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JP2005058979A - Detoxifying apparatus of injurious substance - Google Patents

Detoxifying apparatus of injurious substance Download PDF

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JP2005058979A
JP2005058979A JP2003318990A JP2003318990A JP2005058979A JP 2005058979 A JP2005058979 A JP 2005058979A JP 2003318990 A JP2003318990 A JP 2003318990A JP 2003318990 A JP2003318990 A JP 2003318990A JP 2005058979 A JP2005058979 A JP 2005058979A
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nitrogen
storage container
treatment
heat
chamber
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Hachishiro Isaka
八四郎 井坂
Masaki Shinozuka
正喜 篠塚
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SANSUI TECHNO KK
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SANSUI TECHNO KK
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Abstract

<P>PROBLEM TO BE SOLVED: To obtain an economical detoxifying apparatus of an injurious substance, in which hypoxia can be maintained, and the amount of nitrogen produced as a substitution material can be reduced. <P>SOLUTION: According to this detoxifying apparatus of the injurious substance, a treating chamber in which vacuum can be realized has an infra-red heat treating chamber therein, and a certain amount of the injurious substance is pooled in a before-internal-processing reservoir and thereafter is subjected to vacuum anoxia to be heat-harmlessness treated. Further, the detoxifying is carried out by a batch processing as one cycle composing a throwing-in of the injurious substance into the heat treating chamber, reducing pressure, heating harmlessness treatment, pressure return, and discharging. The treatment is carried out under nitrogen atmosphere instead of treating in air, and nitrogen removes oxygen pooled and mixed in a nitrogen storage case by a nitrogen manufacturing means to increase the purity of nitrogen. Further, the harmlessness treatment is carried out by a method for making the injurious substance pass through the infra-red heat treating chamber and heating it with the infra-red ray. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は焼却灰の処理方法に係り、焼却灰に含まれるダイオキシン等の有機塩素化合物を分解除去する処理方法に関するものである。The present invention relates to a method for treating incineration ash, and relates to a method for decomposing and removing organic chlorine compounds such as dioxin contained in incineration ash.

従来ダイオキシン対策のとられていない焼却場から出る焼却灰にはダイオキシンが残ったままで社会問題を起こしている。この焼却灰からダイオキシンを除去する一方法として図4に示す真空下の炉で加熱する方法がとられている。(例えば。特許文献1参照)
真空を確保するため炉40に焼却灰を投入するにあたり二重扉を設けた小部屋を仲介する方法をとっている。
炉内の空気を真空ポンプで吸引して真空にするとともに窒素を入れ酸素と置換していた。焼却灰を炉に投入する時は炉側扉44を閉め焼却灰を投入小部屋43に入れ、その後大気側扉45を閉じ焼却灰を炉に移し、最後に炉側扉44を閉め投入の1サイクルを終えている。排出は排出小部屋47を設け大気側扉48を閉め灰を排出小部屋47に入れ、その後炉側扉46を閉じ灰を大気側に移し、最後に大気側扉48を閉め排出の1サイクルを終えている。
特開2003−010825号公報
Dioxins remain in the incineration ash from incinerators that have not been treated for dioxins in the past, causing social problems. As a method for removing dioxins from the incinerated ash, a method of heating in a vacuum furnace shown in FIG. 4 is employed. (For example, see Patent Document 1)
In order to secure a vacuum, a method of mediating a small room provided with a double door when incineration ash is introduced into the furnace 40 is employed.
The air in the furnace was sucked with a vacuum pump to form a vacuum, and nitrogen was added to replace oxygen. When charging the incineration ash into the furnace, the furnace side door 44 is closed and the incineration ash is put into the input small chamber 43, then the atmosphere side door 45 is closed and the incineration ash is transferred to the furnace, and finally the furnace side door 44 is closed and input. The cycle is over. For discharge, a discharge small chamber 47 is provided, the atmosphere side door 48 is closed and ash is put into the discharge small room 47, then the furnace side door 46 is closed and the ash is transferred to the atmosphere side. Finally, the atmosphere side door 48 is closed and one cycle of discharge is performed. Finished.
Japanese Patent Laid-Open No. 2003-010825

しかし、この方法では処理量が扉開閉の一巡サイクルで決まり、焼却灰投入時に酸素が混入するため真空度と酸素濃度は真空ポンプの吸引量、窒素注入量で決まってしまい大量の処理をするには限界があった。However, in this method, the processing amount is determined by a cycle of opening and closing the door, and oxygen is mixed when incineration ash is charged. There was a limit.

