JP2001033013A - Method for heat treating material to be treated - Google Patents

Method for heat treating material to be treated

Info

Publication number
JP2001033013A
JP2001033013A JP11202442A JP20244299A JP2001033013A JP 2001033013 A JP2001033013 A JP 2001033013A JP 11202442 A JP11202442 A JP 11202442A JP 20244299 A JP20244299 A JP 20244299A JP 2001033013 A JP2001033013 A JP 2001033013A
Authority
JP
Japan
Prior art keywords
furnace
heat treatment
treated
treatment
heating
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
JP11202442A
Other languages
Japanese (ja)
Inventor
Yoshiyuki Kashiwagi
佳行 柏木
Nobuyuki Yoshioka
信行 吉岡
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.)
Meidensha Corp
Meidensha Electric Manufacturing Co Ltd
Original Assignee
Meidensha Corp
Meidensha Electric Manufacturing 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 Meidensha Corp, Meidensha Electric Manufacturing Co Ltd filed Critical Meidensha Corp
Priority to JP11202442A priority Critical patent/JP2001033013A/en
Publication of JP2001033013A publication Critical patent/JP2001033013A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

PROBLEM TO BE SOLVED: To prevent the generating of dioxins by eliminating a low temperature area causing an incomplete combustion and to prevent the exhaustion of an unburned decomposed gas, by continuing the combustion of the gas in an exhaust gas burning furnace for a given time even after the exhaustion of a material to be treated in a heat treating furnace is completed. SOLUTION: A heat treating apparatus first starts heating of a second heating treating furnace (volume reducing furnace) 20 and a first heat treating furnace (dechlorinating furnace) 10 at a stage of charging no material to be treated. That is, a fuel such as an LNG or the like is burned in a gas burning furnace 35 and an exhaust gas burning furnace 41 to heat the respective furnaces. A hot gas generated in the furnace 35 is supplied to a heating cylinder 22 of the furnace 20 to heat a cylinder 21, and sent into a heating cylinder 12 of the furnace 10 from a communicating tube 37 to heat a cylinder 11. A heating temperature of the furnace 20 at this time is that for carbonizing a material to be treated, and a heating temperature of the furnace 10 is heated to a temperature for decomposing to precipitate harmful substance from the material. A heating temperature of the furnace 41 is heated to 800 deg.C or higher. Thus, exhausting of unburned decomposed gas is prevented.

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、廃棄物等の被処理
物の加熱処理方法に関し、特に、加熱処理炉の運転開示
時および停止時における加熱処理温度の低い段階で発生
するダイオキシン類の発生を防止する加熱処理方法、並
びに、ハロゲン物質(塩素など)等の有機性物質を含有
する被処理物を乾留処理し被処理物から分解析出する有
害物質(塩化水素等)と処理剤とを接解反応させて無害
な塩化物を生成して、無害な排ガスと無害な残渣を得る
ようにした加熱処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for heat-treating an object to be treated such as waste, and more particularly, to the generation of dioxins generated at a low heat-treatment temperature when the operation of a heat treatment furnace is started and when it is stopped. Heat treatment method, and a harmful substance (hydrogen chloride, etc.) decomposed and precipitated from a treatment object by subjecting a treatment object containing an organic substance such as a halogen substance (chlorine, etc.) to a dry distillation treatment and a treatment agent. The present invention relates to a heat treatment method in which a harmless chloride is produced by an intimate reaction to obtain a harmless exhaust gas and a harmless residue.

【0002】[0002]

【従来の技術】産業廃棄物や一般廃棄物等の各種廃棄物
は多量の有機性物質(ハロゲン物質)を含有しており、
これを被処理物として加熱処理すると、各種の有害物質
(例えば、塩化水素、ダイオキシン類)が析出して排ガ
ス中に含まれていることは広く知られている。従って、
この排ガスを大気中にそのまま排出することはできない
ので、大気中に排出する前段階で排ガスの浄化処理を行
うこと(排出の抑制)が一般に行われる。
2. Description of the Related Art Various wastes such as industrial wastes and general wastes contain a large amount of organic substances (halogen substances).
It is widely known that when this is heated as an object to be treated, various harmful substances (for example, hydrogen chloride and dioxins) are precipitated and contained in exhaust gas. Therefore,
Since this exhaust gas cannot be directly discharged into the atmosphere, purification processing of the exhaust gas (suppression of discharge) is generally performed before the exhaust gas is discharged into the air.

【0003】この排ガスの浄化装置として一般的な装置
として、特開平8−108026号などに示されている
バグフィルタ装置がある。この装置は、排ガスの浄化剤
として消石灰を使用して排ガス中の塩化水素、ダイオキ
シン類を除去するようにしている。
As a general exhaust gas purifying device, there is a bag filter device disclosed in Japanese Patent Application Laid-Open No. 8-108026. This apparatus uses slaked lime as a purifying agent for exhaust gas to remove hydrogen chloride and dioxins in the exhaust gas.

【0004】また、加熱処理により多量に発生した塩化
水素は、苛性ソーダなどで中和するか、塩酸にして回収
することも一般に行われている。
[0004] Further, hydrogen chloride generated in large quantities by heat treatment is generally neutralized with caustic soda or the like and recovered with hydrochloric acid.

【0005】しかし、排ガス処理のための、バグフィル
タで使用した消石灰粉末、排ガス中の飛灰、焼却残渣
(焼却灰等)などの、排ガス以外の物にも塩素系ガス成
分は付着・吸着されて、猛毒のダイオキシン類を生成し
てしまうことが知られている。
[0005] However, chlorine-based gas components also adhere to and are adsorbed to substances other than exhaust gas, such as slaked lime powder used in bag filters, fly ash in exhaust gas, and incineration residues (incinerated ash, etc.) for exhaust gas treatment. It is known that they produce highly toxic dioxins.

【0006】一方、本願の出願人は、ハロゲン物質であ
る有機塩素化合物(塩化水素)が、従来の「排出の抑
制」でなく、「発生の抑制」を行うことで、塩化水素な
どの有害物質の発生を抑制し、排ガスの無害化と残渣の
無害化、塩素による処理装置の損傷の低減を行うことを
提案している。
On the other hand, the applicant of the present application has proposed that an organic chlorine compound (hydrogen chloride), which is a halogen substance, performs "suppression of generation" instead of the conventional "suppression of emission", thereby producing harmful substances such as hydrogen chloride. It has been proposed to suppress the generation of waste gas, make the exhaust gas harmless, make the residue harmless, and reduce the damage of the treatment equipment due to chlorine.

