JP2001235125A - Induction heating type equipment for volume reduction treatment of macromolecular-series wastes - Google Patents
Induction heating type equipment for volume reduction treatment of macromolecular-series wastesInfo
- Publication number
- JP2001235125A JP2001235125A JP2000041150A JP2000041150A JP2001235125A JP 2001235125 A JP2001235125 A JP 2001235125A JP 2000041150 A JP2000041150 A JP 2000041150A JP 2000041150 A JP2000041150 A JP 2000041150A JP 2001235125 A JP2001235125 A JP 2001235125A
- Authority
- JP
- Japan
- Prior art keywords
- induction heating
- volume reduction
- waste
- reduction treatment
- polymer
- 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.)
- Withdrawn
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Incineration Of Waste (AREA)
- Gasification And Melting Of Waste (AREA)
- Processing Of Solid Wastes (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、現在埋立処分され
ている高分子系廃棄物を埋立処分地延命の観点から減容
処理する装置に関するものであり、2段階の温度で乾留
処理することによって有害な塩素を含まない乾留生成物
を得ることができる誘導加熱方式の乾留装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for reducing the volume of polymer waste that is currently landfilled from the viewpoint of extending the life of the landfill. The present invention relates to an induction heating type carbonization apparatus capable of obtaining a carbonization product containing no harmful chlorine.
【0002】[0002]
【従来の技術】一般家庭や工場などから排出される高分
子系廃棄物(プラスチック類やゴム類)は、発熱量が高
く焼却した場合に焼却炉内温度が上昇して炉壁を傷める
ため焼却炉の寿命が短くなることや、塩素を含む高分子
系廃棄物を焼却すると猛毒のダイオキシン類が発生する
ことなどの理由から埋立処分されるのが一般的である。
しかしこの埋立という方法は、高分子系廃棄物の嵩密度
が小さく、埋立処分後も体積が変らず、さらには埋立処
分地が不足しているという現状から、これらの高分子系
廃棄物の減容処理やリサイクル処理技術の開発が要望さ
れている。2. Description of the Related Art Polymer-based waste (plastics and rubbers) discharged from households and factories has a high calorific value and, when incinerated, increases the temperature inside the incinerator and damages the furnace wall. In general, the furnace is landfilled for reasons such as shortening the life of the furnace and burning highly toxic polymer-containing waste to produce highly toxic dioxins.
However, this method of landfilling reduces the volume of polymer waste because the bulk density of the polymer waste is low, the volume does not change after landfill, and there is a shortage of landfill sites. There is a demand for the development of waste treatment and recycling technologies.
【0003】この問題に対して、無酸素状態で高分子系
廃棄物を熱分解(乾留)することによって、ダイオキシ
ン類を発生させずに高分子系廃棄物を約1/10〜1/
20に減容・炭化させる装置や、これらの高分子系廃棄
物を高炉の原料としたり、あるいは材質別に選別したの
ちマテリアルリサイクルするなどの技術が開発されてい
る。しかし、このマテリアルリサイクルは、処理コスト
や処理不適物の混入などの問題からあまり適用されてお
らず、大部分の高分子系廃棄物はそのまま、あるいは減
容処理されたのちに埋立地に埋立処分されているのが現
実である。[0003] To solve this problem, the polymer waste is pyrolyzed (distilled) in an oxygen-free state, so that the polymer waste can be reduced to about 1/10 to 1/10 without generating dioxins.
Devices for reducing the volume and carbonizing to 20 have been developed, and techniques have been developed such as using these polymer-based wastes as raw materials for blast furnaces, or sorting them by material and then recycling the material. However, this material recycling is not widely applied due to problems such as treatment costs and contamination of unsuitable materials, and most polymer wastes are landfilled in landfills as they are or after volume reduction. That is the reality.
