JP2013010088A - Magnetic decomposition treatment apparatus for organic matter - Google Patents

Magnetic decomposition treatment apparatus for organic matter Download PDF

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JP2013010088A
JP2013010088A JP2011145832A JP2011145832A JP2013010088A JP 2013010088 A JP2013010088 A JP 2013010088A JP 2011145832 A JP2011145832 A JP 2011145832A JP 2011145832 A JP2011145832 A JP 2011145832A JP 2013010088 A JP2013010088 A JP 2013010088A
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organic matter
decomposition
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Akio Shigeta
昭夫 重田
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ESUJEKKU KK
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Abstract

PROBLEM TO BE SOLVED: To provide a magnetic decomposition treatment apparatus for waste organic matter whose purpose is to improve the treatment efficiency of magnetic decomposition treatment apparatus for organic matter.SOLUTION: The apparatus includes an organic matter input port with a seal lid at the top of a cylindrical treatment tank, and a magnetic air blowing nozzle is arranged at the lower part to decompose the organic matter stored inside the treatment tank by magnetic air. At least two sidewalls of the treatment tank are triple-wall via small gaps, and a plurality of small holes to pass the decomposition gas are provided on the inner wall of the triple-wall. The small gap continuous with the small holes is a gap for a downward passage for the decomposition gas, and the top and bottom of the gap outside of it is open and the gap is made to be a gap for circulation of the decomposition gas.

Description

この発明は、廃棄有機物を強磁場を通過した空気により分解することを目的とした廃棄有機物の磁気分解処理装置に関する。   The present invention relates to a waste organic matter magnetic decomposition treatment apparatus for the purpose of decomposing waste organic matter with air that has passed a strong magnetic field.

従来、廃棄有機物の低温磁気分解処理については、数件の提案がされており、実用化の域に達している装置もあるが、未だ実験中の装置が大部分であり、産業上広く利用される域に達していない。   Conventionally, several proposals have been made for low-temperature magnetic decomposition treatment of organic waste, and there are some devices that have reached practical use, but most of the devices are still being used and are widely used in industry. The area has not been reached.

特開2008−190733号公報JP 2008-190733 A 特許第433712号公報Japanese Patent No. 433712 特開2010−270980号公報JP 2010-270980 A

廃棄有機物の磁気分解処理について、幾多の提案があることは前記のとおりである。例えば、250℃〜400℃の酸素を制限した活性熱気体を、廃棄有機物の中へ吹き込み、該有機物を分解する方法と装置が提案されている(特許文献1)。   As described above, there are many proposals regarding the magnetic decomposition treatment of waste organic matter. For example, a method and an apparatus have been proposed in which an active hot gas in which oxygen at 250 ° C. to 400 ° C. is limited is blown into waste organic matter to decompose the organic matter (Patent Document 1).

また、処理すべき有機物の下部へ磁化空気を給気し、分解された気体を下降させて、前記磁化空気と共に上下対流させ、前記有機物を分解させるようにした低温分解処理装置も提案されている(特許文献2)。   Also proposed is a low-temperature decomposition treatment apparatus in which magnetized air is supplied to the lower part of the organic matter to be treated, the decomposed gas is lowered, and the organic matter is decomposed by vertically convection with the magnetized air. (Patent Document 2).

更に、磁場を通過させた空気を有機物に接触させて分解する低温熱分解炉の提案もある(特許文献3)。   Furthermore, there is also a proposal of a low-temperature pyrolysis furnace that decomposes air that has passed through a magnetic field by bringing it into contact with organic matter (Patent Document 3).

前記各発明については、それぞれ特徴があって、実施できるものと認められるが、磁気分解の効率向上の点については未だ不十分と認められる。   Each of the above inventions has its own characteristics and is recognized as being feasible, but it is still considered insufficient in terms of improving the efficiency of magnetic decomposition.

前記各発明において、処理効率の向上が難しい理由の一つは、磁気分解に際し、多量の水分が生成され、これを気化し、又は微粒水分として排出すると多くのエネルギーを消失するものと認められるからである。   In each of the above inventions, one of the reasons why it is difficult to improve the processing efficiency is that a large amount of water is generated during magnetic decomposition, and it is recognized that a large amount of energy is lost when vaporized or discharged as fine water. It is.

この発明は、磁気分解気体中の水分を分離排除して、前記処理効率の向上を図ることを目的としたものである。   The object of the present invention is to improve the processing efficiency by separating and removing moisture in the magnetic decomposition gas.

この発明は、磁気分解により生成された気体中に水の微粒子が多量に含まれることに着目し、前記水粒子を側壁に沿って下降させ、冷却させることにより下降気体中の水粒子を分離し、水滴に変化させることに成功した。   The present invention pays attention to the fact that a large amount of fine water particles are contained in the gas generated by the magnetic decomposition, and the water particles in the descending gas are separated by lowering and cooling the water particles along the side wall. , Succeeded in changing to water droplets.

即ち、廃棄有機物の分解によって、装置の上部の気圧が必然的に高くなるので、装置の側壁を小間隙による三重壁とし、最内壁に多数の小孔を設けた。そして、上下の気圧差を利用し、水分を含む気体を下降させ、この下降気体の温度を下げることにより水分を分離したのである。   That is, since the atmospheric pressure in the upper part of the apparatus inevitably increases due to decomposition of the waste organic matter, the side wall of the apparatus is a triple wall with a small gap, and a large number of small holes are provided in the innermost wall. Then, using the difference between the upper and lower atmospheric pressures, the moisture-containing gas is lowered and the moisture is separated by lowering the temperature of the descending gas.

前記有機物の分解に際しては、分解熱により装置内は100℃〜300℃位になり、有機物に含まれた水分は水蒸気となって分解された気体と共に上昇するので、装置内の上部の気圧が上昇する。   When the organic matter is decomposed, the inside of the apparatus becomes about 100 ° C. to 300 ° C. due to the heat of decomposition, and the moisture contained in the organic substance rises with the decomposed gas as water vapor. To do.

