じく一部を省略した横断平面図。The cross-sectional top view which abbreviate | omitted a part similarly. 同じく気化空気の配管を示す一部を省略した縦断面図。The longitudinal cross-sectional view which abbreviate | omitted a part which shows piping of vaporized air similarly. 同じく消煙・消臭の処理槽の一部を省略した縦断面図。The longitudinal cross-sectional view which abbreviate | omitted a part of the processing tank of smoke removal / deodorization similarly. 同じく他の装置の実施例の正面図。The front view of the Example of another apparatus similarly. 同じく背面図。Similarly rear view. 同じく右側面図。Similarly right side view. 同じく左側面図。Similarly left side view. 同じく平面図。FIG. (a)同じく一部を省略した断面拡大図、(b)同じく一部拡大断面図。(A) The cross-sectional enlarged view which abbreviate | omitted one part, (b) The same partially enlarged cross-sectional view. 同じく一部を省略した断面拡大図。The cross-sectional enlarged view which abbreviate | omitted one part. 同じく一部を省略した断面拡大平面図。The cross-sectional enlarged plan view which abbreviate | omitted a part similarly. 同じく磁化ケースの拡大平面図。Similarly the enlarged plan view of a magnetization case. 同じく他の装置の実施例の一部を省略した断面図。Sectional drawing which abbreviate | omitted a part of Example of the other apparatus similarly. (a)同じく他の実施例の一部を省略した断面図、(b)同じく(a)におけるハンドル操作の操作状態を示す説明図。(A) Sectional drawing which abbreviate | omitted a part of other Example similarly, (b) Explanatory drawing which shows the operation state of the steering wheel operation in (a). (a)同じく消臭処理槽の他の実施例の一部を省略した縦断面図。(b)同じく一部を省略した横断面図。(A) The longitudinal cross-sectional view which abbreviate | omitted a part of other Example of the deodorizing processing tank similarly. (B) The cross-sectional view which abbreviate | omitted one part. (a)同じく熱交換器をつけた実施例の一部を省略した一部断面図。(b)同じく一部省略した平面図。(c)同じく仕切蓋の動力例を示す一部拡大図。(A) The partial sectional view which abbreviate | omitted a part of the Example which similarly attached the heat exchanger. (B) The top view which abbreviate | omitted partially. (C) The partially enlarged view which shows the example of the power of a partition lid similarly. 同じく処理物の自動投入装置の一例を示す実施例の概念図。The conceptual diagram of the Example which similarly shows an example of the automatic injection apparatus of a processed material.

この発明は、処理装置の加熱室にセラミックス灰の適量(例えば加熱室容量0.3mの容量ならば30kg)を収容し、これを250℃〜350℃に加熱赤熱させると共に(又は当初加熱がなくとも、処理物の分解熱により灰が自動的に加熱される)、処理装置の処理室(例えば容積2m)へ処理物(産業廃棄物、例えば食品残渣とプラスチック容器などの混合物)2mを投入し、投入口を被蓋密封する。また前記処理装置の上部には排気管を連設し、該排気管を排気の処理槽に連結してある。 According to the present invention, an appropriate amount of ceramic ash (for example, 30 kg if the capacity of the heating chamber capacity is 0.3 m 3 ) is accommodated in the heating chamber of the processing apparatus and heated to 250 ° C. to 350 ° C. (or initially heated). even without ash is heated automatically by the decomposition heat of the workpiece), the processing chamber (e.g., volume 2m 3) to the processing of the processing device (industrial waste, such as a mixture of food residue and plastic containers) 2m 3 And seal the cover at the cover. An exhaust pipe is connected to the upper portion of the processing apparatus, and the exhaust pipe is connected to an exhaust treatment tank.

前記条件により、前記セラミックス灰の輻射熱と磁化空気により処理物を乾燥し、ついで炭化し、更に灰化するのであるが、乾燥時に多量の水蒸気が発生して排気管から流出する。従って処理装置内が減圧状態になると、処理装置の下部に設置した磁化筒の一端から磁化されるべき空気が流入するので、前記セラミックス灰の赤熱輻射線と、磁化空気により、処理物はその下部から乾燥分解処理が進行し、炭化、灰化と順次処理される。   Under the above conditions, the treated product is dried by radiant heat and magnetized air of the ceramic ash, then carbonized and further ashed, but a large amount of water vapor is generated and flows out of the exhaust pipe during drying. Therefore, when the inside of the processing apparatus is in a depressurized state, air to be magnetized flows from one end of the magnetized cylinder installed at the lower part of the processing apparatus, so that the processed product is moved to the lower part by the red heat radiation of the ceramic ash and the magnetized air. Then, the dry decomposition process proceeds, followed by carbonization and ashing.

そこで1時間〜2時間処理されると、前記処理物の下部が架橋を構成し、セラミックス灰との距離も大きくなることがあるので、この場合には撹拌軸を回転し、撹拌により架橋を破壊すると、前記セラミックス灰上へ処理物が落下し、磁化空気下で加熱されて炭化し、ついで灰化する。処理物の材質および形状にもよるが、分解進行中の処理物へ分解されていない処理物の自重が加われば、架橋は自然に解消される。   Therefore, when treated for 1 to 2 hours, the lower part of the treated product may form a bridge and the distance from the ceramic ash may increase. In this case, the stirring shaft is rotated and the bridge is broken by stirring. Then, the processed material falls onto the ceramic ash, is heated under magnetized air and carbonized, and then ashed. Although depending on the material and shape of the processed material, if the weight of the processed material that has not been decomposed is added to the processed material being decomposed, the crosslinking is naturally eliminated.

このようにして処理装置の上部に十分の隙間ができたならば蓋を開いて、必要量の処理物を補充する。例えば当初充填した処理物2mが1m位になったならば、新たに処理物1mを追加投入する。このように不足分を追加すれば、処理装置内には常時1m以上の処理物が残留し自重により下圧下降していることになり、処理物は同一状態で継続処理される。処理物の材質にもよるが、2m収容した処理物は、4時間〜5時間で1m処理されるので、追加投入は4時間〜5時間毎に行われる。 When a sufficient gap is formed in the upper part of the processing apparatus in this way, the lid is opened and a necessary amount of processed material is replenished. For example, when the initially filled processed material 2m 3 becomes 1m 3 , the processed material 1m 3 is newly added. If the shortage is added in this way, a processed product of 1 m 3 or more always remains in the processing apparatus and the pressure is lowered by its own weight, and the processed product is continuously processed in the same state. Depending on the material of the workpiece, treated product was 2m 3 accommodated, because it is 1 m 3 at 4 to 5 hours, add-on is carried out every 4 to 5 hours.

処理装置の上部に処理物投入用のホッパーを連設し、このホッパー内に1日分の処理物を収容しておけば、処理物は自重により逐次下降し、自動連続投入処理が行われる。このようにすれば、1日に1回処理物をホッパーに投入すれば、自動連続処理ができる。   If a hopper for inputting a processed material is connected to the upper portion of the processing apparatus and the processed material for one day is accommodated in the hopper, the processed material is successively lowered by its own weight, and automatic continuous charging processing is performed. If it does in this way, if a processed material is thrown into a hopper once a day, automatic continuous processing can be performed.

この発明の実施例を図1(a)に基づいて説明すると、処理装置の加熱室へ、別製のセラミックス灰を収容する。例えば加熱室の容量が0.3mならば、これにセラミックス灰30kgを収容し、加熱室の上部の処理室へ処理物を2m投入すると共に(処理室は2mの容積とする)セラミックス灰を350℃に加熱すると、処理物は、その下部がセラミックス灰の輻射熱により乾燥すると共に、吸入された磁化空気による活性酸素、水素と前記輻射熱と相俟って前記処理物を逐次分解して炭化し、ついで低温分解処理により灰化する。 An embodiment of the present invention will be described with reference to FIG. 1A. Separately produced ceramic ash is accommodated in a heating chamber of a processing apparatus. For example, if the capacity of the heating chamber is 0.3 m 3 , 30 kg of ceramic ash is accommodated therein, and 2 m 3 of processed material is charged into the processing chamber above the heating chamber (the processing chamber has a volume of 2 m 3 ). When the ash is heated to 350 ° C., the lower part of the treated product is dried by the radiant heat of the ceramic ash, and the treated product is sequentially decomposed in combination with the active oxygen, hydrogen and the radiant heat generated by the sucked magnetized air. It is carbonized and then incinerated by low-temperature decomposition treatment.

前記のようにして処理物は灰化すると急激に容積が小さくなるので、前記投入処理物はその自重により逐次下降し、3〜4時間で半減する。そこで処理装置の投入口の開閉蓋を開き、処理物1mを投入する。即ち当初2m投入した処理物は、3〜4時間で半減することになる。前記における処理物とは、例えば産業廃棄物(木材、プラスチック製品の廃物、食品の期限切れ品、工場排出物)、家庭廃棄物その他の有機物を含む雑多の廃棄物をいう。 As described above, when the processed product is ashed, the volume rapidly decreases. Therefore, the input processed product is successively lowered by its own weight, and halved in 3 to 4 hours. Therefore, the opening / closing lid of the charging port of the processing apparatus is opened, and 1 m 3 of the processed material is charged. That is, the processed material initially charged at 2 m 3 is halved in 3 to 4 hours. The treated material in the above refers to miscellaneous waste including, for example, industrial waste (wood, plastic product waste, expired food, factory waste), household waste, and other organic matter.

次にこの発明の実施例を図1(b)に基づいて説明すると、処理装置の排気を処理槽に導き、撒水により脱臭、消臭して、気体は外界へ放出し、又は磁化処理脱臭して外界へ放出する。この場合に、磁化処理の有無はバルブの切り換えにより行う。例えば処理物の材質上(例えばゴム加工物など硫化物を含む場合など、臭気残留のおそれがある場合に、排気を0.25テスラ(2500ガウス)〜0.4テスラ(4000ガウス)の磁場を通過させて脱臭する。この場合に排気温度は比較的低温(例えば150℃以下)であるから、磁石の熱劣化を生じるおそれはなく、長期に亘り同一消臭性能を保持することができる。   Next, an embodiment of the present invention will be described with reference to FIG. 1 (b). The exhaust of the processing apparatus is guided to a processing tank, deodorized and deodorized by flooding, and the gas is released to the outside, or the magnetic treatment is deodorized. To the outside world. In this case, the presence or absence of the magnetization process is performed by switching the valve. For example, if there is a risk of residual odor due to the material of the processed material (for example, when it contains sulfide such as rubber processed material), the exhaust gas is applied with a magnetic field of 0.25 Tesla (2500 Gauss) to 0.4 Tesla (4000 Gauss). In this case, since the exhaust temperature is relatively low (for example, 150 ° C. or less), there is no risk of thermal degradation of the magnet, and the same deodorizing performance can be maintained over a long period of time.