【0004】[0004]
【発明が解決しようとする課題】しかし、この高分子系
廃棄物を無酸素状態で乾留する方法では、廃棄物の体積
が小さくなるので埋立処分地の延命はできるものの、以
下のような解決すべき課題がある。熱分解などの減容処
理では、廃棄物に含まれる塩化ビニルや塩化ビニリデン
などの塩素系高分子が熱分解するときに塩化水素ガスが
発生するが、この塩化水素ガスは冷却塔などによって生
成した油を凝縮させた後にアルカリ剤などで洗浄するこ
とで除去している。しかし、この方法では大気に放出さ
れる塩化水素ガスは除去できるものの、乾留により生成
した油に塩化水素が混入し、この油を燃料油などとして
再利用しようとしたときに、油中に含まれる塩化水素に
よってダイオキシン類が生成する恐れがあり再利用用途
が限定されるという問題があった。However, according to the method of dry-distilling polymer waste in an oxygen-free state, the volume of the waste becomes small, so that the life of the landfill site can be extended, but the following problems are solved. There are issues to be addressed. In volume reduction treatment such as thermal decomposition, hydrogen chloride gas is generated when chlorine-based polymers such as vinyl chloride and vinylidene chloride contained in waste are thermally decomposed, and this hydrogen chloride gas is generated by cooling towers etc. After condensing the oil, it is removed by washing with an alkaline agent or the like. However, this method can remove hydrogen chloride gas released to the atmosphere, but hydrogen chloride is mixed in oil produced by dry distillation, and this oil is included in oil when it is reused as fuel oil etc. There has been a problem that dioxins may be generated by hydrogen chloride, and reuse is limited.
【0005】また、生成する油に塩化水素が混入しない
ように、あらかじめ被乾留廃棄物であるプラスチック類
に塩化水素除去剤である炭酸カルシウムなどを混合、あ
るいは噴霧しながら乾留する方法も実施されているが、
この方法では塩化水素と反応して生成した塩化カルシウ
ムなどが炭化物と一緒に排出されるため,減容率が悪く
なるなどの問題があった。[0005] In order to prevent hydrogen chloride from being mixed into the produced oil, a method has been practiced in which plastics, which are wastes to be distilled, are mixed or sprayed with calcium carbonate as a hydrogen chloride remover in advance. But
In this method, calcium chloride and the like generated by reacting with hydrogen chloride are discharged together with the carbides, so that there has been a problem that the volume reduction rate is deteriorated.
【0006】本発明は、上記の点に鑑みてなされたもの
であり、その目的は高分子廃棄物を乾留したときに生成
する塩化水素ガスを、油などの乾留生成物に混入させな
いで除去でき、かつ減容率を低下させない誘導加熱式減
容処理装置を提供することにある。SUMMARY OF THE INVENTION The present invention has been made in view of the above points, and has as its object to remove hydrogen chloride gas generated when carbonized high-molecular waste is produced without being mixed into a dry-distilled product such as oil. Another object of the present invention is to provide an induction heating type volume reduction processing apparatus which does not lower the volume reduction rate.
【0007】[0007]
【課題を解決するための手段】上記の課題を解決するた
めに、本発明に基づく一般廃棄物あるいは産業廃棄物と
して排出される高分子系廃棄物の誘導加熱式の減容処理
装置は、前記高分子系廃棄物を脱塩素処理する誘導加熱
コイルとスクリュー式フィーダーより成る前段の誘導加
熱部と、脱塩素された前記高分子系廃棄物を脱塩素の温
度より高い温度で乾留炭化する誘導加熱コイルと乾留キ
ルンより成る後段の誘導加熱部とを、溶融した高分子系
廃棄物で塩化水素ガスを遮断しつつ直列に接続した構成
にするものとする。In order to solve the above-mentioned problems, an induction heating type volume reduction treatment apparatus for polymer waste discharged as general waste or industrial waste according to the present invention comprises An induction heating section comprising an induction heating coil and a screw-type feeder for dechlorinating polymer waste, and induction heating for dry distillation and carbonizing the dechlorinated polymer waste at a temperature higher than the dechlorination temperature. The coil and the subsequent induction heating section composed of the carbonization kiln are connected in series while shutting off hydrogen chloride gas with molten polymer waste.
【0008】その際に、前記の脱塩素処理のための前段
の誘導加熱部は150〜300℃の温度であり、乾留炭
化を行うための後段の誘導加熱部の温度は500〜60
0℃であるものとする。また、脱塩素処理のための前段
の誘導加熱部の後には、発生した塩化水素ガスを引き抜
くための配管が接続され、この配管は塩化水素ガス処理
のための薬液洗浄塔に接続されるものとする。At this time, the temperature of the induction heating section in the former stage for the dechlorination treatment is 150 to 300 ° C., and the temperature of the induction heating section in the latter stage for performing dry distillation carbonization is 500 to 60 ° C.
