JPH11263978A - Apparatus for heat treatment with hot gas - Google Patents

Apparatus for heat treatment with hot gas

Info

Publication number
JPH11263978A
JPH11263978A JP10069622A JP6962298A JPH11263978A JP H11263978 A JPH11263978 A JP H11263978A JP 10069622 A JP10069622 A JP 10069622A JP 6962298 A JP6962298 A JP 6962298A JP H11263978 A JPH11263978 A JP H11263978A
Authority
JP
Japan
Prior art keywords
heating
cylindrical body
heat
gas
treated
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn
Application number
JP10069622A
Other languages
Japanese (ja)
Inventor
Yoshiyuki Kashiwagi
佳行 柏木
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 JP10069622A priority Critical patent/JPH11263978A/en
Publication of JPH11263978A publication Critical patent/JPH11263978A/en
Withdrawn legal-status Critical Current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

Landscapes

  • Incineration Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Coke Industry (AREA)
  • Muffle Furnaces And Rotary Kilns (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently receive heat of a hot gas by a cylindrical unit, effectively heat a material to be treated, shorten the heating time and improve the treating efficiency by using an LNG combustion gas as a heat source and further providing a received heat increasing means on the outer surface of the cylindrical unit. SOLUTION: This apparatus for heat treatment with a hot gas is obtained by forming a heat-treating furnace from a rotatable cylindrical unit 1 having a means for moving the material to be treated while stirring the material to be treated in the interior thereof, a received heat increasing means formed from unevennesses on the outer periphery of the cylindrical unit 1 and a heating cylinder 2 covering the nearly total length of the outer periphery of the cylindrical unit 1 and is capable of feeding the hot gas into the interior of the heating cylinder 2 and heating the material to be treated.

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、回転する円筒体か
らなる加熱処理炉に廃棄物等の被処理物を供給し加熱処
理炉内で被処理物を撹拌しながら移送して加熱処理する
加熱処理装置に関し、特に、加熱手段として熱ガスを用
いた加熱処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a heating apparatus for supplying an object such as waste to a heating furnace having a rotating cylindrical body, transferring the object in the heating furnace while stirring, and performing heat treatment. The present invention relates to a processing apparatus, and more particularly, to a heating processing apparatus using a hot gas as a heating unit.

【0002】[0002]

【従来の技術】一般廃棄物(都市ゴミなど)、産業廃棄
物(シュレッダーダストなど)、灰類(焼却灰、飛灰な
ど)、処理済み媒体(バグフィルタなどでの処理粉体な
ど)、汚泥、その他各種有機物含有物などの、被処理物
を、燃焼させるのではなく、蒸し焼き状態で加熱処理
(乾燥、熱分解、炭化、灰化)して、被処理物の改質と
減容化をすることが行われている。
2. Description of the Related Art General waste (municipal waste, etc.), industrial waste (shredder dust, etc.), ash (incinerated ash, fly ash, etc.), treated media (powder treated with a bag filter, etc.), sludge Instead of burning the object to be treated, such as those containing various organic substances, heat treatment (drying, pyrolysis, carbonization, and incineration) in a steamed state to improve the property and reduce the volume of the object. That is being done.

【0003】この種の加熱処理方法として低温乾留法に
より廃棄物を熱処理する方法がある。この方法は例え
ば、特表平8−510789号に開示されているよう
に、回転炉内に低温乾留室(熱分解炉)を有し、低温乾
留室は送り込まれた廃棄物を、低温乾留ガスと熱分解残
留物とに変換し、これを高温燃焼炉で燃焼して溶融液状
のスラグを生成してガラス状に固化し、発生したガスは
ボイラ、除去フィルタ及びガス浄化装置で処理して排出
する。この低温乾留室としては、内部に多数の平行な加
熱管を備え、この加熱管によって廃棄物を、ほぼ空気を
遮断した状態で加熱し、また、回転の際この加熱管によ
って廃棄物が上下動され、低温乾留ドラムの取り出し口
の方向へ移動されるようにするものである。
As a heat treatment method of this kind, there is a method of heat treating waste by a low-temperature carbonization method. In this method, for example, as disclosed in Japanese Patent Publication No. 8-510789, a low-temperature carbonization chamber (pyrolysis furnace) is provided in a rotary furnace, and the low-temperature carbonization chamber converts the fed waste into low-temperature carbonization gas. Is converted to a pyrolysis residue, which is burned in a high-temperature combustion furnace to produce a molten liquid slag and solidified into a glass, and the generated gas is processed and discharged by a boiler, removal filter and gas purification device. I do. The low-temperature carbonization chamber is equipped with a number of parallel heating tubes inside, and heats the waste with the heating tube almost in a state where air is shut off. And moved in the direction of the outlet of the low-temperature carbonization drum.

【0004】また、他の方法として、被処理物を加熱処
理する際、塩素成分と反応しやすいアルカリ系の添加剤
を適量混入して加熱処理し、処理灰に塩素成分を固定化
して無害な排ガスを得、処理灰は水洗浄等により塩素成
分を除去する方法も提案されている(特開平9−155
326)。
[0004] As another method, when heat-treating an object to be treated, an appropriate amount of an alkaline additive which easily reacts with a chlorine component is mixed and heat-treated, and the chlorine component is fixed to treated ash to be harmless. There has also been proposed a method of obtaining exhaust gas and removing the chlorine component from the treated ash by washing with water or the like (Japanese Patent Laid-Open No. 9-155).
326).

【0005】[0005]

【発明が解決しようとする課題】従来の加熱処理装置に
おける加熱手段は、単一の加熱手段によって加熱するの
が一般的である。
The heating means in the conventional heat treatment apparatus is generally heated by a single heating means.

