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JPH0532646B2 - - Google Patents

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Publication number
JPH0532646B2
JPH0532646B2 JP61022963A JP2296386A JPH0532646B2 JP H0532646 B2 JPH0532646 B2 JP H0532646B2 JP 61022963 A JP61022963 A JP 61022963A JP 2296386 A JP2296386 A JP 2296386A JP H0532646 B2 JPH0532646 B2 JP H0532646B2
Authority
JP
Japan
Prior art keywords
microwave
furnace
combustion
incinerator
treated
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
JP61022963A
Other languages
Japanese (ja)
Other versions
JPS62182520A (en
Inventor
Toshiaki Fujii
Mitsuhiko Nomi
Junichi Yamaji
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.)
Ebara Corp
Ebara Research Co Ltd
Original Assignee
Ebara Corp
Ebara Research 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 Ebara Corp, Ebara Research Co Ltd filed Critical Ebara Corp
Priority to JP2296386A priority Critical patent/JPS62182520A/en
Publication of JPS62182520A publication Critical patent/JPS62182520A/en
Publication of JPH0532646B2 publication Critical patent/JPH0532646B2/ja
Granted legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は有機塩素系化合物(例えばPCB、ダ
イオキシンあるいは殺虫剤等の農薬)、もしくは
該有機塩素系化合物を含む廃棄物、又はこれらを
取扱う研究や実験・試験で生じる設備、装置、器
具類などの廃棄物を処理するに際し、マイクロ波
エネルギーにより該化合物又は廃棄物を加熱し該
化合物を分解、燃焼するための装置に関する。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to organic chlorine compounds (for example, PCBs, dioxins, agricultural chemicals such as insecticides), wastes containing the organic chlorine compounds, or research dealing with these compounds. The present invention relates to a device for heating a compound or waste material using microwave energy to decompose and burn the compound when processing waste material such as equipment, equipment, instruments, etc. generated in experiments and tests.

〔従来の技術〕[Conventional technology]

従来、この種廃棄物の処理方法としては、バー
ナを備えた加熱炉により焼却する方法、紫外線照
射により分解する方法、オゾンによる酸化分解法
などが知られている。
Conventionally, known methods for treating this type of waste include incineration in a heating furnace equipped with a burner, decomposition by ultraviolet irradiation, and oxidative decomposition using ozone.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

これらの方法の中、加熱炉による方法では温度
が1200〜1400℃と高温が必要であり、バーナによ
り高温を得るものであるため温度斑が生じ易く、
有害な二次生成物が生成する問題点を伴うもので
あつた。すなわち、局部高温が生じ易いため、炉
の構成材料として高価なものを採用する必要があ
るだけでなく、熱分解効率が安定し難い欠点があ
り、例えば被処理物がPCBの場合、ダイオキシ
ンがジベンゾフランなど猛毒の物質が生成する場
合があり、実用性に欠ける問題があつた。
Among these methods, the method using a heating furnace requires a high temperature of 1200 to 1400℃, and because the high temperature is obtained with a burner, temperature unevenness is likely to occur.
This was accompanied by the problem of generation of harmful secondary products. In other words, localized high temperatures tend to occur, which not only necessitates the use of expensive materials for the construction of the furnace, but also has the drawback that thermal decomposition efficiency is difficult to stabilize.For example, when the material to be treated is PCB, dioxins are In some cases, extremely poisonous substances such as these may be produced, which poses a problem of lack of practicality.

一方、紫外線やオゾンによる分解方法では、加
熱炉による方法と同様二次生成物が生成する場合
があるし、オゾンがリークして排出され二次公害
が生じるおそれもあり、分解効率が充分でない場
合もあつて、実用性に欠けるものであつた。ま
た、装置が大型化し、取扱いが面倒となる問題が
あつた。
On the other hand, decomposition methods using ultraviolet rays or ozone may produce secondary products, similar to methods using heating furnaces, and ozone may leak and be discharged, causing secondary pollution, and the decomposition efficiency may not be sufficient. However, it lacked practicality. In addition, there was a problem that the device became large and difficult to handle.

さらに、この種の装置では微量でも猛毒の物質
を扱うため、安定運転が可能かつ相当に高効率の
性能を有する装置の開発が待たれていたものであ
る。
Furthermore, since this type of device handles highly toxic substances even in minute amounts, there has been a long-awaited development of a device that can operate stably and has considerably high efficiency.