It shall be 0 ° C. Also, after the induction heating section at the former stage for the dechlorination treatment, a pipe for extracting the generated hydrogen chloride gas is connected, and this pipe is connected to the chemical cleaning tower for the hydrogen chloride gas treatment. I do.
【0009】さらに、乾留炭化を行うための後段の誘導
加熱部の後には、炭化物貯留槽と、乾留炭化により生成
した油を凝縮させるための冷却塔と、同時に生成する非
凝縮性の炭化水素ガス類を燃焼させるためのガス燃焼塔
とが接続されるものとする。Further, after the induction heating section at a later stage for performing dry distillation carbonization, a carbide storage tank, a cooling tower for condensing oil generated by dry distillation carbonization, and a non-condensable hydrocarbon gas generated simultaneously. And a gas combustion tower for burning species.
【0010】[0010]
【発明の実施の形態】上記の手段で述べた各装置を全て
含んだ本発明の誘導加熱式減容処理装置は、ホッパーに
投入された高分子系廃棄物を誘導加熱コイル内に押し込
むスクリュー式フィーダーと150〜300℃の温度に
加熱する誘導加熱コイルとで成る前段の誘導加熱部と、
前段の誘導加熱部の後に発生した塩化水素ガスを引き抜
くためのガス洗浄塔と、脱塩素された高分子系廃棄物を
500〜600℃の温度で乾留し炭化する誘導加熱コイ
ルと乾留キルンより成る後段の誘導加熱部と、乾留キル
ンから排出された炭化物をガスと分離し貯留する炭化物
貯留槽と、乾留炭化により生成した油を凝縮させるため
の冷却塔と、乾留により生成する非凝縮性の炭化水素ガ
ス類を燃焼させるためのガス燃焼塔と、から構成され
る。BEST MODE FOR CARRYING OUT THE INVENTION The induction heating type volume reduction treatment apparatus of the present invention including all the apparatuses described in the above means is a screw type for pushing polymer waste put in a hopper into an induction heating coil. A pre-stage induction heating section comprising a feeder and an induction heating coil for heating to a temperature of 150 to 300 ° C;
It consists of a gas washing tower for extracting hydrogen chloride gas generated after the previous induction heating section, an induction heating coil for carbonizing and decarbonizing dechlorinated polymer waste at a temperature of 500 to 600 ° C, and a carbonization kiln. Induction heating section at the later stage, carbide storage tank that separates and stores carbide discharged from carbonization kiln from gas, cooling tower for condensing oil generated by carbonization, and non-condensable carbonization generated by carbonization And a gas combustion tower for burning hydrogen gas.
【0011】なお、脱塩素を行う加熱されたスクリュー
式フィーダーと、脱塩素された高分子系廃棄物を乾留炭
化するための乾留キルンとは、脱塩素され溶融状態にあ
る高分子系廃棄物がスクリューによって乾留キルンに押
し込まれるようになっているため、前段の加熱で発生し
た塩化水素ガスは乾留キルンに入らずに排ガス処理装置
に導かれるようになっている。The heated screw feeder for dechlorination and the carbonization kiln for carbonizing the dechlorinated polymer waste are a polymer waste in a molten and dechlorinated state. Since the screw is pushed into the carbonization kiln, the hydrogen chloride gas generated by the heating in the preceding stage is guided to the exhaust gas treatment device without entering the carbonization kiln.
【0012】前記のように、一旦150〜300℃の温
度で加熱脱塩素した高分子系廃棄物を、さらに高い温度
である500〜600℃で乾留炭化することによって、
高分子系廃棄物の体積を1/10〜1/20に減容でき
るとともに、乾留生成物である炭化物や凝縮油には塩素
が含まれていないため、これらを焼却しても有害なダイ
オキシン類を発生することがなく、さらに体積を減容で
きる。また,150〜300℃の比較的低温でかつ無酸
素状態で脱塩素が行われるため、ダイオキシン類は発生
せず排ガス処理塔の薬剤を水とすれば塩酸の回収もでき
る利点もある。 〔実施例〕以下、本発明に基づく高分子系廃棄物の減容
処理装置の一実施態例を図面を参照しながら説明する。As described above, the polymer waste once heated and dechlorinated at a temperature of 150 to 300 ° C. is dry-distilled and carbonized at a higher temperature of 500 to 600 ° C.
