JPH11148631A - Incinerator and incinerating method for contaminated soil or the like - Google Patents

Incinerator and incinerating method for contaminated soil or the like

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Publication number
JPH11148631A
JPH11148631A JP9334903A JP33490397A JPH11148631A JP H11148631 A JPH11148631 A JP H11148631A JP 9334903 A JP9334903 A JP 9334903A JP 33490397 A JP33490397 A JP 33490397A JP H11148631 A JPH11148631 A JP H11148631A
Authority
JP
Japan
Prior art keywords
incineration
exhaust gas
contaminated soil
waste
high calorie
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.)
Pending
Application number
JP9334903A
Other languages
Japanese (ja)
Inventor
Kanichi Ito
寛一 伊藤
Yoshiaki Ishii
善明 石井
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
Original Assignee
Ebara Corp
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 filed Critical Ebara Corp
Priority to JP9334903A priority Critical patent/JPH11148631A/en
Publication of JPH11148631A publication Critical patent/JPH11148631A/en
Pending legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To reduce high grade fuel, e.g. gas or petroleum, required for incineration by adding high calorie waste to contaminated soil, and the like, and then incinerating them. SOLUTION: Contaminated soil 12 to be incinerated is thrown along with high calorie waste 14, e.g. waste plastic, into the body 21 of a fluidized bed incinerator 20 through a hopper 22. The contaminated soil 12 and the high calorie waste 14 thrown into the body 21 are fluidized along with sand in the fluidizing chamber 24 by means of heated air and then crushed. At the same time, the contaminated soil 12 is subjected to incineration at a constant temperature of 950 deg.C or below through combustion of the high calorie waste 14 fired by a heating burner 26. Consequently, contaminants are volatilized and organic substances are decomposed and evaporated. After incineration, the contaminated soil 12 and coarse inflammable matters 16 contained in the high calorie waste 14 are fed through a discharge pipe 28 to a vibratory sieve 29 and separated from sand. The sand is returned back to the fluidized bed and used in the next incineration process.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、汚染土壌類の焼却
浄化方法及び焼却浄化装置に係り、特に有機ハロゲン化
合物等の汚染物質を含む汚染土壌類の焼却浄化方法及び
焼却浄化装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and apparatus for incineration and purification of contaminated soils, and more particularly to a method and apparatus for incineration and purification of contaminated soils containing contaminants such as organic halogen compounds.

【0002】[0002]

【従来の技術】近年、産業活動により発生する汚染土壌
や汚染スラジ(以下、汚染土壌類という)の処理が大き
な問題となっている。従来より、このような汚染土壌類
は焼却処理されている。しかしながら、汚染土壌類は、
都市ゴミなどの廃棄物と異なり、自然に燃焼しないた
め、その焼却処理にはガス、石油等の高級燃料を必要と
する。一方、ポリ塩化ビニル等の有機ハロゲン化合物を
含む汚染土壌類の焼却をするとダイオキシン等の難分解
性汚染物質が発生する場合があり、このような物質の環
境への影響が懸念されている。難分解性汚染物質の発生
を防止するためには、汚染土壌類をかなりの高温で焼却
処理する必要があり、これが汚染土壌の焼却処理に要す
る高級燃料を更に増大させる一因となっている。
2. Description of the Related Art In recent years, treatment of contaminated soil and sludge (hereinafter referred to as contaminated soil) generated by industrial activities has become a major problem. Conventionally, such contaminated soils have been incinerated. However, contaminated soils
Unlike waste such as municipal waste, it does not burn naturally, so its incineration requires high-grade fuels such as gas and oil. On the other hand, incineration of contaminated soils containing an organic halogen compound such as polyvinyl chloride may generate a hardly decomposable contaminant such as dioxin, and there is a concern that such a substance may affect the environment. In order to prevent the generation of hard-to-decompose pollutants, it is necessary to incinerate contaminated soil at a considerably high temperature, which contributes to further increase in high-grade fuel required for incineration of contaminated soil.