次に処理槽内の撒水は、セラミックスボール層その他の濾過層によって浄水し、かつ固形物を分離してポンプ室に給送し、ポンプにより再び撒水させる。即ち浄水処理を経て撒水を循環使用するので、比較的少量の水により確実に消臭、脱臭処理ができる。従って撒水による循環水の自然減少のみを補充すれば長期に亘り連続運転することができる。前記における無気固形物は、浄化土砂として排出するので環境汚染のおそれはない。   Next, the water in the treatment tank is purified by a ceramic ball layer or other filtration layer, and solids are separated and fed to the pump chamber, and again watered by the pump. That is, since the brine is circulated and used after the water purification treatment, the deodorization and deodorization treatment can be reliably performed with a relatively small amount of water. Therefore, if only natural reduction of circulating water due to flooding is supplemented, continuous operation can be performed for a long time. The airless solid in the above is discharged as purified soil, so there is no risk of environmental pollution.

前記のようにして一定時間(例えば4時間)毎に、処理物を1m宛投入すれば、前記処理装置を連続使用して処理物を連続的に処理することができる。このようにして、実施例の実験処理装置においては、1日(24時間)約6mの処理物を処理することができた。 As described above, if the processed material is charged to 1 m 3 every predetermined time (for example, 4 hours), the processed material can be continuously processed using the processing apparatus. In this way, in the experimental processing apparatus of the example, a processed product of about 6 m 3 per day (24 hours) could be processed.

前記は処理物について、原則として発生時の形状のままダンボール箱に詰めて処理した場合であるが、発生した処理物を破砕(平均5cm程度の大きさ)した所、分解効率が50%以上向上した。実験の結果によれば、前記1日6mの処理が、1日10m程度に向上した。また破砕処理によって、平均2cm程度の大きさにした所、分解効率は更に向上し、実験の結果12m〜15mとなった。前記により明らかなように、処理物の表面積を増加すれば、分解効率を増加させることができるので、比較的小さい処理装置と、破砕装置とをセットして使用すれば、小型高性能の分解装置とすることができる。 The above is the case where the processed product is processed by packing it in a cardboard box as it is in principle, but when the generated processed product is crushed (average size is about 5 cm), the decomposition efficiency is improved by 50% or more. did. According to the result of the experiment, the treatment of 6 m 3 per day was improved to about 10 m 3 per day. By crushing Moreover, when you size having an average 2 cm, the decomposition efficiency is further improved, resulting 12m 3 ~15m 3 experiments. As is clear from the above, if the surface area of the processed material is increased, the decomposition efficiency can be increased. Therefore, if a relatively small processing device and a crushing device are used in combination, a small high-performance decomposition device can be used. It can be.

前記低温処理により生じた排気は、処理物の種類(例えば合成樹脂廃棄物、又は古タイヤ)によっては悪臭があるので、消臭・脱臭槽(処理槽)に入れて撒水脱臭した後、磁化処理して外界へ放出する。前記のように、排気により室内が減圧されるので、磁化空気は排気量に見合う量(事実上、発生水蒸気量と磁化空気量の和に見合う)を自動吸引し、加熱室及び処理室内へ給気する。この給気量は吸入部に設けたバルブの絞め具合により調節することができる。供給する空気量(即ち酸素量)が多いと、通常の酸化燃焼となって目的とする低温分解による灰化処理はできなくなる。前記実施例の実験処理装置を240時間連続燃焼したが、ラミックス灰は当初供給したセラミックス灰30kgを越え、僅かに増加(約35kg位)していることが確認された。   The exhaust generated by the low-temperature treatment may have a bad odor depending on the type of treated material (for example, synthetic resin waste or old tires), so it is put into a deodorizing / deodorizing tank (processing tank) and deodorized with water, and then magnetized. And release it to the outside world. As described above, since the chamber is depressurized by exhaust, magnetized air automatically sucks an amount commensurate with the amount of exhaust (effectively commensurate with the sum of the amount of generated water vapor and magnetized air) and supplies it to the heating chamber and the processing chamber. I care. This air supply amount can be adjusted by the degree of restriction of a valve provided in the suction portion. When the amount of air to be supplied (that is, the amount of oxygen) is large, the ashing process cannot be performed by the intended low-temperature decomposition because of normal oxidation combustion. Although the experimental treatment apparatus of the above example was continuously burned for 240 hours, it was confirmed that the lamix ash exceeded the initially supplied ceramic ash of 30 kg and increased slightly (about 35 kg).

前記のように、240時間で60m3の処理物を処理したので、無機物60kg以上増加により、灰は90kg〜100kgになる筈であるが、35kgの灰ということは当初灰30kgとして、55kg〜65kgの灰が消失したことになる。この理由は不明であるが、灰も気化して排出されたものと考えられる。   As described above, since 60 m3 of the processed product was processed in 240 hours, the ash should be 90 kg to 100 kg due to an increase of 60 kg or more of the inorganic substance. However, 35 kg of ash is initially 30 kg of ash, 55 kg to 65 kg. Ashes have disappeared. The reason for this is unknown, but it is thought that ash was also vaporized and discharged.

前記分解を、有機物の一つである炭水化物について考察するに、次のようになる。   The above-mentioned decomposition is considered as follows for a carbohydrate which is one of organic substances.

(1)C1222O11=12C+11H+5.5O
(2)C1222O11=C+11CO+11H
(3)C1222O11=12C+11H
実験の結果においても水分の増加が認められた(ドレイン及び脱臭処理の為に加えた水量よりも多い排水量が認められた)。
(1) C 12 H 22 O11 = 12C + 11H 2 + 5.5O 2
(2) C 12 H 22 O11 = C + 11CO + 11H 2
(3) C 12 H 22 O11 = 12C + 11H 2 O
The result of the experiment also showed an increase in moisture (a larger amount of drainage than the amount of water added for draining and deodorizing treatment was observed).

この発明の実施例を、図2、3、4、5、6、7に基づいて説明すれば、四角筒状の装置本体1の底板2上へ断面逆台形状の加熱室3を設け、該加熱室3の上部へ処理室4を連設し、前記装置本体1の上部へ投入口5を有する頂板6を設け、該頂板6の投入口5に開閉蓋7を被冠して、処理装置10を構成した(図6,7)。   An embodiment of the present invention will be described with reference to FIGS. 2, 3, 4, 5, 6, and 7. A heating chamber 3 having an inverted trapezoidal cross section is provided on the bottom plate 2 of the apparatus body 1 having a square cylindrical shape. A processing chamber 4 is connected to the upper part of the heating chamber 3, a top plate 6 having an inlet 5 is provided on the upper part of the apparatus main body 1, and an opening / closing lid 7 is crowned on the inlet 5 of the top plate 6. 10 (FIGS. 6 and 7).

前記開閉蓋7の基端に横軸40が固定され(図2)、横軸40は、処理装置10の頂板6へ止環41、41により回転自在に取り付けられ、開閉蓋7の先端部に、前記横軸40と平行な支杆42を固定し、前記横軸40と支杆42の両端に杆体43、43を固定し、杆体43、43の横軸側端に、開閉蓋7と見合う重量の重錘44、44を固定してある。図中45、45は開閉蓋7の掛止片、46は排気管、47は残渣取出口の開閉蓋、48は開閉蓋47のハンドルである(図2)。   A horizontal shaft 40 is fixed to the base end of the opening / closing lid 7 (FIG. 2), and the horizontal shaft 40 is rotatably attached to the top plate 6 of the processing apparatus 10 by retaining rings 41, 41. The support rod 42 parallel to the horizontal shaft 40 is fixed, the housings 43 and 43 are fixed to both ends of the horizontal shaft 40 and the support rod 42, and the opening / closing lid 7 is matched to the horizontal shaft side ends of the housings 43 and 43. Weight weights 44, 44 are fixed. In the drawing, 45 and 45 are latching pieces of the opening / closing lid 7, 46 is an exhaust pipe, 47 is an opening / closing lid for a residue outlet, and 48 is a handle of the opening / closing lid 47 (FIG. 2).

前記装置本体1の加熱室3と、処理室4(図6)の下部には、左右側壁4a、4b方向(斜壁側)から、水平方向へ給気パイプ8、8を上下多段に設ける。該給気パイプ8、8は下段程中央部へ長く、上段程短く突出し、各列の給気パイプ8、8の基端は各列毎に送気パイプ9、9に夫々連結し、送気パイプ9、9の基端(下部)は、夫々磁化筒11内の通気管13に連結する連結パイプ15に連結し(図9)、前記磁化筒11は、前記装置本体1の下部両側へ横設されている。そこで磁化筒11の通気管13の一端を装置本体1外へ開口させ、空気を自由に吸入できるようになっている。前記通気管13にバルブ(図示してない)を介装し、該バルブによりその開度を調節し、送気量を制御できるようにしてある。図5中14は磁化空気量を調節するバルブハンドルである。   In the heating chamber 3 of the apparatus main body 1 and the lower portion of the processing chamber 4 (FIG. 6), supply pipes 8 and 8 are provided in multiple stages in the horizontal direction from the left and right side walls 4a and 4b (slanted wall side). The air supply pipes 8 and 8 are longer in the center of the lower stage and project shorter in the upper stage, and the base ends of the air supply pipes 8 and 8 of each row are connected to the air supply pipes 9 and 9 for each row, respectively. The base ends (lower parts) of the pipes 9 and 9 are connected to connecting pipes 15 connected to the ventilation pipes 13 in the magnetizing cylinder 11 (FIG. 9). It is installed. Therefore, one end of the vent pipe 13 of the magnetizing cylinder 11 is opened to the outside of the apparatus main body 1 so that air can be freely sucked. A valve (not shown) is provided in the vent pipe 13, and the opening degree is adjusted by the valve so that the amount of air supplied can be controlled. In FIG. 5, 14 is a valve handle for adjusting the amount of magnetized air.