【0006】前記の低温乾留法による加熱手段は、回転
炉内に多数配設した加熱管に加熱ガスを導入して加熱す
るので、この加熱管に被処理物が接触し、被処理物を加
熱しやすい利点はあるが、多数の加熱管を設置するの
で、製作時および保守が非常に煩雑となる。また長期間
にわたっての安定した加熱処理性能を維持することは困
難となる。
In the heating means based on the low-temperature carbonization method, a heating gas is introduced into a large number of heating tubes arranged in a rotary furnace to heat the heating tubes. Although there is an advantage that it is easy to perform, since a large number of heating tubes are installed, manufacturing and maintenance become very complicated. Further, it is difficult to maintain stable heat treatment performance over a long period of time.

【0007】しかも、加熱伝達面積を増加するには、加
熱管の本数を増やさなければならず、複雑な構成とな
る。
In addition, in order to increase the heat transmission area, the number of heating tubes must be increased, resulting in a complicated structure.

【0008】更に、熱ガスは排出側から供給側の一方向
にのみ導入しているので、加熱炉の停止状態から加熱炉
内の温度を所定の温度に均一に昇温するには時間がかか
る。
Further, since the hot gas is introduced only in one direction from the discharge side to the supply side, it takes time to uniformly raise the temperature in the heating furnace to a predetermined temperature from the stopped state of the heating furnace. .

【0009】また、前記の処理灰に塩素成分を固定する
方法における加熱手段は、外部から誘導加熱等の電気手
段によるものであるが、この手段は、被処理物の温度が
低下した場合のみ昇温制御は迅速に行える利点はある
が、加熱のためのコストは、ガスに比較して高価なもの
となる。
The heating means in the method for fixing the chlorine component to the treated ash is based on electric means such as induction heating from the outside. However, this means increases only when the temperature of the object to be treated is lowered. Although the temperature control has the advantage that it can be performed quickly, the cost for heating is higher than that of gas.

【0010】本発明は、このような課題を解決するため
になされたものである。
The present invention has been made to solve such a problem.

【0011】[0011]

【課題を解決するための手段】本発明は、回転する円筒
体内部に被処理物を効果的に加熱するために、熱ガスを
使用し、且つこの熱ガスからの受熱面積を大きくして、
円筒体の昇温を早めて効果的に被処理物を加熱処理する
ものである。その具体的手段は一端側に被処理物を供給
する供給口および他端側にこれを排出する排出口を有
し、略水平位置に配置した回転自在な円筒体と、該円筒
体の内部に設けられ被処理物を供給口側から排出口側に
撹拌しながら移送させる手段と、この円筒体を外部から
加熱する加熱手段とで加熱処理炉を構成し、前記加熱手
段は、円筒体の外周に加熱筒を設けて該加熱筒と円筒体
の外周間に密閉空間を形成し、この密閉空間内に燃焼装
置で得た熱ガスを導入して被処理物を加熱するととも
に、円筒体の外表面に熱ガスとの接触面積を増大させる
受熱増加手段を形成するものである。
According to the present invention, in order to effectively heat an object to be processed inside a rotating cylinder, a hot gas is used and a heat receiving area from the hot gas is increased.
This is to heat the cylinder effectively by accelerating the temperature rise of the cylindrical body. The concrete means has a supply port for supplying an object to be processed on one end side and a discharge port for discharging the discharge side on the other end side, and a rotatable cylinder disposed at a substantially horizontal position, and an inside of the cylinder. A heating treatment furnace is constituted by means for stirring and transferring the object to be treated from the supply port side to the discharge port side, and a heating means for externally heating the cylindrical body, wherein the heating means comprises an outer periphery of the cylindrical body. A heating cylinder is provided to form a sealed space between the heating cylinder and the outer periphery of the cylindrical body, and a heated gas obtained by a combustion device is introduced into the sealed space to heat the object to be processed, and the outside of the cylindrical body is heated. The heat receiving means for increasing the contact area with the hot gas is formed on the surface.

【0012】受熱増加手段としては、円筒体の表面に螺
旋状部材,平板状部材,波状部材を設けて形成するか又
は円筒体の表面の周方向に複数の溝を形成し、断面凹状
又は波状として表面積を増大させることで、熱ガスの熱
を効率よく、円筒体に伝達し、内部の被処理物を効果的
に加熱する。
The heat receiving increasing means may be formed by providing a spiral member, a flat plate member, or a corrugated member on the surface of the cylindrical body, or by forming a plurality of grooves in the circumferential direction of the surface of the cylindrical body to form a concave or corrugated cross section. By increasing the surface area, the heat of the hot gas is efficiently transmitted to the cylindrical body, and the object to be processed inside is effectively heated.

【0013】また、円筒体の材料は鉄系材料で形成す
る。
The material of the cylindrical body is formed of an iron-based material.

【0014】熱ガスは、LNGを燃焼して得る。LNG
の燃焼は、大気汚染防止法で規定する有害物質の排出が
なく、排ガス処理が不要でそのまま排出できる。
The hot gas is obtained by burning LNG. LNG
Combustion does not emit harmful substances specified by the Air Pollution Control Law, and can be discharged as it is without the need for exhaust gas treatment.

【0015】[0015]

【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.

【0016】図1は本発明の第1の実施の形態で、
(A)は加熱処理装置の正面から見た概念図、(B)は
円筒体の断面図である。同図において、Fhは加熱処理
炉で、該加熱処理炉Fhは、回転自在の円筒体1と、該
円筒体1の外周にガスダクトを形成し熱ガスを導入して
円筒体1を加熱する加熱筒2と、円筒体1の一方の端部
に設けられ、被処理物を円筒体1内に供給する供給口3
と、円筒体1の他方の端部に設けられた排出口4とで構
成され、この円筒体1は回転駆動手段5によって回転駆
動される。回転駆動手段5は駆動用モータ5a、駆動歯
車5b、円筒体1に設けられた従動歯車5cから成る。
6は供給口3側を包囲する供給側ダクト、7は排出口4
側を包囲する排出側ダクトを示す。
FIG. 1 shows a first embodiment of the present invention.
(A) is a conceptual diagram viewed from the front of the heat treatment apparatus, and (B) is a cross-sectional view of the cylindrical body. In the figure, F h is the heat treatment furnace, heat treatment furnace F h, the heating and cylinder 1 rotatable, forming a gas duct on the outer circumference of the cylindrical body 1 by introducing a hot gas cylinder 1 Heating cylinder 2, and a supply port 3 provided at one end of cylindrical body 1 to supply an object to be processed into cylindrical body 1.
And a discharge port 4 provided at the other end of the cylindrical body 1, and the cylindrical body 1 is rotationally driven by a rotation driving unit 5. The rotation driving means 5 includes a driving motor 5a, a driving gear 5b, and a driven gear 5c provided on the cylindrical body 1.
6 is a supply side duct surrounding the supply port 3 side, and 7 is a discharge port 4
2 shows a discharge duct surrounding the side.