一方、環境問題の深刻化に伴い有機塩素系化合
物を研究室、実験室レベルで取扱う場合が生じて
いる。この場合、実験設備や器具等に有機塩素系
化合物が付着し、これらが汚染されるため、これ
らの汚染された設備や器具類による二次汚染のお
それがあり、これが試験、研究の大きな妨げとな
つていた。したがつて実験室、研究室レベルでも
これらの廃棄物を迅速、かつ簡便に処理出来る装
置が望まれていたものである。
On the other hand, as environmental problems become more serious, there are cases where organic chlorine compounds are handled in laboratories and laboratories. In this case, organic chlorine compounds adhere to and contaminate experimental equipment and instruments, leading to the risk of secondary contamination from these contaminated equipment and instruments, which greatly hinders testing and research. I was getting used to it. Therefore, there has been a desire for a device that can quickly and easily process these wastes even at the laboratory level.

上記問題点及び要望に鑑みて、本発明者らは先
に有機塩素系化合物又は該有機塩素系化合物を含
む廃棄物をマイクロ波を用いて分解燃焼処理する
装置を提案している。(特公平2−50365号公報) ところが、上記の発明においても被処理物の形
状によつては十分に燃焼処理できない欠点があつ
た。例えば、マイクロ波を用いる上記装置はその
炉床に顆粒状のマイクロ波吸収材が充填されてお
り、該炉に導入されたマイクロ波は充填層を形成
するマイクロ波吸収材に選択的に吸収され炉内、
特にマイクロ波吸収材表面及びその近傍が高温状
態になるが、被処理物の形状が大きくなると高温
のマイクロ波吸収材からの熱が形状の大きい物質
に伝らず不完全な燃焼が生ずる。
In view of the above problems and demands, the present inventors have previously proposed an apparatus for decomposing and burning an organic chlorine compound or waste containing the organic chlorine compound using microwaves. (Japanese Patent Publication No. 2-50365) However, even in the above invention, there is a drawback that depending on the shape of the object to be treated, sufficient combustion treatment cannot be performed. For example, in the above-mentioned apparatus using microwaves, the hearth is filled with granular microwave absorbing material, and the microwaves introduced into the furnace are selectively absorbed by the microwave absorbing material forming a packed bed. Inside the furnace,
In particular, the surface of the microwave absorbing material and its vicinity are in a high temperature state, but if the shape of the object to be treated becomes large, the heat from the high temperature microwave absorbing material is not transferred to the large material, resulting in incomplete combustion.

本発明は、上記発明を改善するためになされた
もので、有機塩素系化合物を高収率で、かつ温度
斑を伴うことなく分解、燃焼でき、二次公害の原
因となる二次生成物が発生するおそれのない好適
な装置を経済的に提供することを目的とするもの
である。
The present invention has been made to improve the above invention, and is capable of decomposing and burning organochlorine compounds in high yield and without temperature unevenness, and eliminates secondary products that cause secondary pollution. The purpose is to economically provide a suitable device that is free from the risk of such occurrence.

〔課題を解決するための手段〕[Means to solve the problem]

本発明の処理装置は、有機塩素系化合物又は有
機塩素系化合物を含む廃棄物をマイクロ波エネル
ギーにより分解、燃焼処理するための装置におい
て、前記被処理物の受入槽と、該受入槽内の下方
位置に配設した受け入れた被処理物の破砕装置
と、破砕された被処理物を移送するための移送装
置と、該移送された被処理物を燃焼処理するため
の燃焼装置とを備えて成り、該燃焼装置は少なく
とも炉床の一部が耐火性マイクロ波吸収材より成
る焼却炉と、炉材及び/又は炉壁の少なくととも
一部が耐火性マイクロ波吸収材より成る二次燃焼
炉とを備えると共に、これら焼却炉、二次燃焼炉
のそれぞれにマイクロ波導波管を介してマイクロ
波発生装置を接続して構成されていることを特徴
とするものである。
The treatment apparatus of the present invention is an apparatus for decomposing and burning organic chlorine compounds or waste containing organic chlorine compounds using microwave energy, which includes a receiving tank for the material to be treated and a lower part of the receiving tank. The apparatus is equipped with a crushing device for the received processed material arranged at a location, a transfer device for transferring the crushed processed material, and a combustion device for burning the transferred processed material. , the combustion apparatus includes an incinerator in which at least a part of the hearth is made of a refractory microwave absorbing material, and a secondary combustion furnace in which at least a part of the furnace material and/or the furnace wall is made of a refractory microwave absorbing material. The present invention is characterized in that a microwave generator is connected to each of the incinerator and the secondary combustion furnace via a microwave waveguide.

