JPH0573968B2 - - Google Patents

Info

Publication number
JPH0573968B2
JPH0573968B2 JP6234286A JP6234286A JPH0573968B2 JP H0573968 B2 JPH0573968 B2 JP H0573968B2 JP 6234286 A JP6234286 A JP 6234286A JP 6234286 A JP6234286 A JP 6234286A JP H0573968 B2 JPH0573968 B2 JP H0573968B2
Authority
JP
Japan
Prior art keywords
main body
microwaves
heat
exhaust gas
catalyst
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP6234286A
Other languages
Japanese (ja)
Other versions
JPS62218715A (en
Inventor
Kunyoshi Idota
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Panasonic Ecology Systems Co Ltd
Original Assignee
Matsushita Seiko Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Matsushita Seiko Co Ltd filed Critical Matsushita Seiko Co Ltd
Priority to JP6234286A priority Critical patent/JPS62218715A/en
Publication of JPS62218715A publication Critical patent/JPS62218715A/en
Publication of JPH0573968B2 publication Critical patent/JPH0573968B2/ja
Granted legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Constitution Of High-Frequency Heating (AREA)

Description

【発明の詳細な説明】 産業上の利用分野 この発明は、生ゴムをマイクロ波で焼却減量処
理する厨芥処理装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION Field of Industrial Application The present invention relates to a kitchen waste processing apparatus for reducing raw rubber by incineration using microwaves.

従来の技術 従来、この種の厨芥処理装置は第3図に示すよ
うにマイクロ波共振体とした箱形の本体1の内底
部にマイクロ波で発熱する発熱容器2を配置して
いる。また、本体1の一側面に生ゴミ4の投入口
3が設けられ、この投入口3は開閉自在な蓋15
により開閉される。本体1の他に側面に供給口6
を設け、この供給口6の臨ませて本体1内にマイ
クロ波を送り込むマイクロ波発生用のマグネトロ
ン装置5を取付けている。供給口6の下方には給
気口7を設け、給気送風機8と連結され本体1内
に燃焼に必要な空気を供給する。また給気送風機
8はマグネトロン装置5側にも分岐し、冷却風を
送り込む。本体1の上部にはゴミ燃焼により発生
する排ガスの排気口9を設け、この排気口9は煙
道9aを介して排ガス浄化ユニツト12、排気送
風機13に接続されている。排ガス浄化ユニツト
12は加熱ヒータ10と酸化触媒11とから構成
されている。これら排ガス浄化ユニツト12、排
気送風機13は本体1を覆う外殻14の上部に取
付けられている。
BACKGROUND ART Conventionally, as shown in FIG. 3, this type of kitchen waste processing apparatus has a heat-generating container 2 that generates heat using microwaves disposed at the inner bottom of a box-shaped main body 1 that is a microwave resonator. Further, an input port 3 for garbage 4 is provided on one side of the main body 1, and this input port 3 has a lid 15 that can be opened and closed.
It is opened and closed by In addition to the main body 1, there is a supply port 6 on the side.
A magnetron device 5 for generating microwaves for sending microwaves into the main body 1 is installed facing the supply port 6. An air supply port 7 is provided below the supply port 6 and is connected to a supply air blower 8 to supply air necessary for combustion into the main body 1. The supply air blower 8 also branches to the magnetron device 5 side and sends cooling air. An exhaust port 9 for exhaust gas generated by combustion of trash is provided in the upper part of the main body 1, and this exhaust port 9 is connected to an exhaust gas purification unit 12 and an exhaust blower 13 via a flue 9a. The exhaust gas purification unit 12 is composed of a heater 10 and an oxidation catalyst 11. These exhaust gas purification unit 12 and exhaust blower 13 are attached to the upper part of an outer shell 14 that covers the main body 1.