【0003】[0003]

【発明が解決しようとする課題】本発明は上述した問題
点を解決するためになされたもので、汚染土壌類の焼却
に必要な高級燃料を大幅に低減することが可能な汚染土
壌類の焼却浄化方法及び焼却浄化装置を提供することを
目的とする。さらに、汚染土壌類の焼却及びダイオキシ
ン等の難分解性汚染物質の処理に用いたエネルギーを別
途有効に利用することが可能な汚染土壌類の焼却浄化方
法及び焼却浄化装置を提供することを目的とする。
SUMMARY OF THE INVENTION The present invention has been made in order to solve the above-mentioned problems, and is intended to incinerate contaminated soils capable of greatly reducing the high-grade fuel required for incineration of contaminated soils. It is an object to provide a purification method and an incineration purification device. Furthermore, it is an object of the present invention to provide a method and apparatus for incineration and purification of contaminated soil that can separately and effectively use the energy used for incineration of contaminated soil and treatment of hardly decomposable pollutants such as dioxins. I do.

【0004】[0004]

【課題を解決するための手段】本発明の汚染土壌類の焼
却浄化方法は、汚染土壌類に高カロリー廃棄物を加えて
焼却するように構成したことを特徴とする。また、上記
の方法において、焼却により発生した排ガスを更に加熱
して排ガス中の難分解性汚染物質を完全分解すると共
に、加熱された排ガスを別途熱源として利用するように
構成したことを特徴とする。
The method for incineration and purification of contaminated soils according to the present invention is characterized in that high-calorie waste is added to the contaminated soils for incineration. Further, in the above method, the exhaust gas generated by the incineration is further heated to completely decompose the hardly decomposable pollutants in the exhaust gas, and the heated exhaust gas is used as a separate heat source. .

【0005】また、本発明の汚染土壌類の焼却浄化装置
は、汚染土壌類に高カロリー廃棄物を加えて焼却する焼
却装置と、焼却装置より発生する排ガスを加熱して排ガ
ス中に含まれる難分解性汚染物質を完全分解する排ガス
加熱装置と、排ガス加熱装置で加熱された排ガスを熱源
とする熱機関とを有するように構成したことを特徴とす
る。
[0005] Further, the incineration and purification apparatus for contaminated soils according to the present invention includes an incineration apparatus for incinerating contaminated soils by adding high-calorie wastes, and a method for heating exhaust gas generated from the incineration apparatus to be contained in the exhaust gas. The exhaust gas heating device for completely decomposing the decomposable pollutants and a heat engine using the exhaust gas heated by the exhaust gas heating device as a heat source are provided.

【0006】以上のように構成した本発明によれば、汚
染土壌類に高カロリー廃棄物を加えて燃焼することによ
り、汚染土壌類の焼却に必要な燃料を節約することが可
能になる。また、焼却により発生した排ガスを更に加熱
することにより、高カロリー廃棄物や汚染土壌の焼却に
より生じた排ガス中に含まれるダイオキシン等の難分解
性汚染物質を完全に分解することが可能になる。その結
果、ポリ塩化ビニル等の有機ハロゲン化合物を含む混合
廃棄プラスチックを高カロリー廃棄物として使用するこ
とにより、処理困難物と汚染土壌とを同時に処理するこ
とが可能になる。さらに、加熱された排ガスを別途熱源
として利用することにより、焼却や加熱に利用した高い
エネルギーを効率的に再利用することが可能になる。
According to the present invention having the above-described structure, it is possible to save fuel required for incineration of the contaminated soil by burning the contaminated soil with high calorie waste. Further, by further heating the exhaust gas generated by the incineration, it becomes possible to completely decompose hard-to-decompose contaminants such as dioxin contained in the exhaust gas generated by the incineration of high calorie waste and contaminated soil. As a result, by using mixed waste plastic containing an organic halogen compound such as polyvinyl chloride as high calorie waste, it becomes possible to simultaneously treat difficult-to-treat materials and contaminated soil. Furthermore, by separately using the heated exhaust gas as a heat source, it becomes possible to efficiently reuse high energy used for incineration and heating.

【0007】[0007]

【発明の実施の形態】以下、図面を参照して本発明の実
施の形態について説明する。図1は本発明に係る汚染土
壌類の焼却浄化装置を示す。図1において焼却浄化装置
10は汚染土壌類を焼却処理する流動床焼却炉20と、
汚染土壌類の焼却により発生した排ガスから固体粒子を
分離するためのサイクロン30と、排ガスを更に加熱す
る二次加熱室40と、二次加熱室40で加熱された排ガ
スを熱源として蒸気を発生させると共に、流動床焼却炉
20に加熱空気を供給するためのボイラ50を備えてい
る。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 shows an incineration and purification apparatus for contaminated soils according to the present invention. In FIG. 1, an incineration purification apparatus 10 includes a fluidized bed incinerator 20 for incinerating contaminated soils,
A cyclone 30 for separating solid particles from exhaust gas generated by incineration of contaminated soil, a secondary heating chamber 40 for further heating the exhaust gas, and steam generated using the exhaust gas heated in the secondary heating chamber 40 as a heat source. In addition, a boiler 50 for supplying heated air to the fluidized bed incinerator 20 is provided.