【0017】加熱筒2は、円筒体1のほぼ全長にわたっ
て円筒体を覆い、円筒体全体を熱ガスで加熱するように
する。そして、加熱筒2で覆われた円筒体1の外表面に
は熱ガスから熱を効率良く受熱するための受熱増加手段
を設ける。
The heating cylinder 2 covers the cylindrical body over substantially the entire length of the cylindrical body 1, and heats the entire cylindrical body with a hot gas. Further, on the outer surface of the cylindrical body 1 covered with the heating cylinder 2, a heat receiving increasing means for efficiently receiving heat from the hot gas is provided.

【0018】図2はこの受熱増加手段の例で、図1
(A)のG部分を断面して拡大した図で、図2(A)
は、円筒体1の外表面に螺旋状の突起1aを設けた場
合、同図(B)は円筒体1の外表面に、円筒体の周方向
に所定間隔をもって所定幅の板体を軸線方向にづらして
形成した板状突起1bを設けた場合、(C),(D)
は、円筒体1の外表面に複数の溝で凹部1C又は波部1
dを形成した場合である。
FIG. 2 shows an example of this heat receiving increasing means.
FIG. 2 (A) is an enlarged cross-sectional view of a portion G of FIG.
FIG. 4B shows a case where a spiral projection 1a is provided on the outer surface of the cylindrical body 1 and a plate body having a predetermined width is provided on the outer surface of the cylindrical body 1 at a predetermined interval in a circumferential direction of the cylindrical body. (C), (D) when the plate-like projection 1b formed in accordance with
Is a concave portion 1C or a corrugated portion
This is the case where d was formed.

【0019】8は燃焼装置で、天然ガス(LNG)をL
NGタンク8TからのLNGを燃焼して熱ガスを発生さ
せる。この熱ガスは、円筒体1の外周に設けた加熱筒2
内に供給され、円筒体1を加熱した後、排出管vを介し
て排出するか、または他の加熱源として利用する。Hは
被処理物および処理剤とを投入するホッパを示してい
る。
Reference numeral 8 denotes a combustion device which converts natural gas (LNG) into L
The LNG from the NG tank 8T is burned to generate hot gas. This hot gas is supplied to a heating cylinder 2 provided on the outer periphery of the cylindrical body 1.
After heating the cylindrical body 1, it is discharged through a discharge pipe v or used as another heating source. H indicates a hopper into which an object to be processed and a processing agent are charged.

【0020】なお、図中Pはメカニカルシール等の動的
シールで、ダクト6,7と回転する円筒体1の接合部お
よび加熱筒2と円筒体1の接合部に設けられ、ダクト内
及び加熱筒内を密封する。
In the figure, P denotes a dynamic seal such as a mechanical seal, which is provided at the joint between the rotating cylinder 1 and the ducts 6 and 7 and the joint between the heating cylinder 2 and the cylindrical body 1 and inside the duct and heating. Seal the inside of the cylinder.

【0021】図1(B)は円筒体1の縦断面図で、内部
に複数の羽根Sを有し、円筒体の回転により、内部に供
給された被処理物、また被処理物と処理剤の混合物を撹
拌しながら供給口側から排出口側に移動させる。この移
動をスムーズにするため、円筒体1の供給口側を排出口
側より若干高く傾斜して設備してもよい。
FIG. 1B is a vertical cross-sectional view of the cylindrical body 1 having a plurality of blades S therein, the workpiece supplied inside by rotation of the cylindrical body, and the workpiece and the processing agent. Is moved from the supply port side to the discharge port side while stirring. In order to make this movement smooth, the supply port side of the cylindrical body 1 may be slightly inclined higher than the discharge port side.

【0022】一連の加熱処理は、まず、燃焼装置8でL
NGを燃焼して熱ガスを発生させ、加熱筒2に供給す
る。
A series of heat treatments is performed by first
The NG is burned to generate a hot gas, which is supplied to the heating cylinder 2.

【0023】次に(又は同時に)被処理物と処理剤とを
混合したもの、又は混合しながらホッパHから円筒体1
内に供給する。この円筒体1内で被処理物を乾留処理す
る。加熱処理された被処理物は、回転する円筒体の内部
を羽根Sにより撹拌されながら排出口側に移動し、排出
側ダクト7から排出され、次工程の処理装置等に送出さ
れる。加熱筒2内に導入された熱ガスは、円筒体1を介
して被処理物を加熱した後、排出管vを介して排出さ
れ、次工程の加熱源として再利用する。熱ガスが加熱筒
2内を通過するとき、円筒体に受熱増加手段を施してあ
るので、円筒体は効率良く受熱する。
Next (or simultaneously), a mixture of the object to be treated and the treatment agent, or the cylinder 1 from the hopper H while mixing.
Supply within. The object to be treated is subjected to dry distillation in the cylindrical body 1. The heat-treated object moves to the discharge port side while being stirred by the blades S inside the rotating cylindrical body, is discharged from the discharge side duct 7, and is sent out to a processing device or the like in the next process. The hot gas introduced into the heating cylinder 2 heats the object to be processed through the cylindrical body 1 and then is discharged through the discharge pipe v, and is reused as a heating source in the next step. When the hot gas passes through the inside of the heating cylinder 2, the cylinder receives heat increasing means because the cylinder receives heat increasing means.