本発明の第1の課題は従来の無害化装置に比べ時間あたりの処理量を増やす装置を提供することである。A first object of the present invention is to provide an apparatus that increases the amount of processing per hour as compared with a conventional detoxifying apparatus.

第2の課題は低酸素が維持でき、置換材料の窒素の製造量を少なくてすむ経済的な有害物質の無害化装置を提供することである。The second problem is to provide an economically detoxifying device for harmful substances that can maintain low oxygen and reduce the production amount of nitrogen as a replacement material.

上記課題を解決するために本発明の有害物質の無害化装置は真空が実現できる処理室の中に赤外線加熱処理室を持ち、一定量を内部処理前貯留容器に貯留した後減圧無酸素にして加熱無害化処理することを特徴とする。In order to solve the above-mentioned problems, the harmful substance detoxification apparatus of the present invention has an infrared heat treatment chamber in a treatment chamber capable of realizing a vacuum, and after storing a certain amount in a storage container before internal treatment, it is made oxygen-free under reduced pressure. It is characterized by heat detoxification treatment.

また、無害化は加熱処理室への投入、減圧、加熱無害化処理、圧力復帰、排出を1サイクルとするバッチ処理で行うことを特徴とする。Further, the detoxification is performed by batch processing in which one cycle is input to the heat treatment chamber, pressure reduction, heat detoxification treatment, pressure return, and discharge.

また、無酸素は空気中で処理する代わりに窒素雰囲気で処理することを特徴とする。Further, oxygen-free treatment is characterized by treating in a nitrogen atmosphere instead of treating in air.

また、窒素は窒素保管容器に貯留し混入した酸素を窒素製造手段により除去して窒素の純度をあげることを特徴とする。Further, nitrogen is stored in a nitrogen storage container, and the mixed oxygen is removed by nitrogen production means to increase the purity of nitrogen.

また、無害化処理は赤外線加熱処理室を通過させ赤外線で加熱することによる。Further, the detoxification treatment is performed by passing through an infrared heat treatment chamber and heating with infrared rays.

本発明による効果は次のとおりである。
従来方式に比べ時間当たりの処理量を増やせる。
無害化反応に最適な低酸素の雰囲気を容易に実現できる。
置換材料の窒素を再生する窒素製造手段が小さな設備ですみ経済的である。
The effects of the present invention are as follows.
The amount of processing per hour can be increased compared to the conventional method.
A low-oxygen atmosphere optimal for the detoxification reaction can be easily realized.
Nitrogen production means to regenerate nitrogen as a replacement material is small and economical.

本発明の有害物質の無害化装置は内部に赤外線加熱処理室3と内部貯留容器および駆動機構8と開閉ならびに密閉ができる扉で処理室2を構成する。
処理室2は減圧無酸素で有害物質を分解・無害化する部屋である。
処理前の焼却灰は外部処理前貯留容器6に貯留されており、処理後の灰は外部処理後貯留容器7に貯留される。
The harmful substance detoxification apparatus of the present invention comprises a processing chamber 2 with an infrared heat processing chamber 3, an internal storage container and a drive mechanism 8, and a door that can be opened and closed and sealed.
The processing chamber 2 is a chamber for decomposing and detoxifying harmful substances under reduced pressure and oxygen.
Incinerated ash before treatment is stored in a storage container 6 before external processing, and ash after processing is stored in a storage container 7 after external processing.