上記破砕装置には、一般に(1)圧縮力、(2)衝撃
力、(3)せん断力又は(4)摩擦力を利用する装置があ
り、効率の良い破砕を行なうことができるが、こ
れらのうち何れを適用するか、すなわち破砕方式
として何れを採用するかは被処理物の形状、物性
(例えば大きさ、破砕され易さ)、破砕後の寸法等
を検討して適宜に決定することができる。すなわ
ち(1)圧縮式は粗砕用又は中間破砕用に、(2)衝撃式
は中間破砕、微破砕又は超微破砕用に、(3)せん断
式は微破砕用又は靭性材料の微細化用に、(4)摩擦
式は超微破砕用に、それぞれ好適であるが、衝撃
式とせん断式が特に好ましく、所望により、衝撃
式で中間破砕を行なつたのち、せん断式で微破砕
を行なうのも極めて効果的であり、したがつて破
砕機としては衝撃式破砕機又は二軸せん断式破砕
機が特に好適である。
The above-mentioned crushing devices generally include devices that utilize (1) compression force, (2) impact force, (3) shear force, or (4) friction force, and can perform efficient crushing. Which of these methods to apply, that is, which crushing method to adopt, can be determined appropriately by considering the shape, physical properties (for example, size, ease of crushing), and dimensions of the object to be treated after crushing. can. In other words, (1) the compression type is for coarse crushing or intermediate crushing, (2) the impact type is for intermediate crushing, fine crushing, or ultra-fine crushing, and (3) the shear type is for fine crushing or refining tough materials. (4) The friction type is suitable for ultra-fine crushing, but the impact type and shear type are particularly preferred, and if desired, after performing intermediate crushing with the impact type, fine crushing can be performed with the shear type. This is also extremely effective, and therefore, impact type crushers or twin-shaft shear type crushers are particularly suitable as crushers.

〔作用〕[Effect]

廃棄物をマイクロ波を用いて処理する方法は、
公知の技術であり、この方法では通常マイクロ波
エネルギーを廃棄物に直接作用させて行つてい
る。直接作用させる場合は、マイクロ波エネルギ
ーが廃棄物内部まで達し、廃棄物の破砕を十分に
行わなくても燃焼処理はできた。
The method of processing waste using microwaves is
This is a well-known technique and typically involves applying microwave energy directly to the waste. In the case of direct action, the microwave energy reached inside the waste, and combustion treatment was possible without sufficiently crushing the waste.

これに対し、本発明では、マイクロ波エネルギ
ーを一旦炉床に充填された顆粒状のマイクロ波吸
収材に吸収させ、該吸収材表面を高温にし、この
吸収材表面の高温状態により廃棄物の処理を行う
ものであるから、廃棄物の形状、大きさにより燃
焼効率に差ができる。本発明では、被処理物であ
る廃棄物を破砕装置で破砕して細かい形状として
燃焼処理するから、被処理物は炉材表面又はその
近傍で瞬時に分解燃焼させることができる。
In contrast, in the present invention, microwave energy is once absorbed into a granular microwave absorbing material filled in a hearth, the surface of the absorbing material is heated to a high temperature, and waste is processed using the high temperature state of the surface of the absorbing material. Therefore, the combustion efficiency varies depending on the shape and size of the waste. In the present invention, the waste material to be treated is crushed by a crushing device and burnt in a fine shape, so that the material to be treated can be instantaneously decomposed and burned on or near the surface of the furnace material.

本発明において、破砕装置によつて破砕される
被処理物の大きさは、処理装置の大きさ、形状、
被処理物の種類などにより異なるが、少なくとも
一方の長さが5cm以下、より好ましくは1cm以下
がよい。
In the present invention, the size of the workpiece to be crushed by the crushing device depends on the size and shape of the treatment device,
The length of at least one of them is preferably 5 cm or less, more preferably 1 cm or less, although this varies depending on the type of the object to be treated.

〔実施例〕〔Example〕

以下、本発明を具体的に説明する。 The present invention will be explained in detail below.

実施例 1 本発明の実施態様を図面に基づいて説明する
と、PCBを含む廃棄物(被処理物)例えばコン
デンサは、受入槽1に受け入れられ破砕機11
より破砕されたのち定量フイーダ2により焼却炉
3に送られ焼却される。
Example 1 An embodiment of the present invention will be described based on the drawings. Waste containing PCBs (materials to be treated), such as capacitors, are received in a receiving tank 1, crushed by a crusher 11 , and then incinerated by a quantitative feeder 2. It is sent to furnace 3 and incinerated.