前記通気管13には、0.8テスラ(8000ガウス)の永久磁石16を嵌装設置してある(図9)。前記永久磁石16には、ヨーク(図示してない)を介装しているが、永久磁石16と、ヨークとの関係は、ヨークにより磁束を合理的に集中的に送達することを目的とし、具体的形状、設置構造を特定するものでなく、従来公知のヨークによる磁束集構造はそのまま使用又は改良して使用することができる。   A 0.8 Tesla (8000 gauss) permanent magnet 16 is fitted and installed in the vent pipe 13 (FIG. 9). The permanent magnet 16 is provided with a yoke (not shown), and the relationship between the permanent magnet 16 and the yoke is to provide a magnetic flux that is reasonably concentrated by the yoke. The specific shape and installation structure are not specified, and a conventionally known magnetic flux collecting structure using a yoke can be used as it is or improved.

また処理装置10の排気管17を消煙・消臭の処理槽18に連結する(図7)。前記消煙・消臭の処理槽18内は、複数の仕切板19a、19b、19c、19d、19eにより縦に仕切られ、前記仕切板の上方又は下方を順次開口して排煙が屈曲流動できるようにすると共に、上部に撒水パイプ20を設け、撒水により排煙の清浄化を図っている(図10)。前記において、排煙は図7中矢示21のように消煙・消臭の処理槽18へ入り、撒水パイプ20、20から放出する水粒子によって固形物を分離落下と、煙を吸収させて清浄化すると共に、図10中矢示21、22、23、24、25、26、27、28のように屈曲流動中に粒子類を分離落下させる。そこで水粒に付着した異物と、屈曲流動中に落下した粒子は、槽底上に溜まった排水中に混入し、排水パイプ29から矢示30のように排出される。前記仕切板19bの上部には、排煙の通過パイプ31が介装されており、排出パイプ32と共に、永久磁石33、33が固定してある。そこで前記通過パイプ31と排水パイプ32を通過する排気中に固形物が混入していると、これを磁化(又はイオン化)して団粒化し、自重を増加して落下させ又は臭気を分解して、排気の清浄化を図ることができる(図10)。   Further, the exhaust pipe 17 of the processing apparatus 10 is connected to a smoke / deodorant treatment tank 18 (FIG. 7). The smoke / deodorant treatment tank 18 is vertically partitioned by a plurality of partition plates 19a, 19b, 19c, 19d, 19e, and the exhaust gas can be bent and flow by opening sequentially above or below the partition plates. At the same time, a soaking pipe 20 is provided at the top, and the flue gas is purified by soaking (FIG. 10). In the above description, the flue gas enters the smoke / deodorant treatment tank 18 as shown by an arrow 21 in FIG. 7, and solids are separated and dropped by the water particles discharged from the submerged pipes 20, 20, and the smoke is absorbed and cleaned. At the same time, particles are separated and dropped during bending flow as indicated by arrows 21, 22, 23, 24, 25, 26, 27, and 28 in FIG. Accordingly, the foreign matter adhering to the water droplets and the particles dropped during the bending flow are mixed in the waste water accumulated on the bottom of the tank and are discharged from the drain pipe 29 as indicated by an arrow 30. A smoke passage pipe 31 is interposed on the upper part of the partition plate 19b, and permanent magnets 33 and 33 are fixed together with the discharge pipe 32. Therefore, if solid matter is mixed in the exhaust gas passing through the passage pipe 31 and the drain pipe 32, this is magnetized (or ionized) to form agglomerate, which increases its own weight and falls or decomposes odor. The exhaust can be cleaned (FIG. 10).

そこで撒水と、永久磁石による磁化と脱異物により、排気はほぼ完全に清浄化される。然して排気の温度は高くとも150℃以下であるから、この処理槽を長年使用しても永久磁石の磁化能力の熱低下を来したり、老化を生じるおそれはない。従って一般廃棄物の処理における排煙は、無色(又は淡い水蒸気のみ)となり、微粒固形物も殆ど見当たらない程度に浄化される。図中49、50は送水ポンプ、51は撒水パイプへ給水する送水パイプ、52は水位である。   Therefore, the exhaust gas is almost completely cleaned by flooding, magnetization by the permanent magnet, and foreign matter. However, since the temperature of the exhaust gas is 150 ° C. or less at the highest, even if this treatment tank is used for many years, there is no possibility that the magnetization capacity of the permanent magnet will be lowered or that aging will occur. Therefore, the flue gas in the treatment of general waste becomes colorless (or only light water vapor) and is purified to such an extent that fine solids are hardly found. In the figure, 49 and 50 are water supply pumps, 51 is a water supply pipe for supplying water to a flooded pipe, and 52 is a water level.

前記処理装置の加熱室3の上部には、撹拌軸34、34が所定間隔で横架され(図6)、前記撹拌軸34、34の中間部下方(ほぼ加熱室の中間高さ)に撹拌軸35が前記撹拌軸34、34と平行に架設され、各撹拌軸34、35に複数の撹拌杆36、36が突設されている。前記撹拌軸34、35の撹拌杆36は、投入処理物の架橋化を防止する目的であって、設置本数と位置については特に限定はない(図6、8)。前記において、撹拌軸35にハンドル37を固定し、撹拌軸34,35に夫々ギヤー(34a、35a)を固定し、このギヤーを噛み合わせれば、1つのハンドル37で3本の撹拌軸34,34,35を回転させることができる(図6,8)。   Stirring shafts 34, 34 are horizontally mounted at predetermined intervals on the upper portion of the heating chamber 3 of the processing apparatus (FIG. 6), and stirring is performed below the middle portion of the stirring shafts 34, 34 (almost at the intermediate height of the heating chamber). A shaft 35 is installed in parallel with the stirring shafts 34, 34, and a plurality of stirring rods 36, 36 project from the stirring shafts 34, 35. The stirring rods 36 of the stirring shafts 34 and 35 are for the purpose of preventing cross-linking of the input processed products, and there are no particular limitations on the number and position of the stirring rods (FIGS. 6 and 8). In the above description, the handle 37 is fixed to the stirring shaft 35, the gears (34a, 35a) are fixed to the stirring shafts 34, 35, and the gears are engaged with each other. , 35 can be rotated (FIGS. 6 and 8).

前記処理物53(図6)は、その下面側から逐次乾燥し、炭化し、灰化するので、ほぼ下面から処理されるが、時には加熱室3の内壁と接触掛止して落下することなく、架橋状態(例えば中央下面のみ処理が進み、周辺の処理が進まない為に凸弧状)の空洞54ができることがある(図6)。このような場合には、廃棄物の下面に対するセラミックス灰の赤熱による輻射線の強弱となり、処理速度の遅速を生じ、全体として処理遅延のおそれがある。そのような時には、前記撹拌軸のハンドル37を握り(図2)、撹拌杆36を回転することによって、容易に架橋を崩し正常処理に戻すことができる。前記においては、撹拌軸35にギヤーを固定したが、例えば前記ハンドル37の撹拌軸34、35に夫々スプロケット34a、34aを固定し、このスプロケットにチェーンを装着して撹拌軸34、35を同時に回転させることもできる(図8)。   The processed material 53 (FIG. 6) is dried from the lower surface side, carbonized, and incinerated, so that the processed material 53 is processed from the lower surface, but sometimes does not come into contact with the inner wall of the heating chamber 3 and fall. In some cases, a cavity 54 is formed in a bridged state (for example, a convex arc shape because processing proceeds only at the center lower surface and peripheral processing does not proceed) (FIG. 6). In such a case, the intensity of the radiation due to red heat of the ceramic ash with respect to the lower surface of the waste is increased, resulting in a slow processing speed, and there is a risk of processing delay as a whole. In such a case, by holding the handle 37 of the stirring shaft (FIG. 2) and rotating the stirring rod 36, it is possible to easily break the bridge and return to normal processing. In the above, the gear is fixed to the stirring shaft 35. For example, sprockets 34a and 34a are fixed to the stirring shafts 34 and 35 of the handle 37, respectively, and a chain is attached to the sprocket to rotate the stirring shafts 34 and 35 simultaneously. (FIG. 8).

前記撹拌軸の回転間隔は、処理物の材質により異なるが、ほぼ1時間〜2時間に1回、1分〜5分前後回転すれば目的を達成することができる(1分間に5〜10回転)。例えば4時間に1回宛処理物を補充する時には、補充の都度とその中間に1〜2回回転すれば目的を達成するものと思われる。   The rotation interval of the agitation shaft varies depending on the material of the processed material, but the object can be achieved by rotating about once every 1 to 2 hours and about 1 to 5 minutes (5 to 10 rotations per minute). ). For example, when replenishing the processed material once every four hours, it is considered that the object can be achieved by rotating once or twice between each replenishment.

前記撹拌軸34、35の本数と、架設位置については、特定の数、構造はないが、数は2本〜3本で、位置は加熱室3の付近が望ましい。   There is no specific number and structure for the number of the stirring shafts 34 and 35 and the installation position, but the number is 2 to 3 and the position is preferably in the vicinity of the heating chamber 3.

この発明の加熱室3は、低温処理であるから、処理装置10の側壁等に特別の配慮の必要はないが、作業者が過って接触しても、何等の火傷を生じないように、2重壁(例えば2cm〜5cm間隔の空間をおいて外壁1aと、内壁1bを設ける)とすることが好ましく(図6)、2重壁により、熱経済にもなる。また送水管38と給湯管39とを継ぐパイプに水を流動させて温水を生成し、この温水を温室暖房などに使用することもできる。   Since the heating chamber 3 of the present invention is a low-temperature treatment, there is no need for special consideration on the side wall of the processing apparatus 10, etc. It is preferable to use a double wall (for example, an outer wall 1a and an inner wall 1b are provided with a space of 2 cm to 5 cm apart) (FIG. 6). Further, hot water can be generated by flowing water through a pipe connecting the water supply pipe 38 and the hot water supply pipe 39, and this hot water can be used for greenhouse heating or the like.