【0007】即ち、被処理物にアルカリ物質の処理剤を
添加混合して所定の温度で加熱することで塩化水素を分
解析出させると同時に、添加混合している処理剤と接触
反応させて無害な塩化物に置換生成する技術を見出し、
既に、特開平9−155326号,特開平10−437
13号,特開平10−235186号,特開平10−2
35187号などで提案し、更に、処理剤を多孔質化し
て接触反応する面積を増加させて反応効果を高めた処理
剤も提案している(特開平10−193844号)。
That is, a treatment agent of an alkali substance is added to and mixed with the object to be treated and heated at a predetermined temperature to decompose and precipitate hydrogen chloride, and at the same time, contact and react with the added and mixed treatment agent to be harmless. Technology to displace and generate chloride
Already disclosed in JP-A-9-155326 and JP-A-10-437
13, JP-A-10-235186, JP-A-10-235
No. 35187, etc., and a treatment agent in which the treatment effect is increased by making the treatment agent porous and increasing the area of the contact reaction has been proposed (JP-A-10-193844).

【0008】これらの処理剤を使用し被処理物を加熱処
理して炭化物の残渣を得、この炭化物は多孔質である特
性から、土壌改良材、水質浄化剤、融雪剤、保温剤に使
用され、また、燃料としても利用できるなど、幅広い分
野でリサイクル品としての利用を可能としている。
[0008] Using these treatment agents, the material to be treated is heat-treated to obtain a carbide residue, and the carbide is used as a soil improving material, a water purification agent, a snow melting agent, and a heat insulator due to its porous nature. It can also be used as a recycled product in a wide range of fields, such as being used as fuel.

【0009】[0009]

【発明が解決しようとする課題】被処理物を加熱処理す
る場合、被処理物の加熱処理温度が低い温度域を通過す
る運転開始時と停止時に、ダイオキシン類が多く発生す
ることが知られている。これは、不完全燃焼領域が存在
することに起因しており、この不完全燃焼領域を形成し
ないように、運転開始と停止を極力少なくした運転条件
(例えば、24時連続運転)で処理することが推奨され
ている。
When heat-treating an object to be treated, it is known that a large amount of dioxins is generated at the start and stop of the operation when the heat treatment temperature of the object passes through a low temperature range. I have. This is due to the presence of an incomplete combustion region. In order not to form this incomplete combustion region, processing must be performed under operating conditions (for example, 24-hour continuous operation) in which operation start and stop are minimized. Is recommended.

【0010】しかし、現実には、24時間連続運転する
には、被処理物を大量に集積する必要があり、被処理物
が連続して所定の量を確保できないとか、断続的に発生
する場合は実現できない。
However, in actuality, in order to operate continuously for 24 hours, it is necessary to accumulate a large amount of objects to be processed, and if the predetermined amount of objects to be processed cannot be secured continuously or intermittently occurs. Cannot be realized.

【0011】しかも、加熱処理炉の停止後においても、
炉内には分解ガスが残存しており、分解ガス燃焼炉の停
止が加熱処理炉と同時期では、未燃焼の分解ガスが排出
されることになり、悪臭を施設外に及ぼすことになる。
また、有害物質も排出してしまう危険性もある。
Moreover, even after the heat treatment furnace is stopped,
Decomposed gas remains in the furnace, and when the decomposed gas combustion furnace is shut down at the same time as the heat treatment furnace, unburned decomposed gas is discharged, causing an odor outside the facility.
There is also a danger of emitting harmful substances.

【0012】本発明はこのような課題に鑑みなされたも
ので、その目的とするところは、加熱処理炉の運転開
始、停止時の不完全燃焼となる低温度域を無くすること
でダイオキシン類の発生を防止し、加熱処理炉の所定時
間間隔での運転・停止を可能とするとともに、未燃焼の
分解ガスの排出を防止する加熱処理方法を提供するにあ
る。
The present invention has been made in view of such problems, and an object of the present invention is to eliminate dioxins by eliminating a low temperature range where incomplete combustion occurs when a heat treatment furnace is started and stopped. An object of the present invention is to provide a heat treatment method which prevents generation of unburned cracked gas while preventing generation and operation of the heat treatment furnace at predetermined time intervals.

【0013】[0013]

【課題を解決するための手段】上記の課題を解決すべく
発明者らは、加熱処理炉を24時間連続運転することな
く、少量の被処理物でも確実に、且つダイオキシン類を
発生させることなく安全に処理する方法として、被処理
物を乾留処理することを見出し、且つ加熱処理炉を停止
後一定時間、発生分解ガスの燃焼を継続することで悪臭
その他の弊害要因を除去するようにし、更には、発生す
る塩化水素と接触反応して無害な塩化物を生成するアル
カリ物質の処理剤を添加混合して処理することで被処理
物を無害化処理することを見出した。その具体的手段
は、被処理物を加熱処理炉に投入して加熱分解処理し、
且つ発生した分解ガスを排ガス燃焼炉で燃焼処理する被
処理物の加熱処理方法であって、前記の排ガス燃焼炉で
の分解ガスの燃焼は、加熱処理炉内の被処理物の排出が
完了した後も所定時間継続させることを特徴とする。
Means for Solving the Problems In order to solve the above-mentioned problems, the present inventors have made it possible to operate a heat treatment furnace continuously for 24 hours, to ensure that even a small amount of an object to be treated, and to generate dioxins. As a method of safely treating, it is found that the material to be treated is carbonized, and for a certain time after the heat treatment furnace is stopped, the burning of the generated decomposition gas is continued to remove the bad smell and other adverse factors, and Has found that an object to be treated is rendered harmless by adding and mixing a treating agent of an alkaline substance that generates a harmless chloride by contacting with generated hydrogen chloride. The concrete means is to put the object to be treated into a heat treatment furnace and perform thermal decomposition treatment,
A method for heating an object to be processed in which generated decomposition gas is burned in an exhaust gas combustion furnace, wherein the combustion of the decomposition gas in the exhaust gas combustion furnace completes discharge of the object to be processed in the heat treatment furnace. It is characterized in that it is continued for a predetermined time thereafter.

【0014】上記の加熱処理炉での加熱処理は、脱塩素
処理と減容化処理とを少なくとも2つの異なる加熱処理
炉で行うことが望ましい。
In the heat treatment in the heat treatment furnace, it is desirable that the dechlorination treatment and the volume reduction treatment are performed in at least two different heat treatment furnaces.