本発明の有害物質の無害化装置は請求項4に提案するように処理室2への投入、減圧、加熱無害化処理、圧力復帰、排出を1サイクルとするバッチ処理を行う。
処理室2の内部には受け入れ用として最低1個の内部処理前貯留容器を有する、内部処理前貯留容器が複数個あると熱効率をあげることができる。
The hazardous substance detoxification apparatus of the present invention performs batch processing with one cycle of charging into the processing chamber 2, depressurization, heating detoxification, pressure return and discharge as proposed in claim 4.
If there are a plurality of pre-internal storage containers having at least one pre-internal storage container for receiving inside the processing chamber 2, the thermal efficiency can be increased.

処理過程を順に説明する。投入は入口側扉10が開いた状態で外部処理前貯留容器6と内部処理前貯留容器4を連結し灰を外部処理前貯留容器6から内部処理前貯留容器4へ移動する。灰の移動が終わったら連結を切り離し入口側扉10を閉じる。The processing process will be described in order. The charging is performed by connecting the pre-external storage container 6 and the pre-internal storage container 4 with the entrance door 10 open, and moving the ash from the pre-external storage container 6 to the pre-internal storage container 4. When the movement of the ash is finished, the connection is disconnected and the entrance door 10 is closed.

次に処理室2の減圧にはいるが、減圧はこの作業と同時に処理室2の他端ではバッチ処理の最終サイクルである処理済の灰を外へ出す排出作業が行われており、投入と排出の両過程が終わった時点で扉10,11が閉まったあと行う。減圧は真空ポンプ21を作動させ処理室内気体を吸引することで実現し、真空度は10KP以下に減圧することが望ましい。Next, the processing chamber 2 is depressurized. At the same time as this operation, the depressurization is performed at the other end of the processing chamber 2 to discharge the processed ash, which is the final cycle of the batch processing, to the outside. This is performed after the doors 10 and 11 are closed at the time when both processes of discharging are completed. Depressurization is realized by operating the vacuum pump 21 and sucking the gas in the processing chamber, and the degree of vacuum is desirably reduced to 10 KP or less.

次に加熱無害化処理の詳細について説明する。
減圧達成後赤外線加熱処理室3の温度が600℃以上に上がるのを待って処理を開始する。もちろん、処理が継続していた場合で温度が600℃以上に達している場合には、減圧達成を待って処理が開始できる。
赤外線加熱処理室3は高温耐熱セラミックを素材とする炉であって赤外線放射性能に優れている。
赤外線加熱処理室3は入口に投入した灰を順次回転しながら送り出していき、この移動途中で炉壁からの赤外線によって加熱されダイオキシンを分解無害化する。
Next, the details of the heat detoxification process will be described.
After the pressure reduction is achieved, the process is started after the temperature of the infrared heat treatment chamber 3 rises to 600 ° C. or higher. Of course, when the process is continued and the temperature has reached 600 ° C. or higher, the process can be started after the pressure reduction is achieved.
The infrared heat treatment chamber 3 is a furnace made of a high-temperature heat-resistant ceramic and has excellent infrared radiation performance.
The infrared heat treatment chamber 3 sequentially feeds out the ash thrown into the inlet while rotating it, and is heated by infrared rays from the furnace wall during the movement to decompose and detoxify the dioxins.

加熱無害化処理するに当たっての内部貯留容器の動きについて入口・出口に各1個の貯留容器を設けた例で説明する。
外部貯留容器から投入された焼却灰は内部処理前貯留容器4に受け入れる、処理室を減圧した後焼却灰を排出して赤外線加熱処理室3に連続的に送り込む。
また、内部処理前貯留容器4は赤外線加熱処理室3から出た灰の熱と熱交換をし、2次加熱を行う。
内部処理後貯留容器5は赤外線加熱処理室3から出た灰を受け入れる容器であり、処理室2の灰を処理室外へ移し変える容器である。
The movement of the internal storage container during the heat detoxification process will be described with an example in which one storage container is provided at each of the inlet and the outlet.
The incinerated ash introduced from the external storage container is received in the pre-internal storage container 4, the processing chamber is decompressed, and then the incinerated ash is discharged and continuously sent to the infrared heat processing chamber 3.
In addition, the internal pre-treatment storage container 4 exchanges heat with the heat of the ash emitted from the infrared heat treatment chamber 3 and performs secondary heating.
The post-internal treatment storage container 5 is a container that receives the ash from the infrared heat treatment chamber 3, and is a container that transfers the ash in the processing chamber 2 to the outside of the processing chamber.