上記構成により、生ゴミ4を発熱容器2に入
れ、マイクロ波を放射すると、生ゴミ自体の内部
発熱による加熱と発熱容器2の発熱による加熱で
燃焼し、この際、発生する排ガスは排ガス浄化ユ
ニツト12を通過する。この排ガス浄化ユニツト
は加熱ヒータ10により排ガスを加熱して触媒作
用を高めた後、酸化触媒11により浄化排出する
ものであつた。
With the above configuration, when food waste 4 is placed in the heat generating container 2 and microwaves are radiated, the food waste is burned by heating due to internal heat generation of the food waste itself and heating due to heat generated by the heat generating container 2. At this time, the generated exhaust gas is passed through the exhaust gas purification unit. Pass 12. This exhaust gas purification unit heats the exhaust gas with a heater 10 to enhance the catalytic action, and then purifies and discharges the exhaust gas with an oxidation catalyst 11.

発明が解決しようとする問題点 このような従来の構成では、燃焼熱で充分熱い
排ガスが煙道9aを通過する間に冷却されるた
め、排ガス浄化ユニツト12へ入つて酸化触媒1
1に接する前に加熱ヒータ10により触媒の機能
温度(250℃以上)まで再加熱を必要としていた。
そのため、排ガスを再加熱するための加熱エネル
ギーを必要で省エネルギーに適しないものであつ
た。また、煙道9aおよび加熱ヒータ10等の構
造物を要するという問題点を有していた。
Problems to be Solved by the Invention In such a conventional configuration, exhaust gas that is sufficiently hot due to combustion heat is cooled while passing through the flue 9a, and therefore enters the exhaust gas purification unit 12 and is heated by the oxidation catalyst 1.
1, it was necessary to reheat the catalyst to its functional temperature (250° C. or higher) using a heater 10.
Therefore, heating energy is required to reheat the exhaust gas, which is not suitable for energy saving. Further, there was a problem in that structures such as the flue 9a and the heater 10 were required.

本発明はこのような問題点を解決するもので、
生ゴミ処理に再して発生する排ガスを再加熱する
ことなく排ガスを浄化できる省エネルギー型の経
済的な厨芥処理装置を提供することを目的とする
ものである。
The present invention solves these problems,
It is an object of the present invention to provide an energy-saving and economical kitchen waste processing device that can purify exhaust gas generated during food waste processing without reheating the waste gas.

問題点を解決するための手段 この問題点を解決するために本発明の厨芥処理
装置は、マイクロ波共振体とした本体に給気口と
排気口を設け、前記排気口にはマイクロ波により
発熱する酸化物触媒体を設けた構成である。
Means for Solving the Problem In order to solve this problem, the kitchen waste processing apparatus of the present invention is provided with an air supply port and an exhaust port in the main body which is a microwave resonator, and the exhaust port generates heat by the microwave. This is a configuration in which an oxide catalyst body is provided.

作 用 この構成により、本体内へマイクロ波を放射す
ると、生ゴミの燃焼により排ガスが発生し、排気
口を通過して外部へ排出される。この排ガスは排
出されるときに、マイクロ波により自己発熱して
触媒機能温度に達した酸化物触媒体によつて水お
よび炭酸ガス等の酸化分解される。
Effect With this configuration, when microwaves are radiated into the main body, exhaust gas is generated by combustion of garbage, which passes through the exhaust port and is discharged to the outside. When this exhaust gas is discharged, it is oxidized and decomposed into water, carbon dioxide, etc. by the oxide catalyst which self-heats due to microwaves and reaches the catalytic function temperature.

実施例 以下、本発明の一実施例を第1図および第2図
にもとづき説明する。なお従来の構成と同一部分
には同一番号を付し、その説明は省略する。
Embodiment An embodiment of the present invention will be described below with reference to FIGS. 1 and 2. Note that parts that are the same as those in the conventional configuration are given the same numbers, and their explanations will be omitted.