【0015】また、脱塩素処理および減容化処理する加
熱処理炉の炉内温度は、夫々200℃以上および300
℃以上、排ガス燃焼炉の炉内温度は750℃以上とする
ことが望ましい。
The temperature inside the heat treatment furnace for dechlorination and volume reduction is 200 ° C. or more and 300 ° C., respectively.
C. or higher, and the furnace temperature of the exhaust gas combustion furnace is preferably 750 C. or higher.

【0016】そして、加熱処理炉での脱塩素処理は、被
処理物にアルカリ物質の処理剤を添加混合して加熱処理
し、発生した分解ガスの有害物質と処理剤とを接触反応
させて有害物質を無害な反応物に置換することで排ガス
・残渣の無害化を図るようにする。
[0016] In the dechlorination treatment in the heat treatment furnace, a treatment agent of an alkali substance is added to an object to be treated, mixed and heated, and a harmful substance of the generated decomposition gas is brought into contact with the treatment agent to cause a harmful reaction. By replacing substances with harmless reactants, harmless exhaust gas and residues can be achieved.

【0017】脱塩素処理に使用する処理剤は、アルカリ
物質の粉体で、処理物に対して5〜30重量%添加する
ことが望ましい。
The treating agent used in the dechlorination treatment is a powder of an alkaline substance, and is desirably added in an amount of 5 to 30% by weight based on the treated material.

【0018】この、アルカリ物質の処理剤は、加熱によ
り被処理物から分解析出する有害成分と反応して無害な
塩化物を生成するアルカリ金属、アルカリ金属化合物、
アルカリ土類金属、アルカリ土類金属化合物に含まれる
物質の中から、少なくとも1種類を選択、又は2種類以
上の混合物を含み、アルカリ金属は、Na,Kなど、ア
ルカリ土類金属は、Ca,Sr,Ba,Raなど、アル
カリ土類金属化合物は、石灰、消石灰、炭酸カルシウ
ム、ドロマイトなどである。
The treating agent for an alkaline substance is an alkali metal or an alkali metal compound which reacts with a harmful component decomposed and precipitated from an object to be treated by heating to form a harmless chloride;
At least one selected from alkaline earth metals and substances contained in alkaline earth metal compounds, or a mixture of two or more of them, including alkali metals such as Na and K, alkaline earth metals such as Ca, Alkaline earth metal compounds such as Sr, Ba and Ra are lime, slaked lime, calcium carbonate, dolomite and the like.

【0019】また、アルカリ金属化合物は、水酸化物、
炭酸化物のナトリウム系、カリウム系の物質で、 (a)炭酸水素ナトリウム、別称、酸性炭酸ナトリウ
ム、重炭酸ナトリウム、重炭酸ソーダ(俗称、重曹) (b)炭酸ナトリウム、別称、炭酸ソーダ、ソーダ、ソ
ーダ灰、洗濯ソーダ、結晶ソーダ (c)セスキ炭酸ナトリウム、別称、二炭酸一水素ナト
リウム、三二炭酸水素ナトリウム、ナトリウムセスキカ
ーボネート (d)天然ソーダ、別称、トロナ (e)炭酸カリウム (f)炭酸水素カリウム (g)炭酸ナトリウムカリウム (h)水酸化ナトリウム (i)水酸化カリウム から選択した単体、又は複数種を混合したものを含む。
The alkali metal compound may be a hydroxide,
Sodium and potassium-based substances of carbonate, (a) sodium bicarbonate, another name, acidic sodium carbonate, sodium bicarbonate, sodium bicarbonate (common name, baking soda) (b) Sodium carbonate, another name, sodium carbonate, soda, soda ash , Washing soda, crystalline soda (c) sodium sesquicarbonate, also known as sodium monohydrogen dicarbonate, sodium tricarbonate, sodium sesquicarbonate (d) natural soda, also known as trona (e) potassium carbonate (f) potassium hydrogen carbonate (G) Sodium potassium carbonate (h) Sodium hydroxide (i) Potassium hydroxide A simple substance or a mixture of two or more kinds selected from potassium hydroxide is included.

【0020】なお、塩化水素の無害化効果に対して苛性
ソーダは有効であるが、取り扱いに工夫が必要であり、
取り扱いが簡便で、それ自体無害である物質を選択する
ことが好ましい。
Although caustic soda is effective for the detoxification effect of hydrogen chloride, it requires special handling.
It is preferable to select a substance that is easy to handle and harmless per se.

【0021】加熱処理炉を加熱するガス燃焼炉、排ガス
燃焼炉の燃料としては、LNG又はLPGを使用するこ
とが望ましい。
It is desirable to use LNG or LPG as fuel for the gas combustion furnace and the exhaust gas combustion furnace for heating the heat treatment furnace.

【0022】[0022]

【発明の実施の形態】以下、本発明の実施の形態を図面
によって説明する。
Embodiments of the present invention will be described below with reference to the drawings.

【0023】図1は、本発明の加熱処理方法を適用する
被処理物の加熱処理装置の概念図で、該加熱処理装置
は、同じ構成の加熱処理炉を2基用い、第1の加熱処理
炉10に、被処理物を乾留し脱塩素処理の機能を持た
せ、第2の加熱処理炉20に、炭化又は灰化処理による
減容化処理の機能を持たせた場合である。
FIG. 1 is a conceptual view of a heat treatment apparatus for an object to which a heat treatment method according to the present invention is applied. The heat treatment apparatus uses two heat treatment furnaces having the same configuration and performs a first heat treatment. This is a case where the furnace 10 is provided with a function of dechlorination by subjecting the material to be treated to dry distillation, and the second heat treatment furnace 20 is provided with a function of volume reduction by carbonization or incineration.

【0024】第1の加熱処理炉10は、内部に被処理物
を撹拌しながら移動させる羽根11a(図2を参照)を
有する回転自在の円筒体11と、該円筒体11の外周に
ガスダクトを形成し、熱ガスを導入して円筒体11を加
熱する加熱筒12と、円筒体11の一方の端部に設けら
れ、被処理物を円筒体11内に供給する供給口13と、
円筒体11の他方の端部に設けられた排出口14とで構
成され、この円筒体11は回転駆動手段15によって回
転駆動される。回転駆動手段15は駆動用モータ15
a,駆動歯車15b,円筒体11に設けられた従動歯車
15cから成る。
The first heat treatment furnace 10 has a rotatable cylindrical body 11 having a blade 11a (see FIG. 2) for moving an object to be processed while being stirred, and a gas duct on the outer periphery of the cylindrical body 11. A heating cylinder 12 that is formed and heats the cylindrical body 11 by introducing a hot gas; a supply port 13 provided at one end of the cylindrical body 11 to supply an object to be processed into the cylindrical body 11;
A discharge port 14 is provided at the other end of the cylindrical body 11, and the cylindrical body 11 is rotationally driven by a rotation driving unit 15. The rotation driving means 15 is a driving motor 15
a, a driving gear 15b, and a driven gear 15c provided on the cylindrical body 11.