入口・出口各2個の容器を設けた例を図3にもとづき説明する。
外部貯留容器から投入された焼却灰は第1内部処理前貯留容器4aに受け入れる、第1内部処理前貯留容器4aでは一次加熱を行う、第2内部処理前貯留容器4bは焼却灰を赤外線加熱処理室3に連続的に送り込む容器である。
減圧加熱サイクルに入るときの入口側は第1内部処理前貯留容器4a、第2内部処理前貯留容器4b共に満杯にする、出口側は第1内部処理後貯留容器5aを空、第2内部処理後貯留容器5bを満杯にする。
第1内部処理前貯留容器4aから第2内部処理前貯留容器4bへの移動は第1内部処理前貯留容器4aから赤外線加熱処理室3への投入が完了した後行う。
第1内部処理後貯留容器5aは赤外線加熱処理室3から出た灰を受け入れる容器である、第2内部処理後貯留容器5bは処理室2の灰を処理室外へ移し変える容器である。
処理が開始されると赤外線加熱処理室3から出る灰を第1内部処理後貯留容器5aに受け入れる。
灰の移し変えは処理室2を大気圧にした後、第2内部処理後貯留容器5bを外部貯留容器に移し変え、空になった後第1内部処理後貯留容器5aから第2内部処理後貯留容器5bへの移しかえを行う。
An example in which two containers each for the inlet and outlet are provided will be described with reference to FIG.
The incinerated ash charged from the external storage container is received by the first pre-internal storage container 4a, the primary pre-internal storage container 4a performs primary heating, and the second internal pre-storage container 4b is subjected to infrared heat treatment of the incinerated ash. It is a container that continuously feeds into the chamber 3.
At the time of entering the reduced pressure heating cycle, the first pre-internal storage container 4a and the second pre-internal storage container 4b are filled on the inlet side, and the post-first internal storage container 5a is empty on the outlet side, the second internal process The rear storage container 5b is filled.
The movement from the first pre-internal storage container 4a to the second pre-internal storage container 4b is performed after the introduction from the first internal pre-storage container 4a to the infrared heat treatment chamber 3 is completed.
The first post-internal storage container 5a is a container that receives ash from the infrared heat treatment chamber 3, and the second post-internal storage container 5b is a container that transfers ash in the processing chamber 2 to the outside of the processing chamber.
When the treatment is started, the ash that comes out of the infrared heat treatment chamber 3 is received in the storage container 5a after the first internal treatment.
As for the transfer of ash, after the processing chamber 2 is brought to atmospheric pressure, the second internal post-treatment storage container 5b is transferred to the external storage container, and after emptying, the first internal post-treatment storage container 5a is used after the second internal treatment. Transfer to the storage container 5b is performed.

減圧無酸素手段について説明する。
処理室2でのダイオキシン分解・無害化は無酸素状態で行う。無酸素実現の第1の方法は処理室を大気圧に戻すとき大気を入れ、処理に先立ち真空ポンプで吸引し、無酸素実現のため処理室2へ窒素を注入する。この方法は処理室2が密閉された状態で窒素を置換するため注入する窒素が少量ですむ。
The decompression oxygen-free means will be described.
Dioxin decomposition and detoxification in the processing chamber 2 are performed in an oxygen-free state. In the first method for realizing oxygen-free, air is introduced when returning the processing chamber to the atmospheric pressure, and suction is performed with a vacuum pump prior to processing, and nitrogen is injected into the processing chamber 2 for realizing oxygen-free. In this method, a small amount of nitrogen is required to replace nitrogen while the processing chamber 2 is sealed.