【0024】次に、本発明の加熱処理装置を、ハロゲン
物質や硫化物等の有害成分を多量に含有する廃棄物など
の被処理物を、熱分解などの熱的処理を行って処理する
有害成分含有物の処理装置に適用した場合を第2の実施
の形態として説明する。
Next, the heat treatment apparatus according to the present invention is used to treat an object to be treated such as waste containing a large amount of harmful components such as halogen substances and sulfides by performing a thermal treatment such as thermal decomposition. A case where the present invention is applied to a component-containing material processing apparatus will be described as a second embodiment.

【0025】図3は、この処理装置の概念図で、図1の
加熱処理炉を2基用い、且つ補助的に電気加熱コイルを
用いた例で、第1の加熱処理炉で、後述する被処理物の
無害化のための分解反応処理を行い、第2の加熱処理炉
で炭化等による減容化を行う場合である。
FIG. 3 is a conceptual view of this processing apparatus, in which two heat processing furnaces shown in FIG. 1 are used and an auxiliary electric heating coil is used. This is a case in which a decomposition reaction treatment for detoxifying the treated material is performed, and the volume is reduced by carbonization or the like in the second heat treatment furnace.

【0026】図3において、10は第1の加熱処理炉、
20は第2の加熱処理炉を示す。第1の加熱処理炉10
は、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15a、駆
動歯車15b,円筒体11に設けられた従動歯車15c
から成る。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
は加熱コイル(誘導加熱又は抵抗体)で、加熱筒12の
両側の円筒体11の外周に、円筒体11とは非接触で且
つ近接して設けられ、加熱筒12と共に加熱手段を構成
する。
In FIG. 3, reference numeral 10 denotes a first heat treatment furnace;
Reference numeral 20 denotes a second heat treatment furnace. First heat treatment furnace 10
Is provided at one end of the cylindrical body 11, a heating cylinder 12 for forming a gas duct around the outer periphery of the cylindrical body 11, introducing a hot gas to heat the cylindrical body 11, and
The cylindrical body 11 is constituted by a supply port 13 for supplying an object to be processed into the cylindrical body 11 and a discharge port 14 provided at the other end of the cylindrical body 11. . The rotation driving means 15 includes a driving motor 15a, a driving gear 15b, and a driven gear 15c provided on the cylindrical body 11.
Consists of 16 is a supply duct surrounding the supply port 13 side, 17 is a discharge duct surrounding the discharge port 14 side, 18
Denotes a heating coil (induction heating or resistor), which is provided on the outer periphery of the cylindrical body 11 on both sides of the heating cylinder 12 in a non-contact and close proximity to the cylindrical body 11 and constitutes a heating means together with the heating cylinder 12.

【0027】なお、図中19は温度センサ装着用筒、P
は動的シールを示している。
In the drawing, reference numeral 19 denotes a cylinder for mounting a temperature sensor;
Indicates a dynamic seal.

【0028】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の次の一桁を同じ数字とし(例
えば、21は円筒体、22は加熱筒)説明を省略する。
The second heat treatment furnace 20 has the same basic configuration as the first heat treatment furnace 10 described above. Therefore, the same or corresponding part is designated by the same digit after 20 (for example, 21 is a cylindrical body, 22 is a heating cylinder), and description thereof is omitted.

【0029】30はホッパで、被処理物とアルカリ金属
化合物からなる処理剤とを混合して投入し、開閉バルブ
(開閉扉)31を介して円筒体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。
Reference numeral 30 denotes a hopper, which mixes and throws in the processing object and a processing agent comprising an alkali metal compound, and feeds the mixture from the supply port 13 of the cylindrical body 11 into the cylindrical body 11 through an open / close valve (open / close door) 31. Supply. The material to be treated may be any of solid matter such as general waste and industrial waste, ash, and sludge.

【0030】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 may have 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.

【0031】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と円筒体21の供給
口23とは、開閉バルブ(開閉扉)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は開閉バルブ(開閉トビラ)33を介して溶
解槽34に連通し、加熱処理後の残渣および反応済みの
処理剤を排出する。
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 of the cylindrical body 11 and the supply of the cylindrical body 21 are provided. The opening 23 is communicated with an opening / closing valve (opening / closing door) 32, and the discharge side duct 27 of the cylindrical body 21 of the second heat treatment furnace 20 is connected to a melting tank 34 via an opening / closing valve (opening / closing door) 33. To discharge the residue after the heat treatment and the reacted treating agent.

【0032】35は燃焼装置で、例えばLNGを燃焼さ
せる場合はLNGタンク36からのLNG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21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を介して
乾燥手段39に送出して、乾燥手段の熱として利用した
後、管路41を介して燃焼手段42に送り込まれる。
Reference numeral 35 denotes a combustion device, for example, when LNG is burned, burns LNG from the LNG tank 36 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 heats the cylindrical body 21.
After being fed into the heating cylinder 12 of the cylindrical body 11 through the connecting pipe 37 and heating the cylindrical body 11, it is sent out to the drying means 39 through the discharge pipe 38 and used as heat of the drying means. , And is sent to the combustion means 42 through the pipe 41.

【0033】燃焼手段42は、第1の加熱処理炉10の
排出側ダクト17,第2の加熱処理炉20の供給側ダク
ト26内のガスと、燃焼装置35から送出され、各加熱
部に利用し後のガスとを燃焼させ、次工程のバグフィル
タ40に送り込む。
The combustion means 42 is supplied to the gas in the discharge duct 17 of the first heat treatment furnace 10 and the gas in the supply duct 26 of the second heat treatment furnace 20 and is sent from the combustion device 35 to be used for each heating part. The burned gas is burned and sent to the bag filter 40 in the next step.

【0034】この燃焼手段42では、ガスを燃焼してタ
ール分を除去し、且つバグフィルタ40の耐久温度以下
にガスを冷却して送り込む。
In the combustion means 42, the gas is burned to remove tar components, and the gas is cooled and sent to a temperature lower than the endurable temperature of the bag filter 40.