【0025】16は供給口13側を包囲する供給側ダク
ト、17は排出口14側を包囲する排出側ダクト、18
は動的シール(メカニカルシール)で、円筒体10の外
周に接するダクト16,17(図示省略)および加熱筒
12との接触部をシールしている。
16 is a supply duct surrounding the supply port 13 side, 17 is a discharge duct surrounding the discharge port 14 side, 18
Is a dynamic seal (mechanical seal) for sealing ducts 16 and 17 (not shown) in contact with the outer periphery of the cylindrical body 10 and a contact portion with the heating cylinder 12.

【0026】19は円筒体11を両端側で回転自在に支
持する支持ローラである。
Reference numeral 19 denotes a support roller for rotatably supporting the cylindrical body 11 at both ends.

【0027】第2の加熱処理炉20は、前記の第1の加
熱処理炉10とは基本的構成は同じである。よって、同
一又は相当部分には20の一桁を同じ数字とし(例え
ば、21は円筒体、22は加熱筒、29は支持ローラ)
説明を省略する。
The basic structure of the second heat treatment furnace 20 is the same as that of the first heat treatment furnace 10 described above. Therefore, in the same or equivalent part, one digit of 20 is set to the same number (for example, 21 is a cylindrical body, 22 is a heating cylinder, and 29 is a supporting roller).
Description is omitted.

【0028】30はホッパで、被処理物とアルカリ物質
からなる脱塩素材(以下、処理剤と称す)とを添加混合
して投入し、円筒体11の供給口13から円筒体11内
に供給する。被処理物としては、一般廃棄物、産業廃棄
物等の固形物や灰類、汚泥いずれでもよい。
Numeral 30 denotes a hopper, which adds and mixes an object to be treated and a desalting material (hereinafter, referred to as a treating agent) composed of an alkali substance, and supplies the mixture through the supply port 13 of the cylinder 11 into the cylinder 11. I do. The material to be treated may be any of solid matter such as general waste and industrial waste, ash, and sludge.

【0029】また、このホッパ30は、破砕機能と処理
剤の混合機能を持たせ、固形物を破砕しながら処理剤と
混合してもよいし、また、あらかじめ破砕した被処理物
と処理剤とを混合して投入してもよい。
The hopper 30 has a crushing function and a function of mixing the processing agent, and may mix the processing agent while crushing the solid material. May be mixed and charged.

【0030】第1の加熱処理炉10の円筒体11と、第
2の加熱処理炉20の円筒体21とは上下方向に配設さ
れ、円筒体11の排出側ダクト17と供給側ダクト26
とは、ロータリーバルブ32を介して連通され、また、
第2の加熱処理炉20の円筒体21の排出側ダクト27
はロータリーバルブ33を介して溶解槽34に、加熱処
理後の炭化物又は処理灰を排出する。
The cylindrical body 11 of the first heat treatment furnace 10 and the cylindrical body 21 of the second heat treatment furnace 20 are disposed vertically, and the discharge duct 17 and the supply duct 26 of the cylinder 11 are arranged vertically.
Is communicated via a rotary valve 32, and
Discharge side duct 27 of cylindrical body 21 of second heat treatment furnace 20
Discharges the carbide or treated ash after the heat treatment to the melting tank via the rotary valve 33.

【0031】35はガス燃焼炉で、LNG又はLPGの
燃料を燃焼して熱ガスを発生させる。この熱ガスは円筒
体21の外周に設けた加熱筒22内に供給され円筒体2
1を加熱した後、連絡管37を介して円筒体11の加熱
筒12内に送入し、この円筒体11を加熱した後、排出
管38から乾燥手段39の加熱に利用した後、排ガス冷
却部40に送り込まれる。
Reference numeral 35 denotes a gas combustion furnace, which burns LNG or LPG fuel to generate hot gas. This hot gas is supplied into a heating cylinder 22 provided on the outer periphery of the cylindrical body 21 and is supplied to the cylindrical body 2.
1 is heated and then sent into the heating cylinder 12 of the cylindrical body 11 through the connecting pipe 37. After the cylindrical body 11 is heated, it is used for heating the drying means 39 from the discharge pipe 38. It is sent to the unit 40.

【0032】41は排ガス燃焼炉で、第1の加熱処理炉
10および第2の加熱処理炉20内で加熱処理中に発生
する排ガスを排ガス管e1およびe2を介して導入し、燃
焼処理する。
Reference numeral 41 denotes an exhaust gas combustion furnace, which introduces exhaust gas generated during heat treatment in the first heat treatment furnace 10 and the second heat treatment furnace 20 through exhaust gas pipes e 1 and e 2 , and performs combustion treatment. I do.

【0033】この排ガス燃焼炉41でガスを燃焼してタ
ール分等の可燃成分を除去した後、排ガス冷却部40で
バグフィルタ42の使用適温まで冷却してバグフィルタ
42に送り込み、ここで清浄化して煙突43より排出す
る。この冷却には熱交換器を使用して廃熱を利用しなが
ら冷却するようにするとよい。
After the gas is burned in the flue gas combustion furnace 41 to remove combustible components such as tar components, the flue gas cooling unit 40 cools the bag filter 42 to a suitable temperature for use and sends the bag filter 42 to the bag filter 42 where it is purified. And discharged from the chimney 43. It is preferable to use a heat exchanger for cooling while utilizing waste heat.

【0034】44は脱水手段で、溶解槽34内で減容化
された被処理物と反応した後の処理剤等を水に溶解した
ものを、この脱水手段44で固体物と液体とを分離し、
固体物は乾燥手段39で乾燥した後、炭化物などを取り
出す。一方、液体は排水処理手段45で、処理済みの処
理剤を回収し、中和剤等を注入して処理した後排水す
る。
Reference numeral 44 denotes a dehydrating means, which is obtained by dissolving a treating agent or the like after reacting with the object to be treated reduced in the dissolving tank 34 in water, and separating the solid substance and the liquid by the dehydrating means 44. And
After the solid matter is dried by the drying means 39, a carbide or the like is taken out. On the other hand, the liquid is treated by a wastewater treatment means 45, which collects the treated treatment agent, injects a neutralizing agent or the like, processes the liquid, and then drains the liquid.