本発明ではさらに強固な無酸素を実現するための第2の手段として請求項3を提案する。処理室2の圧力を大気圧に戻すとき大気の代わりに窒素を全量注入する。
毎回窒素の全量を入れ替えるのは不経済であり、真空ポンプ21の吸引ガスを窒素保管容器20に回収する。窒素は後述の熱交換媒体を兼ねており、処理室2から真空ポンプ21の間には吸引ガスの温度を下げる冷却手段23、飛灰、有害ガスを除去する集塵機22が付加されている。
The present invention proposes claim 3 as the second means for realizing stronger oxygen-free. When returning the pressure in the processing chamber 2 to atmospheric pressure, nitrogen is entirely injected instead of the atmosphere.
It is uneconomical to replace the entire amount of nitrogen each time, and the suction gas of the vacuum pump 21 is collected in the nitrogen storage container 20. Nitrogen also serves as a heat exchange medium, which will be described later. Between the processing chamber 2 and the vacuum pump 21, a cooling means 23 for lowering the temperature of the suction gas and a dust collector 22 for removing fly ash and harmful gas are added.

処理室2から窒素保管容器20へ回収した気体には処理室2の扉を開けたときに入り込んだ酸素等が混入していて窒素純度が下がっている。
この窒素保管容器20の窒素を処理室へ注入循環するには酸素を除去し純度をあげる必要がある、加えて、窒素の減量した分を補充する必要がある。
このため、請求項4に提案するように窒素製造手段19を加えている。窒素保管容器20の一部を抜き取り窒素製造手段19にいれ、純度の上がった窒素を窒素保管容器20に戻す、減量分は大気を窒素製造手段19に取り込み補充する。この方法により純度維持の図れた窒素が得られる。
The gas recovered from the processing chamber 2 to the nitrogen storage container 20 is mixed with oxygen or the like that has entered when the door of the processing chamber 2 is opened, and the purity of nitrogen is lowered.
In order to inject and circulate the nitrogen in the nitrogen storage container 20 into the processing chamber, it is necessary to remove oxygen and increase the purity. In addition, it is necessary to replenish the reduced amount of nitrogen.
For this reason, nitrogen production means 19 is added as proposed in claim 4. A part of the nitrogen storage container 20 is extracted and placed in the nitrogen production means 19, and the nitrogen having increased purity is returned to the nitrogen storage container 20. By this method, nitrogen having a maintained purity can be obtained.

焼却灰を加熱処理するために貯留容器を移しかえたり赤外線加熱処理室3を通すときに粉体の状態だと有害物質が灰に付着した状態で飛散してしまう。このため固形状態であることが望ましく、焼却灰に水を加え造粒加工することで固形状態の焼却灰が造れる。
ダイオキシンの分解は高温状態の滞留時間が長いほど完全になる。
焼却灰を処理室2に入れる前に乾燥し、温度を上げておくほと早く分解可能温度に達し分解も完全になる。
If the storage container is moved to heat the incinerated ash or passed through the infrared heat treatment chamber 3, if it is in a powder state, harmful substances will be scattered in a state of adhering to the ash. For this reason, it is desirable to be in a solid state, and incineration ash in a solid state can be made by adding water to the incineration ash and granulating it.
Dioxin decomposition becomes more complete as the residence time in the high temperature state increases.
The incinerated ash is dried before entering the processing chamber 2, and the temperature reaches a decomposable temperature as soon as the temperature is raised, and the decomposition becomes complete.