図において、外殻14内にマイクロ波共振体と
した本体1が設けられており、この本体1の内底
部に発熱容器2が配置されている。そして、本体
1の一側面に開閉自在に取付けた扉15を開き投
入口3より生ゴミ4を発熱容器2に入れる。ま
た、本体1の他の側面に供給口6を開口し、この
供給口6に連らなる導波管6aの奥にマグネトロ
ン装置5を設けている。供給口6の下方には給気
口7が設けられ、給気送風機8に連結されてい
る。また、給気送風機8の吐出側を分岐させマグ
ネトロン装置5に冷却風を供給する構成である。
発熱容器2は炭化けい素とチタン酸バリウムの焼
結体で構成され、1000℃以上の耐熱性を有し、か
つマイクロ波により発熱する。本体1の上部側面
に設けた排気口101にはハニカム形状に形成さ
れた酸化物触媒体100が取付けられている。こ
の排気口101は煙道101aを介して排気送風
機102が接続されている。なお本体1の各開口
部はマイクロ波の供給口6を除いて電波漏れ防止
の手段が施されている。
In the figure, a main body 1 as a microwave resonator is provided within an outer shell 14, and a heat generating container 2 is disposed at the inner bottom of the main body 1. Then, a door 15 attached to one side of the main body 1 so as to be openable and closable is opened, and the garbage 4 is put into the heat generating container 2 through the input port 3. Further, a supply port 6 is opened on the other side of the main body 1, and a magnetron device 5 is provided at the back of a waveguide 6a connected to the supply port 6. An air supply port 7 is provided below the supply port 6 and is connected to a supply air blower 8 . Further, the discharge side of the supply air blower 8 is branched to supply cooling air to the magnetron device 5.
The heat generating container 2 is made of a sintered body of silicon carbide and barium titanate, has a heat resistance of 1000° C. or more, and generates heat by microwaves. An oxide catalyst body 100 formed in a honeycomb shape is attached to an exhaust port 101 provided on the upper side surface of the main body 1 . This exhaust port 101 is connected to an exhaust blower 102 via a flue 101a. Note that each opening of the main body 1, except for the microwave supply port 6, is provided with means for preventing leakage of radio waves.