The volume of polymer waste can be reduced to 1/10 to 1/20 and dioxins that are harmful even if they are incinerated, because carbonization and condensed oil as dry distillation products do not contain chlorine. Does not occur, and the volume can be further reduced. In addition, since dechlorination is performed at a relatively low temperature of 150 to 300 ° C. and in an oxygen-free state, there is an advantage that dioxins are not generated and hydrochloric acid can be recovered if water is used as a chemical in the exhaust gas treatment tower. [Embodiment] An embodiment of a polymer waste volume reducing apparatus according to the present invention will be described below with reference to the drawings.
【0013】図1は、本発明に基づく高分子系廃棄物の
減容装置の一構成例を説明するための模式図である。こ
の図において、減容処理する高分子系廃棄物は、ホッパ
ー1の中に投入される。このホッパ1にはスクリューフ
ィーダー2および3が設置されており、このスクリュー
フィーダー2および3は、誘導加熱コイルa4で150
〜300℃に加熱され、投入された高分子系廃棄物は圧
縮されつつ加熱溶融し、次工程へと送られる。このとき
溶融した高分子系廃棄物に含まれる塩化ビニルや塩化ビ
ニリデンなどの含塩素高分子からは、脱塩素反応により
塩化水素が発生する。スクリューフィーダー2で脱離し
た塩化水素ガスは、配管5を通ってガス洗浄塔6に送ら
れ、ここで無害化処理され大気に放出される。そして脱
塩素化された高分子系廃棄物は、次段のスクリューフィ
ーダー3により溶融しながら乾留キルン9に送られるの
で、スクリューフィーダー2の工程で発生した塩化水素
ガスは乾留キルン9に入ることはない。FIG. 1 is a schematic diagram for explaining one configuration example of a polymer-based waste volume reducing apparatus according to the present invention. In this figure, polymer waste to be subjected to volume reduction processing is put into a hopper 1. The hopper 1 is provided with screw feeders 2 and 3.
The polymer waste that is heated to about 300 ° C. and injected is heated and melted while being compressed, and sent to the next step. At this time, hydrogen chloride is generated from a chlorine-containing polymer such as vinyl chloride and vinylidene chloride contained in the molten polymer waste by a dechlorination reaction. The hydrogen chloride gas desorbed by the screw feeder 2 is sent to a gas washing tower 6 through a pipe 5, where it is detoxified and released to the atmosphere. Then, the dechlorinated polymer waste is sent to the carbonization kiln 9 while being melted by the screw feeder 3 at the next stage, so that the hydrogen chloride gas generated in the step of the screw feeder 2 cannot enter the carbonization kiln 9. Absent.
【0014】乾留キルン9は、誘導加熱コイルb8によ
り500〜600℃に加熱されながら、キルン回転モー
タ7により一定速度で回転し、乾留キルン9に投入され
た高分子系廃棄物は乾留されながら出口へと運ばれる。
乾留キルン9に導入された高分子系廃棄物は、乾留キル
ン9内で無酸素状態で熱分解して炭化減容される。この
際、発生するガスは配管11を通って接続されたガス冷
却塔12によって冷却され、冷却されることによって凝
縮した油、水等はガス冷却塔12の下部に溜まる。な
お、乾留は塩素がなく、かつ無酸素状態で行われるの
で、この乾留生成ガス中にはダイオキシン類は含まれな
い。この冷却によって凝縮しなかった低級炭化水素類
は、さらに配管13を介して接続されたガス燃焼塔14
により焼却処理される。乾留生成物である炭化物、油お
よびガス中には塩素が含まれていないため、これらを焼
却してもダイオキシン類は発生しない。したがって、こ
れらの乾留生成物を焼却して、サーマルリサイクルする
ことができる利点もある。 〔比較例〕図2は従来の高分子系廃棄物の減容処理装置
の一構成例を説明するための模式図であるが、この従来
の装置を用いて高分子系廃棄物の減容処理を行った結果
の一例を表1に示す。なお、図2には図1と共通な部材
は同一符号を付してあるが、図1と異なる点は、500
〜600℃で乾留炭化する前に脱塩素していない点にあ
り、したがって、ガス洗浄塔もガス冷却塔の後段に設置
されている。The carbonization kiln 9 is rotated at a constant speed by the kiln rotating motor 7 while being heated to 500 to 600 ° C. by the induction heating coil b8. Transported to
The polymer waste introduced into the carbonization kiln 9 is thermally decomposed in an oxygen-free state in the carbonization kiln 9 and carbonized and reduced in volume. At this time, the generated gas is cooled by a gas cooling tower 12 connected through a pipe 11, and oil, water, and the like condensed by the cooling accumulate in a lower portion of the gas cooling tower 12. Since dry distillation is performed without chlorine and in an oxygen-free state, dioxins are not contained in the dry distillation product gas. The lower hydrocarbons that have not been condensed by this cooling are further separated into gas combustion towers 14 connected via a pipe 13.