前記装置は、例えば角筒状の処理槽であって、上端部は有機物投入口となっており、該投入口は開閉蓋により密封する。前記処理槽の上と中央部は有機物の収容部であって、該部は有機物の分解処理部である。また、下部内側は、灰の集積場所であると共に、磁化空気吹出し用の複数のノズルが設置されている。   The apparatus is, for example, a rectangular tube-shaped treatment tank, and an upper end portion is an organic substance inlet, and the inlet is sealed with an open / close lid. The upper part and the center part of the treatment tank are organic substance storage parts, which are organic substance decomposition treatment parts. In addition, the lower inner side is an accumulation place of ash and a plurality of nozzles for blowing magnetized air are installed.

前記ノズルは、収容した有機物の下部へ磁化空気を均等に吹き付けるべく、底板上に均等に配置されている。前記底板上には灰が溜まるので、前記ノズルは灰に埋まらないような配慮が必要である。   The nozzles are evenly arranged on the bottom plate so as to uniformly blow magnetized air to the lower part of the organic matter contained. Since ash accumulates on the bottom plate, it is necessary to consider that the nozzle is not buried in the ash.

この発明の処理槽は、四周を三重壁とし、各壁間に小間隙を設けて、水蒸気の多い排気体と分解気体の多い排気体とを下降させる排気路としてある。前記最内側の側壁には多数の小孔が穿設してあり、水蒸気及び分解気体を自動的に吸入し、排気路内を下降させ、冷却して水蒸気を水滴とする。前記において、処理槽内の上部は高気圧となり、下部は低気圧となるので、小間隙は必然的に下降気体の通路となり、中央部の上昇気体と循環流動する。   The treatment tank according to the present invention has a triple wall around the four sides and a small gap between the walls, and serves as an exhaust path for lowering the exhaust body rich in water vapor and the exhaust body rich in cracked gas. A large number of small holes are formed in the innermost side wall, and water vapor and decomposition gas are automatically sucked, lowered in the exhaust passage, and cooled to form water vapor as water droplets. In the above, since the upper part in the processing tank is at high pressure and the lower part is at low pressure, the small gap inevitably becomes a passage for the descending gas, and circulates and flows with the ascending gas in the central part.

前記磁化空気による分解は化学変化であるから、分解熱を生じ、ほぼ200℃〜350℃となる。即ち、有機物は磁化空気に接触して磁気分解するが、分解熱によって加温(例えば200℃〜350℃)されるので、加温により磁気分解が促進される。   Since the decomposition by the magnetized air is a chemical change, heat of decomposition is generated and the temperature is approximately 200 ° C to 350 ° C. In other words, the organic matter is magnetically decomposed upon contact with the magnetized air, but is heated by decomposition heat (for example, 200 ° C. to 350 ° C.), so that the magnetic decomposition is accelerated by the heating.

前記のように分解した空気は、槽内を上昇し開閉蓋に達すると、外壁側の小間隙に沿って下降し、そのまま槽の下部から排気される。また、排気の一部は、ノズルの吹出し方向に沿って上昇し、磁化空気と共に有機物に接触してこれを分解する。前記において、有機物は自重により下降するので、必然的に混合されて撹拌されるが、撹拌機を付設すれば確実にかつ均等に撹拌することができる。   When the air decomposed as described above rises in the tank and reaches the opening / closing lid, the air descends along the small gap on the outer wall side and is exhausted as it is from the lower part of the tank. Moreover, a part of the exhaust gas rises along the blowing direction of the nozzle, contacts the organic matter together with the magnetized air, and decomposes it. In the above, since the organic matter descends due to its own weight, it is inevitably mixed and stirred, but if a stirrer is provided, it can be stirred reliably and evenly.

前記磁化空気は、強い磁場(例えば0.4テスラ以上)を通過して槽内へ吸入される。この場合に、ファンを用いて吸入量、吸入圧力をコントロールすれば、磁化空気の吹出し量を規制し、分解の進行をコントロールすることができる。この発明においては、有機物へ磁化空気を均等に吹き付けることを必須要件とするものである。   The magnetized air passes through a strong magnetic field (for example, 0.4 Tesla or more) and is sucked into the tank. In this case, if the suction amount and suction pressure are controlled using a fan, the amount of magnetized air blown out can be regulated and the progress of decomposition can be controlled. In the present invention, it is an essential requirement to uniformly spray magnetized air onto the organic matter.

一方、装置の下部は、排気と磁化気体の吹出しなどで比較的気圧が低いので、装置内部の気体は、側壁の小孔から吸入されて、自動的に下降する。そして、比較的低温の下部で冷却され、排気に含まれた水蒸気は水滴となって装置底に溜まることになる。また、下降気体を水分で冷却することもできる。   On the other hand, since the lower part of the apparatus has a relatively low atmospheric pressure due to exhaust and blowing of magnetized gas, the gas inside the apparatus is sucked from the small hole in the side wall and automatically descends. And the water vapor | steam cooled by the comparatively low temperature lower part and contained in exhaust_gas | exhaustion becomes a water droplet, and accumulates on the apparatus bottom. The descending gas can also be cooled with moisture.

即ち、気水分離について特別の装置を設置しなくても、冷却によって水滴が生成され、装置の下部に溜まる。従って、前記により生成された水分を蒸発させるエネルギーは使用されないことになるので、化学分解がスムーズに進行し、結果的に有機物の処理効率を向上させることになる。   That is, even without installing a special device for air-water separation, water droplets are generated by cooling and accumulate in the lower part of the device. Therefore, since the energy for evaporating the water generated as described above is not used, the chemical decomposition proceeds smoothly, and as a result, the processing efficiency of the organic matter is improved.

この発明における磁化空気の吹出ノズルは、前記のように底板上へ上向きに複数均等配置する。これにより磁化空気を有機物へ均等に接触させることができる。元来有機物は、磁化空気に接触すると分解されるから、均等接触は基本条件となる。前記磁化空気は常時上向きに放出されるので、循環気体は上向きに流動することになり、両者は同一方向へ流動する。   In the present invention, a plurality of magnetized air blowing nozzles are equally arranged upward on the bottom plate as described above. Thereby, magnetized air can be made to contact organic substance equally. Since organic substances are originally decomposed when they come into contact with magnetized air, uniform contact is a basic condition. Since the magnetized air is always released upward, the circulating gas flows upward, and both flow in the same direction.