【0008】流動床焼却炉20は焼却される汚染土壌類
等を収容するための本体21と、本体21内に汚染土壌
類12及び廃棄プラスチック等の高カロリー廃棄物14
を投入するためのホッパ22を備えている。本体21の
内部には空気透過性の隔壁23が設けられており、これ
によって、本体の内部に汚染土壌類12を熱処理するた
めの流動室24と、流動室24に加熱空気を供給する下
部空気室25が形成されている。流動室24には熱媒体
として砂が収容されており、ボイラ50から下部空気室
25及び隔壁23を経て加熱空気が流動室24内に圧送
されると、流動室24内に投入された汚染土壌類12及
び高カロリー廃棄物14は、砂と共に流動され、粉砕さ
れる。また、流動室24には着火用ないし焼却温度調節
用の加熱バーナ26及び加熱バーナ26にガス、石油等
の燃料を供給するための燃料供給路27が設けられてい
る。
The fluidized bed incinerator 20 includes a main body 21 for containing contaminated soil and the like to be incinerated, and a contaminated soil 12 and high-calorie waste 14 such as waste plastic in the main body 21.
Is provided with a hopper 22 for charging the hopper. An air-permeable partition 23 is provided inside the main body 21, whereby a flow chamber 24 for heat-treating the contaminated soil 12 is provided inside the main body, and lower air for supplying heated air to the flow chamber 24. A chamber 25 is formed. Sand is housed in the flow chamber 24 as a heat medium, and when heated air is pumped into the flow chamber 24 from the boiler 50 through the lower air chamber 25 and the partition 23, the contaminated soil introduced into the flow chamber 24 is conveyed. Class 12 and high calorie waste 14 are fluidized with sand and ground. The flow chamber 24 is provided with a heating burner 26 for ignition or incineration temperature control, and a fuel supply passage 27 for supplying fuel such as gas or oil to the heating burner 26.

【0009】本体21の底部には加熱処理された汚染土
壌類12や高カロリー廃棄物14に含まれている粗大不
燃物を排出するための排出管28が設けられいる。この
排出管は粗大不然物と砂とを分離するための振動篩29
を備えており、粗大不然物16は外部に排出され、砂は
流動層に戻されるように構成されている。また、本体2
1の上部には汚染土壌類の燃焼により生じた排ガスや固
体粒子を排出するためのガス排出口21aが形成されて
いる。このような流動床焼却炉20において、加熱バー
ナ26により着火されると、砂と共に流動室内を流動し
ている汚染土壌類12は高カロリー廃棄物14の燃焼熱
により焼却処理される。
At the bottom of the main body 21, a discharge pipe 28 for discharging coarse incombustible substances contained in the heat-treated contaminated soil 12 and high calorie waste 14 is provided. The discharge pipe is provided with a vibrating sieve 29 for separating coarse foreign matters and sand.
, And is configured so that the coarse contaminants 16 are discharged to the outside and the sand is returned to the fluidized bed. Also, body 2
A gas outlet 21a for discharging exhaust gas and solid particles generated by the combustion of contaminated soils is formed in the upper part of the fuel cell. In such a fluidized bed incinerator 20, when ignited by the heating burner 26, the contaminated soil 12 flowing in the fluidized chamber together with the sand is incinerated by the combustion heat of the high calorie waste 14.

【0010】流動床焼却炉20の排ガスの搬送方向下流
側には、サイクロン30が設けられている。サイクロン
30の側壁の上部には流動床焼却炉20で発生した排ガ
スが導かれる排ガス導入口30aが形成されている。ま
た、サイクロン30内部には、排ガス中に含まれる固体
粒子成分を分離するための遠心分離機構(図示せず)が
設けられている。サイクロン30の底部には遠心分離機
構により分離された固体粒子を回収するための固体粒子
回収部31が設けられており、排ガスから分離された固
体粒子は浄化土壌33として回収される。サイクロン3
0の最頂部には固体粒子が除去された排ガス成分を排出
するための排ガス排出口30bが形成されている。
A cyclone 30 is provided on the downstream side of the fluidized bed incinerator 20 in the conveying direction of the exhaust gas. An exhaust gas inlet 30 a through which exhaust gas generated in the fluidized bed incinerator 20 is guided is formed at an upper portion of the side wall of the cyclone 30. Further, a centrifugal separation mechanism (not shown) for separating solid particle components contained in the exhaust gas is provided inside the cyclone 30. At the bottom of the cyclone 30 is provided a solid particle recovery unit 31 for recovering the solid particles separated by the centrifugal separation mechanism, and the solid particles separated from the exhaust gas are recovered as purified soil 33. Cyclone 3
An exhaust gas outlet 30b for discharging an exhaust gas component from which solid particles have been removed is formed at the top of 0.