By incineration. Since carbonization, oil and gas, which are the products of carbonization, do not contain chlorine, even if they are incinerated, no dioxins are generated. Therefore, there is an advantage that these dry distillation products can be incinerated and thermally recycled. [Comparative Example] FIG. 2 is a schematic diagram for explaining an example of the configuration of a conventional polymer waste volume reduction apparatus. The conventional apparatus is used to reduce the volume of polymer waste. Table 1 shows an example of the result of the above. In FIG. 2, members common to FIG. 1 are denoted by the same reference numerals, but the difference from FIG.
The point is that it is not dechlorinated before carbonization at -600 ° C., and therefore, the gas washing tower is also installed after the gas cooling tower.
【0015】[0015]
【表1】 表1の結果から明らかなように、従来の高分子系廃棄物
の減容処理装置での処理では、脱塩素しないで乾留した
生成物中には塩素が含まれており(炭化物中塩素濃度:
62g/kg)、この生成物を焼却処理した場合には、
燃焼排ガス中にダイオキシン類が含まれるおそれがあ
る。[Table 1] As is evident from the results in Table 1, in a conventional polymer waste treatment in a volume reduction treatment device, chlorine was contained in a product that was carbonized without dechlorination (chlorine concentration in carbide:
62 g / kg), when this product is incinerated,
Dioxins may be contained in the combustion exhaust gas.
【0016】ところで、図3の各種プラスチックの加熱
温度と重量減少の関係を示す線図によると、塩素を含む
プラスチックである塩化ビニル樹脂は150℃から重量
減少が始まり、約300℃付近で一旦重量減少が止まっ
ている。この最初の重量減少は脱塩素が起っていること
を示している。また、塩化ビニル樹脂で350℃付近か
ら再び始まる重量減少は熱分解を示しており、塩化ビニ
ル樹脂がより低分子の炭化水素に分解していることを示
している。しかし、その他のプラスチックのユリア樹脂
とポリウレタンを除くと、大部分の塩素を含まないプラ
スチックは,300℃付近から熱分解による重量減少が
始まっている。したがって、この図からは高分子系廃棄
物を150〜300℃の温度で加熱すれば、プラスチッ
クは軟化するものの熱分解は起らず脱塩素のみが起るこ
とが分かる。According to the graph of FIG. 3 showing the relationship between the heating temperature of various plastics and the weight loss, the vinyl chloride resin, which is a plastic containing chlorine, starts to lose weight at 150 ° C. and once at about 300 ° C. The decline has stopped. This initial weight loss indicates that dechlorination has occurred. The weight loss of the vinyl chloride resin, which starts again at around 350 ° C., indicates thermal decomposition, indicating that the vinyl chloride resin is decomposed into lower-molecular hydrocarbons. However, except for other plastics such as urea resin and polyurethane, most chlorine-free plastics begin to lose weight at about 300 ° C. due to thermal decomposition. Therefore, it can be seen from this figure that when the polymer-based waste is heated at a temperature of 150 to 300 ° C., the plastic is softened but the thermal decomposition does not occur but only the dechlorination occurs.
【0017】そこで、従来、単純に500〜600℃で
乾留炭化するようになっていた誘導加熱式減容処理装置
を、図1に示す本発明の誘導加熱式減容処理装置のよう
に500〜600℃で乾留炭化する前に、150〜30
0℃で脱塩素処理して発生した塩化水素ガスを除去し、
その後500〜600℃乾留すれば、その生成物である
炭化物や凝縮油中には塩素は含まれないことになる。Therefore, an induction heating type volume reduction treatment apparatus which has been conventionally simply carbonized at 500 to 600 ° C. is replaced with an induction heating type volume reduction treatment apparatus as shown in FIG. Before carbonizing at 600 ° C, 150 ~ 30
Removes hydrogen chloride gas generated by dechlorination at 0 ° C,
After that, if carbonization is performed at 500 to 600 ° C., chlorine is not contained in the carbonized product or the condensed oil as the product.