前記において、分解気体は外壁内側の間隙に沿って下降し、一部はノズルからの吹出しに伴って上昇し、再び有機物に接触してその分解を促進させる(循環流動)。前記において、分解気体は分解熱により加温されながら(例えば300℃前後)上昇するので、槽内の上部は気圧が高くなる。一方、槽内の下部は、外界への排気とノズルからの吹出し作用によって気圧が下降する。そこで、槽上部内の高い気圧の気体は、間隙を通って低い気圧の槽下部に至り、必然的に循環流動することになる。   In the above, the decomposition gas descends along the gap inside the outer wall, and part of it rises as it blows from the nozzle, and again comes into contact with the organic matter to promote its decomposition (circulation flow). In the above, the decomposition gas rises while being heated by the decomposition heat (for example, around 300 ° C.), so that the pressure in the upper part in the tank becomes high. On the other hand, at the lower part in the tank, the atmospheric pressure is lowered by the exhaust to the outside and the blowing action from the nozzle. Therefore, the high-pressure gas in the upper part of the tank passes through the gap to reach the lower part of the low-pressure tank, and inevitably circulates and flows.

この発明の処理槽は基本的に角筒又は円筒であり、角筒は通常断面正方形又は矩形である。そして、分解部位と側壁の流通部との処理槽は、断面正方形又は円形が最も普通に考えられる。   The treatment tank of the present invention is basically a square tube or cylinder, and the square tube is usually square or rectangular in cross section. And the processing tank of the decomposition | disassembly site | part and the distribution | circulation part of a side wall can consider the cross-sectional square or circular shape most normally.

次に、有機物の投入時に、処理槽の開閉蓋を開くと内部の気体が排出するおそれがある。(通常処理槽内の気圧は常圧より高い)。そこで、処理槽の上端開口部にホッパーを接続し、ホッパーの基部とホッパーの上部にそれぞれ開閉蓋(例えばスライド蓋)を設置すれば、前記開閉蓋を交互に開放することにより、有機物投入時の排気洩れを未然に防止することができる。   Next, when the organic matter is charged, the internal gas may be discharged if the opening / closing lid of the treatment tank is opened. (The atmospheric pressure in the normal treatment tank is higher than the normal pressure). Therefore, if a hopper is connected to the upper end opening of the treatment tank, and an opening / closing lid (for example, a slide lid) is installed on the base of the hopper and the upper portion of the hopper, the opening / closing lid is opened alternately, so Exhaust leakage can be prevented in advance.

また、磁化装置の大きさは、一定時間に必要な総磁化空気量と磁化空気の適正な流速との関係から容易に導くことができる。前記必要な磁化空気量は予め算定できるので、この点から、磁化空気室の容積、磁化空気の流動断面積及び流速を定める必要がある。要するに、処理すべき有機物へ所定量の磁化空気を均等に吹き付けるようにする。   Further, the size of the magnetizing device can be easily derived from the relationship between the total amount of magnetized air required for a certain time and the appropriate flow velocity of magnetized air. Since the necessary amount of magnetized air can be calculated in advance, it is necessary to determine the volume of the magnetized air chamber, the flow cross-sectional area of the magnetized air, and the flow velocity from this point. In short, a predetermined amount of magnetized air is uniformly sprayed on the organic matter to be treated.

この発明においては、処理装置の中央部へ回転軸を架設し、この回転軸に撹拌羽根を固定する。前記撹拌羽根は、図2中左右一対の軸に取り付けられており、同一軸については、方向の異なる羽根を図1中左右に固定する。そこで、回転軸、例えば右回転させれば、有機物が中央側へ寄せられ、左回転させれば、有機物が側壁側へ寄せられるように左右の羽根はその角度を変えてある。即ち、羽根は単に撹拌だけでなく、有機物の横移動(回転軸と平行)もできる。   In this invention, a rotating shaft is installed at the center of the processing apparatus, and a stirring blade is fixed to the rotating shaft. The agitation blades are attached to a pair of left and right shafts in FIG. 2, and the blades having different directions are fixed to the left and right in FIG. Therefore, the rotation angle, for example, the right and left blades are changed so that the organic matter is moved toward the center when rotated to the right, and the organic matter is moved toward the side wall when rotated to the left. That is, the blade can not only simply agitate but also move the organic substance laterally (parallel to the rotation axis).

また、羽根の外縁に切刃を付けることにより、接触した有機物を部分的に切断することができる。例えば有機物の一部が合成樹脂袋の場合には、袋を破らない限り磁化空気の働きが遅くなり、分解処理時間が長くかかる原因の一つになることがあるので、これを未然に防止する。   Moreover, the organic substance which contacted can be partially cut | disconnected by attaching a cutting blade to the outer edge of a blade | wing. For example, when a part of the organic material is a synthetic resin bag, unless the bag is torn, the action of magnetized air will slow down, which may be one of the causes of a long decomposition treatment time. .

次に、水分の多い有機物(塩素を含む)の場合には、遊離水分が塩素と結合して塩酸が生じ、有毒気体となるおそれがあるので、分解気体中の水分を可及的速やかに水滴とし排水する必要がある。この点からも、この発明は分解気体中の水分を除去するので、塩素を含む有機物であっても分解気体からの塩酸の生成を未然に防止することができる。   Next, in the case of organic substances with a high water content (including chlorine), free water is combined with chlorine to produce hydrochloric acid, which may become a toxic gas. It is necessary to drain. Also from this point, the present invention removes moisture in the cracked gas, so that it is possible to prevent the generation of hydrochloric acid from the cracked gas even if it is an organic substance containing chlorine.