上記構成において、生ゴミ4は本体1の投入口
3より発熱容器4内へ投入される。そして、マグ
ネトロン装置5へ通電するとマイクロ波が発生
し、導波管6a内を通つて供給口6より本体1内
へ導入される。マイクロ波は直接生ゴミ4へ作用
する。一般に生ゴミ4は含水率が高く熱伝導率が
低く、しかも生ゴミどうしの間に空間が多く介在
しているため、非常に外部加熱しにくいが、マイ
クロ波は瞬時に生ゴミ4の内部まで加熱する。ま
た、同時に発熱容器2へも作用する。発熱容器2
は炭化けい素と強誘電体であるチタン酸バリウム
の焼結体で構成されているため、チタン酸バリウ
ムの誘電損相当分の熱を発生し、熱伝導率のよい
炭化けい素により発熱容器7全体が加熱される。
この結果、第2図に示すように発熱容器2内で
は、生ゴミ4の内部加熱による熱と発熱容器2か
らの熱で極めて温度の度き高温部103が形成さ
れ、生ゴミ4をほぼ完全に焼ききりわずかに白い
灰が残るだけとなる。一方、マイクロ波による加
熱が進むだけとなる。一方、マイクロ波による加
熱が進むと、生ゴミ4は当初水の沸点まで加熱さ
れどんどん脱水される。そして、脱水が終わると
沸点を越えて温度が上昇し、やがて発火点に達し
て燃焼を始める。この脱水から発火に至る時点
は、くすぶり状態が生じ煙と臭いが発生する。こ
れはCO、HCやタール性状の未燃焼炭化水素が主
な成分である。これらの排ガスは排気送風機10
2により吸引され、ハニカム構造で多数の筒状の
穴が開口した酸化物触媒体100へ送られる。酸
化物触媒体100は、結合剤であるアルミン酸石
炭内へ、溶融シリカ、チタン酸バリウム、炭化け
い素、二酸化チタンを混ぜて焼結した担体をハニ
カム構造に構成し、二酸化チタンを担持母材と
し、白金族金属を触媒として担持させてある。こ
のため、マイクロ波を受けると強誘電物質である
チタン酸バリウムの作用で、酸化物触媒100自
体が触媒の機能温度(約250℃以上)以上に加熱
され、さらに送られて来る排ガスも加熱し、触媒
効果により排ガスを酸化して、水または炭酸ガス
に変えて浄化する。このとき、排ガス中の未燃焼
生成物であるCO、HCの濃度が比較的高いため、
浄化とともに触媒酸化燃焼が発生し発熱するた
め、酸化物触媒体100の温度は、マイクロ波発
熱による温度をはるかに上回る高温(約800℃)
に達する。このため、排ガス中の酸化処理に適さ
ない臭い成分もこの温度域ではほぼ完全に分解し
てしまい良好な脱臭ができるものである。そし
て、浄化された排ガスは、排送風機102によつ
て排気されるものである。
In the above configuration, the garbage 4 is thrown into the heat generating container 4 through the inlet 3 of the main body 1. When the magnetron device 5 is energized, microwaves are generated and introduced into the main body 1 through the supply port 6 through the waveguide 6a. The microwave acts directly on the garbage 4. In general, food waste 4 has a high moisture content and low thermal conductivity, and there are many spaces between the food wastes, so it is very difficult to externally heat it, but microwaves can instantly reach the inside of food waste 4. Heat. Moreover, it also acts on the heat generating container 2 at the same time. Heat generating container 2
Since it is composed of a sintered body of silicon carbide and barium titanate, which is a ferroelectric substance, it generates heat equivalent to the dielectric loss of barium titanate, and the heat generating container 7 is made of silicon carbide, which has good thermal conductivity. The whole thing gets heated.
As a result, as shown in FIG. 2, a high-temperature part 103 is formed in the heat generating container 2, where the temperature is extremely high due to the heat generated by the internal heating of the garbage 4 and the heat from the heat generating container 2, and the garbage 4 is almost completely heated. After burning, only a small amount of white ash remains. On the other hand, heating by microwaves only progresses. On the other hand, as the heating by the microwave progresses, the garbage 4 is initially heated to the boiling point of water and is gradually dehydrated. Once dehydration is complete, the temperature rises above the boiling point, and eventually reaches the ignition point, where combustion begins. When dehydration leads to ignition, a smoldering state occurs, producing smoke and odor. The main components are CO, HC, and unburned hydrocarbons in the form of tar. These exhaust gases are removed by an exhaust blower 10.
2 and sent to the oxide catalyst body 100, which has a honeycomb structure and has a large number of cylindrical holes. The oxide catalyst body 100 has a honeycomb structure in which a carrier is formed by mixing and sintering fused silica, barium titanate, silicon carbide, and titanium dioxide into aluminate coal as a binder, and a base material supporting titanium dioxide. A platinum group metal is supported as a catalyst. Therefore, when exposed to microwaves, the oxide catalyst 100 itself is heated to a temperature higher than the catalyst's functional temperature (approximately 250°C or higher) due to the action of barium titanate, which is a ferroelectric substance, and the exhaust gas being sent is also heated. , purifies exhaust gas by oxidizing it and converting it into water or carbon dioxide using a catalytic effect. At this time, since the concentration of unburned products such as CO and HC in the exhaust gas is relatively high,
As catalytic oxidation combustion occurs and heat is generated during purification, the temperature of the oxide catalyst body 100 is a high temperature (approximately 800°C), which is much higher than the temperature caused by microwave heat generation.
reach. Therefore, odor components in the exhaust gas that are not suitable for oxidation treatment are almost completely decomposed in this temperature range, and good deodorization can be achieved. The purified exhaust gas is then exhausted by the exhaust blower 102.

なお本発明では生ゴミが灰となり負荷としてゼ
ロになつても、発熱容器2と酸化物触媒体100
が負荷として残るためマグネトロン装置5はいわ
ゆる空だき状態で損傷することはない。また、マ
イクロ波発熱のための素材としてチタン酸バリウ
ムを用いたが、要は耐熱性を有する強誘電物質で
あればよい。また、本実施例では酸化物触媒体を
用いたが、デオライト系触媒やインターカーレシ
ヨン(積層)化合物などのセラミツク系触媒でも
同様の効果を奏するものである。
In addition, in the present invention, even if the garbage becomes ash and the load becomes zero, the heat generating container 2 and the oxide catalyst body 100
remains as a load, so the magnetron device 5 is not damaged in the so-called dry state. Furthermore, although barium titanate was used as the material for microwave heating, any ferroelectric material with heat resistance may be used. Further, although an oxide catalyst was used in this example, a ceramic catalyst such as a deolite catalyst or an intercalation (stacking) compound may also have the same effect.