前記において、給水管38と、給水管39をパイプで連結することなく二重壁へ直接給水する場合には、二重壁を熱交換用と、磁化空気の下降用とに区切る必要がある。即ち、二重壁は、断熱を兼用して磁化空気の下降用に使用されているからである。   In the above, when water is supplied directly to the double wall without connecting the water supply pipe 38 and the water supply pipe 39 with a pipe, it is necessary to divide the double wall into one for heat exchange and one for lowering the magnetized air. In other words, the double wall is also used for lowering the magnetized air while also serving as heat insulation.

前記2重壁において断熱板を挟み込む場合もある。例えば寒冷地仕様の際に内部で発生した熱を外部へ逃さないようにする配慮が必要な場合もある。   In some cases, a heat insulating plate is sandwiched between the double walls. For example, there is a case where it is necessary to take care not to let the heat generated inside during the cold district specification escape to the outside.

前記実施例において、加熱室3内の灰は分解熱によって300℃前後に加熱されているので、流入空気を加熱して上昇流となり(図6中矢示90,91)、その一部は矢示92,93のように2重壁を経て下降し、下部から矢示94,94のように加熱室3に入り、循環流動する。従って磁化空気は加温を経て処理物53内を通過するので、処理物53は均等に加温乾燥、分解及び処理されることになる。前記において、図6中2重壁と、送気パイプ9は重なっているが、2重壁内へ送気パイプが設置されているので、磁化空気の循環に支障はない。   In the above embodiment, the ash in the heating chamber 3 is heated to around 300 ° C. by the decomposition heat, so the inflowing air is heated to become an upward flow (indicated by arrows 90 and 91 in FIG. 6), part of which is indicated by the arrows. It descends through the double wall as shown by 92 and 93, enters the heating chamber 3 from the lower part as indicated by arrows 94 and 94, and circulates and flows. Accordingly, since the magnetized air passes through the processed object 53 through heating, the processed object 53 is uniformly heated, dried, decomposed and processed. In FIG. 6, the double wall and the air supply pipe 9 are overlapped with each other. However, since the air supply pipe is installed in the double wall, there is no problem in the circulation of the magnetized air.

この装置によれば、加熱室3が下部にあって、付近の空気を加温するので、何等の動力を用いることなく、自然に上下対流を生起することができる。従って動力を使用することなく分解効率を最良にすることができる。   According to this apparatus, since the heating chamber 3 is in the lower part and the air in the vicinity is heated, vertical convection can be naturally generated without using any power. Therefore, the decomposition efficiency can be optimized without using power.

この発明の他の実施例を図11〜18に基づいて説明すれば、四角筒状の装置本体61の底板62上へ、漏斗状の加熱室63を設け、該加熱室63の上部を処理室64とし(図16)、前記装置本体61の口部へ投入口66aを有する頂板66を固定し、該投入口66aへ開閉蓋67を開閉自在に被冠する(図13,16)。   Another embodiment of the present invention will be described with reference to FIGS. 11 to 18. A funnel-shaped heating chamber 63 is provided on a bottom plate 62 of a rectangular cylindrical apparatus body 61, and the upper portion of the heating chamber 63 is disposed in a processing chamber. 64 (FIG. 16), a top plate 66 having an insertion port 66a is fixed to the mouth of the apparatus main body 61, and an opening / closing lid 67 is crowned on the insertion port 66a so as to be freely opened and closed (FIGS. 13 and 16).

前記装置本体61の口部は、前壁61a側を低くして斜に開口し(図13左側が前側)、前記開閉蓋67は、後縁部の支軸55を中心にして矢示56のように開閉することができる(図13)。   The mouth of the apparatus main body 61 is opened obliquely with the front wall 61a side lowered (the left side in FIG. 13 is the front side), and the opening / closing lid 67 has an arrow 56 centered on the support shaft 55 at the rear edge. (FIG. 13).

前記装置本体61の加熱室63の上部と、処理室64の下部には、左右側壁64a、64b方向から給気パイプ68、68を上下多段(図16)に水平方向に突設し、その先端は何れも下向きに斜切68aにしてある。前記給気パイプ68は磁化空気を供給する為に設けてあるが、吹き出し口を投入処理物に塞がれることがないように前記のように下向き斜切68aにし、又は網68bを被冠することもできる。   At the upper part of the heating chamber 63 of the apparatus main body 61 and the lower part of the processing chamber 64, air supply pipes 68, 68 are provided in the upper and lower multi-stages (FIG. 16) in the horizontal direction from the left and right side walls 64a, 64b. Are diagonally cut 68a downward. The air supply pipe 68 is provided to supply magnetized air. However, the air outlet 68 is inclined downward 68a as described above so as not to be blocked by the charged material, or the net 68b is covered. You can also.

前記給気パイプ68、68の基端側は、前記装置本体61の底板62上へ設置されたヘッダー管57、57に連結し(図16,20)、ヘッダー管57、57は磁化ケース71の通気管73aと連通してあり、前記磁化ケース71の通気管74aにバルブ74を介装し、バルブ74のハンドルにより通気量(磁化空気)を調節することができる(図18,19)。前記通気管74aは外界に開口し、空気を自由に吸入できるようになっている。前記磁化ケース71内には0.4テスラ(4000ガウス)〜0.8テスラ(8000ガウス)の永久磁石体75が設置され、その磁極N、S76、77の間隙78を前記空気が流動して磁化され(図19)、その通気管73aを、前記通気管73と連結する。   The proximal ends of the air supply pipes 68, 68 are connected to header pipes 57, 57 installed on the bottom plate 62 of the apparatus main body 61 (FIGS. 16, 20). The header pipes 57, 57 are connected to the magnetizing case 71. The vent pipe 73a communicates with the vent pipe 74a of the magnetizing case 71, and a valve 74 is interposed between the vent pipe 73a and the vent quantity (magnetized air) can be adjusted by the handle of the valve 74 (FIGS. 18 and 19). The vent pipe 74a opens to the outside and can suck air freely. A permanent magnet body 75 of 0.4 Tesla (4000 Gauss) to 0.8 Tesla (8000 Gauss) is installed in the magnetized case 71, and the air flows through the gap 78 between the magnetic poles N, S76, 77. Magnetized (FIG. 19), the vent pipe 73a is connected to the vent pipe 73.

従って前記給気パイプ68、68から処理室4内へ磁化空気が吹き出されると、磁化空気は加熱室63及び処理室64に入り、灰、処理物に作用して処理物を乾燥し、炭化し、灰化する。処理に際しては気体としてCO、HO(蒸気)、H、O、NOその他廃棄物の分解よりなる気体を生じると共に、金属類、セラミックス(石の類、硝子類)その他の無機物が金属及び灰として残留する。 Therefore, when magnetized air is blown out from the supply pipes 68, 68 into the processing chamber 4, the magnetized air enters the heating chamber 63 and the processing chamber 64, acts on the ash and the processed material, dries the processed material, and carbonizes. And ash. During processing, gases such as CO, H 2 O (vapor), H 2 , O 2 , NO 2 and other wastes are decomposed, and metals, ceramics (stones, glass) and other inorganic substances are present. Remains as metal and ash.

前記のように分解処理を続けると、前記灰も若干気体に変化(例えばCa、Siその他)する為か、処理物を継続的に処理しても灰の増加が認められない。例えば1日8mの処理物を30日連続処理しても処理物の量に見合う灰量の増加は見られない(例えば処理室の容量2mの場合に灰量は30kg〜40kgに止まっている)。 If the decomposition treatment is continued as described above, the ash is also slightly changed into a gas (for example, Ca, Si, etc.). For example, even if the processed material of 8 m 3 per day is processed continuously for 30 days, the amount of ash corresponding to the amount of processed material does not increase (for example, when the capacity of the processing chamber is 2 m 3 , the ash amount is only 30 kg to 40 kg. )

前記開閉蓋67と、頂板66に設けた排気筒65とをホース69、69で連結し(図15)、前記排気筒65と排気ポンプ70の吸入口とをパイプ72で結び排気ポンプ70の吐出口と、消臭、消煙の処理槽79とを排気パイプ80で連結する。そこで開閉蓋67を用いて処理物を投入する際に、前記排気ポンプ70を稼働すると、処理室64の上部気体が排気ホース69を介して矢示129のように排気筒65に吸い込まれるので、処理室64の上部は瞬時に負圧となり外部空気が処理室64の上部へ流入する。即ち処理室64内の排気が、外部へ流出するおそれを未然に防止することができる。一般処理時には、通常ポンプ70を停止しているので、処理室の排気が強制流動するおそれはない。   The opening / closing lid 67 and the exhaust pipe 65 provided on the top plate 66 are connected by hoses 69 and 69 (FIG. 15), and the exhaust pipe 65 and the suction port of the exhaust pump 70 are connected by a pipe 72 to discharge the exhaust pump 70. The outlet and the deodorizing / smoke removing treatment tank 79 are connected by an exhaust pipe 80. Therefore, when the exhaust pump 70 is operated when the processing object is introduced using the open / close lid 67, the upper gas in the processing chamber 64 is sucked into the exhaust pipe 65 as indicated by an arrow 129 through the exhaust hose 69. The upper part of the processing chamber 64 immediately becomes negative pressure, and external air flows into the upper part of the processing chamber 64. That is, it is possible to prevent the exhaust in the processing chamber 64 from flowing out to the outside. During general processing, the pump 70 is normally stopped, so there is no risk that the exhaust from the processing chamber will flow forcibly.

前記処理槽79に入った排気は、散水処理によって脱臭作用、粒子分離作用を受ける(実施例2と同様に付き説明省略)。前記処理槽79の排気は、該処理槽79の上部に連結した排気パイプ81を介して遠心分離機82に入り、固形物を分離して外界へ矢示83のように放出される(図11、12、15)。また遠心分離機82に入らない場合には、矢示83aのように排出される。   The exhaust gas that has entered the treatment tank 79 is subjected to a deodorizing action and a particle separating action by watering treatment (the description is omitted as in the second embodiment). The exhaust from the treatment tank 79 enters the centrifuge 82 through an exhaust pipe 81 connected to the upper part of the treatment tank 79, separates solid matter, and is discharged to the outside as indicated by an arrow 83 (FIG. 11). , 12, 15). When the centrifuge 82 is not entered, it is discharged as indicated by an arrow 83a.