【0035】バグフィルタ40では処理剤で反応処理し
た後、未反応の処理剤をホッパ30に送って再利用し、
排ガスは排ガス燃焼部43に送り込み、ここでLNG等
により燃焼処理を行い、煙突44から放出する。
In the bag filter 40, after the reaction treatment with the treatment agent, the unreacted treatment agent is sent to the hopper 30 for reuse.
The exhaust gas is sent to an exhaust gas combustion section 43, where the exhaust gas is subjected to combustion processing by LNG or the like, and is discharged from a chimney 44.

【0036】45は脱水手段で、溶解槽34内の水溶液
を固、液分離し、固形物は乾燥手段39で乾燥した後、
炭化物ホッパ46に排出し、液体は、水処理手段47で
中和剤等により中和した後、溶解槽34に返送して、再
利用を図る。
Reference numeral 45 denotes a dehydrating means, which solidifies and separates the aqueous solution in the dissolving tank 34, and after the solid matter is dried by the drying means 39,
The liquid discharged to the carbide hopper 46 is neutralized by a water treatment means 47 with a neutralizing agent or the like, and then returned to the dissolving tank 34 for reuse.

【0037】次に一連の処理方法について説明すると、
まず、燃焼装置35でLNGを燃焼して熱ガスを発生さ
せ、加熱筒22及び12に供給する。また必要に応じて
加熱コイル18,28に交流電力を供給して円筒体2
1,11を加熱する。次に、(又は同時に)ハロゲン物
質,硫化物を含有する被処理物とアルカリ金属化合物か
らなる処理剤とを混合したもの、又は混合しながらホッ
パ30から第1の加熱処理炉10の円筒体11内に供給
する。
Next, a series of processing methods will be described.
First, LNG is burned by the combustion device 35 to generate hot gas, which is supplied to the heating cylinders 22 and 12. If necessary, AC power is supplied to the heating coils 18 and 28 so that the cylindrical body 2
Heat 1,11. Next, (or simultaneously) a mixture of an object to be treated containing a halogen substance and a sulfide and a treatment agent made of an alkali metal compound, or a cylinder 11 of a first heat treatment furnace 10 from a hopper 30 while mixing. Supply within.

【0038】この第1の加熱処理炉10での加熱処理
は、被処理物からあらかじめ乾燥手段で水分を除去した
後、HClガス,SOxガス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(200℃〜350℃)と時
間で処理する。
In the heat treatment in the first heat treatment furnace 10, after moisture is removed from the object to be treated in advance by a drying means, the temperature and time at which HCl gas and SOx gas are deposited are investigated in advance, and the heat treatment is performed. The properties of the processed material are grasped, and the processing is performed at a temperature (200 ° C. to 350 ° C.) and time that can sufficiently cover the results of the investigation.

【0039】なお、この時間と温度は、加熱炉の状態
(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 heating furnace (conditions depending on the furnace, such as the size and heating means), the processing amount, the processing time, the processing temperature, and the like. It needs to be done well, and it is necessary to collect and store data.

【0040】また、第1の加熱処理炉での加熱は、「燃
焼、焼却」ではなく、「蒸し焼き、熱分解」での処理と
すると、析出した有害なHClガス、SOxガスとアル
カリ金属化合物の処理剤とを効果的に接触反応させるこ
とができる。
When the heating in the first heat treatment furnace is not "combustion and incineration" but "steaming and pyrolysis", the harmful HCl gas, SOx gas and the alkali metal compound which are deposited are removed. The contacting reaction with the treating agent can be effectively performed.

【0041】第1の加熱処理炉10内においては、HC
l,SOx成分を含む分解ガスが発生するが、直ちにH
Cl,SOx成分は添加しているアルカリ金属化合物、
例えば、炭酸水素ナトリウムと反応して無害な塩化ナト
リウム(NaCl)、亜硫酸塩(Na2SO3)を生成
し、分解ガスから有害なHCl,SOxを無くする。こ
れによって、分解ガス中のHCl,SOx成分の無害化
と残渣の無害化が同時に行える。
In the first heat treatment furnace 10, HC
Decomposed gas containing l, SOx components is generated, but H
Cl and SOx components are added alkali metal compounds,
For example, it reacts with sodium hydrogen carbonate to produce harmless sodium chloride (NaCl) and sulfite (Na 2 SO 3 ), and eliminates harmful HCl and SOx from the decomposition gas. Thereby, the detoxification of the HCl and SOx components in the decomposition gas and the detoxification of the residue can be performed at the same time.

【0042】この有害成分を析出し、無害化した後の被
処理物はダクト17,開閉バルブ32を介して第2の加
熱処理炉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(紙類は350℃程度で
炭化が始まる。)350℃〜700℃に加熱して炭化処
理、又は800℃以上に加熱して灰化処理して減容化す
る。この減容化工程の第2の加熱処理炉20内には、H
Cl,SOx成分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。
After the harmful components are precipitated and detoxified, the object is sent to the supply port 23 of the cylindrical body 21 of the second heat treatment furnace 20 through the duct 17 and the opening / closing valve 32,
Here, the temperature at which the material to be treated is carbonized (carbonization of paper starts at about 350 ° C.) Carbonization by heating to 350 ° C. to 700 ° C. or incineration by heating to 800 ° C. or more to reduce the volume I do. In the second heat treatment furnace 20 in this volume reduction step, H
Since there is no cracked gas containing Cl and SOx components, it is not absorbed by the carbonized or incinerated object.

【0043】この減容化した被処理物と、反応後の塩化
ナトリウム,亜硫酸塩等はダクト、開閉バルブ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45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、炭化物ホッパ
46から取り出し、一方、液体は水処理手段47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、溶解槽43に戻し再利用する。
The volume-reduced material to be processed and the reacted sodium chloride, sulfite and the like are discharged into a dissolution tank 34 via a duct and an opening / closing valve 33. In this melting tank 34,
The reduced volume of the object to be treated, the treated agent after the reaction, and the like are dissolved in water, and this is separated into a solid and a liquid by a dehydrating means 45, and the solid is dried by a drying means 39, and then dried. On the other hand, the liquid is recovered from the hopper 46, and the liquid is recovered by the water processing means 47, and the liquid is returned to the dissolving tank 43 after being treated by injecting a neutralizing agent or the like.