破砕機11は受入槽1内の下方位置に配設され
ているので、受入槽1に投入された被処理物はそ
のまま順次破砕され焼却炉3に移送される。この
破砕機11としては、被処理物を破砕し定量フイ
ーダ2により焼却炉3へ移送できる形状、寸法、
物性に変換しうる機能を有するものであれば、ど
のようなものでも適用可能である。
Since the crusher 1 1 is disposed at a lower position within the receiving tank 1 , the materials to be processed that have been put into the receiving tank 1 are sequentially crushed as they are and transferred to the incinerator 3 . This crusher 11 has a shape, size, and size that can crush the material to be processed and transfer it to the incinerator 3 by the quantitative feeder 2.
Any material can be applied as long as it has a function that can be converted into physical properties.

なお破砕機を被処理物受入槽の後段に設け、破
砕後の被処理物を一旦貯留槽に貯留したのち定量
フイーダにより焼却炉3へ供給するように構成し
てもよい。
Note that the crusher may be provided downstream of the processing material receiving tank, and the processing material after the processing may be temporarily stored in the storage tank and then supplied to the incinerator 3 by a quantitative feeder.

しかして、焼却炉3内はマイクロ波発生装置4
からのマイクロ波により高温状態が保持され焼却
が行われる。すなわち、焼却炉3は、下部に回転
駆動装置5を介して撹拌羽根6等の撹拌機構を、
上部にマイクロ波導波管71を有しており、更に
前記撹拌羽根配設部位には顆粒状で耐火性のマイ
クロ波吸収材8が充填されており、燃焼用空気は
送気フアン9により撹拌機構を介して炉下部に設
けた燃焼用空気供給管(図示せず)より供給され
るが、撹拌羽根6として空気供給用のノズルを兼
ねた構造のものを適用することもできる。
However, inside the incinerator 3 is a microwave generator 4.
The high temperature state is maintained by microwaves and incineration is carried out. That is, the incinerator 3 has a stirring mechanism such as stirring blades 6 via the rotary drive device 5 in the lower part.
It has a microwave waveguide 71 in its upper part, and the part where the stirring blade is installed is filled with a granular fire-resistant microwave absorbing material 8, and the combustion air is stirred by an air supply fan 9. Although the combustion air is supplied via a mechanism from a combustion air supply pipe (not shown) provided in the lower part of the furnace, it is also possible to use a structure that also serves as an air supply nozzle as the stirring blade 6.

焼却炉3内に導入されたマイクロ波はマイクロ
波吸収材8に選択的に吸収されて高温状態が形成
され、定量フイーダ2により供給されたPCBは、
高温のマイクロ波吸収材表面部で瞬時にして分解
し、燃焼する。
The microwave introduced into the incinerator 3 is selectively absorbed by the microwave absorber 8 to form a high temperature state, and the PCBs supplied by the quantitative feeder 2 are
It instantly decomposes and burns on the surface of the high-temperature microwave absorber.

すなわち、撹拌流動状態にある高温のマイクロ
波吸収材8の表面に供給された被処理物が、即燃
焼しながら炉全面に分散され、高温で十分な酸化
雰囲気に保たれるため、炉内全域で良好な分解、
燃焼が達せられる。
In other words, the material to be treated is supplied to the surface of the high-temperature microwave absorbing material 8 which is in an agitated and fluidized state, and is instantly combusted and dispersed over the entire surface of the furnace, and a sufficient oxidizing atmosphere is maintained at high temperature, so that the entire area inside the furnace is Good disassembly,
Combustion is achieved.

マイクロ波吸収材8の材質としては、マイクロ
波を吸収して発熱するものであれば何でも良く金
属又は非金属の、酸化物又は炭化物が一般的で、
これらを任意に組み合わせて併用することもでき
る。具体的としては炭化ケイ素、酸化チタン、窒
化ケイ素入り炭化ケイ素が実用的で好都合であ
る。
The material of the microwave absorbing material 8 may be any material as long as it absorbs microwaves and generates heat, and metals or non-metals, oxides or carbides are generally used.
These can also be used in any combination. Specifically, silicon carbide, titanium oxide, and silicon carbide containing silicon nitride are practical and convenient.

また、マイクロ波吸収材8の形状は、一般的に
は顆粒状(例えば直径5〜20mm)とするのが好ま
しい。
Further, it is generally preferable that the microwave absorbing material 8 has a granular shape (for example, a diameter of 5 to 20 mm).