【0018】[0018]
【発明の効果】以上述べたように、本発明の高分子系廃
棄物の誘導加熱式減容処理装置では、従来の誘導加熱式
減容処理装置に比べて、同じ程度の減容率を確保しつつ
乾留生成物には塩素が含まれないので、これらの乾留生
成物を焼却しても有害なダイオキシン類は発生しないた
め燃料として再利用でき、ほとんど埋立処分量をゼロと
することができる。また、脱塩素処理により回収された
塩化水素は不純物をほとんど含まないため、中和剤など
の塩酸として再利用可能である。As described above, the induction heating type volume reduction treatment apparatus for polymer waste of the present invention secures the same volume reduction rate as the conventional induction heating type volume reduction processing apparatus. In addition, since the carbonized product does not contain chlorine, harmful dioxins are not generated even if these carbonized products are incinerated, so that they can be reused as fuel, and the amount of landfill disposal can be reduced to almost zero. Further, hydrogen chloride recovered by the dechlorination treatment contains almost no impurities, and can be reused as hydrochloric acid such as a neutralizing agent.
【図1】本発明に基づく高分子系廃棄物の誘導加熱式減
容処理装置の一構成例を説明するための模式図FIG. 1 is a schematic view for explaining an example of the configuration of an apparatus for induction-heating volume reduction of polymer waste according to the present invention.
【図2】従来の高分子系廃棄物の誘導加熱式減容処理装
置の一構成例を説明するための模式図。FIG. 2 is a schematic diagram for explaining one configuration example of a conventional polymer heating waste induction heating type volume reduction treatment apparatus.
【図3】各種プラスチックの加熱温度と重量減少を示す
線図FIG. 3 is a diagram showing the heating temperature and weight loss of various plastics.
1: ホッパー 2: スクリューフィーダー 3: スクリューフィーダー 4: 誘導加熱コイルa 5: 配管 6: ガス洗浄塔 7: キルン回転モータ 8: 誘導加熱コイルb 9: 乾留キルン 10: 炭化物貯留槽 11: 配管 12: ガス冷却塔 13: 配管 14: ガス燃焼塔 1: hopper 2: screw feeder 3: screw feeder 4: induction heating coil a 5: piping 6: gas washing tower 7: kiln rotating motor 8: induction heating coil b 9: dry distillation kiln 10: carbide storage tank 11: piping 12: Gas cooling tower 13: Piping 14: Gas combustion tower
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F23G 5/02 ZAB B09B 3/00 ZAB 5/14 ZAB 303G (72)発明者 林 静男 神奈川県川崎市川崎区田辺新田1番1号 富士電機株式会社内 Fターム(参考) 3K061 AA07 AB02 AC13 BA04 BA05 BA08 CA13 FA10 3K065 AA07 AB02 AC13 BA04 BA05 BA08 CA20 3K078 AA04 AA05 AA08 BA03 BA08 BA22 BA26 CA02 4D004 AA07 AA08 AB06 AC05 BA03 BA06 BB03 CA22 CA24 CA25 CA26 CA27 CA29 CB09 CB33 DA03 DA06 4F301 AA03 AA11 AA21 CA09 CA25 CA26 CA36 CA46 CA52 CA68 CA72 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) F23G 5/02 ZAB B09B 3/00 ZAB 5/14 ZAB 303G (72) Inventor Shizuo Hayashi Kawasaki Kawasaki, Kanagawa Prefecture 1-1, Tanabe-Shinden-ku, Fuji Electric Co., Ltd. F-term (reference) BA06 BB03 CA22 CA24 CA25 CA26 CA27 CA29 CB09 CB33 DA03 DA06 4F301 AA03 AA11 AA21 CA09 CA25 CA26 CA36 CA46 CA52 CA68 CA72
Claims (5)
される高分子系廃棄物の誘導加熱式の減容処理装置にお
いて、前記高分子系廃棄物を脱塩素処理する誘導加熱コ
イルとスクリュー式フィーダーより成る前段の誘導加熱
部と、脱塩素された前記高分子系廃棄物を脱塩素の温度
より高い温度で乾留炭化する誘導加熱コイルと乾留キル
ンより成る後段の誘導加熱部とを、直列に接続したこと
を特徴とする高分子系廃棄物の誘導加熱式減容処理装
置。1. An induction heating type volume reduction treatment apparatus for polymer waste discharged as general waste or industrial waste, wherein an induction heating coil and a screw type feeder for dechlorinating the polymer waste. A series induction heating section comprising a pre-stage induction heating section, an induction heating coil configured to dry-carbonize the dechlorinated polymer waste at a temperature higher than the dechlorination temperature, and a post-stage induction heating section including a carbonization kiln. An induction heating type volume reduction treatment device for polymer waste, characterized in that:
前記脱塩素処理のための前段の誘導加熱部は150〜3
00℃の温度であり、前記乾留炭化を行うための後段の
誘導加熱部の温度は500〜600℃であることを特徴
とする高分子系廃棄物の減容処理装置。2. The volume reduction processing device according to claim 1,
The induction heating section at the preceding stage for the dechlorination treatment is 150 to 3
An apparatus for reducing volume of polymer-based waste, wherein the temperature is 00 ° C., and the temperature of a subsequent induction heating section for performing the carbonization is 500 to 600 ° C.