【0044】第1および第2の加熱処理炉の温度制御手
段は、次のように行われる。第1の加熱処理炉10にお
いては、第2の加熱処理炉20の加熱筒22との連絡管
37にバルブ(開閉バルブ又は3方弁)を設け、このバ
ルブの開閉制御により、又は連絡管37を複数本設けて
使用本数をバルブ開閉制御により選択する手段により熱
ガスの流量を制御し、次に、補助として加熱コイル18
に供給する交流電流、もしくは誘導加熱の場合は周波数
を制御する手段により昇温制御が行われる。これらの制
御はダクト17内のHCl等のガス濃度をガス濃度計4
5又は温度センサ装着用筒19内に設けられた温度セン
サによる検出温度により自動又は手動で制御される。
The temperature control means of the first and second heat treatment furnaces is performed as follows. In the first heat treatment furnace 10, a valve (open / close valve or three-way valve) is provided in the communication pipe 37 with the heating cylinder 22 of the second heat treatment furnace 20. Are provided, and the flow rate of the hot gas is controlled by means for selecting the number of used by the valve opening / closing control.
The temperature is controlled by means for controlling the alternating current supplied to the heater or the frequency in the case of induction heating. These controls are performed by measuring the gas concentration of HCl or the like in the duct 17 with a gas
5 or is automatically or manually controlled according to the temperature detected by a temperature sensor provided in the temperature sensor mounting cylinder 19.

【0045】また、第2の加熱処理炉20の温度制御手
段は、上記とほぼ同じであるが、燃焼装置35によるL
NG燃焼手段の制御がメインとなり、電気加熱手段が補
助となる。これらの制御も、ダクト26,27内のHC
l濃度を計測するガス濃度計46,47および温度セン
サ装着用筒29内の温度センサによる検出温度を反映し
て制御する。
The temperature control means of the second heat treatment furnace 20 is substantially the same as that described above.
The control of the NG combustion means becomes main, and the electric heating means assists. These controls are also performed by the HC in the ducts 26 and 27.
The control is performed by reflecting the temperature detected by the gas concentration meters 46 and 47 for measuring the l concentration and the temperature sensor in the temperature sensor mounting cylinder 29.

【0046】このとき、第1および第2の加熱処理炉1
0および20の加熱筒内を熱ガスが通過するとき、円筒
体の外周に受熱増加手段が設けられているので熱ガスの
熱を円筒体に効率良く伝達され、被処理物の加熱も効果
的に行われる。
At this time, the first and second heat treatment furnaces 1
When the hot gas passes through the 0 and 20 heating cylinders, the heat receiving increasing means is provided on the outer periphery of the cylindrical body, so that the heat of the hot gas is efficiently transmitted to the cylindrical body, and the object to be processed is also effectively heated. Done in

【0047】加熱処理炉内で被処理物とアルカリ金属化
合物とを加熱処理すると、分解した塩素系ガスおよび硫
黄酸化物系ガスとアルカリ金属化合物とが反応して分解
ガスの無害化と残渣の無害化が同時に行うことができ
る。このことは、本願の発明者の、次の実験調査により
明らかとなっている。
When the object to be treated and the alkali metal compound are heat-treated in a heat treatment furnace, the decomposed chlorine gas and sulfur oxide gas react with the alkali metal compound to render the decomposed gas harmless and the residue harmless. Can be performed simultaneously. This is clear from the following experimental investigation by the inventor of the present application.

【0048】実験は、試料として被処理物に硫黄成分を
含む固形化燃料(以下、RDFと称す)を使用して行っ
た。
The experiment was carried out using a solidified fuel (hereinafter, referred to as RDF) containing a sulfur component in an object to be treated as a sample.

【0049】RDFとは、可燃できるように固形化処理
したものを言い、広義には、 (1)厨芥類(肉類、魚頭、骨、卵殻、野菜、果物等の
残り物で「コンポスト」と称されている。) (2)プラスチック類(ポリエチレン、ポリプロピレ
ン、ポリスチン、ポリ塩化ビニリデン、等) (3)紙類(ティッシュペーパ、新聞紙、広告紙、袋
類、箱類、飲料パック、等) (4)その他可燃物(布などの繊維類、木片、ゴム、皮
革、等) の混合物を固形化したものを言う。
The RDF is a product which is solidified so as to be combustible. In a broad sense, (1) kitchen waste (remaining material such as meat, fish head, bone, eggshell, vegetables, fruits, etc., is called "compost") (2) Plastics (polyethylene, polypropylene, polystin, polyvinylidene chloride, etc.) (3) Papers (tissue paper, newspaper, advertising paper, bags, boxes, beverage packs, etc.) (4) ) A solidified mixture of other combustible materials (fibers such as cloth, wood chips, rubber, leather, etc.).

【0050】狹義には、(1)のコンポストを含まない
(2)、(3)、(4)のものを言う。今回はコンポス
トを含まないRDFを使用した。
In a narrow sense, (2), (3) and (4) which do not include the compost of (1) are mentioned. This time, RDF without compost was used.

【0051】このような試料のRDFを破砕し、本発明
によるアルカリ金属化合物の中から数種の物質を用い、
また、未破砕のRDFを用いて比較実験を行った。
The RDF of such a sample is crushed, and several kinds of substances are selected from the alkali metal compounds according to the present invention.
A comparative experiment was performed using uncrushed RDF.

【0052】なお、一般に知られている処理済みのRD
Fの硫黄成分は、約1.0重量%含有し、プラスチック
系のRDFは、0.29〜0.89重量%の塩素成分を
含有している。また、古紙系のRDFは、0.2重量%
の塩素成分を含有している。
It should be noted that a generally known processed RD
The sulfur component of F contains about 1.0% by weight, and the plastic RDF contains 0.29 to 0.89% by weight of a chlorine component. In addition, waste paper RDF is 0.2% by weight.
Contains a chlorine component.