【0011】サイクロン30の排ガスの搬送方向下流側
にはサイクロン30を経た排ガスの二次加熱を行う二次
加熱室40が設けられている。二次加熱室40には、排
ガスの二次加熱を行うアフタバーナ41及びアフタバー
ナ41にガス又は油等の燃料を供給する燃料供給路42
が設けられている。二次加熱室40において、排ガスは
1000℃以上、好ましくは1200℃以上に加熱され
る。
A secondary heating chamber 40 for performing secondary heating of the exhaust gas passing through the cyclone 30 is provided downstream of the cyclone 30 in the direction of transport of the exhaust gas. The secondary heating chamber 40 is provided with an afterburner 41 for performing secondary heating of the exhaust gas and a fuel supply passage 42 for supplying a fuel such as gas or oil to the afterburner 41.
Is provided. In the secondary heating chamber 40, the exhaust gas is heated to 1000 ° C. or higher, preferably 1200 ° C. or higher.

【0012】二次加熱室40のさらに下流側には、二次
加熱室40からの高温排ガスを熱源としてボイラ用水5
1から蒸気52を発生させるボイラ50が設けられてい
る。この蒸気52は、隣設された発電装置60に送られ
て発電に用いられる。さらに、このボイラ50には外気
53をボイラ50中に導入するとともに、ボイラ50中
で加熱された外気を流動床焼却炉20の下部空気室25
に圧送するためのブロワ54が設けられている。更に、
このボイラ50には熱源として用いられた排ガスを最終
的に清浄化するためのガス洗浄装置58及びこの排ガス
を外部に排出するための排ガス吸引ブロワ55が設けら
れており、ガス清浄装置58を経た排ガスが煙突56か
ら清浄ガス57となって大気中に放出されるように構成
されている。
[0012] Further downstream of the secondary heating chamber 40, the boiler water 5 using the high temperature exhaust gas from the secondary heating chamber 40 as a heat source.
A boiler 50 for generating steam 52 from 1 is provided. The steam 52 is sent to an adjacent power generation device 60 and used for power generation. Further, outside air 53 is introduced into the boiler 50 and the outside air heated in the boiler 50 is supplied to the lower air chamber 25 of the fluidized bed incinerator 20.
Is provided with a blower 54 for pressure feeding. Furthermore,
The boiler 50 is provided with a gas cleaning device 58 for finally purifying exhaust gas used as a heat source and an exhaust gas suction blower 55 for discharging the exhaust gas to the outside. The exhaust gas is configured to be released from the chimney 56 as clean gas 57 into the atmosphere.

【0013】以下、上記の装置を用いた汚染土壌類の焼
却浄化方法について説明する。焼却される汚染土壌12
類は廃棄プラスチック等の高カロリー廃棄物14と共に
ホッパ22を介して流動床焼却炉20の本体21内に投
入される。本体21内に投入された汚染土壌類12及び
高カロリー廃棄物14は流動室24で加熱空気により砂
と共に流動され、粉砕される。これと同時に、汚染土壌
類12は、加熱バーナ26により点火された高カロリー
廃棄物14の燃焼により950℃以下の一定温度で焼却
処理される。これによって、汚染土壌類12及び高カロ
リー廃棄物14は均一に加熱され、汚染物質は揮発し、
有機物質は分解、蒸発される。焼却後、汚染土壌類12
や高カロリー廃棄物14に含まれている粗大不燃物16
は排出管28において振動篩29により砂と分離され、
砂は次の焼却工程のために流動層に戻される。
Hereinafter, a method for incineration and purification of contaminated soils using the above apparatus will be described. Contaminated soil 12 to be incinerated
The products are put into the body 21 of the fluidized bed incinerator 20 via the hopper 22 together with the high-calorie waste 14 such as waste plastic. The contaminated soils 12 and high-calorie wastes 14 introduced into the main body 21 are fluidized together with sand by heated air in a fluidizing chamber 24, and pulverized. At the same time, the contaminated soil 12 is incinerated at a constant temperature of 950 ° C. or lower by burning the high-calorie waste 14 ignited by the heating burner 26. As a result, the contaminated soils 12 and the high-calorie wastes 14 are uniformly heated, and the pollutants are volatilized.
Organic substances are decomposed and evaporated. After incineration, contaminated soil 12
Incombustibles 16 contained in high calorie waste 14
Is separated from the sand by a vibrating sieve 29 in a discharge pipe 28,
The sand is returned to the fluidized bed for the next incineration step.