焼却炉3内における被処理物の加熱温度つまり
炉壁温度(実際の運転では該炉壁温度を測定し制
御している)は好ましくは800〜1500℃、特に好
ましくは1000〜1400℃とするが、被処理物の種類
や形状、後述の添加剤の種類等により異なる。例
えば被処理物が殺虫剤の場合は比較的低い温度で
もよいが、PCBの場合は1000℃以上の高温が好
ましい。また前記添加剤として融剤や燃焼促進剤
を加えた場合は被処理物の分解、燃焼が促進され
るので、比較的低い温度でよい。
The heating temperature of the material to be treated in the incinerator 3, that is, the furnace wall temperature (in actual operation, the furnace wall temperature is measured and controlled) is preferably 800 to 1500°C, particularly preferably 1000 to 1400°C. , differs depending on the type and shape of the object to be treated, the type of additives described below, etc. For example, if the object to be treated is an insecticide, a relatively low temperature may be sufficient, but in the case of PCBs, a high temperature of 1000° C. or higher is preferable. Furthermore, when a flux or a combustion promoter is added as the additive, the decomposition and combustion of the material to be treated is promoted, so a relatively low temperature is sufficient.

しかして、前記融剤としては水酸化アルカリ、
炭酸アルカリ等の塩基性融剤、KHSO4、K2S2O7
等の酸性融剤、KNO3、PbOあるいはNa2CO3
K2CO3の混合物、Na2CO3とKNO3の混合物、
Na2CO3とMgOの混合物等、各種のものが適用で
きるが、これらのうちNa2CO3、K2CO3、KOH
のような塩基性融剤が好ましく、また後処理、効
率の観点からはKOHが好ましい。これらを2種
以上を混合して使用してもよい。これら融剤の添
加量は5W/W%以上で用いられるが、経済性や
効率の観点から5〜50W/W%の範囲内で用いる
のが好ましい。
Therefore, as the fluxing agent, alkali hydroxide,
Basic flux such as alkali carbonate, KHSO 4 , K 2 S 2 O 7
With acidic fluxes such as KNO 3 , PbO or Na 2 CO 3
A mixture of K2CO3 , a mixture of Na2CO3 and KNO3 ,
Various materials can be applied, such as a mixture of Na 2 CO 3 and MgO, but among these, Na 2 CO 3 , K 2 CO 3 , KOH
Basic fluxes such as are preferred, and KOH is preferred from the viewpoint of post-treatment and efficiency. Two or more of these may be used in combination. The amount of these fluxes added is 5 W/W% or more, but from the viewpoint of economy and efficiency, it is preferably used within the range of 5 to 50 W/W%.

一方、前記燃焼促進剤としては酸素、微粉炭及
び油が好ましい、酸素以外の燃焼促進剤の添加量
は10W/W%以上の範囲内の量で用いられるが、
経済性や効率の観点から10〜100W/W%の範囲
内で用いるのが好ましい。また酸素は、酸素含有
量25〜50%(容積)の酸素含有ガスとして炉中に
導入するのが一般的である。なお、酸素の供給方
法としては深冷分離法、吸着法及び酸素富化膜法
があるが、コスト及び操作性から酸素富化膜法が
好ましい。
On the other hand, the combustion accelerator is preferably oxygen, pulverized coal, and oil, and the amount of the combustion accelerator other than oxygen is within the range of 10 W/W% or more,
From the viewpoint of economy and efficiency, it is preferable to use it within the range of 10 to 100 W/W%. Further, oxygen is generally introduced into the furnace as an oxygen-containing gas having an oxygen content of 25 to 50% (by volume). Methods for supplying oxygen include a cryogenic separation method, an adsorption method, and an oxygen-enriched membrane method, and the oxygen-enriched membrane method is preferred from the viewpoint of cost and operability.

このような融剤や燃焼促進剤を添加することに
より分解、燃焼が促進され高効率の処理が出来る
し、融剤としてKOHのような水酸基を含有する
物質を添加した場合、マイクロ波がKOHの水酸
基に迅速に感応する特性を有するので、加熱速度
が大となるなど加熱効率が著しく向上する効果が
ある。
By adding such fluxing agents and combustion accelerators, decomposition and combustion are promoted and highly efficient processing is possible.If a substance containing hydroxyl groups such as KOH is added as a fluxing agent, microwaves can Since it has the property of rapidly responding to hydroxyl groups, it has the effect of significantly improving heating efficiency, such as increasing heating rate.