【0035】次に、一連の被処理物の加熱処理方法を、
図3の加熱時間と温度との関係図を参照して説明する。
Next, a series of heat treatment methods for the object to be treated are as follows.
A description will be given with reference to a relationship diagram between the heating time and the temperature in FIG.

【0036】まず、被処理物を投入しない段階の時間t
1で、第2の加熱処理炉20(以下、減容炉と称す)、
第1の加熱処理炉10(以下、脱塩素炉と称す)の加熱
運転を開始する。即ち、ガス燃焼炉35と排ガス燃焼炉
41でLNG等の燃料を燃焼させ、各炉を加熱する。
First, the time t in the stage where the object is not charged
In 1 , the second heat treatment furnace 20 (hereinafter, referred to as volume reduction furnace),
The heating operation of the first heat treatment furnace 10 (hereinafter, referred to as a dechlorination furnace) is started. That is, fuel such as LNG is burned in the gas combustion furnace 35 and the exhaust gas combustion furnace 41, and each furnace is heated.

【0037】ガス燃焼炉35で発生した熱ガスは、減容
炉20の加熱筒22に供給され、円筒体21を加熱した
後、連絡管37から脱塩素炉10の加熱筒12内に送り
込まれ、円筒体11を加熱する。
The hot gas generated in the gas combustion furnace 35 is supplied to the heating cylinder 22 of the volume reduction furnace 20, and after heating the cylindrical body 21, is sent from the communication pipe 37 into the heating cylinder 12 of the dechlorination furnace 10. Then, the cylindrical body 11 is heated.

【0038】このときの減容炉20の加熱温度は、被処
理物が炭化する温度(300℃〜600℃)に、また、
脱塩素炉10の加熱温度は、被処理物から有害物質が分
解析出する温度(200℃〜400℃)に加熱する。ま
た排ガス燃焼炉41の加熱温度は800℃以上に加熱す
る。
The heating temperature of the volume reduction furnace 20 at this time is set to a temperature (300 ° C. to 600 ° C.) at which the material to be treated is carbonized.
The heating temperature of the dechlorination furnace 10 is set to a temperature (200 ° C. to 400 ° C.) at which the harmful substance is decomposed and precipitated from the object. The heating temperature of the exhaust gas combustion furnace 41 is set to 800 ° C. or higher.

【0039】そして、図3に示すように、排ガス燃焼炉
41の温度が750℃程度になった時間t2のとき、ポ
ッパ30から被処理物と処理剤とを混合したもの、又は
混合しながら脱塩素炉10内に供給する。
Then, as shown in FIG. 3, at time t 2 when the temperature of the exhaust gas combustion furnace 41 has reached about 750 ° C., the material to be treated and the treatment agent are mixed from the popper 30 or while being mixed. It is supplied into the dechlorination furnace 10.

【0040】この脱塩素炉10での加熱処理は、本例で
は、乾燥・脱塩素処理を行わせるもので、被処理物から
有害成分が析出する温度と時間を事前に調査して、被処
理物の性質を把握し、この調査結果を十分にカバーでき
る温度と時間で処理する。
In the heat treatment in the dechlorination furnace 10, in this example, drying and dechlorination are performed. The temperature and time at which harmful components are precipitated from the object to be treated are investigated in advance, and the heat treatment is performed. Understand the nature of the object and process at a temperature and time that can adequately cover the findings.

【0041】なお、この時間と温度は、加熱処理炉の状
態(大きさ、加熱手段などの炉に依存する条件)、処理
量、処理時間、処理温度などにも関係するので、事前に
調査などを十分に行っておく必要があり、またデータを
取り蓄積しておく必要がある。
The time and temperature are related to the state of the heat treatment furnace (conditions depending on the furnace such as the size and heating means), the amount of treatment, the treatment time, the treatment temperature, and the like. Must be performed sufficiently, and data must be collected and stored.

【0042】また、この脱塩素炉10での加熱処理は、
「燃焼、焼却」ではなく、乾留処理、「蒸し焼き、熱分
解」での処理とし、塩素系ガス等を被処理物から分解析
出して処理剤と反応させ、無害な塩類を生成させる。
The heat treatment in the dechlorination furnace 10 is as follows.
Instead of "combustion and incineration", it is a process of dry distillation and "steaming and pyrolysis", in which chlorine-based gas and the like are decomposed and precipitated from the object to be treated and reacted with the treating agent to produce harmless salts.

【0043】被処理物と混合又は添加する処理剤は、少
なくともHCl(塩化水素)と接触反応して無害な塩化
物を生成するアルカリ物質を使用する。例えば、本願の
出願人が先に出願した特開平9−155326号、特開
平10−43731号、特開平10−235186号、
特開平10−235187号に示すように、アルカリ土
類金属、アルカリ土類金属化合物、アルカリ金属、アル
カリ金属化合物で、具体的にはカルシウム、石灰、消石
灰、炭酸カルシウム、ドロマイト、珪酸塩(珪酸カルシ
ウムなど)、炭酸水素ナトリウム、炭酸ナトリウム、セ
スキ炭酸ナトリウム、天然ソーダ、水酸化ナトリウム、
水酸化カリウム、炭酸水素カリウム、炭酸カリウムの中
から1種類選択するか、数種類混合して使用する。使用
量としては、被処理物に対して5〜30重量%を混合ま
たは添加する。
As the treating agent to be mixed or added with the article to be treated, use is made of an alkali substance which forms a harmless chloride by reacting at least with HCl (hydrogen chloride). For example, JP-A-9-155326, JP-A-10-43731, and JP-A-10-235186, which the applicant of the present application previously filed,
As shown in JP-A-10-235187, alkaline earth metals, alkaline earth metal compounds, alkali metals, and alkali metal compounds, specifically, calcium, lime, slaked lime, calcium carbonate, dolomite, silicate (calcium silicate) Sodium bicarbonate, sodium carbonate, sodium sesquicarbonate, natural soda, sodium hydroxide,
One kind is selected from potassium hydroxide, potassium hydrogen carbonate, and potassium carbonate, or several kinds are mixed and used. As an amount to be used, 5 to 30% by weight of the material to be treated is mixed or added.