【0053】実験は、排気管付きで、開閉扉を有する密
閉容器にて低酸素雰囲気を作り、この密閉容器に試料を
入れ、電気炉にて加熱し、250℃から600℃まで5
0℃間隔で各温度にて5分間保持し、昇温時、キープ時
で排気管を開けてHC1,SO2ガス濃度(ppm)を
測定した。また、600℃〜1000℃についても測定
した。
In the experiment, a low-oxygen atmosphere was created in a closed vessel equipped with an exhaust pipe and having an opening / closing door, a sample was placed in this closed vessel, heated in an electric furnace, and heated from 250 ° C. to 600 ° C. for 5 hours.
The temperature was held at 0 ° C. for 5 minutes at each temperature, and the HC1 and SO 2 gas concentrations (ppm) were measured by opening the exhaust pipe at the time of heating and keeping. In addition, the measurement was also performed at 600 ° C to 1000 ° C.

【0054】ガス濃度の測定は、JIS−K0804に
規定されている検知管によって測定した。
The gas concentration was measured using a detector tube specified in JIS-K0804.

【0055】表1および表2にこの測定結果を示す。H
Clガス,SO2ガス濃度は実験10回における測定値
で表2の比較例1〜比較例3は最低値、表1の実施例1
〜7は最高値を示す。
Tables 1 and 2 show the measurement results. H
The Cl gas and SO 2 gas concentrations were measured values in ten experiments, and Comparative Examples 1 to 3 in Table 2 were the lowest values, and Example 1 in Table 1 was the lowest value.
To 7 indicate the highest values.

【0056】なお、“ND”は“検出されず”を表し、
10回の実験でいずれも検出されなかったことを示す。
Note that "ND" represents "not detected",
It shows that none was detected in 10 experiments.

【0057】最初に、上記の未破砕のRDF40gを破
砕して、これに処理剤としてNaHCO3を10g添加
したものと、4gを添加したものを夫々実施例1および
実施例2とし、またRDFを破砕した20gに、処理剤
としてKHCO3を3gおよびNa2CO3+K2CO3
3g添加したものを夫々実施例3および4とし、また、
RDFを破砕した20gに、処理剤としてNaOHおよ
びKOHを3g添加したものを夫々実施例5および6と
し、更に、RDFを破砕しない塊状のもの40gに処理
剤としてNaHCO3を10gを添加したものを実施例
7として各試料についてHCl濃度およびSO2濃度を
測定をした。その結果を表1に示す。
First, 40 g of the above uncrushed RDF was crushed, and 10 g of NaHCO 3 was added as a treating agent to the crushed RDF, and those obtained by adding 4 g were referred to as Examples 1 and 2, respectively. Examples 3 and 4 were obtained by adding 3 g of KHCO 3 and 3 g of Na 2 CO 3 + K 2 CO 3 as treating agents to 20 g of the crushed, respectively.
Examples 5 and 6 were obtained by adding 3 g of NaOH and KOH as a treating agent to 20 g of RDF crushed, and further adding 10 g of NaHCO 3 as a treating agent to 40 g of a lump that did not crush RDF. As Example 7, the HCl concentration and the SO 2 concentration of each sample were measured. Table 1 shows the results.

【0058】[0058]

【表1】 [Table 1]

【0059】次に、従来知られている処理済みのRDF
を破砕したものを40gと20gを使用したものを夫々
比較例1および比較例2とし、また、RDFを破砕せず
に塊状のものを40g使用したものを比較例3として、
それぞれについてHCl濃度およびSO2濃度を測定し
た。その結果を表2に示す。
Next, a conventionally-processed RDF
Those obtained by using 40 g and 20 g of crushed RDF were referred to as Comparative Examples 1 and 2, respectively, and those obtained by using 40 g of lump without crushing RDF were used as Comparative Example 3.
The HCl concentration and the SO 2 concentration were measured for each. Table 2 shows the results.

【0060】[0060]

【表2】 [Table 2]

【0061】これら表1および表2の実験結果から、次
のように考察される。
From the experimental results in Tables 1 and 2, the following is considered.

【0062】塩化水素(HCl)の場合 (1)破砕した場合には、実施例4で400℃で微量に
検出されたが、他の例では検出されず非常に良好な結果
が得られた。
In the case of hydrogen chloride (HCl) (1) In the case of crushing, a very small amount was detected at 400 ° C. in Example 4, but was not detected in other examples, and very good results were obtained.

【0063】比較例1〜2と比較しても相当低減してい
ることが判る。
As can be seen from comparison with Comparative Examples 1 and 2, there is a considerable reduction.

【0064】(2)塊の場合には、350〜450℃で
破砕した場合に比較して若干検出されているが、比較例
3に比較して相当低減していることが判る。
(2) In the case of lumps, the amount was slightly detected as compared with the case of crushing at 350 to 450 ° C., but it was found that it was considerably reduced as compared with Comparative Example 3.

【0065】硫化ガス(SO2)の場合、 (1)破砕した場合には、400〜450℃でSO2
若干発生するが全体として非常に良好である(実施例1
〜6)。
In the case of sulfide gas (SO 2 ), (1) When crushed, SO 2 is slightly generated at 400 to 450 ° C., but very good as a whole (Example 1)
~ 6).

【0066】比較例1〜2としても相当低減しているこ
とが判る。
It can be seen that Comparative Examples 1 and 2 are considerably reduced.

【0067】(2)塊のままの場合には、350〜45
0℃で破砕した場合に比較してSO2が若干多く発生す
るが全体としては良好である(実施例7)。
(2) In the case of a lump, 350 to 45
Although slightly more SO 2 is generated than when crushed at 0 ° C., it is good as a whole (Example 7).

【0068】比較例3と比較しても相当低減しているこ
とが判る。
As can be seen from the comparison with Comparative Example 3, it is considerably reduced.