次に請求項5の熱交換について説明する。
赤外線加熱処理で加熱された灰と赤外線加熱処理室3から回収した熱をもちい処理前の焼却灰と熱交換をする。
完全真空中の熱交換は接触による熱伝導が、あるいは輻射熱の利用が可能であり、気体の対流による熱交換では熱交換できない。本装置は完全真空に至らない減圧下で処理を行なう、このため内部に存在する気体を熱交換媒体として利用する。気体の1つは窒素であり、もうひとつは焼却灰に含まれる水分が赤外線加熱処理室3で蒸発した水蒸気である。
処理室外の貯留容器では外気を取り込み出側の灰から熱を回収し、入り側の焼却灰を温める。入り側の焼却灰を温めた余熱は外気取り込み口に戻し更に熱を回収する。
Next, heat exchange according to claim 5 will be described.
The ash heated by the infrared heat treatment and the heat recovered from the infrared heat treatment chamber 3 are used to exchange heat with the incinerated ash before the treatment.
For heat exchange in a complete vacuum, heat conduction by contact or radiant heat can be used, and heat exchange by gas convection cannot be performed. This apparatus performs the process under a reduced pressure that does not reach a complete vacuum. For this reason, the gas existing inside is used as a heat exchange medium. One of the gases is nitrogen, and the other is water vapor in which water contained in the incinerated ash is evaporated in the infrared heat treatment chamber 3.
In the storage container outside the processing chamber, outside air is taken in, heat is recovered from the ash on the exit side, and the incineration ash on the entry side is warmed. Residual heat that warms the incineration ash on the entry side is returned to the outside air intake and further recovered.

熱の流れについて詳細に説明する。
第1の流れは窒素である、処理室2に注入する窒素は配管により内部処理後貯留容器5に入る。
内部処理後貯留容器5を出た窒素の一部は赤外線加熱処理室3に入る、内部処理後貯留容器5を出た窒素の残りは内部処理前貯留容器4に入る、赤外線加熱処理室3を出た窒素は次に内部処理前貯留容器4に入る。内部処理前貯留容器4に入った窒素は真空ポンプ20に吸引され処理室2の外へ出る。
処理室2の外に出た窒素は熱交換器24に入り第2の流れとなる空気と熱交換する。
次に冷却器23に入り常温まで温度が下げられる。次に集塵機22に入り混入した飛灰が除去される。最後に真空ポンプ21に入る。
The heat flow will be described in detail.
The first flow is nitrogen. Nitrogen injected into the processing chamber 2 enters the storage container 5 after internal processing through a pipe.
Part of the nitrogen that exits the storage container 5 after the internal treatment enters the infrared heat treatment chamber 3, and the rest of the nitrogen that exits the storage container 5 after the internal treatment enters the storage container 4 before the internal treatment. The discharged nitrogen then enters the pre-internal storage container 4. Nitrogen that has entered the pre-internal storage container 4 is sucked into the vacuum pump 20 and goes out of the processing chamber 2.
The nitrogen that has flowed out of the processing chamber 2 enters the heat exchanger 24 and exchanges heat with the air that forms the second flow.
Next, it enters the cooler 23 and the temperature is lowered to room temperature. Next, the fly ash mixed into the dust collector 22 is removed. Finally, the vacuum pump 21 is entered.

第2の流れは空気であり、この流れの最後につけたブロワー27により吸引され途中の容器中の灰や熱交換器で熱交換する。取り込まれた外気は熱交換器25に入りこの流れで取り込んだ熱と熱交換する。
熱交換器25を出た空気は外部処理後貯留容器7に入り灰の熱を奪い出て行く、次に熱交換器24に入り窒素と熱交換する。次に外部処理前貯留容器6に入り焼却灰の熱を奪い出て行く、次に熱交換器25に入る、最後に集塵機26で飛灰・ダイオキシンを除去する。
The second flow is air, which is sucked by the blower 27 attached at the end of this flow and exchanges heat with the ash in the container on the way or a heat exchanger. The taken outside air enters the heat exchanger 25 and exchanges heat with the heat taken in by this flow.
The air exiting the heat exchanger 25 enters the storage container 7 after external processing and takes away the heat of the ash, and then enters the heat exchanger 24 to exchange heat with nitrogen. Next, it enters the pre-external storage container 6 to take out the heat of the incinerated ash, then enters the heat exchanger 25, and finally the fly ash / dioxin is removed by the dust collector 26.