また、融剤や燃焼促進剤を用いる場合、予め被
処理物にこれらの添加剤を付着、吸収などさせて
おく前処理が出来るので、取扱いを簡便・安全に
行うことができる(有機塩素系化合物は、微量で
あつても猛毒なため取扱いが難しかつた)。
In addition, when using fluxing agents or combustion accelerators, it is possible to perform pre-treatment such as adhering and absorbing these additives to the object to be treated, which allows for easy and safe handling (organic chlorine compounds, etc.). It was difficult to handle because it was highly toxic even in small amounts).

かくて焼却炉3において高効率で分解、燃焼し
た被処理物は、二次燃焼炉10に導入されさらに
分解、燃焼が行われる。二次燃焼炉10は、その
炉材及び/又は炉壁の一部が焼却炉と同様の耐火
性マイクロ波吸収材によつて構成されており、マ
イクロ波発生装置4からのマイクロ波により同様
に高温状態に保持される。なお、72はマイクロ
波導波管である。
The material to be treated that has been decomposed and combusted with high efficiency in the incinerator 3 is introduced into the secondary combustion furnace 10, where it is further decomposed and combusted. The secondary combustion furnace 10 has a furnace material and/or a part of the furnace wall made of a fire-resistant microwave absorbing material similar to that of an incinerator, and the microwaves from the microwave generator 4 can be used in the same way. maintained at high temperatures. Note that 7 2 is a microwave waveguide.

二次燃焼炉10内の温度は800〜1500℃で、最
適温度は焼却炉3と同様に被処理物の種類や炉の
形状(滞留時間)などにより異なる。
The temperature inside the secondary combustion furnace 10 is 800 to 1500°C, and the optimum temperature, like the incinerator 3, varies depending on the type of material to be treated, the shape of the furnace (residence time), etc.

このように、焼却炉(加熱炉)と二次燃焼炉と
を組み合わせて行うと、極めて高効率で安定な処
理、運転が出来る。なお、経済性等から比較的高
効率のみでよい場合は、焼却炉3のみで目的が達
せられる。
In this way, by combining an incinerator (heating furnace) and a secondary combustion furnace, extremely highly efficient and stable processing and operation can be achieved. Note that if only relatively high efficiency is required due to economical reasons, the purpose can be achieved with only the incinerator 3.

しかして分解、燃焼後の排ガスはオフガスフア
ン11により排ガス洗浄塔12に送られ、該塔上
方から散布される吸収液中の吸収剤により洗浄さ
れ、被処理物から生成した塩素及び塩化水素が除
去される。吸収液タンク13に補給され、吸収液
ポンプ14により循環使用される。
The exhaust gas after decomposition and combustion is sent to the exhaust gas cleaning tower 12 by the off-gas fan 11, where it is cleaned by the absorbent in the absorption liquid sprayed from above the tower, and chlorine and hydrogen chloride generated from the material to be treated are removed. be done. It is replenished into the absorption liquid tank 13 and circulated by the absorption liquid pump 14.

循環する吸収液の一部は廃液処理槽15におい
て処理され、有害ガスを洗浄除去されたガスは煙
突16から排出される。
A part of the circulating absorption liquid is treated in a waste liquid treatment tank 15, and the gas from which harmful gases have been removed is discharged from a chimney 16.

実施例 2 図1に示した装置の焼却炉3による塩化ビニル
廃棄物の処理において、塩化ビニル廃棄物を破砕
処理した場合と破砕処理無しの場合について、焼
却炉3における処理速度を比較した。
Example 2 In the treatment of vinyl chloride waste by the incinerator 3 of the apparatus shown in FIG. 1, the processing speed in the incinerator 3 was compared between a case where the vinyl chloride waste was crushed and a case where the vinyl chloride waste was not crushed.

処理条件を以下に示す。 The processing conditions are shown below.

焼却炉の大きさ:50 マイクロ波吸収材:顆粒状炭化ケイ素 マイクロ波出力:4KW 塩化ビニル廃棄物の大きさ (処理なし):約6×5×1cm。Incinerator size: 50 Microwave absorber: granular silicon carbide Microwave power: 4KW Size of vinyl chloride waste (No treatment): Approximately 6 x 5 x 1 cm.

(処理有り):約1×1×1cmないしそれ以下。 (With treatment): Approximately 1 x 1 x 1 cm or less.

塩化ビニル廃棄物の処理法:衝撃式破砕機で破
砕後に、二軸せん断式破砕機で破砕。
Processing method for vinyl chloride waste: Crush it with an impact crusher and then crush it with a twin-shaft shear crusher.