【0014】燃焼工程で発生した排ガスは排ガス導入口
30aよりサイクロン30内に導かれる。排ガスは、サ
イクロン30において、遠心分離機構(図示せず)によ
り固体粒子が除去され、この除去された固体粒子は、固
体粒子回収部31において浄化土壌33として回収され
る。一方、固体粒子が除去された排ガスは、二次加熱室
40に送られる。二次加熱室40において、排ガスはア
フターバーナ41により1000℃以上、好ましくは1
200℃以上に加熱される。これによって、ここで排ガ
スに含まれるダイオキシン等の難分解性有機物質は完全
に酸化分解される。
Exhaust gas generated in the combustion process is guided into the cyclone 30 from an exhaust gas inlet 30a. In the cyclone 30, solid particles are removed from the exhaust gas by a centrifugal separation mechanism (not shown), and the removed solid particles are collected as purified soil 33 in a solid particle collection unit 31. On the other hand, the exhaust gas from which the solid particles have been removed is sent to the secondary heating chamber 40. In the secondary heating chamber 40, the exhaust gas is heated to 1000 ° C. or more, preferably 1 ° C., by the afterburner 41.
Heated above 200 ° C. Thereby, the hardly decomposable organic substances such as dioxin contained in the exhaust gas are completely oxidatively decomposed.

【0015】二次加熱室40で加熱された高温の排ガス
はさらにボイラ50に導かれる。ボイラ50において
は、排ガスは熱源として用いられ、ボイラ用水51を加
熱して蒸気52を発生させる。この蒸気52は発電装置
60に送られ、発電に利用される。また、ブロワ54に
よりボイラ50中に吸引された外気53は加熱されて流
動床焼却炉20の下部空気室25に送られる。以上のよ
うな構成により、汚染土壌類12の焼却及び排ガスの加
熱に用いられたエネルギーを効率的に再利用することが
可能になる。ボイラ50を経た排ガスは更にガス洗浄装
置58で浄化され、排ガス吸引ブロワ55により吸引さ
れて、煙突56から清浄ガス57として大気中に放出さ
れる。
The high-temperature exhaust gas heated in the secondary heating chamber 40 is further guided to a boiler 50. In the boiler 50, the exhaust gas is used as a heat source, and heats the boiler water 51 to generate steam 52. The steam 52 is sent to the power generator 60 and used for power generation. The outside air 53 sucked into the boiler 50 by the blower 54 is heated and sent to the lower air chamber 25 of the fluidized bed incinerator 20. With the above configuration, it is possible to efficiently reuse the energy used for incineration of the contaminated soils 12 and heating of the exhaust gas. The exhaust gas that has passed through the boiler 50 is further purified by a gas cleaning device 58, sucked by an exhaust gas suction blower 55, and released into the atmosphere as a clean gas 57 from a chimney 56.

【0016】[0016]

【発明の効果】以上のように構成した本発明によれば、
汚染土壌類の焼却及び難分解性汚染物質の処理に必要な
燃料を大幅に低減することが可能になる。さらに、汚染
土壌類の焼却及びダイオキシン等の難分解性汚染物質の
処理に用いられたエネルギーを、別途有効に利用するこ
とが可能になる。
According to the present invention configured as described above,
The fuel required for incineration of contaminated soils and treatment of hardly decomposable pollutants can be greatly reduced. Furthermore, the energy used for the incineration of contaminated soils and the treatment of hardly decomposable pollutants such as dioxin can be separately and effectively used.

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

【図1】本発明に係る実施例の説明図である。FIG. 1 is an explanatory diagram of an embodiment according to the present invention.