以上の処理を続けると内部処理前貯留容器4が空になり、内部処理後貯留容器5が満杯になる。このことを検知して加熱処理を終了にする。
処理室2の灰を排出するに当たり処理中は減圧しているため扉の開閉がしにくい。扉の開閉をスムーズに行うには扉開閉前に窒素保管容器20から窒素を処理室2へ注入し処理室内外の気圧を一致させる。
If the above processing is continued, the pre-internal storage container 4 becomes empty, and the post-internal storage container 5 becomes full. This is detected and the heat treatment is finished.
When discharging the ash in the processing chamber 2, the pressure is reduced during the processing, so it is difficult to open and close the door. In order to smoothly open and close the door, nitrogen is injected from the nitrogen storage container 20 into the processing chamber 2 before the door is opened and closed, and the atmospheric pressure inside and outside the processing chamber is matched.

次に最終ステップとして灰の排出について説明する。
灰の外だし作業は扉を開け内部処理後貯留容器5の灰を外部処理後貯留容器7に移動させる。
灰の移動は扉を開き、出側の外部処理後貯留容器7と内部処理後貯留容器5をそれぞれ連結して行う。
灰の移動が終了した後連結を切り離し扉を閉じて1バッチの処理が終了する。
Next, ash discharge will be described as a final step.
In the ash removal operation, the door is opened and the ash in the storage container 5 after the internal treatment is moved to the storage container 7 after the external treatment.
The ash is moved by opening the door and connecting the outlet external storage container 7 and the internal internal storage container 5 respectively.
After the movement of the ash is completed, the connection is cut off and the door is closed to complete one batch of processing.

本発明の開示例にはダイオキシンを含む焼却灰を例に開示しているが他の利用分野として有害物質を含むヘドロ、汚染土壌、汚泥、肉骨粉の無害化、あるいは重金属類の分離等に利用できる。In the disclosure example of the present invention, incinerated ash containing dioxin is disclosed as an example, but other fields of use include sludge containing hazardous substances, contaminated soil, sludge, meat and bone powder detoxification, or separation of heavy metals it can.

本装置の構成を示す図Diagram showing the configuration of this device 本装置の真空と熱交換の流れを示す図Diagram showing the flow of vacuum and heat exchange of this device 内部貯留容器が各2個の実施例を示す図The figure which shows an Example with two internal storage containers each 従来の無害化装置の構成を示す図The figure which shows the structure of the conventional harmless device

符号の説明Explanation of symbols

1・・本装置、2・・処理室、3・・赤外線加熱処理室、4・・内部処理前貯留容器、4a・・第1内部処理前貯留容器、4b・・第2内部処理前貯留容器、5・・内部処理後貯留容器、5a・・第1内部処理後貯留容器、5b・・第2内部処理後貯留容器、6・・外部処理前貯留容器、7・・外部処理後貯留容器、
10・・入口側扉、11・・出口側扉、19・・窒素製造手段、20・・窒素保管容器、21・・真空ポンプ、22・・集塵機、23・・冷却手段、24・・熱交換器、25・・熱交換器、26・・集塵機、27・・ブロワー、
40・・従来装置、41・・投入手段、42・・投入小部屋、43・・炉側扉、44・・大気側扉、46・・排出手段、47・・排出小部屋、48・・炉側扉、49・・大気側扉
1 .... this apparatus, 2 .... processing chamber, 3 .... infrared heat treatment chamber, 4 .... storage container before internal processing, 4a..first storage container before internal processing, 4b..second storage container before internal processing. 5, a storage container after internal processing, 5a, a storage container after first internal processing, 5b, a storage container after second internal processing, a storage container before external processing, a storage container after external processing,
10 .... Inlet side door, 11 .... Outlet side door, 19 .... Nitrogen production means, 20 .... Nitrogen storage container, 21 ... Vacuum pump, 22 .... Dust collector, 23 ... Cooling means, 24 ... Heat exchange , 25 ... Heat exchanger, 26 ... Dust collector, 27 ... Blower,
40 ··· Conventional device, 41 ············································································································· Side door, 49 ... Air side door