この発明においては、多数のノズルを使用するので、この各ノズルへ磁化空気を均等に送る必要がある。そこで、一方法としては、容量の大きい磁化空気室を作り、該磁化空気室の磁化空気をブロアなどで強制、定量移送することが考えられる。   In the present invention, since a large number of nozzles are used, it is necessary to uniformly send magnetized air to the nozzles. Therefore, as one method, it is conceivable to create a magnetized air chamber having a large capacity and forcibly and quantitatively transfer the magnetized air in the magnetized air chamber with a blower or the like.

前記磁化空気は、加圧流入させることもあるが、循環気体は磁化空気の吹出しによりその速度が助長される。これは溜灰が加温され、溜灰の温度(中央部の温度は200℃〜350℃位)による上昇気流が前記磁化空気の加速原因と考えられる。   The magnetized air may be injected under pressure, but the speed of the circulating gas is promoted by blowing out magnetized air. It is thought that this is because the accumulated ash is heated, and the rising air flow due to the temperature of the accumulated ash (the temperature at the center is about 200 ° C. to 350 ° C.) is the cause of acceleration of the magnetized air.

即ち、前記循環流動の力は、磁化空気の吹出しと灰の加温による上昇流動とが考えられる。更に、煙道へ適度に流動させ、又は処理槽内の下部へ冷水を流動させて排気を冷却し、これにより下部気圧を低くして、内部気圧を調整すれば、内部気体の流動制御をすることができる。   In other words, the force of the circulating flow is considered to be an upward flow caused by blowing out magnetized air and heating ash. Furthermore, the flow of the internal gas is controlled by allowing the air to flow appropriately to the flue, or cooling the exhaust by flowing cold water to the lower part of the treatment tank, thereby lowering the lower atmospheric pressure and adjusting the internal atmospheric pressure. be able to.

この発明によれば、分解により生成した水分を可及的に分離し、水にすることで、水分を蒸発させるのに要したエネルギーが節約されると共に、分解に有効に使用されるので、分解効率を向上させる効果がある。   According to the present invention, the water generated by the decomposition is separated as much as possible, and the water required for evaporating the water is saved and used effectively for the decomposition. It has the effect of improving efficiency.

また、分解により生成した気体の一部を水分混入のまま下降させ、下部で水分を分離するので、上昇気体が軽くなり、磁化空気と共にスムーズに上昇し、磁化空気の吹出しを阻害しないで容易に混合できる効果がある。   In addition, a part of the gas generated by the decomposition is lowered with moisture mixed, and the water is separated at the lower part, so the rising gas becomes lighter and rises smoothly with the magnetized air, easily without disturbing the blowing of magnetized air There is an effect that can be mixed.

更に、水分の上昇が少ないので、塩素などの有害物含む分解気体であっても、塩素と水と結合して有害液(例えば塩酸)の生成を妨げる効果がある。   Furthermore, since the rise in moisture is small, even a decomposed gas containing harmful substances such as chlorine has an effect of preventing the generation of a harmful liquid (for example, hydrochloric acid) by combining with chlorine and water.

また、少なくとも二側壁、可能ならば四側壁へ小孔を設ければ、分解により生成した気体は、それぞれの高さから気圧に応じて下降し、自動的に気圧変化が調整されるので、局部的に高圧部分を生じるおそれがなく、下降した排気中の水蒸気が冷却され水滴となり分離されるので、下部槽内の気圧は低下する。   In addition, if a small hole is provided in at least two side walls, if possible, four side walls, the gas generated by decomposition descends according to the atmospheric pressure from each height, and the change in atmospheric pressure is automatically adjusted. In particular, there is no possibility of generating a high-pressure portion, and the water vapor in the exhaust gas that has descended is cooled and separated as water droplets, so that the atmospheric pressure in the lower tank decreases.

この発明の実施例の一部を省略した縦断正面図。BRIEF DESCRIPTION OF THE DRAWINGS FIG. 同じく一部を省略した縦断側面図。The vertical side view which abbreviate | omitted one part. (a)同じく一部を省略した横断平面図、(b)同じく側壁の一部断面拡大図。(A) The cross-sectional top view which abbreviate | omitted one part, (b) The partial cross-sectional enlarged view of a side wall similarly. 同じく処理槽の上端部にホッパーを設置した実施例の一部を省略した正面図。The front view which abbreviate | omitted a part of Example which similarly installed the hopper in the upper end part of the processing tank.

この発明は、筒状の処理槽の上部内側へ廃棄有機物を収容し、上部を閉塞すると共に、前記有機物の下部へ磁化空気を吹き出して、これにより有機物を順次気体(例えばCO、HO、H、O、Nなど)と灰(無機物)とに分解するものである。即ち、灰以外は前記気体となり排出されるが、前記成分中窒素が化合物を作り、臭気を発することもあるので、この場合には臭気を処理して無色無臭の気体とする排気処理が必要となる。 The present invention accommodates waste organic matter inside the upper part of the cylindrical treatment tank, closes the upper part, and blows out magnetized air to the lower part of the organic matter, whereby the organic matter is sequentially gasified (for example, CO 2 , H 2 O). , H 2 , O 2 , N 2 etc.) and ash (inorganic). That is, other than ash is discharged as the gas, but nitrogen in the component may form a compound and emit an odor. In this case, an exhaust treatment is required to treat the odor to a colorless and odorless gas. Become.

前記磁化空気による処理の際、分解熱を生じるが、ほぼ400℃以下である。従って、有機物の処理は磁気分解を主としており、燃焼とは明らかに異なるので、分解の際の発熱により(例えば200℃〜350℃)、磁化空気と前記加熱気体或いは水蒸気などの気体の中で急速に分解されることになる。   During the treatment with the magnetized air, heat of decomposition is generated, but is approximately 400 ° C. or less. Accordingly, the treatment of organic substances is mainly magnetic decomposition, which is clearly different from combustion. Therefore, due to the heat generated during decomposition (for example, 200 ° C. to 350 ° C.), it is rapidly generated in magnetized air and a gas such as the heated gas or water vapor. Will be disassembled.

有機物の種類によって生成される気体の成分比は異なるが、有機物がその構成成分に分解されて気体となり、固体は無機物(灰)のみになることは明らかである。   Although the component ratio of the gas produced differs depending on the type of the organic substance, it is clear that the organic substance is decomposed into its constituent components to become a gas, and the solid is only an inorganic substance (ash).