その結果は以下のようであつた。 The results were as follows.

破砕処理した場合:3Kg/h 破砕処理無しの場合:1Kg/h 破砕した廃棄物の方が、燃焼速度は3倍もよか
つた。
With crushing treatment: 3 kg/h Without crushing treatment: 1 kg/h The combustion rate of crushed waste was three times higher.

〔発明の効果〕〔Effect of the invention〕

1 本発明の処理装置では、被処理物を予め破砕
しマイクロ波を加熱源として分解、燃焼処理す
るので 被処理物を、効率良く高温加熱することが
できる、 マイクロ波の出力制御が容易なことから、
加熱制御が容易である、 出力のON、OFFが迅速、簡便にできるの
で緊急時、スタート時、運転休止時の作業を
迅速、簡便に行うことができる、 排出ガス量が少なく構成機器が少なくて済
むので、装置を小型化でき、経済的に提供が
できる。、 温度斑が無く均一加熱ができ、最適で安定
な運転を継続することができる、 被処理物の分解、燃焼時に二時公害の原因
となる物質が生成する問題がない、 被処理物を予め破砕するものであるから、
種々、雑多の形状、寸法、物性の廃棄物を効
率良く処理することができる。したがつて実
験室、研究室レベルでも迅速かつ簡便に、有
機塩素系化合物により汚染された実験器具等
の処理・処分を行なうことができる。また、
有機塩素系化合物を試験、研究、実験で扱う
場合の器具類は塩ビ系、ポリエチレン系、テ
フロン系など有機系の樹脂が多いが、これら
も本発明方法により容易に燃焼処理できる、 などの効果がある。
1. In the processing apparatus of the present invention, the object to be processed is crushed in advance, and the object to be processed is decomposed and burned using microwaves as a heating source. Therefore, the object to be processed can be efficiently heated to a high temperature, and the output of the microwave can be easily controlled. from,
Heating is easy to control. Output can be turned on and off quickly and easily, so work can be done quickly and easily during emergencies, starting, and stopping operations. Low exhaust gas volume and fewer components. Therefore, the device can be downsized and provided economically. , Enables uniform heating with no temperature unevenness, allowing optimal and stable operation to continue; There is no problem of generation of substances that cause secondary pollution during decomposition or combustion of the processed material; Pre-heating of the processed material Because it is meant to be crushed,
Waste materials of various shapes, sizes, and physical properties can be efficiently processed. Therefore, it is possible to quickly and easily treat and dispose of laboratory equipment contaminated with organic chlorine compounds even at the laboratory level. Also,
The equipment used when handling organochlorine compounds in tests, research, and experiments is often made of organic resins such as PVC, polyethylene, and Teflon, and the method of the present invention has the advantage that these can also be easily burned and treated. be.

2 また、本発明の処理装置は被処理物の受入
槽、破砕装置、破砕物の移送装置及び燃焼装置
を備えてなるものであるから(必要により燃焼
排ガス処理用のスクラバーを設ける)、全体装
置を小型化することができ、設置面積の縮小化
が可能となる効果があり、さらに、前記燃焼装
置にマイクロ波を使用する焼却炉と、同じくマ
イクロ波を適用する二次燃焼炉とを組み合わせ
て構成したものであるため被処理物の分解、燃
焼処理の円滑、安定かつ効率良く実施する(焼
却炉は固体又は液体状の原料そのものの分解、
燃焼を、二次燃焼炉はガス化して同伴、飛散し
てくる被燃物の分解、燃焼を行なう)ことがで
きるなどの利点がある。
2. Furthermore, since the processing apparatus of the present invention is equipped with a receiving tank for the material to be treated, a crushing device, a transportation device for the crushed material, and a combustion device (a scrubber for processing combustion exhaust gas is provided if necessary), the entire device It has the effect of making it possible to downsize and reduce the installation area, and furthermore, by combining an incinerator that uses microwaves as the combustion device and a secondary combustion furnace that also applies microwaves. Because of its structure, it enables smooth, stable and efficient decomposition and combustion of the material to be treated.
The secondary combustion furnace has the advantage of being able to gasify and entrain, decompose and burn the scattered combustibles.