Claims (5)

内部に加熱炉と貯留容器と駆動手段を有する真空室を持ち、有害物質を間欠的に投入し無酸素の負圧下で加熱処理する有害物質の無害化装置。A harmful substance detoxifying device that has a vacuum chamber having a heating furnace, a storage container, and driving means inside, and intermittently throws in harmful substances and heat-treats them under oxygen-free negative pressure. 貯留容器を単位として有害物質を処理室外から内部処理前貯留容器入れる、と同時に処理後の有害物質を内部処理後貯留容器から処理室外に排出をする、有害物質の出し入れ終了後処理室を密閉し減圧無酸素にする、次に内部処理前貯留容器の有害物を順次加熱処理をする、ついで内部処理前貯留容器の有害物の処理が終了後処理室圧力を大気圧と同等に戻す、これら一連の処理を1バッチとして処理する処理方法。Toxic substances are put into the storage container before the internal treatment from the outside of the treatment chamber in units of storage containers, and at the same time, the harmful substances after treatment are discharged from the internal storage container to the outside of the treatment chamber. A series of these processes are performed in which the pressure is reduced and oxygen-free, then the harmful substances in the pre-internal storage container are sequentially heated, and then the processing chamber pressure is returned to the atmospheric pressure after the pre-internal storage container is processed. A processing method for processing the above as one batch. 処理室の無酸素化手段として窒素を用いる、処理室の減圧時に排出する窒素を回収する窒素保管容器を有し、処理室の圧力を外気圧と等しくするとき窒素保管容器から窒素を充填する有害物質の無害化装置。Hazardous in using nitrogen as an oxygen-free means in the processing chamber, having a nitrogen storage container that recovers nitrogen discharged when the processing chamber is depressurized, and filling the nitrogen from the nitrogen storage container when the processing chamber pressure is equal to the external pressure Substance detoxification equipment. 窒素保管容器の窒素は窒素再生手段へ循環させ酸素を除去し窒素の純度を上げることのできる有害物質の無害化装置。A detoxifying device for harmful substances that can circulate the nitrogen in the nitrogen storage container to the nitrogen regeneration means to remove oxygen and increase the purity of the nitrogen. 加熱処理室を出た有害物の熱と加熱処理室の熱を回収し処理前の有害物を加熱する手段を有する有害物質の無害化装置。A harmful substance detoxifying device having means for recovering the heat of a harmful substance leaving the heat treatment chamber and the heat of the heat treatment chamber and heating the harmful substance before the treatment.
JP2003318990A 2003-08-08 2003-08-08 Detoxifying apparatus of injurious substance Pending JP2005058979A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011088041A (en) * 2009-10-20 2011-05-06 Eads Co Ltd Continuous treatment method for vacuum oxygen-free pyrolysis treatment machine and unit type apparatus for the same
FR2961722A1 (en) * 2010-06-29 2011-12-30 Aprochim METHOD AND DEVICE FOR DECONTAMINATING POLLUTED MATERIALS
US9661848B2 (en) 2012-12-21 2017-05-30 Bayer Cropscience Ag Substituted 4-cyan-3-(pyridyl)-4-phenylbutanoates, method for the production thereof and uses as herbicides and plant growth regulators

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011088041A (en) * 2009-10-20 2011-05-06 Eads Co Ltd Continuous treatment method for vacuum oxygen-free pyrolysis treatment machine and unit type apparatus for the same
FR2961722A1 (en) * 2010-06-29 2011-12-30 Aprochim METHOD AND DEVICE FOR DECONTAMINATING POLLUTED MATERIALS
WO2012001247A3 (en) * 2010-06-29 2012-03-22 Aprochim Method and device for decontaminating polluted materials
US9661848B2 (en) 2012-12-21 2017-05-30 Bayer Cropscience Ag Substituted 4-cyan-3-(pyridyl)-4-phenylbutanoates, method for the production thereof and uses as herbicides and plant growth regulators

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