【0044】例えば、上記の炭酸水素ナトリウム(Na
HCO3)を使用した場合、第1の加熱処理炉である脱
塩素炉内においてHCl成分の分解ガスが発生するが、
直ちに炭酸水素ナトリウムと反応して(NaHCO3
+(HCl)→(NaCl)+(H2O)+(CO2)と
なり、無害な塩化ナトリウム(NaCl)を生成し、分
解ガスから有害なHClが無くなる。このことによっ
て、分解ガス中のHCl成分の無害化と残渣の無害化が
同時に行われる。
For example, sodium bicarbonate (Na
When HCO 3 ) is used, a decomposition gas of the HCl component is generated in the dechlorination furnace which is the first heat treatment furnace.
Reacts immediately with sodium bicarbonate (NaHCO 3 )
+ (HCl) → (NaCl) + (H 2 O) + (CO 2 ), producing harmless sodium chloride (NaCl) and eliminating harmful HCl from the decomposition gas. Thereby, the detoxification of the HCl component in the decomposition gas and the detoxification of the residue are simultaneously performed.

【0045】この有害成分を析出した後の被処理物はダ
クト17,ロータリーバルブ32,ダクト26を介して
減容炉20の円筒体21の供給口23に送り込まれ、こ
こで被処理物が炭化する温度(300℃〜600℃)で
加熱して炭化処理、又は800℃以上に加熱して灰化処
理して減容化する。
The object after the harmful components are precipitated is sent to the supply port 23 of the cylindrical body 21 of the volume reduction furnace 20 through the duct 17, the rotary valve 32, and the duct 26, where the object is carbonized. At a temperature (300 ° C. to 600 ° C.) for carbonization, or at 800 ° C. or more for incineration to reduce the volume.

【0046】この減容化処理する減容炉20内には、H
Cl等の有害成分、ダイオキシン類を含む分解ガスは存
在しないので、炭化又は灰化した被処理物にはこれを吸
収することはない。
In the volume reducing furnace 20 for performing the volume reducing process, H
Since there is no decomposition gas containing harmful components such as Cl and dioxins, the carbonized or incinerated object does not absorb it.

【0047】この減容化した被処理物と、反応後の処理
剤はダクト27,ロータリーバルブ33を介して溶解槽
34内に排出される。この溶解槽34内で、減容化され
た被処理物、反応した後の処理剤等を水に溶解し、これ
を脱水手段44で固体物と液体とを分離して、固体物は
乾燥手段39で乾燥した後取り出し、一方、液体は水処
理手段45で中和剤等を注入して処理した後排水する。
The reduced volume of the object to be treated and the treatment agent after the reaction are discharged into the dissolution tank 34 via the duct 27 and the rotary valve 33. In the dissolving tank 34, the reduced volume of the object to be treated, the treated agent after the reaction, and the like are dissolved in water, which is separated into a solid and a liquid by a dehydrating means 44, and the solid is dried by a drying means. After being dried at 39, the liquid is taken out. On the other hand, the liquid is treated by injecting a neutralizing agent or the like by a water treatment means 45 and then drained.

【0048】減容炉20の温度制御は、ガス燃焼炉35
による燃料供給量の制御によって、また脱塩素炉10の
温度制御は連絡管37に温度調整空気36の送風量を調
整することで行うことができる。
The temperature of the volume reduction furnace 20 is controlled by the gas combustion furnace 35.
And the temperature of the dechlorination furnace 10 can be controlled by adjusting the amount of temperature-adjusted air 36 supplied to the connecting pipe 37.

【0049】一方、脱塩素炉10および減容炉20で発
生した排ガスは、ガス排出管e1およびe2から排ガス燃
焼炉41に導入され燃焼される。この排ガス燃焼炉41
での燃焼は、ダイオキシン類を生成されないように85
0℃とされているので、この温度に近い800℃〜90
0℃が望ましい。図3では750℃で加熱しても発生し
た排ガスの燃焼によって800℃以上に昇温される。
On the other hand, the exhaust gas generated in the dechlorination furnace 10 and the volume reduction furnace 20 is introduced into the exhaust gas combustion furnace 41 from the gas discharge pipes e 1 and e 2 and burned. This exhaust gas combustion furnace 41
Combustion at 85% to prevent the production of dioxins
0 ° C., 800 ° C. to 90 °
0 ° C. is desirable. In FIG. 3, even when heated at 750 ° C., the temperature is raised to 800 ° C. or more by the combustion of the generated exhaust gas.

【0050】この排ガス燃焼炉41でタール分等の可燃
性成分および残存する有害物質を燃焼して除去した後、
排ガス冷却部40でバグフィルタ42の使用適温にまで
冷却し、バグフィルタ42を介して煙突43から排出さ
れる。
After combustible components such as tar components and remaining harmful substances are removed by burning in the exhaust gas combustion furnace 41,
The exhaust gas is cooled by the exhaust gas cooling unit 40 to a temperature suitable for use of the bag filter 42, and is discharged from the chimney 43 via the bag filter 42.

【0051】上記の加熱処理炉での加熱処理で生じた排
ガス中には、前記のように基本的に有害な塩素系ガスは
含まれていないが、被処理物の性質は千差万別であり、
また、処理条件等により不完全反応等の原因により、塩
素成分を完全に除去できない場合も起こり得るが、燃焼
することで分解し、完全に除去される。
Although the harmful chlorine-based gas is not basically contained in the exhaust gas generated by the heat treatment in the heat treatment furnace as described above, the properties of the object to be treated vary widely. Yes,
In addition, the chlorine component may not be completely removed due to incomplete reaction or the like due to processing conditions or the like. However, the chlorine component is decomposed by burning and completely removed.

【0052】加熱処理炉の加熱を停止する場合は、図3
に示すように、まず時間t3で被処理物の投入を停止
し、停止後、加熱処理された被処理物が全て排出される
時間を見計らった時間t4で減容炉20および脱塩素炉
10の加熱を停止する。そして、排ガス燃焼炉41は、
減容炉20および脱塩素炉10の加熱停止後も燃焼を継
続し、所定時間(30〜60分)後の時間t5で、ガス
燃焼炉41の運転(燃焼)を停止する。
When the heating of the heat treatment furnace is stopped, as shown in FIG.
As shown in the figure, first, the charging of the object to be processed is stopped at a time t 3 , and after the time is stopped, the volume reducing furnace 20 and the dechlorination furnace are set at a time t 4 when the time for discharging all the heat-processed objects is measured. The heating of 10 is stopped. And the exhaust gas combustion furnace 41 is
After heating stop volume reduction furnace 20 and dechlorination reactor 10 also continues to burn, at time t 5 after a predetermined time (30-60 minutes), and stops the operation of the gas combustion furnace 41 (combustion).