前記分解速度は、有機物の材質、大きさ、磁気の強さなどによって大差がある。例えば、0.4テスラ〜0.6テスラの磁場を通過した磁化空気で、平均的な大きさが3cm〜5cmの木片、鋸屑などの場合に、従来の装置では1mの処理に3時間〜4時間かかっていたが、この発明の実施装置を用いた場合には、2.5時間〜3時間で処理できることが確認された。従って、平均25%の効率改善が見込まれた。分解気体の流動状態と水蒸気の処理をすれば、更なる効率の改善が見込まれる。 The decomposition rate varies greatly depending on the material, size, magnetic strength, and the like of the organic substance. For example, in the case of magnetized air that has passed through a magnetic field of 0.4 Tesla to 0.6 Tesla and an average size of 3 cm to 5 cm, such as a piece of wood, sawdust, etc., in a conventional apparatus, it takes 3 hours to process 1 m 3. Although it took 4 hours, it was confirmed that the treatment can be performed in 2.5 to 3 hours when using the apparatus of the present invention. Therefore, an efficiency improvement of 25% on average was expected. If the flow state of the decomposition gas and the water vapor are treated, further improvement in efficiency is expected.

また、前記有機物に、放射性土壌を20%(重量)混入したところ、処理終了時に、灰の放射能は10分の1以下に低減していた。従って、磁気分解に伴って、放射能も低減されることが確認された。前記における放射能の低減については、放射性土壌の場合と、放射性有機物(例えば合成樹脂衣類)とでは、効果に格段の相違が認められたが、処理態様の相違に帰因するものと推定される。   Moreover, when 20% (weight) of radioactive soil was mixed in the organic matter, the radioactivity of ash was reduced to 1/10 or less at the end of the treatment. Therefore, it was confirmed that the radioactivity was reduced with the magnetic decomposition. Regarding the reduction of radioactivity in the above, a marked difference in the effect was observed between radioactive soil and radioactive organic matter (for example, synthetic resin clothing), but it is presumed to be attributed to the difference in treatment mode. .

前記によれば、水蒸気として排気されるべき気体が水滴となるために放出された熱量と、水滴となった時の潜熱とが有効に働くために、化学分解時の熱損失が少なくなり、その分だけ分解効率の向上につながったものと推定される。   According to the above, since the amount of heat released because the gas to be exhausted as water vapor becomes water droplets and the latent heat when it becomes water droplets work effectively, heat loss during chemical decomposition is reduced, It is estimated that the decomposition efficiency was improved by the amount.

この発明の実施例を図1〜3に基づいて説明する。鋼板製の四角筒状外壁1内へ、小間隙1a、1bを介して内壁2、3を順次併設し、三重胴の本体5を構成する。   An embodiment of the present invention will be described with reference to FIGS. An inner wall 2 and 3 are sequentially provided in a rectangular tubular outer wall 1 made of a steel plate via small gaps 1a and 1b to constitute a triple cylinder main body 5.

本体5の内底板4a上には、磁化空気の吹出しノズル6、6を配置する。吹出しノズル6、6は、処理すべき有機物7の下面へ磁化空気を均等に吹き出すことを目的としているので、吹出しノズルの数に応じて均等に配置する。   On the inner bottom plate 4 a of the main body 5, magnetized air blowing nozzles 6 and 6 are arranged. The blow-out nozzles 6 and 6 are intended to blow the magnetized air evenly onto the lower surface of the organic matter 7 to be processed, and therefore are arranged equally according to the number of blow-off nozzles.

前記吹出しノズル6、6は、それぞれパイプ25、25を介して磁化空気室26に連結され、磁化空気室26は、パイプ27を介して磁化室28に連結されている。図中29は磁化室28の吸入パイプである。磁化室28内には、強磁性体が小間隙を介して対向設置され強磁場を構成している。前記吸入パイプ29で吸入した空気は、磁化室28の強磁場を通過し、パイプ27を介して磁化空気室26に送られる。そこで、磁化空気室26からパイプ25を介して吹出しノズル6、6に送られる。前記磁化空気室26とパイプ25との間にブロア40を介在させて、吹出し圧力を調整する。   The blowing nozzles 6 and 6 are connected to a magnetized air chamber 26 via pipes 25 and 25, respectively. The magnetized air chamber 26 is connected to a magnetized chamber 28 via a pipe 27. In the figure, 29 is a suction pipe of the magnetization chamber 28. In the magnetization chamber 28, a ferromagnetic material is installed oppositely through a small gap to constitute a strong magnetic field. The air sucked by the suction pipe 29 passes through the strong magnetic field of the magnetization chamber 28 and is sent to the magnetized air chamber 26 through the pipe 27. Therefore, the air is sent from the magnetized air chamber 26 to the blowing nozzles 6 and 6 through the pipe 25. A blower 40 is interposed between the magnetized air chamber 26 and the pipe 25 to adjust the blowing pressure.

前記内壁3には、上下左右に多数の小孔8、8を設ける。小孔8について大きさに制約はないが、内壁3の内側(処理空間)に収容した有機物7の小片などが入って小孔8を塞がないことを要件とする。従って、例えば実施例のようにカバー8a、8aを有する矩形小孔(打ち出し孔)が好ましい。   The inner wall 3 is provided with a large number of small holes 8 on the top, bottom, left and right. There is no restriction on the size of the small hole 8, but it is a requirement that the small hole 8 is not blocked by entering a small piece of the organic substance 7 accommodated inside the inner wall 3 (processing space). Therefore, for example, rectangular small holes (launch holes) having covers 8a and 8a as in the embodiment are preferable.