前記処理室64の中央部へ(最高の給気パイプとほぼ同一高さ)に、回転軸58を水平に架設し、前記回転軸58に撹拌板59を突設し、前記回転軸58の一端を処理室外へ突設して、該突出部へハンドル60を固定する。従ってハンドル60を回転すると、撹拌板59が回転して、処理室64の下部を撹拌し、処理物の架橋を防止することができる(図14,20)。   A rotating shaft 58 is installed horizontally to the center of the processing chamber 64 (approximately the same height as the highest air supply pipe), and a stirring plate 59 is provided on the rotating shaft 58 so as to project one end of the rotating shaft 58. And the handle 60 is fixed to the protruding portion. Therefore, when the handle 60 is rotated, the stirring plate 59 is rotated to stir the lower portion of the processing chamber 64, thereby preventing the cross-linking of the processed product (FIGS. 14 and 20).

前記は手動のハンドル60を例示したが、回転をモータで回転し、モータ回路にタイマーを介装すれば、設定時間毎に自動的に回転、撹拌作用を付与することもできる。図中84は灰点検口の開閉蓋、85は処理室下部の点検口の開閉蓋、86は処理槽79の水位点検口の開閉蓋、87、87は処理槽79上部の点検口の開閉蓋である。   Although the manual handle 60 has been exemplified above, the rotation and the stirring action can be automatically given every set time if the rotation is rotated by a motor and a timer is provided in the motor circuit. In the figure, 84 is an opening / closing lid for the ash inspection port, 85 is an opening / closing lid for the inspection port at the bottom of the processing chamber, 86 is an opening / closing lid for the water level inspection port of the processing tank 79, and 87, 87 are opening / closing lids for the inspection port above the processing tank 79. It is.

前記実施例において、排気を撒水処理すれば臭気は皆無に近くなるが、この処理装置を船舶その他密閉室に設置した場合には、微量の臭気も発生させないことが好ましいので、この場合には脱臭剤撒布と併用すれば、完全無臭を実現することができる。   In the above embodiment, if the exhaust gas is treated with water, the odor will be almost zero. However, when this processing apparatus is installed in a ship or other sealed chamber, it is preferable not to generate a trace amount of odor. If it is used in combination with the agent coating, odorlessness can be achieved.

この発明の処理装置において、木材の処理に際しては、油分が水に混入して装置の内側壁に沿って流下することがある。このような時には、装置の下部内側へ、液体受け皿156を設置し、この液体受け皿156に前記液体(水と油分の混合)を受け入れる。この場合に、液体は内側に沿って流下するので、受け皿156を内側壁158に連設し、上部に蓋157を被冠する(灰などが入らないようにする)。この場合に、周囲の温度は150℃〜250℃が考えられるので、必然的に水は蒸発し、油分が濃縮されるから、油分を外部へ抜き取り、鋸屑、紙などを混入し、分解処理すれば前記内部に発生する油分には特別の配慮は不必要となる。   In the processing apparatus of the present invention, when processing wood, oil may be mixed in water and flow down along the inner wall of the apparatus. In such a case, a liquid tray 156 is installed inside the lower part of the apparatus, and the liquid (mixed water and oil) is received in the liquid tray 156. In this case, since the liquid flows down along the inner side, the receiving tray 156 is connected to the inner wall 158 and the upper portion is covered with a lid 157 (to prevent ash and the like from entering). In this case, since the ambient temperature can be 150 ° C to 250 ° C, the water inevitably evaporates and the oil content is concentrated, so the oil content is extracted to the outside, and sawdust, paper, etc. are mixed and decomposed. For example, no special consideration is required for the oil generated inside.

次にこの発明の実験例(セラミックス灰の量の不変)について説明する。   Next, an experimental example of the present invention (the amount of ceramic ash unchanged) will be described.

[実験例1]
1.試験項目:
(1)定量評価
(a) 一般廃棄物の減少(重量・容積)
(b) セラミック灰の消滅
(2)定性評価
(a) 一般廃棄物のセラミック化及び消滅
2.実施日
平成19年10月24日〜12月9日
3.場所:
栃木県那須烏山市 他
4.実施要領
(1)牛糞等の処理能力
14日間の試験期間中、毎日約3〜4トン(4〜5m)の牛糞および敷き藁等を処理機に投入し、灰等は一切取り出さない。
[Experimental Example 1]
1. Test items:
(1) Quantitative evaluation (a) Reduction of general waste (weight / volume)
(B) Disappearance of ceramic ash (2) Qualitative evaluation (a) Ceramics and disappearance of general waste 2. Implementation date October 24-December 9, 2007 3. place:
3. Nasu Kashiyama City, Tochigi Prefecture, etc. Implementation procedure (1) Processing capacity of cow dung, etc. During the 14-day test period, about 3 to 4 tons (4-5 m 3 ) of cow dung and litter are put into the processor every day, and no ash etc. are taken out.

処理量が増加しているにも関わらず、灰、その他残留物が増加しないことを確認する。   Confirm that ash and other residues do not increase despite the increased throughput.

(2)産業廃棄物処理能力
14日間の試験期間中、毎日2〜3トンの産業廃棄物を処理装置に投入し、金属、コンクリート片以外は、一切取り出さない。
(2) Industrial waste treatment capacity During the 14-day test period, 2 to 3 tons of industrial waste is put into the treatment equipment every day, and no metal or concrete pieces are taken out.

処理量が増加しているにも関わらず、灰、その他残留物が増加しないことを確認する。   Confirm that ash and other residues do not increase despite the increased throughput.

5.試験結果
(1)牧場から排出される牛糞及び敷き藁等、一定の品質を保った廃棄物
約50トンの牛糞を投入したにも関わらず、処理機内の炭化物(黒色)、灰化物(灰色)及びセラミック灰(白色)の目視による量に変化が見られず、全体の処理速度も変化がない。
5). Test results (1) Wastes that maintain a certain level of quality, such as cow dung and bedding discharged from the ranch Despite the introduction of about 50 tons of cow dung, carbide (black) and ash (gray) in the processing machine In addition, there is no change in the visual amount of the ceramic ash (white), and there is no change in the overall processing speed.

この間、灰化物等の取り出しは一切行っておらず、処理機の内部で消滅しているものと考えられる。   During this time, it is considered that ash and the like have not been removed at all and disappeared inside the processing machine.

(2)産業廃棄物処理場における産業廃棄物の処理
期間中、推定35トンの産業廃棄物を投入したにも関わらず、処理機内の残留物(灰状)の目視による量の増加は認められなかった。
(2) Disposal of industrial waste at industrial waste disposal sites During the period, an increase in the amount of residue (ash) in the processing machine was visually observed despite an estimated 35 tons of industrial waste being input. There wasn't.

なお、これらの廃棄物には、木片、廃棄プラスチック、各種包装容器、ペット類からの廃棄物、紙類、自動車タイヤ、ポリウレタン製バンパー等の雑多なものがそのまま投
入された。
In addition, miscellaneous things such as wood chips, waste plastics, various packaging containers, wastes from pets, papers, automobile tires, polyurethane bumpers, and the like were directly put into these wastes.

この間、一日に一度、処理機の最下部に出てきた、タイヤの鋼製ワイヤ等の金属類及び砂利、コンクリート片を取り出す以外は灰化物等の取り出しは一切行っておらず、処理機の内部で消滅しているものと考えられる。   During this time, the ash was not removed at all, except for the metal, gravel, and concrete pieces such as steel wires of the tire that came out at the bottom of the processor once a day. It is thought that it has disappeared inside.

この発明の投入物乾燥の実施例を図20について説明する。装置本体61の上部に頂板を除き同一断面の補助筒61aを連設する。前記頂板に代えて、投入物の支持板95,95を支軸96,96により水平位置より垂直位置へ矢示88,88のように回動自在に架設して、処理室64と、乾燥室97とに分設する。前記乾燥室97の一側下部には、乾燥空気の吹出口98を設け、他側上部には排気口99を設け、前記排気口99はパイプ101を介し、吸引器100(送風機)を連設し、吸引器100は冷却器102に連結し、冷却器102は加熱器103に連結し、加熱器103の送気側にホース104の一端を連結し、ホース104の他端を前記吹出口98と連結する。   An embodiment of the input drying according to the present invention will be described with reference to FIG. An auxiliary cylinder 61 a having the same cross section is provided continuously on the upper portion of the apparatus main body 61 except for the top plate. Instead of the top plate, the support plates 95 and 95 of the input material are rotatably supported from the horizontal position to the vertical position by the support shafts 96 and 96 as indicated by arrows 88 and 88, and the processing chamber 64 and the drying chamber. Divided into 97. A drying air blow-off port 98 is provided at a lower part of one side of the drying chamber 97, and an exhaust port 99 is provided at an upper part of the other side. The exhaust port 99 is connected to a suction device 100 (blower) through a pipe 101. The suction device 100 is connected to the cooler 102, the cooler 102 is connected to the heater 103, one end of the hose 104 is connected to the air supply side of the heater 103, and the other end of the hose 104 is connected to the outlet 98. Concatenate with

前記において、吸引器100を駆動して、空気を矢示105,106,107,108,109のように流動させると、パイプ101により吸入された多湿空気は、冷却器102で冷却されて水滴を生じ、そのドレーンはドレーンパイプ110から矢示111のように排出されるので乾燥空気となり、加熱器103により、70℃〜80℃の加熱乾燥空気となり、ホース104を通過して矢示207のように乾燥室97に入り、投入物112を乾燥しつつ通過する。前記装置によれば、多湿空気は冷却によって水分を分離した後加熱によって乾燥空気となるので、高い効率で乾燥することができると共に、投入物は加温(例えば90℃前後)されるので、処理室64における分解効率を向上させることができる。この種分解においては、水分70%以上ある投入物については、分解効率が著しく低下するが、水分90%の投入物であっても、効率よく水分60%以下に乾燥できることが確認されている。従って前記乾燥によりエネルギーの消費はあるけれども分解効率の向上により損失エネルギーを十分補修することができる。   In the above description, when the aspirator 100 is driven to cause the air to flow as indicated by arrows 105, 106, 107, 108, and 109, the humid air sucked by the pipe 101 is cooled by the cooler 102 to form water droplets. As a result, the drain is discharged from the drain pipe 110 as indicated by an arrow 111, and thus becomes dry air. By the heater 103, the dry air is heated to 70 ° C. to 80 ° C. and passes through the hose 104 as indicated by an arrow 207. And enters the drying chamber 97 and passes through the input 112 while drying. According to the apparatus, since the humid air separates moisture by cooling and becomes dry air by heating, the humid air can be dried with high efficiency and the input is heated (for example, around 90 ° C.). The decomposition efficiency in the chamber 64 can be improved. In the seed decomposition, the decomposition efficiency is remarkably reduced for an input having a water content of 70% or more, but it has been confirmed that even an input having a water content of 90% can be efficiently dried to a water content of 60% or less. Therefore, although energy is consumed by the drying, the loss energy can be sufficiently repaired by improving the decomposition efficiency.