【符号の説明】[Explanation of symbols]

10 焼却浄化装置 12 汚染土壌類 14 高カロリー廃棄物 20 流動床焼却炉 40 二次加熱装置 50 ボイラ 60 発電装置 DESCRIPTION OF SYMBOLS 10 Incineration purification apparatus 12 Contaminated soils 14 High calorie waste 20 Fluidized bed incinerator 40 Secondary heating device 50 Boiler 60 Power generation device

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 汚染土壌類に高カロリー廃棄物を加えて
焼却することを特徴とする汚染土壌類の焼却浄化方法。
1. A method for incineration and purification of contaminated soils, comprising adding high calorie waste to the contaminated soils and incinerating them.
【請求項2】 前記焼却により発生した排ガスを更に加
熱して前記排ガス中の難分解性汚染物質を完全分解する
と共に、加熱された前記排ガスを別途熱源として利用す
ることを特徴とする請求項1記載の焼却浄化方法。
2. The exhaust gas generated by the incineration is further heated to completely decompose the hardly decomposable pollutants in the exhaust gas, and the heated exhaust gas is used as a separate heat source. The incineration purification method described.
【請求項3】 前記汚染土壌類は950℃以下で焼却さ
れ、前記排ガスは1000℃以上に加熱されることを特
徴とする請求項2記載の焼却浄化方法。
3. The incineration purification method according to claim 2, wherein said contaminated soil is incinerated at 950 ° C. or lower, and said exhaust gas is heated to 1000 ° C. or higher.
【請求項4】 汚染土壌類に高カロリー廃棄物を加えて
焼却する焼却装置と、前記焼却装置より発生する排ガス
を加熱して前記排ガス中に含まれる難分解性汚染物質を
完全分解する排ガス加熱装置と、前記排ガス加熱装置で
加熱された前記排ガスを熱源とする熱機関とを有するこ
とを特徴とする汚染土壌類の焼却浄化装置。
4. An incinerator for adding high-calorie waste to contaminated soil for incineration, and heating the exhaust gas generated from the incinerator to completely decompose the hardly decomposable pollutants contained in the exhaust gas. An apparatus for incineration and purification of contaminated soils, comprising: an apparatus; and a heat engine that uses the exhaust gas heated by the exhaust gas heating apparatus as a heat source.
JP9334903A 1997-11-19 1997-11-19 Incinerator and incinerating method for contaminated soil or the like Pending JPH11148631A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9334903A JPH11148631A (en) 1997-11-19 1997-11-19 Incinerator and incinerating method for contaminated soil or the like

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9334903A JPH11148631A (en) 1997-11-19 1997-11-19 Incinerator and incinerating method for contaminated soil or the like

Publications (1)

Publication Number Publication Date
JPH11148631A true JPH11148631A (en) 1999-06-02

Family

ID=18282535

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9334903A Pending JPH11148631A (en) 1997-11-19 1997-11-19 Incinerator and incinerating method for contaminated soil or the like

Country Status (1)

Country Link
JP (1) JPH11148631A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004025087A (en) * 2002-06-27 2004-01-29 Hitachi Zosen Corp Soil decontamination apparatus
CN109174945A (en) * 2018-08-17 2019-01-11 南通劲凌智能科技有限公司 A kind of soil repair system and its method based on heat-conducting oil heating
CN109848198A (en) * 2019-04-01 2019-06-07 南京师范大学 A kind of soil thermal desorption ex-situ repair system
CN111438170A (en) * 2020-03-27 2020-07-24 生态环境部南京环境科学研究所 Laboratory soil screening and harmful gas purification circulating device
CN111495953A (en) * 2020-04-27 2020-08-07 长沙柳腾科技有限公司 Pretreatment equipment for ectopic leaching of petroleum-polluted gravel-containing soil

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004025087A (en) * 2002-06-27 2004-01-29 Hitachi Zosen Corp Soil decontamination apparatus
CN109174945A (en) * 2018-08-17 2019-01-11 南通劲凌智能科技有限公司 A kind of soil repair system and its method based on heat-conducting oil heating
CN109848198A (en) * 2019-04-01 2019-06-07 南京师范大学 A kind of soil thermal desorption ex-situ repair system
CN111438170A (en) * 2020-03-27 2020-07-24 生态环境部南京环境科学研究所 Laboratory soil screening and harmful gas purification circulating device
CN111495953A (en) * 2020-04-27 2020-08-07 长沙柳腾科技有限公司 Pretreatment equipment for ectopic leaching of petroleum-polluted gravel-containing soil

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