即ち、カバー8a、8aが小孔8、8を覆うので、有機物7の小片が小孔8、8に入るおそれがなく、かつ小片により小孔8を塞ぐおそれもない。図中10はこの発明の処理装置、19は残渣物点検口、20は灰点検口、21は開閉蓋である。前記開閉蓋21は、軸49を中心にして開閉される。図中47は開閉蓋21の把手、48は把手47を固定する係止環である。   That is, since the covers 8a and 8a cover the small holes 8 and 8, there is no possibility that a small piece of the organic substance 7 enters the small holes 8 and 8 and there is no possibility that the small hole 8 is blocked by the small pieces. In the figure, 10 is a processing apparatus of the present invention, 19 is a residue inspection port, 20 is an ash inspection port, and 21 is an open / close lid. The opening / closing lid 21 is opened / closed about a shaft 49. In the figure, 47 is a handle of the opening / closing lid 21, and 48 is a locking ring for fixing the handle 47.

前記本体5の中央部であって、側面図中、中央左右へ所定間隔で回転軸30、30を水平に架設し、各回転軸30、30の図1中、左右へ撹拌羽根31、32をそれぞれ固定する。前記撹拌羽根31、32は、それぞれ逆傾斜になっており、回転軸30、30の回転に伴って、有機物を矢示33、34又は35、36のように撹拌、移動させる。従って、撹拌羽根31、32に接触する有機物は、矢示33、34のように中央部へ寄せられ、又は矢示35、36のように側壁側へ寄せられ大きく撹拌される。   In the central part of the main body 5, in the side view, the rotary shafts 30 and 30 are horizontally installed at predetermined intervals to the left and right of the center, and the stirring blades 31 and 32 are left and right in FIG. Fix each one. The agitation blades 31 and 32 are inclined in reverse directions, and agitate and move organic substances as indicated by arrows 33 and 34 or 35 and 36 as the rotation shafts 30 and 30 rotate. Accordingly, the organic matter that contacts the stirring blades 31 and 32 is brought close to the central portion as indicated by arrows 33 and 34, or is moved toward the side wall as indicated by arrows 35 and 36 and greatly stirred.

また、撹拌羽根31、32の外周には、刃31a、32aが設けられており(図2)、この刃に接触した有機物を切断する。例えば、合成樹脂袋又は合成樹脂袋の近似物は31a、32aによって細断されるので、磁化空気に均等に接触し、分解を促進する。通常、合成樹脂袋に入っている有機物は、袋が分解されてから分解が始まるが、前記のように、羽根の刃により袋が破られると、袋と内容物が同時に分解されるので、全体の分解処理時間を著しく短縮することができる。図1中46は回転軸30、30を回転するモータである。   Further, blades 31a and 32a are provided on the outer circumferences of the stirring blades 31 and 32 (FIG. 2), and the organic matter in contact with the blades is cut. For example, since the synthetic resin bag or an approximation of the synthetic resin bag is shredded by 31a and 32a, it contacts evenly with magnetized air and promotes decomposition. Usually, the organic matter contained in the synthetic resin bag begins to decompose after the bag is decomposed, but as described above, if the bag is broken by the blade of the blade, the bag and contents are decomposed at the same time. It is possible to significantly shorten the decomposition processing time. In FIG. 1, reference numeral 46 denotes a motor that rotates the rotary shafts 30 and 30.

前記本体5の上部にホッパー45を連結し(図4)、ホッパー45の下端面と本体5の上端面との間に、開閉蓋41を設置し、前記ホッパー45の上端部へ開閉蓋42を設置する。開閉蓋41、42を交互に開閉すれば、本体5(処理槽)からの排気の洩れだしを未然に防止することができる。   A hopper 45 is connected to the upper part of the main body 5 (FIG. 4), an opening / closing lid 41 is installed between the lower end surface of the hopper 45 and the upper end surface of the main body 5, and the opening / closing lid 42 is connected to the upper end portion of the hopper 45. Install. If the open / close lids 41 and 42 are alternately opened and closed, it is possible to prevent leakage of exhaust gas from the main body 5 (treatment tank).

即ち、実施例の如く、本体5の上部に開閉蓋21のみを取り付けた場合には、開閉蓋21を開閉する度に処理槽内の分解気体が上昇して排出され、付近に臭気を拡散させるおそれがあるが、前記のように、本体5の上部にホッパー45を連結し、ホッパー45の上下端部に開閉蓋41、42を設ければ、本体5からの排気が外部へ排出するのを未然に防止することができる。   That is, when only the opening / closing lid 21 is attached to the upper part of the main body 5 as in the embodiment, every time the opening / closing lid 21 is opened / closed, the decomposition gas in the treatment tank rises and is discharged, and the odor is diffused in the vicinity. As described above, if the hopper 45 is connected to the upper part of the main body 5 and the open / close lids 41 and 42 are provided at the upper and lower ends of the hopper 45, the exhaust from the main body 5 can be discharged to the outside. It can be prevented in advance.

従って、ホッパー45内へ有機物を収容する時には、下の開閉蓋41を閉鎖して本体5内から排気が洩れるの遮断し、本体5内へ有機物を入れる時には、上の開閉蓋42を閉鎖して本体5内から排気が洩れるのを防止することができる。開閉蓋41、42は通常平塞してある。   Therefore, when the organic matter is stored in the hopper 45, the lower opening / closing lid 41 is closed to prevent the exhaust from leaking from the inside of the main body 5, and when the organic matter is put into the main body 5, the upper opening / closing lid 42 is closed. It is possible to prevent the exhaust gas from leaking from the inside of the main body 5. The open / close lids 41 and 42 are normally flattened.

前記において、ホッパー45内の有機物を本体5内へ移動させるには、有機物の自重に依存するけれども、有機物の状態によっては自由落下が不正確な場合もあるので、積極的に有機物投入用補助手段を架設することもある。   In the above, although the organic matter in the hopper 45 is moved into the main body 5 depending on the weight of the organic matter, depending on the state of the organic matter, the free fall may be inaccurate. May be erected.

前記有機物投入については、ホッパー45の下部の詰まりを解消するもので、回転羽根又はロールその他従来公知の手段を採用することができる。   About the said organic substance input, the clogging of the lower part of the hopper 45 is eliminated, A rotary blade, a roll, and other conventionally well-known means can be employ | adopted.