この実施例4は、処理物の事前乾燥であるが、装置本体61の上部に設置されているので、乾燥済み処理物の処理については実施例3と全く同一である。即ち図20の装置本体61は、図16の装置本体と全く同一であり、同一符号を付している。従って処理物の分解処理についての説明を省略する。   The fourth embodiment is a pre-drying of the processed product, but is disposed on the upper part of the apparatus main body 61. Therefore, the processing of the dried processed product is exactly the same as the third embodiment. That is, the apparatus main body 61 in FIG. 20 is exactly the same as the apparatus main body in FIG. 16, and is given the same reference numerals. Therefore, the description about the decomposition | disassembly process of a processed material is abbreviate | omitted.

この発明の他の実施例(開閉蓋の開閉時に臭気の排出されない装置)に付、図21により説明する。装置本体61の上部へ、同一横断面積で1回で処理する量の投入容積(例えば1m)を有する補助筒112を連設すると共に、装置本体61の上部内側へ支持板113,113を対向し、装置本体61の内壁に沿って回転軸114,114を水平に回転自在に架設し、前記支持板113,113の先端部は気密に重ね合わせることができる。 A description will be given of another embodiment of the present invention (apparatus that does not discharge odor when the lid is opened / closed) with reference to FIG. An auxiliary cylinder 112 having an input volume (for example, 1 m 3 ) that can be processed at a time with the same cross-sectional area is connected to the upper portion of the apparatus main body 61, and the support plates 113 are opposed to the upper inner side of the apparatus main body 61. Then, the rotation shafts 114 and 114 are installed horizontally along the inner wall of the apparatus main body 61 so that the front ends of the support plates 113 and 113 can be airtightly overlapped.

前記補助筒112の内側には、案内板115,115を漏斗状に傾斜して対向設置し、かつ案内板115,115の下端面と支持板113,113の上面とは気密に当接するのが好ましい。このようにして、装置本体61の上部の補助筒112は、支持板113,113と、蓋116により二重に気密を保たれる。   Inside the auxiliary cylinder 112, the guide plates 115, 115 are inclined and arranged in a funnel shape, and the lower end surfaces of the guide plates 115, 115 and the upper surfaces of the support plates 113, 113 are in airtight contact. preferable. In this way, the auxiliary cylinder 112 on the upper part of the apparatus main body 61 is double-tightened by the support plates 113 and 113 and the lid 116.

前記において、装置本体61の下部の処理物が分解し、上部の処理物が矢示117のように移動し、支持板113,113を水平に戻すことができるようになったならば、回転軸114,114のハンドル118,118を矢示119,119のように回動して、支持板113,113を水平位置に戻し、ハンドル118,118をロックすれば、装置本体61の上部を密閉することができる。そこで蓋116を矢示121のように開いても、装置本体61内の排気が外部に洩れるおそれはない。   In the above description, if the processed product at the lower part of the apparatus main body 61 is disassembled and the processed product at the upper part moves as indicated by an arrow 117 so that the support plates 113 and 113 can be returned to the horizontal position, the rotating shaft When the handles 118 and 118 of the 114 and 114 are rotated as indicated by arrows 119 and 119 to return the support plates 113 and 113 to the horizontal position and the handles 118 and 118 are locked, the upper portion of the apparatus main body 61 is sealed. be able to. Therefore, even if the lid 116 is opened as indicated by an arrow 121, there is no possibility that the exhaust in the apparatus main body 61 leaks to the outside.

そこで支持板113,113上へ処理物122を収容した後に、蓋116を密閉し、ハンドル118,118を矢示123,123のように回動して、支持板113,113を矢示124,124のように開放すれば、処理物122は自重により矢示126のように落下する。この場合に蓋116は密閉してあるので、処理装置内の排気が外界へ排出されるおそれはない。前記のように、支持板113,113と、蓋116とを利用して処理物122を補充する時の排気洩れを未然に防止することができる。   Then, after accommodating the processed material 122 on the support plates 113 and 113, the lid 116 is sealed, and the handles 118 and 118 are rotated as indicated by arrows 123 and 123, so that the support plates 113 and 113 are indicated by arrows 124, If it opens like 124, the processed material 122 will fall like an arrow 126 with dead weight. In this case, since the lid 116 is sealed, there is no possibility that the exhaust in the processing apparatus is discharged to the outside. As described above, exhaust leakage when replenishing the processed material 122 using the support plates 113 and 113 and the lid 116 can be prevented in advance.

この発明の消臭処理の他の実施例を図22に基づいて説明する。消臭処理については、処理槽18(図10)において説明したが、この実施例6は前記実施例2とは異なるものである。即ち縦断面方形の処理槽130内を複数の仕切板131a、131bにより複数室(例えば8室)に分割する。前記仕切板131aは下端部に通気口132を設けてあり、仕切板131bは下端部に通水口133を設け、上端部に通気口134が設けてある。従って排気管17から矢示136のように入った煙は、矢示137,138,139,140,141,142、143,144,145のように流動し、排気管46から外界へ放出される。   Another embodiment of the deodorizing process of the present invention will be described with reference to FIG. Although the deodorizing process has been described in the processing tank 18 (FIG. 10), the sixth embodiment is different from the second embodiment. That is, the inside of the processing tank 130 having a rectangular cross section is divided into a plurality of chambers (for example, eight chambers) by a plurality of partition plates 131a and 131b. The partition plate 131a is provided with a vent 132 at the lower end, and the partition plate 131b is provided with a water vent 133 at the lower end and a vent 134 at the upper end. Therefore, the smoke that has entered from the exhaust pipe 17 as indicated by arrow 136 flows as indicated by arrows 137, 138, 139, 140, 141, 142, 143, 144, and 145 and is discharged from the exhaust pipe 46 to the outside. .

前記処理槽130の上部内側には送水パイプ146が架設され、送水パイプ146には複数の撒水パイプ147,147が連結してある。また、処理槽130の下部には、ポンプ室148が設置され、ポンプ室148に浄化室149が連設されている。そこで撒水パイプ147から矢示150のように撒水された水は、処理槽130の底上を矢示151のように流動して浄化室149に入り、セラミックスボールよりなる濾層175を通過し、フィルター152を通過してポンプ室148に入る。そこでポンプ室148内の水中ポンプ153により、給水パイプ154から送水パイプ146を経て撒水パイプ147に送水され、撒水パイプ147から撒水される。   A water supply pipe 146 is installed inside the upper part of the treatment tank 130, and a plurality of flooding pipes 147 and 147 are connected to the water supply pipe 146. In addition, a pump chamber 148 is installed in the lower part of the processing tank 130, and a purification chamber 149 is connected to the pump chamber 148. Then, the water that has been flooded from the flooded pipe 147 as indicated by arrow 150 flows on the bottom of the treatment tank 130 as indicated by arrow 151, enters the purification chamber 149, passes through the filter layer 175 made of ceramic balls, Passes through the filter 152 and enters the pump chamber 148. Therefore, the submersible pump 153 in the pump chamber 148 supplies water from the water supply pipe 154 through the water supply pipe 146 to the flooded pipe 147 and then floods from the flooded pipe 147.

前記セラミックスボールは、例えばSiO,Al,NaO、KO、又はSiO、Al,NaO,TiOの成分よりなる直径5mm〜20mmの麦飯石のハードセラミックスボールであって、前記ポンプによる循環水は、前記セラミックスボールによって浄化される。セラミックスボールは遠赤外線を発生し、水中の有機物を分解するので、いわゆる自浄能力があり、長期間連続して使用することができる。試用運転によれば、6ヶ月〜1年間連続使用しても自浄能力は劣化しなかった。 The ceramic balls are, for example, hard barley stones having a diameter of 5 mm to 20 mm made of SiO 2 , Al 2 O 3 , Na 2 O, K 2 O, or SiO 2 , Al 2 O 3 , Na 2 O, TiO 2 components. In the ceramic ball, the circulating water by the pump is purified by the ceramic ball. Ceramic balls generate far infrared rays and decompose organic substances in water, so that they have a so-called self-cleaning ability and can be used continuously for a long time. According to the trial operation, the self-cleaning ability did not deteriorate even after 6 months to 1 year of continuous use.

前記セラミックスボールに代えて、ゼオライトと貝化石の混合物を濾層として使用することも有効であるが、この発明のような有機物の磁化分解により生じる排水浄化については更なる検討を要する。   It is also effective to use a mixture of zeolite and shell fossil as a filter layer in place of the ceramic balls, but further examination is required for the purification of waste water caused by the magnetic decomposition of organic matter as in the present invention.

前記浄化室149の下部に、固形物(主として砂177)が沈澱した際には、ドレインパイプ178から矢示176のように排出する。前記固形物177は、セラミックスボールによって浄化されているので、外界へ取り出しても臭気などがなく、環境汚染のおそれもなく自由に放棄することができる。   When solid matter (mainly sand 177) is deposited in the lower part of the purification chamber 149, it is discharged from the drain pipe 178 as indicated by an arrow 176. Since the solid 177 is purified by a ceramic ball, there is no odor even if it is taken out to the outside, and it can be abandoned freely without fear of environmental pollution.

またポンプ室148内の循環水が減少した場合には、給水パイプ178から矢示のように自由に給水することができるので、循環水の不足を来すおそれはない。前記排気管46に磁気脱臭器135を設置する場合がある。前記磁気脱臭器135には、0.3テスラ(3000ガウス)〜0.4テスラ(4000ガウス)の強磁場が設けられており、通過排気の臭気を分解することができる。例えばゴム材を処理した場合のように、脱臭処理後でも若干の臭気が残留した場合などに有効な脱臭効果がある。   Further, when the circulating water in the pump chamber 148 decreases, the water can be freely supplied from the water supply pipe 178 as shown by the arrow, so there is no possibility of causing shortage of the circulating water. A magnetic deodorizer 135 may be installed in the exhaust pipe 46. The magnetic deodorizer 135 is provided with a strong magnetic field of 0.3 Tesla (3000 Gauss) to 0.4 Tesla (4000 Gauss), and can decompose the odor of the passing exhaust gas. For example, there is an effective deodorizing effect when a slight odor remains even after the deodorizing process, such as when a rubber material is processed.