発明の効果 以上のように本発明によれば、生ゴミはマイク
ロ波による、直接の内部加熱と発熱容器からの熱
で二重に加熱されて自己燃焼し、そのとき発生す
る排ガスは酸化物媒体が自己発熱するため、補助
ヒータで再加熱しなくとも完全に分解される。よ
つて熱エネルギー損失の少ない効率的な排ガス処
理ができるとともに、従来必要であつた加熱ヒー
タも不要となり、製造コストを低くすることがで
きる。
Effects of the Invention As described above, according to the present invention, food waste is heated twice by direct internal heating by microwaves and heat from a heat-generating container and self-combusts, and the exhaust gas generated at that time is an oxide medium. Since it self-heats, it is completely decomposed without reheating with an auxiliary heater. As a result, efficient exhaust gas treatment with less thermal energy loss is possible, and the conventionally required heater is not required, making it possible to reduce manufacturing costs.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は本発明の一実施例の厨芥処理装置の縦
断面図、第2図は同厨芥処理装置の発熱容器の処
理状態を示す縦断面図、第3図は従来の厨芥処理
装置を示す縦断面図である。 1……本体、2……発熱容器、3……投入口、
5……マグネトロン装置、6……供給口、7……
給気口、100……酸化物触媒体、101……排
気口。
Fig. 1 is a longitudinal cross-sectional view of a kitchen waste processing apparatus according to an embodiment of the present invention, Fig. 2 is a longitudinal cross-sectional view showing the processing state of a heat generating container of the same kitchen waste processing apparatus, and Fig. 3 is a longitudinal cross-sectional view showing a conventional kitchen waste processing apparatus. FIG. 1... Main body, 2... Heat generating container, 3... Inlet,
5... Magnetron device, 6... Supply port, 7...
Air supply port, 100... Oxide catalyst body, 101... Exhaust port.

Claims (1)

【特許請求の範囲】 1 マイクロ波共振体とした本体と、この本体に
設けられた給気口および排気口と、前記本体内に
配置され、マイクロ波により発熱する発熱容器を
備え、前記排気口にはマイクロ波により発熱する
触媒体を設けた厨芥処理装置。 2 触媒体は酸化物触媒体とし、この酸化物の触
媒体をアルミン酸石灰、溶融シリカ、チタン酸バ
リウム、炭化けい素、二酸化チタンで担体を構成
し、白金族金属を触媒として担持させた特許請求
の範囲第1項記載の厨芥処理装置。
[Scope of Claims] 1. A main body configured as a microwave resonator, an air supply port and an exhaust port provided in the main body, and a heat generating container disposed within the main body that generates heat by microwaves, and the exhaust port is a kitchen waste processing device equipped with a catalyst that generates heat using microwaves. 2. A patent in which the catalytic body is an oxide catalytic body, the oxide catalytic body is composed of a support made of lime aluminate, fused silica, barium titanate, silicon carbide, and titanium dioxide, and a platinum group metal is supported as a catalyst. A kitchen waste processing device according to claim 1.
JP6234286A 1986-03-20 1986-03-20 Garbage disposing device Granted JPS62218715A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6234286A JPS62218715A (en) 1986-03-20 1986-03-20 Garbage disposing device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6234286A JPS62218715A (en) 1986-03-20 1986-03-20 Garbage disposing device

Publications (2)

Publication Number Publication Date
JPS62218715A JPS62218715A (en) 1987-09-26
JPH0573968B2 true JPH0573968B2 (en) 1993-10-15

Family

ID=13197351

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6234286A Granted JPS62218715A (en) 1986-03-20 1986-03-20 Garbage disposing device

Country Status (1)

Country Link
JP (1) JPS62218715A (en)

Also Published As

Publication number Publication date
JPS62218715A (en) 1987-09-26

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