前記実施例において、有機物7は通常下側部から分解するが、分解により生じた気体と水蒸気との混合物は、矢示11、11、12、12のように側方及び上方に拡散する。そこで、主として側方に流動した気体は、矢示12から小孔8、8に入り、矢示14、14のように下降する(図1)。   In the said Example, although the organic substance 7 normally decomposes | disassembles from a lower side part, the mixture of the gas and water vapor | steam produced | generated by decomposition | disassembly spread | diffuses to the side and upper direction like the arrows 11, 11, 12, and 12. Therefore, the gas that has flowed mainly to the side enters the small holes 8 and 8 from the arrow 12 and descends as indicated by the arrows 14 and 14 (FIG. 1).

分解気体の多くは矢示11、11のように上昇し、矢示13、13のように下降する。また、下部に溜まった水と排気は矢示17のように外界(例えば煙突(非図示))へ排出され、他部は矢示18、18のように内部へ上昇する。そして磁化空気と混合して有機物に接触し、分解を促進する。前記磁化空気はほぼ常温(例えば20℃〜25℃)であるが、分解気体は100℃〜300℃位になっているので、加温により有機物の分解を促進する。前記磁化空気は、その量を調整することが好ましいので、ブロワーなどで加圧して吹き出すこともある。   Most of the decomposition gas rises as indicated by arrows 11 and 11 and descends as indicated by arrows 13 and 13. Further, the water and the exhaust gas accumulated in the lower part are discharged to the outside (for example, a chimney (not shown)) as indicated by an arrow 17, and the other parts are raised to the inside as indicated by arrows 18 and 18. Then, it mixes with magnetized air and comes into contact with organic matter to promote decomposition. Although the magnetized air is at a normal temperature (for example, 20 ° C. to 25 ° C.), the decomposition gas is about 100 ° C. to 300 ° C., so that the decomposition of organic substances is promoted by heating. Since the amount of the magnetized air is preferably adjusted, it may be blown out by being pressurized with a blower or the like.

図3において、ノズル6、6aに二重円と三重円が表れているが、三重円(ノズル6a)にはヒーター(最高300℃)が付けてある。このヒーターは、装置による分解の立ち上がり時に5分程つけるヒーターである。前記ヒーターに通電することによって、付近の空気を加温して上昇気流が生じる(矢示18a)ので、立ち上がり時に新聞紙などを燃やして上昇気流を生成させるなどの、立ち上がり動作は不要となる。   In FIG. 3, a double circle and a triple circle appear in the nozzles 6 and 6a, and a heater (maximum 300 ° C.) is attached to the triple circle (nozzle 6a). This heater is a heater that is applied for about 5 minutes at the start of decomposition by the apparatus. By energizing the heater, the air in the vicinity is heated to generate an updraft (arrow 18a), so that a rising operation such as burning a newspaper or the like to generate an updraft at the time of rising is unnecessary.

図に示した実施例の装置にあっては、主スイッチを入れると同時にヒーターにも通電すると、付近の空気が加熱され、上昇気流が生じるが、通電後5分位で通常の進行になって、前記スイッチが切れるようにしてある。従って、通常運転では、運転開始時における管理者の注意が不要となる。   In the apparatus of the embodiment shown in the figure, if the heater is energized at the same time as the main switch is turned on, the air in the vicinity is heated and an upward air flow is generated. The switch is turned off. Therefore, in normal operation, the manager's attention at the start of operation becomes unnecessary.

前記における磁化空気(空気中の微粒子が磁化される)により、酸素が活性化されて、有機物を分解するものと推定される。また、有機物は分解熱により加熱されるので(例えば、有機物の下面は200℃以上)、磁化空気の活性酸素による分解が促進されるものと認められる。   It is presumed that oxygen is activated by the magnetized air (the fine particles in the air are magnetized) to decompose organic substances. Further, since the organic matter is heated by the decomposition heat (for example, the lower surface of the organic matter is 200 ° C. or higher), it is recognized that the decomposition of the magnetized air by the active oxygen is promoted.

前記有機物の水分が仮に50%〜60%としても、圧倒的に水分が多いことになり、加温と分解促進とは必然的に生起され、水蒸気の発生も著しいと思われる。   Even if the water content of the organic substance is 50% to 60%, the water content is overwhelmingly high, so that heating and decomposition are inevitably caused, and the generation of water vapor seems to be remarkable.

前記水蒸気が加温されて加熱蒸気となり、分解して活性酸素と水素を生成すれば、分解効率は著しく促進される。この発明の場合には、著しく多い水蒸気中から水分の一部を分離することになる。この水分は、本体5の底板4上へ溜まり、矢示17のように流れて処理槽外へ排出される(図1)。   If the water vapor is heated to become heated steam and decomposed to generate active oxygen and hydrogen, the decomposition efficiency is remarkably accelerated. In the case of this invention, a part of water | moisture content will be isolate | separated from very much water vapor | steam. This moisture collects on the bottom plate 4 of the main body 5, flows as indicated by an arrow 17, and is discharged out of the processing tank (FIG. 1).

前記実施例は、本体の四側壁を三重壁としたが、三側壁又は二側壁を三重壁とした場合にも処理効率の向上が認められた。   In the above example, the four side walls of the main body are triple walls, but the improvement of the processing efficiency was also observed when three or two side walls were triple walls.