この発明の処理物の一括装入についての実施例を図23に基づいて説明する。前記実施例5において、開蓋時に臭気の洩れない装入装置について説明したが、図23は前記図21と趣旨を等しくし、構造の異なる装入装置である。そこで、前記装置と実施例7の装置とは処理物の性質に応じて、適宜選択使用することが好ましい。即ち装置本体160の頂板161の投入口縁に、ホッパー162の下端部を連設し、前記投入口159に仕切蓋163を開閉自在に被冠する。前記ホッパー162の口部に口蓋164を開閉自在に被冠する。   An embodiment of batch loading of processed materials according to the present invention will be described with reference to FIG. In the fifth embodiment, the charging device that does not leak odor when the lid is opened has been described. FIG. 23 is a charging device having the same concept as that of FIG. Therefore, it is preferable to appropriately select and use the apparatus and the apparatus of Example 7 according to the properties of the processed material. That is, the lower end portion of the hopper 162 is connected to the insertion port edge of the top plate 161 of the apparatus main body 160, and the partition lid 163 is covered with the input port 159 so as to be freely opened and closed. A palate 164 is crowned on the mouth of the hopper 162 so as to be freely opened and closed.

前記仕切蓋163の上面に該仕切蓋163の開閉方向と平行して、二条の溝155を設け、この溝155内へ夫々ラツク165,165を溝内に設け、前記ラツク165,165にピニオン166を噛み合わせ、ピニオン166の軸167は減速モータ168の軸と連結してある。前記のように、ラツク165を溝内に設けることにより、前記仕切り蓋163とその上面当接部の気密保持を容易にしている。   Two grooves 155 are provided on the upper surface of the partition lid 163 in parallel with the opening / closing direction of the partition lid 163, and racks 165 and 165 are provided in the grooves 155, respectively, and pinions 166 are provided on the racks 165 and 165. The shaft 167 of the pinion 166 is connected to the shaft of the reduction motor 168. As described above, by providing the rack 165 in the groove, the partition lid 163 and its upper surface contact portion can be easily kept airtight.

前記において、モータ168を始動し、ピニオン166を矢示169の方向へ回転すると、仕切蓋163は矢示170の方向へ移動し、開蓋することになり、ピニオン166を前記と逆に矢示175の方向へ回転すると、仕切蓋163は閉蓋することになる。また前記装置本体160の内側壁には、熱交換器171を設置してある。図中172は給水パイプ、173は給湯パイプである。前記熱交換器171の具体的形状については規制はないので、従来知られている気水間の熱交換に用いる熱交換器と同様である。従って多管式、又は薄盤式の何れも使用することができる。前記溝155内へラツク165を設け、ラツクの上端が、溝155から突出しないようにしてある。   In the above, when the motor 168 is started and the pinion 166 is rotated in the direction of the arrow 169, the partition lid 163 moves in the direction of the arrow 170 and opens, and the pinion 166 is indicated by the arrow in the opposite direction. When rotating in the direction of 175, the partition lid 163 is closed. A heat exchanger 171 is installed on the inner wall of the apparatus main body 160. In the figure, 172 is a water supply pipe, and 173 is a hot water supply pipe. Since there is no restriction | limiting about the specific shape of the said heat exchanger 171, it is the same as that of the heat exchanger used for the heat exchange between the conventionally known steam. Therefore, either a multi-tube type or a thin plate type can be used. A rack 165 is provided in the groove 155 so that the upper end of the rack does not protrude from the groove 155.

前記熱交換器171は、装置本体160の内側中央部から上方にかけて設置されているので、排気温を低下させたり、壁面からの熱放散を防止する効果があるが、処理物の分解効率を低下させるおそれはない。何故ならば、熱交換器171を設置しても処理物の分解部分の温度低下を来すおそれはないからである。   Since the heat exchanger 171 is installed from the inner central portion of the apparatus main body 160 to the upper side, the heat exchanger 171 has an effect of lowering the exhaust temperature and preventing the heat dissipation from the wall surface, but lowers the decomposition efficiency of the processed material. There is no fear. This is because even if the heat exchanger 171 is installed, there is no possibility that the temperature of the decomposed portion of the processed product will decrease.

前記実施例において、処理物125を投入する場合には、仕切蓋163を閉じた後口蓋164を開いて、処理物125をホッパー162内へ矢示127のように投入する。次いで、口蓋164をとじてから仕切蓋163を開くと、処理物は自重により装置本体160内へ矢示128のように落下する。また装置本体160内に、ホッパー内の処理物が全部落下するだけの空間がない場合には、ホッパー内に処理物125が残留するけれども、口蓋164が閉鎖しているので排気が外部へ洩れるおそれはない。即ち処理物投入時の排気の外界への洩れは未然に防止される。   In the above-described embodiment, when the processed material 125 is charged, the partition lid 163 is closed, the mouth lid 164 is opened, and the processed material 125 is loaded into the hopper 162 as indicated by an arrow 127. Next, when the partition lid 163 is opened after closing the palate 164, the processed material falls into the apparatus main body 160 by its own weight as indicated by an arrow 128. Further, when there is not enough space in the apparatus main body 160 to drop all the processed material in the hopper, the processed material 125 remains in the hopper, but the palate 164 is closed, so that the exhaust leaks to the outside. It is not. That is, the leakage of the exhaust gas to the outside at the time of introducing the treatment object is prevented in advance.

この発明の他の実施例(処理物の自動供給)を図24に基づいて説明すると、装置本体180の上部頂板181の落下興79上にへホッパー182を連設し、前記ホッパー182の口部へ開閉蓋183を開閉自在に設置する。前記ホッパー182は装置本体180による1日(24時間)の処理量(例えば1m4時間で処理できる容量ならば6m)を収容できるようにしてある。前記落下口179には、仕切蓋174が開閉自在に設けてある。この仕切蓋174は自動又は手動で矢示159のように摺動し、開閉できるようになっている。 Another embodiment of the present invention (automatic supply of the processed material) will be described with reference to FIG. 24. A hopper 182 is continuously provided on the falling top 79 of the upper top plate 181 of the apparatus main body 180, and the mouth portion of the hopper 182 is provided. An open / close lid 183 is installed to be openable and closable. The hopper 182 can accommodate a processing amount of one day (24 hours) by the apparatus main body 180 (for example, 6 m 3 if the capacity can be processed in 1 m 3 4 hours). A partition lid 174 is provided at the dropping port 179 so as to be freely opened and closed. The partition lid 174 can be opened or closed by sliding automatically or manually as indicated by an arrow 159.

前記実施例において、開閉蓋183は、エアシリンダー184のロッド185を矢示186の方向へ突き出すことにより閉蓋し、矢示187の方向へ引っ込めることにより開蓋する。図中188,189は給排気パイプである。前記給気はコンプレッサー(図示してない)から送られ、各給排気パイプ188,189に介装してあるバルブ(図示してない)により調節する。即ち給排気パイプ188に加圧空気を供給すると、ロッド185に固定してあるピストン(図示してない)が矢示187の方向へ移動するので、ロッドも同方向へ移動し、開閉蓋183は支軸190を中心にして矢示191の方向へ回転するので開蓋する。   In the above embodiment, the open / close lid 183 is closed by protruding the rod 185 of the air cylinder 184 in the direction of the arrow 186 and opened by retracting in the direction of the arrow 187. In the figure, reference numerals 188 and 189 denote supply and exhaust pipes. The supply air is supplied from a compressor (not shown) and is adjusted by a valve (not shown) interposed in each of the supply and exhaust pipes 188 and 189. That is, when pressurized air is supplied to the supply / exhaust pipe 188, a piston (not shown) fixed to the rod 185 moves in the direction of the arrow 187, so the rod also moves in the same direction, and the opening / closing lid 183 Since it rotates in the direction of the arrow 191 around the support shaft 190, the lid is opened.

次に給排気パイプ189に加圧空気を供給すると、ロッド185に固定してあるピストンは矢示186の方向へ移動するので、開閉蓋183は支軸190を中心にして矢示192の方向へ回転するので開閉蓋183は閉蓋することになる。   Next, when pressurized air is supplied to the air supply / exhaust pipe 189, the piston fixed to the rod 185 moves in the direction of the arrow 186, so that the opening / closing lid 183 is centered on the support shaft 190 in the direction of the arrow 192. Since it rotates, the open / close lid 183 is closed.

前記はエアシリンダー184を利用した開閉蓋183の操作であるから、詳細な説明は省略した。図中193は排気パイプ、194は処理物を投入する際に用いるベルトコンベアである。     Since the above is the operation of the opening / closing lid 183 using the air cylinder 184, the detailed description is omitted. In the figure, 193 is an exhaust pipe, and 194 is a belt conveyor used when a processed material is introduced.