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

図面は本発明の実施態様を示すフローシートで
ある。 1……受入槽、11……破砕機、2……定量フ
イーダ、3……焼却炉、4……マイクロ波発生装
置、5……回転駆動装置、6……撹拌羽根、71
2……マイクロ波導波管、8……マイクロ波吸
収材、9……送気フアン、10……二次燃焼炉、
11……オフガスフアン、12……排ガス洗浄
塔、13……吸収液タンク、14……吸収液ポン
プ、15……廃液処理槽、16……煙突。
The drawings are flow sheets illustrating embodiments of the invention. 1... Receiving tank, 1 1 ... Crushing machine, 2... Quantitative feeder, 3... Incinerator, 4... Microwave generator, 5... Rotation drive device, 6... Stirring blade, 7 1 ,
7 2 ...Microwave waveguide, 8...Microwave absorber, 9...Air supply fan, 10...Secondary combustion furnace,
11...off gas fan, 12...exhaust gas cleaning tower, 13...absorption liquid tank, 14...absorption liquid pump, 15...waste liquid treatment tank, 16...chimney.

Claims (1)

【特許請求の範囲】 1 有機塩素系化合物又は有機塩素系化合物を含
む廃棄物をマイクロ波エネルギーにより分解、燃
焼処理するための装置において、前記被処理物の
受入槽と、該受入槽内の下方位置に配設した受け
入れた被処理物の破砕装置と、破砕された被処理
物を移送するための移送装置と、該移送された被
処理物を燃焼処理するための燃焼装置とを備えて
成り、該燃焼装置は少なくとも炉床の一部が耐火
性マイクロ波吸収材より成る焼却炉と、炉材及
び/又は炉壁の少なくとも一部が耐火性マイクロ
波吸収材より成る二次燃焼炉とを備えると共に、
これら焼却炉、二次燃焼炉のそれぞれにマイクロ
波導波管を介してマイクロ波発生装置を接続して
構成されていることを特徴とする有機塩素系化合
物又は有機塩素系化合物を含む廃棄物の処理装
置。 2 前記破砕装置が衝撃式破砕機及び/又は二軸
せん断式破砕機である特許請求の範囲第1項記載
の処理装置。
[Scope of Claims] 1. An apparatus for decomposing and burning organic chlorine compounds or waste containing organic chlorine compounds using microwave energy, including a receiving tank for the material to be treated and a lower part of the receiving tank. The apparatus is equipped with a crushing device for the received processed material arranged at a location, a transfer device for transferring the crushed processed material, and a combustion device for burning the transferred processed material. , the combustion apparatus includes an incinerator in which at least a part of the hearth is made of a refractory microwave absorbing material, and a secondary combustion furnace in which at least a part of the furnace material and/or the furnace wall is made of a refractory microwave absorbing material. Along with preparing,
Processing of organic chlorine compounds or waste containing organic chlorine compounds, characterized in that the incinerator and secondary combustion furnace are each connected to a microwave generator via a microwave waveguide. Device. 2. The processing device according to claim 1, wherein the crushing device is an impact crusher and/or a biaxial shear crusher.
JP2296386A 1986-02-06 1986-02-06 Disposal of organic chlorine family compound or waste containing organic chlorine family compound and its device Granted JPS62182520A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2296386A JPS62182520A (en) 1986-02-06 1986-02-06 Disposal of organic chlorine family compound or waste containing organic chlorine family compound and its device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2296386A JPS62182520A (en) 1986-02-06 1986-02-06 Disposal of organic chlorine family compound or waste containing organic chlorine family compound and its device

Publications (2)

Publication Number Publication Date
JPS62182520A JPS62182520A (en) 1987-08-10
JPH0532646B2 true JPH0532646B2 (en) 1993-05-17

Family

ID=12097239

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2296386A Granted JPS62182520A (en) 1986-02-06 1986-02-06 Disposal of organic chlorine family compound or waste containing organic chlorine family compound and its device

Country Status (1)

Country Link
JP (1) JPS62182520A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2014142114A1 (en) * 2013-03-11 2014-09-18 有限会社明幸経営企画研究所 Microwave type incineration method, and power generation device and recycling-based power generation system which utilize same

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4870378A (en) * 1971-12-27 1973-09-22
JPS4917466A (en) * 1972-04-07 1974-02-15
JPS62169913A (en) * 1986-01-22 1987-07-27 Ebara Res Co Ltd Disposing method and device for organic chlorine series compound or waste containing organic chlorine series compound

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4870378A (en) * 1971-12-27 1973-09-22
JPS4917466A (en) * 1972-04-07 1974-02-15
JPS62169913A (en) * 1986-01-22 1987-07-27 Ebara Res Co Ltd Disposing method and device for organic chlorine series compound or waste containing organic chlorine series compound

Also Published As

Publication number Publication date
JPS62182520A (en) 1987-08-10

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