【0053】なお、脱塩素炉10及び減容炉20の回転
停止は、炉内温度が200℃以下になったときに停止す
ることが好ましい。
It is preferable that the rotation of the dechlorination furnace 10 and the volume reduction furnace 20 be stopped when the temperature in the furnace becomes 200 ° C. or less.

【0054】このように排ガス燃焼炉41の運転を最後
に停止させると次の効果がある。
When the operation of the exhaust gas combustion furnace 41 is finally stopped as described above, the following effects are obtained.

【0055】即ち、脱塩素炉10,減容炉20内には、
分解ガスが残存しており、これをブロアにより誘導排出
しているが、このガスを未燃焼のまま排出すると、悪臭
を伴った排ガスを排出することになり、しかも、有害物
質を含んだ排ガスを排出する恐れもある。従って、脱塩
素炉、減容炉の停止後も燃焼を継続することでその恐れ
は解消される。
That is, in the dechlorination furnace 10 and the volume reduction furnace 20,
Decomposed gas remains and is discharged by induction with a blower.If this gas is discharged without burning, it will emit exhaust gas with a bad smell, and furthermore, exhaust gas containing harmful substances will be emitted. There is a risk of emission. Therefore, the fear is eliminated by continuing the combustion even after the dechlorination furnace and the volume reduction furnace are stopped.

【0056】このように、被処理物の加熱処理および排
ガスの燃焼処理におけるダイオキシンの発生原因となる
低温領域での不完全燃焼を無くしたので、毎日運転・停
止を繰り返してもダイオキシン類の発生の恐れがない。
As described above, since incomplete combustion in a low-temperature region, which is a cause of generation of dioxin in the heating treatment of the object to be treated and the combustion treatment of exhaust gas, is eliminated, the generation of dioxins can be prevented even if the operation is repeated every day. There is no fear.

【0057】従って、1日の廃棄物の処理作業を、例え
ば、午前8時に開始し、被処理物の投入開始は、30〜
60分後、作業停止は、午後3時、終了は午後5時とな
るような運転サイクルを定め、加熱処理施設の各種の機
器をこのサイクルに合うように構成することで、好まし
い中・小規模の処理施設が実現できる。
Therefore, the daily waste disposal operation is started, for example, at 8:00 am,
After 60 minutes, an operation cycle in which the operation is stopped at 3:00 pm and the operation is ended at 5:00 pm is set, and various equipments of the heat treatment facility are configured to meet this cycle. Processing facility can be realized.

【0058】[0058]

【発明の効果】本発明は以上のように、加熱処理炉の加
熱停止後においても分解ガス燃焼炉を運転し、発生した
分解ガスの燃焼を継続するので、未燃焼の分解ガスを排
出することはなく、悪臭その他弊害要因の除去ができ
る。
As described above, the present invention operates the cracked gas combustion furnace even after the heating of the heat treatment furnace is stopped and continues burning the generated cracked gas, so that unburned cracked gas is discharged. No odor and other adverse factors can be removed.

【0059】また、加熱処理炉の加熱停止時には、被処
理物の投入を停止し、加熱処理された被処理物の排出完
了後、所定時間をおいて排ガス燃焼炉の運転を停止する
ようにしたので、一般的に言われている、運転開始時と
停止時における不完全燃焼によるダイオキシン類の発生
はなく、しかも、アルカリ物質の処理剤を添加・混合し
て塩化水素と接触反応させて無害な塩化物に置換してい
るので、無害な排ガスと残渣を得ることができ、運転開
始・停止時のみならず、全処理工程において安全、且つ
安定した加熱処理が出来る、等環境上極めて好ましい処
理効果を発揮する。
When the heating of the heat treatment furnace is stopped, the charging of the object to be treated is stopped, and after the discharge of the object to be heated is completed, the operation of the exhaust gas combustion furnace is stopped after a predetermined time. Therefore, there is no generation of dioxins due to incomplete combustion at the start and stop of operation, and it is harmless by adding and mixing an alkaline substance treating agent and reacting it with hydrogen chloride. Since it is replaced with chloride, harmless exhaust gas and residue can be obtained, and safe and stable heat treatment can be performed not only at the start and stop of the operation, but also in all treatment steps, which is an extremely environmentally favorable treatment effect. Demonstrate.

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

【図1】本発明の加熱処理方法を説明するための被処理
物の加熱処理装置の概念図。
FIG. 1 is a conceptual diagram of a heat treatment apparatus for an object to be treated for explaining a heat treatment method of the present invention.

【図2】回転円筒体の断面図。FIG. 2 is a sectional view of a rotating cylinder.

【図3】本発明の加熱処理方法を説明するための加熱時
間−加熱温度の関係図。
FIG. 3 is a relationship diagram of heating time and heating temperature for explaining the heat treatment method of the present invention.

【符号の説明】[Explanation of symbols]

10,20…加熱処理炉 11,21…円筒体 12,22…加熱筒 13,23…供給口 14,24…排出口 15,25…回転駆動手段 16,26…供給側ダクト 17,27…排出側ダクト 18…動的シール 19,29…支持ローラー 30…ホッパ 31,32,33…ロータリ−バルブ 34…溶解槽 35…ガス燃焼炉 36…温度調整空気 37…連絡管 38…排出管 39…乾燥手段 40…排ガス冷却部 41…排ガス燃焼炉 42…バグフィルタ 43…煙突 44…脱水手段 45…排水処理手段 10, 20 ... heat treatment furnace 11, 21 ... cylindrical body 12, 22 ... heating cylinder 13, 23 ... supply port 14, 24 ... discharge port 15, 25 ... rotation drive means 16, 26 ... supply side duct 17, 27 ... discharge Side duct 18 ... Dynamic seal 19, 29 ... Support roller 30 ... Hopper 31, 32, 33 ... Rotary valve 34 ... Melting tank 35 ... Gas combustion furnace 36 ... Temperature adjusted air 37 ... Connecting pipe 38 ... Discharge pipe 39 ... Drying Means 40: Exhaust gas cooling unit 41: Exhaust gas combustion furnace 42: Bag filter 43: Chimney 44: Dewatering means 45: Wastewater treatment means