1 装置本体
2 底板
3 加熱室
4 処理室
5 投入口
6 頂板
7 開閉蓋
8 給気パイプ
9 送気パイプ
10 処理装置
11 磁化筒
12 バルブ
13 通気管
14 バルブハンドル
15 連結パイプ
16 永久磁石
17 排気管
18 消煙・消臭の処理槽
19 仕切板
20 撒水パイプ
29 排水パイプ
31 通過パイプ
32 排出パイプ
33 永久磁石
55 支軸
57 ヘッダー管
58 回転軸
59 撹拌板
60 ハンドル
61 装置本体
63 加熱室
64 処理室
65 排気筒
67 開閉蓋
68 給気パイプ
69 排気ホース
70 排気ポンプ
71 磁化ケース
73 通気管
79 処理槽
80 廃棄パイプ
81 排気パイプ
82 遠心分離機
97 乾燥室
100 吸引器
102 冷却器
103 過熱器
130 処理槽
131a 仕切板
131b 仕切板
148 ポンプ室
149 浄水室
160 装置本体
163 仕切蓋
164 口蓋
171 熱交換器
174 仕切蓋
180 装置本体
DESCRIPTION OF SYMBOLS 1 Apparatus main body 2 Bottom plate 3 Heating chamber 4 Processing chamber 5 Input port 6 Top plate 7 Opening and closing lid 8 Air supply pipe 9 Air supply pipe 10 Processing apparatus 11 Magnetizing cylinder 12 Valve 13 Vent pipe 14 Valve handle 15 Connection pipe 16 Permanent magnet 17 Exhaust pipe 18 Smoke / deodorant treatment tank 19 Partition plate 20 Flooded pipe 29 Drain pipe 31 Passing pipe 32 Discharge pipe 33 Permanent magnet 55 Support shaft 57 Header pipe 58 Rotating shaft 59 Stirring plate 60 Handle 61 Apparatus body 63 Heating chamber 64 Processing chamber 65 Exhaust cylinder 67 Opening / closing lid 68 Air supply pipe 69 Exhaust hose 70 Exhaust pump 71 Magnetizing case 73 Vent pipe 79 Treatment tank 80 Disposal pipe 81 Exhaust pipe 82 Centrifuge 97 Drying chamber 100 Suction device 102 Cooler 103 Superheater 130 Treatment tank 131a Partition plate 131b Partition plate 148 Pump chamber 149 Water purification chamber 160 Device body 163 Setsufuta 164 palate 171 heat exchanger 174 the partition cover 180 device body

Claims (13)

処理装置の上部から処理物を投入し、該処理物の中央下部を加温し上昇気流を生起し、処理装置の内側壁部に下降気流を生起して磁化空気を上下対流させて、0.25テスラ〜1.0テスラの磁場を通過した磁化空気を処理物内に導き、前記処理物をその下部から順次分解処理することにより、前記処理物を炭化し、次いで灰化させると共に、前記処理装置の一側上部の排気管からの排気に伴って、前記処理装置の下部内側に磁化空気を流入させ、前記処理物の処理の進行に伴い、前記処理物はその上部の未分解部分の自重が加えられて順次下降してその空洞化が防止され、前記処理物の減少に伴い、新しい処理物を間欠投入することにより、処理物を自動連続分解処理することを特徴とした処理物の低温分解処理方法。   A processing object is introduced from the upper part of the processing apparatus, the lower central part of the processing object is heated to generate an ascending air current, a descending air current is generated on the inner wall of the processing apparatus, and magnetized air is vertically convected. The magnetized air that has passed through a magnetic field of 25 Tesla to 1.0 Tesla is guided into the treatment object, and the treatment object is sequentially decomposed from the lower part thereof to carbonize the treatment object, and then ash it. With the exhaust from the exhaust pipe on the upper side of the apparatus, magnetized air is allowed to flow into the lower inner side of the processing apparatus, and as the processing of the processed object proceeds, the processed object has its own undecomposed portion weight. Is added to prevent the hollowing out of the processed material, and with the decrease in the processed material, the processed material is automatically continuously decomposed by intermittently introducing a new processed material. Decomposition method. 処理装置からの排気に伴って、磁化空気を自動流入させると共に、該流入空気量を調節できるようにすることを特徴とした請求項1記載の処理物の低温分解処理方法。   2. The method for low-temperature decomposition of a processed product according to claim 1, wherein magnetized air is automatically flowed in along with the exhaust from the processing apparatus, and the amount of the flow-in air can be adjusted. 磁化空気は、処理装置の下部側壁から、中央部にかけて装置内へ上下複数段に突出設置した給気管から流出させることを特徴とした請求項1記載の処理物の低温分解処理方法。   2. The method for low-temperature decomposition of a processed product according to claim 1, wherein the magnetized air is caused to flow out from a supply pipe projecting and installed in a plurality of upper and lower stages into the apparatus from the lower side wall of the processing apparatus toward the center. 処理装置の内壁に熱交換器を設置して、内部気体と水とを熱交換させ、温水を生成することを特徴とした請求項1記載の処理物の低温分解処理方法。   The method for low-temperature decomposition treatment of a treated product according to claim 1, wherein a heat exchanger is installed on the inner wall of the treatment apparatus to exchange heat between the internal gas and water to generate hot water. 排気管からの排気は、消煙、消臭処理槽内の循環水で撒水処理されて消煙、消臭処理されることを特徴とした請求項1記載の処理物の低温分解処理方法。   2. The method for low-temperature decomposition treatment of a treated product according to claim 1, wherein the exhaust from the exhaust pipe is subjected to a soaking treatment with circulating water in the smoke-eliminating / deodorizing treatment tank and smoke-deodorizing treatment is performed. 処理物の処理が進行し、処理装置の上部に空隙が生じた際に新しい処理物を排気を排出することなく投入する間欠投入方式とすることを特徴とした請求項1記載の処理物の低温分解処理方法。   2. The low temperature of the processed product according to claim 1, wherein an intermittent charging method is employed in which a new processed product is input without discharging exhaust gas when processing of the processed product proceeds and a gap is generated in the upper portion of the processing apparatus. Decomposition method. 空洞化防止は、投入処理物の中部下部付近を定期的又は不定期的に撹拌し、又は処理物の自重により架橋を防止することを特徴とした請求項1記載の処理物の低温分解処理方法。   2. The method of low-temperature decomposition treatment of a treated product according to claim 1, wherein the prevention of cavitation is performed by periodically or irregularly stirring the vicinity of the lower part of the middle of the input treated product, or preventing crosslinking by the weight of the treated product. . 処理装置の上部内側に処理物の投入ホッパーを設け、該投入ホッパーの下部に仕切板を設け、上部に開閉蓋を設けて、前記仕切板と開閉蓋を交互に開閉させて処理物を投入させることを特徴とした請求項1記載の処理物の低温分解処理方法。   A processing material input hopper is provided inside the upper part of the processing apparatus, a partition plate is provided at the lower part of the input hopper, an opening / closing lid is provided at the upper part, and the partition plate and the opening / closing lid are alternately opened and closed to input the processing object. The low-temperature decomposition processing method of the processed material of Claim 1 characterized by the above-mentioned. 有底筒状の処理装置の下部に、加熱室を設け、該加熱室の上部に処理物を収容し、磁化空気を給気して、処理する2重壁の処理室を連設し、前記加熱室と処理室の下部に、磁化空気の給気管を側壁から中央部に向けて上下多段に複数水平方向に設置し、前記給気管は、流入空気を磁化する磁化筒に連設し、前記処理室の上部に処理物の投入口を設けると共に、排気管を連設し、前記投入口へ開閉蓋を被冠し、前記排気管に処理槽を連結し、該処理槽内に撒水管と撒水の循環装置を設けて前記処理室内の上下対流の為に2重壁の上下部へ通気口を設け、前記加熱室の側壁下部に、開閉蓋付残渣取り出し口を設けたことを特徴とする処理物の低温分解処理装置。   A heating chamber is provided in the lower part of the bottomed cylindrical processing apparatus, a processing object is accommodated in the upper part of the heating chamber, magnetized air is supplied, and a double-walled processing chamber for processing is continuously provided, In the lower part of the heating chamber and the processing chamber, magnetized air supply pipes are installed in a plurality of horizontal directions in multiple upper and lower stages from the side wall toward the central part, and the air supply pipes are connected to a magnetized cylinder for magnetizing the inflow air, Provided with a processing material inlet at the top of the processing chamber, and connected to an exhaust pipe, covered with an opening / closing lid, connected to the exhaust pipe, a processing tank, and a submerged pipe in the processing tank A water circulation device is provided, vents are provided above and below the double wall for vertical convection in the processing chamber, and a residue outlet with an open / close lid is provided at the bottom of the side wall of the heating chamber. Low-temperature decomposition processing equipment for processed products. 有底筒状の処理装置の下部に、加熱室を設け、該加熱室の上部に処理物を収容し、磁化空気を給気して、処理する2重壁の処理室を連設し、前記加熱室と処理室の下部に、磁化空気の給気管を側壁から中央部に向けて上下多段に複数水平方向に設置し、前記給気管は、流入空気を磁化する磁化筒に連設し、前記処理室の上部に処理物の投入口を設けると共に、排気管を連設し、前記投入口へ開閉蓋を被冠し、前記排気管に処理槽を連結し、前記処理室内の上下対流の為に2重壁の上下部へ通気口を設け、前記処理室の内側壁へ熱交換器を設置したことを特徴とする処理物の低温分解処理装置。   A heating chamber is provided in the lower part of the bottomed cylindrical processing apparatus, a processing object is accommodated in the upper part of the heating chamber, magnetized air is supplied, and a double-walled processing chamber for processing is continuously provided, In the lower part of the heating chamber and the processing chamber, magnetized air supply pipes are installed in a plurality of horizontal directions in multiple upper and lower stages from the side wall toward the central part, and the air supply pipes are connected to a magnetized cylinder for magnetizing the inflow air, Provided with a processing material inlet at the upper part of the processing chamber, connected to an exhaust pipe, covered with an opening / closing lid, connected to a processing tank to the exhaust pipe, for vertical convection in the processing chamber A low-temperature decomposition treatment apparatus for a treated product, wherein a vent is provided in the upper and lower portions of the double wall, and a heat exchanger is installed on the inner wall of the treatment chamber. 処理槽は、複数の仕切板で縦に仕切り、排気の上下屈曲流動路を設けると共に、撒水により消煙、消臭することを特徴とした請求項9又は10記載の処理物の低温分解処理装置。   The processing tank low-temperature decomposition treatment apparatus according to claim 9 or 10, characterized in that the treatment tank is vertically partitioned by a plurality of partition plates, and is provided with a vertically bent flow path for exhaust gas, and smoke is removed and deodorized by flooding. . 磁化筒内には、一端に磁化空気の給気管を連結し、他端を外界に開口し、中央部に高磁化用の永久磁石を介装した通気管を内装したことを特徴とする請求項9又は10記載の処理物の低温分解処理装置。   The magnetized cylinder is provided with a magnetized air supply pipe connected to one end, the other end opened to the outside, and a vent pipe interposing a permanent magnet for high magnetization at the center. The low-temperature decomposition processing apparatus of the processed material of 9 or 10. 処理槽の撒水は、濾過層を経て循環流動装置によることとした請求項9又は10記載の処理物の低温分解処理装置。   The low-temperature decomposition treatment apparatus for processed products according to claim 9 or 10, wherein the brine in the treatment tank is obtained by a circulating fluidizer through a filtration layer.
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