装置において、前記脱塩素処理のための前段の誘導加熱
部の後に、発生した塩化水素ガスを引き抜くための配管
が接続され、この配管は塩化水素ガス処理のための薬液
洗浄塔に接続されることを特徴とする高分子系廃棄物の
減容処理装置。3. A volume reduction treatment apparatus according to claim 1, wherein a pipe for extracting generated hydrogen chloride gas is connected after an induction heating section at a former stage for the dechlorination treatment, The pipe is connected to a chemical cleaning tower for treating hydrogen chloride gas.
装置において、前記乾留炭化を行うための後段の誘導加
熱部の後に、炭化物貯留槽と、乾留炭化により生成した
油を凝縮させるための冷却塔と、同時に生成する非凝縮
性の炭化水素ガス類を燃焼させるためのガス燃焼塔とが
接続されることを特徴とする高分子系廃棄物の減容処理
装置。4. A volume reduction treatment apparatus according to claim 1, wherein a carbide storage tank and an oil generated by the dry distillation carbonization are condensed after a subsequent induction heating section for performing the dry distillation carbonization. And a cooling tower for burning a non-condensable hydrocarbon gas generated at the same time.
装置において、請求項3の前記配管と前記薬液洗浄塔、
および請求項4の前記炭化物貯留槽と前記冷却塔と、前
記ガス燃焼塔とが共に接続されることを特徴とする高分
子系廃棄物の減容処理装置。5. The volume reduction treatment apparatus according to claim 1, wherein the pipe and the chemical liquid washing tower according to claim 3 are provided.
5. The apparatus for reducing volume of polymer-based waste according to claim 4, wherein the carbide storage tank, the cooling tower, and the gas combustion tower are connected together.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000041150A JP2001235125A (en) | 2000-02-18 | 2000-02-18 | Induction heating type equipment for volume reduction treatment of macromolecular-series wastes |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000041150A JP2001235125A (en) | 2000-02-18 | 2000-02-18 | Induction heating type equipment for volume reduction treatment of macromolecular-series wastes |
Publications (1)
Publication Number | Publication Date |
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JP2001235125A true JP2001235125A (en) | 2001-08-31 |
Family
ID=18564424
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Application Number | Title | Priority Date | Filing Date |
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JP2000041150A Withdrawn JP2001235125A (en) | 2000-02-18 | 2000-02-18 | Induction heating type equipment for volume reduction treatment of macromolecular-series wastes |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005083633A (en) * | 2003-09-08 | 2005-03-31 | Fuji Electric Systems Co Ltd | Induction heating type pyrolysis furnace |
CN111678155A (en) * | 2020-06-10 | 2020-09-18 | 青岛羚角化工技术有限责任公司 | Tubular furnace incineration system |
-
2000
- 2000-02-18 JP JP2000041150A patent/JP2001235125A/en not_active Withdrawn
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005083633A (en) * | 2003-09-08 | 2005-03-31 | Fuji Electric Systems Co Ltd | Induction heating type pyrolysis furnace |
CN111678155A (en) * | 2020-06-10 | 2020-09-18 | 青岛羚角化工技术有限责任公司 | Tubular furnace incineration system |
CN111678155B (en) * | 2020-06-10 | 2021-09-10 | 广东洁冠科技有限公司 | Tubular furnace incineration system |
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