───────────────────────────────────────────────────── 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) B09B 3/00 304H Fターム(参考) 3K061 AA07 AA24 AB02 AC01 BA05 BA08 BA10 CA01 CA07 FA10 FA21 3K065 AA07 AA23 AB02 AC01 BA05 BA08 BA10 CA16 3K078 AA05 AA08 AA10 BA06 BA08 BA26 CA02 CA21 4D004 AA46 AB07 BA03 CA24 CA41 CA42 CB09 CB34 CC12 DA03 DA06 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) B09B 3/00 304H F-term (Reference) 3K061 AA07 AA24 AB02 AC01 BA05 BA08 BA10 CA01 CA07 FA10 FA21 3K065 AA07 AA23 AB02 AC01 BA05 BA08 BA10 CA16 3K078 AA05 AA08 AA10 BA06 BA08 BA26 CA02 CA21 4D004 AA46 AB07 BA03 CA24 CA41 CA42 CB09 CB34 CC12 DA03 DA06

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】 被処理物を加熱処理炉に投入して加熱分
解処理し、且つ発生した分解ガスを排ガス燃焼炉で燃焼
処理する被処理物の加熱処理方法であって、前記排ガス
燃焼炉での分解ガスの燃焼は、加熱処理炉内の被処理物
の排出が完了した後も所定時間継続させることを特徴と
した被処理物の加熱処理方法。
1. A method for heating an object to be treated, wherein the object to be treated is charged into a heat treatment furnace for thermal decomposition treatment, and the generated decomposition gas is burned in an exhaust gas combustion furnace. Combustion of the decomposition gas is continued for a predetermined time even after the discharge of the object in the heat treatment furnace is completed.
【請求項2】 加熱処理炉での加熱処理は、脱塩素処理
と減容化処理とを少なくとも2つの異なる加熱処理炉で
行うことを特徴とした請求項1記載の被処理物の加熱処
理方法。
2. The heat treatment method for an object to be processed according to claim 1, wherein the heat treatment in the heat treatment furnace is such that the dechlorination treatment and the volume reduction treatment are performed in at least two different heat treatment furnaces. .
【請求項3】 脱塩素処理および減容化処理する加熱処
理炉の炉内温度は、夫々200℃以上および300℃以
上、排ガス燃焼炉の炉内温度は、750℃以上としたこ
とを特徴とする請求項1又は2記載の被処理物の加熱処
理方法。
3. The furnace temperature of the heat treatment furnace for dechlorination treatment and volume reduction treatment is 200 ° C. or more and 300 ° C. or more, respectively, and the furnace temperature of the exhaust gas combustion furnace is 750 ° C. or more. The method for heat-treating an object to be processed according to claim 1 or 2.
【請求項4】 脱塩素処理は、被処理物にアルカリ物質
の処理剤を添加混合して加熱処理し、発生した分解ガス
の有害物質と処理剤とを接触反応させて有害物質を無害
な反応物に置換することで排ガス・残渣の無害化を図っ
たことを特徴とする請求項2又は3記載の被処理物の加
熱処理方法。
4. The dechlorination treatment comprises adding a treatment agent for an alkaline substance to an object to be treated, heating the mixture, contacting the harmful substance of the generated decomposition gas with the treatment agent, and reacting the harmful substance harmlessly. 4. The heat treatment method for an object to be treated according to claim 2, wherein the exhaust gas / residue is rendered harmless by substituting the substance.
【請求項5】 処理剤はアルカリ物質の粉体で、処理物
に対して5〜30重量%添加することを特徴とする請求
項2,3又は4のいずれか1項に記載の被処理物の加熱
処理方法。
5. The processing object according to claim 2, wherein the processing agent is a powder of an alkaline substance and is added in an amount of 5 to 30% by weight based on the processing object. Heat treatment method.
【請求項6】 アルカリ物質の処理剤は、加熱により被
処理物から分解析出する有害成分と反応して無害な塩化
物を生成するアルカリ金属、アルカリ金属化合物、アル
カリ土類金属、アルカリ土類金属化合物に含まれる物質
の中から、少なくとも1種類を選択、又は2種類以上の
混合物であることを特徴とする請求項4又は5記載の被
処理物の加熱処理方法。
6. A treatment agent for an alkaline substance, which reacts with a harmful component decomposed and precipitated from an object to be treated by heating to form a harmless chloride, an alkali metal compound, an alkaline earth metal, and an alkaline earth. The method for heat treating an object to be treated according to claim 4 or 5, wherein at least one kind is selected from substances contained in the metal compound, or a mixture of two or more kinds.
【請求項7】 アルカリ金属化合物は、炭酸水素ナトリ
ウム、炭酸ナトリウム、セスキ炭酸ナトリウム、天然ソ
ーダ、炭酸カリウム、炭酸水素カリウム、炭酸ナトリウ
ムカリウム、水酸化ナトリウム、水酸化カリウムから選
択した単体、又は複数種の混合であることを特徴とする
請求項6記載の被処理物の加熱処理方法。
7. The alkali metal compound is selected from the group consisting of sodium hydrogencarbonate, sodium carbonate, sodium sesquicarbonate, natural soda, potassium carbonate, potassium hydrogencarbonate, sodium potassium carbonate, sodium hydroxide, and potassium hydroxide, or a plurality thereof. 7. The method for heat treating an object to be treated according to claim 6, wherein
【請求項8】 加熱処理炉を加熱するガス燃焼炉、排ガ
ス燃焼炉の燃料として、LNG又はLPGを使用したこ
とを特徴とする請求項1ないし3のいずれか1項に記載
の被処理物の加熱処理方法。
8. An object to be treated according to claim 1, wherein LNG or LPG is used as a fuel for a gas combustion furnace and an exhaust gas combustion furnace for heating the heat treatment furnace. Heat treatment method.
JP11202442A 1999-07-16 1999-07-16 Method for heat treating material to be treated Pending JP2001033013A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11202442A JP2001033013A (en) 1999-07-16 1999-07-16 Method for heat treating material to be treated

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11202442A JP2001033013A (en) 1999-07-16 1999-07-16 Method for heat treating material to be treated

Publications (1)

Publication Number Publication Date
JP2001033013A true JP2001033013A (en) 2001-02-09

Family

ID=16457602

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11202442A Pending JP2001033013A (en) 1999-07-16 1999-07-16 Method for heat treating material to be treated

Country Status (1)

Country Link
JP (1) JP2001033013A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009202124A (en) * 2008-02-28 2009-09-10 Mhi Environment Engineering Co Ltd Rotary kiln sludge drying apparatus and safely stopping method thereof

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009202124A (en) * 2008-02-28 2009-09-10 Mhi Environment Engineering Co Ltd Rotary kiln sludge drying apparatus and safely stopping method thereof

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