1 外壁
2、3 内壁
4a 内底板
5 本体
6 吹出しノズル
7 有機物
8 小孔
10 処理装置
21 開閉蓋
26 磁化空気室
28 磁化室
30 回転軸
31、32 撹拌羽根
41、42 開閉蓋
45 ホッパー
DESCRIPTION OF SYMBOLS 1 Outer wall 2, 3 Inner wall 4a Inner bottom plate 5 Main body 6 Blowing nozzle 7 Organic substance 8 Small hole 10 Processing apparatus 21 Opening / closing lid 26 Magnetized air chamber 28 Magnetizing chamber 30 Rotating shaft 31, 32 Stirring blades 41, 42 Opening / closing lid 45 Hopper

Claims (8)

筒状処理槽の上部に密閉蓋付きの有機物投入口を有し、下部に磁化空気の吹出しノズルを配置して、前記処理槽の内側に収容した有機物を磁化空気により分解する装置において、前記処理槽の少なくとも二側壁を、小間隙を介する三重壁とし、該三重壁の内壁に分解気体を通過させる多数の小孔を設け、該小孔と連続する小間隙は分解気体の下降通路用間隙とし、その外側の間隙は、上下を槽内に開放して分解気体の循環用間隙としたことを特徴とする有機物の磁気分解処理装置。   In the apparatus for disposing organic matter contained in the inside of the treatment tank with magnetized air having an organic substance inlet with a sealed lid in the upper part of the cylindrical treatment tank and arranging a blowout nozzle for magnetized air in the lower part, the treatment At least two side walls of the tank are a triple wall through a small gap, and a plurality of small holes are provided on the inner wall of the triple wall to allow the decomposition gas to pass. The small gap continuous with the small hole is a gap for the descending passage of the decomposition gas. An organic matter magnetic decomposition treatment apparatus characterized in that the outer gap is opened to the inside of the tank as a gap for circulating the decomposition gas. 筒状処理槽の上部に密閉蓋付きの有機物投入口を有し、下部に磁化空気の吹出しノズルを配置して、前記処理槽の内側に収容した有機物を磁化空気により分解する装置において、前記処理槽の少なくとも二側壁を、小間隙を介する三重壁とし、該三重壁の内壁に分解気体を通過させる多数の小孔を設け、該小孔と連続する小間隙は分解気体の下降通路用間隙とし、その外側の間隙は、上下を槽内に開放して分解気体の循環用間隙とし、前記筒状処理槽の下部から排気するようにしたことを特徴とする有機物の磁気分解処理装置。   In the apparatus for disposing organic matter contained in the inside of the treatment tank with magnetized air having an organic substance inlet with a sealed lid in the upper part of the cylindrical treatment tank and arranging a blowout nozzle for magnetized air in the lower part, the treatment At least two side walls of the tank are a triple wall through a small gap, and a plurality of small holes are provided on the inner wall of the triple wall to allow the decomposition gas to pass. The small gap continuous with the small hole is a gap for the descending passage of the decomposition gas. An organic matter magnetic decomposition treatment apparatus characterized in that the outer gap is opened into the tank at the top and bottom to circulate the decomposition gas and exhausted from the lower part of the cylindrical treatment tank. 筒状処理槽の上部に密閉蓋付きの有機物投入口を有し、下部に磁化空気の吹出しノズルを配置して、前記処理槽の内側に収容した有機物を磁化空気により分解する装置において、前記処理槽の前後左右の側壁に、小間隙を介する三重壁をそれぞれ設け、前記三重壁の内壁に分解気体を通過させる多数の小孔を設け、該小孔と連続する小間隙は分解気体の下降通路用間隙とし、その外側の間隙は、上下を槽内に開放して分解気体の循環用間隙としたことを特徴とする有機物の磁気分解処理装置。   In the apparatus for disposing organic matter contained in the inside of the treatment tank with magnetized air having an organic substance inlet with a sealed lid in the upper part of the cylindrical treatment tank and arranging a blowout nozzle for magnetized air in the lower part, the treatment Triple walls through small gaps are respectively provided on the front, rear, left and right side walls of the tank, and a large number of small holes are provided on the inner wall of the triple wall to allow the decomposition gas to pass therethrough. An organic magnetic decomposition treatment apparatus characterized in that a gap for use is provided, and a gap on the outside of the gap is opened in the tank for circulation of the decomposition gas. 筒状処理槽の上部に密閉蓋付きの有機物投入口を有し、下部に磁化空気の吹出しノズルを配置して、前記処理槽の内側に収容した有機物を磁化空気により分解する装置において、前記処理槽の前後左右の側壁に、小間隙を介する三重壁をそれぞれ設け、前記三重壁の内壁に分解気体を通過させる多数の小孔を設け、該小孔と連続する小間隙は分解気体の下降通路用間隙とし、その外側の間隙は、上下を槽内に開放して分解気体の循環用間隙とし、前記小孔にカバーを設けたことを特徴とする有機物の磁気分解処理装置。   In the apparatus for disposing organic matter contained in the inside of the treatment tank with magnetized air having an organic substance inlet with a sealed lid in the upper part of the cylindrical treatment tank and arranging a blowout nozzle for magnetized air in the lower part, the treatment Triple walls through small gaps are respectively provided on the front, rear, left and right side walls of the tank, and a large number of small holes are provided on the inner wall of the triple wall to allow the decomposition gas to pass therethrough. An organic magnetic decomposition treatment apparatus, characterized in that a gap for use is provided, the gap on the outside thereof is opened to the inside of the tank to be a gap for circulation of decomposition gas, and a cover is provided in the small hole. 筒状処理槽の中央部に回転軸を水平に架設し、回転軸の左右に撹拌羽根を所定間隔をおいて夫々固定したことを特徴とする請求項1乃至4記載の有機物の磁気分解処理装置。   5. An organic matter magnetic decomposition treatment apparatus according to claim 1, wherein a rotating shaft is horizontally installed at a central portion of the cylindrical processing tank, and stirring blades are respectively fixed to the left and right of the rotating shaft at predetermined intervals. . 回転軸は同一高さで二本並列架設したことを特徴とする請求項5記載の有機物の磁気分解処理装置。   6. The organic matter magnetic decomposition processing apparatus according to claim 5, wherein two rotating shafts are installed in parallel at the same height. 撹拌羽根の外周部に切断刃を設けたことを特徴とする請求項5記載の有機物の磁気分解処理装置。   6. An organic matter magnetic decomposition treatment apparatus according to claim 5, wherein a cutting blade is provided on an outer peripheral portion of the stirring blade. 吹出ノズルと磁化室との間に磁化空気室を介装したことを特徴とする請求項1乃至4記載の有機物の磁気分解処理装置。   5. An organic matter magnetic decomposition treatment apparatus according to claim 1, wherein a magnetized air chamber is interposed between the blowout nozzle and the magnetizing chamber.
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