【0069】以上の実験調査により、塩素成分と硫黄成
分を含有する処理物を処理する場合には、有害なHCl
及びSOxと反応して無害な塩化物及び亜硫酸塩を生成
する、アルカリ金属化合物を添加して処理することで、
HCl及びSOxの無害化処理できることが確認でき
た。
According to the above experimental investigation, when treating a treated product containing a chlorine component and a sulfur component, harmful HCl
And reacting with SOx to generate harmless chlorides and sulfites,
It was confirmed that HCl and SOx could be detoxified.

【0070】なお、600℃以上においても同様な脱塩
素効果はあるが、設備の形態、時間、処理量などに基づ
いて決定すればよい。
Although a similar dechlorination effect can be obtained even at 600 ° C. or higher, it may be determined based on the type of equipment, time, throughput, and the like.

【0071】アルカリ金属化合物を添加して処理する
と、HClおよびSOxの無害化処理ができる理由は、
次のような反応による。
The reason why HCl and SOx can be detoxified by adding an alkali metal compound for the treatment is as follows.
According to the following reaction.

【0072】(A)、HClの場合の反応 有害な塩化水素が無害な塩化物に置換生成される理由は
下記のように反応していることから明らかとなった。
(A) Reaction in the case of HCl The reason why harmful hydrogen chloride is replaced with harmless chloride is produced from the following reaction.

【0073】炭酸水素ナトリウム (NaHCO3)+(HCl)→(NaCl)+(H
2O)+(CO2) 炭酸水素カリウム (KHCO3)+(HCl)→(KCl)+(H2O)+
(CO2) 水酸化ナトリウム (NaOH)+(HCl)→(NaCl)+(H2O) 水酸化カリウム (KOH)+(HCl)→(KCl)+(H2O) 特に炭酸水素系の場合の効果が顕著であるが、これは、
塩化水素(HCl)が分解析出する温度(250℃以
上)以下の温度でまず、CO2が分離することで、残り
のNaOH,KOHと発生したHClとの反応がスムー
ズに行える雰囲気状態となっているものと考えられる。
Sodium hydrogen carbonate (NaHCO 3 ) + (HCl) → (NaCl) + (H
2 O) + (CO 2 ) potassium hydrogen carbonate (KHCO 3 ) + (HCl) → (KCl) + (H 2 O) +
(CO 2 ) Sodium hydroxide (NaOH) + (HCl) → (NaCl) + (H 2 O) Potassium hydroxide (KOH) + (HCl) → (KCl) + (H 2 O) Especially in the case of hydrogen carbonate Is remarkable, this is because
First, CO 2 is separated at a temperature lower than the temperature (250 ° C. or higher) at which hydrogen chloride (HCl) decomposes and precipitates, so that an atmosphere state in which the reaction between the remaining NaOH and KOH and the generated HCl can be performed smoothly. It is thought that it is.

【0074】すなわち、反応状態は、 炭酸水素ナトリウムの場合 (NaHCO3)→(NaOH)+(CO2) (NaOH)+(HCl)→(NaCl)+(H2O) 炭酸水素カリウム (KHCO3)→(KOH)+(CO2) (KOH)+(HCl)→(KCl)+(H2O) となり、NaOH、KOHとHClとが迅速に反応して
無害な塩化物(NaCl,KCl)を新たに生成するも
のである。
That is, when the reaction state is sodium hydrogen carbonate, (NaHCO 3 ) → (NaOH) + (CO 2 ) (NaOH) + (HCl) → (NaCl) + (H 2 O) Potassium hydrogen carbonate (KHCO 3) ) → (KOH) + (CO 2 ) (KOH) + (HCl) → (KCl) + (H 2 O), and NaOH, KOH and HCl react rapidly to form harmless chlorides (NaCl, KCl). Is newly generated.

【0075】一方、炭酸カルシウム(CaCO3)、消
石灰(Ca(OH)2)の場合には、同様に無害な塩化
物(CaCl)を生成するもののCaとの反応がスムー
ズでないものと思われる。
On the other hand, in the case of calcium carbonate (CaCO 3 ) and slaked lime (Ca (OH) 2 ), harmless chloride (CaCl) is similarly produced, but the reaction with Ca seems not to be smooth.

【0076】上記のように生成した、NaCl,KCl
は無害な塩化物であり、上記物質以外にも、同様に、N
aCl,KClを生成するナトリウム系、カリウム系の
下記の物質があり、同様な効果が得られる。
NaCl, KCl produced as described above
Is a harmless chloride. In addition to the above substances, N
There are the following sodium-based and potassium-based substances that produce aCl and KCl, and similar effects can be obtained.

【0077】炭酸ナトリウム、炭酸カリウム、炭酸ナト
リウムカリウム、炭酸ナトリウム水和物、セスキ炭酸ナ
トリウム、天然ソーダ。
Sodium carbonate, potassium carbonate, sodium potassium carbonate, sodium carbonate hydrate, sodium sesquicarbonate, natural soda.

【0078】次に処理後の塩素系物質の確認を行った。Next, the chlorine-based substance after the treatment was confirmed.

【0079】得られた残渣を分析した結果、有害な塩素
系ガス成分は検出されず、無害な塩化物である塩化ナト
リウム、塩化カリウムが検出された。更に残渣を10分
間撹拌して水洗浄することにより、塩化ナトリウム、塩
化カリウムは水に溶解し、炭化物が残存するが、この炭
化物中にも有害な塩素系ガス成分は検出されなかった。
As a result of analyzing the obtained residue, no harmful chlorine-based gas components were detected, and harmless chlorides such as sodium chloride and potassium chloride were detected. Further, the residue was stirred for 10 minutes and washed with water, so that sodium chloride and potassium chloride were dissolved in water and a carbide remained, but no harmful chlorine-based gas component was detected in the carbide.

【0080】従って、有害な塩素成分は、残渣の一部と
なる、塩化ナトリウム(NaCl)、塩化カリウム(K
Cl)、水分(H2O)、気体(CO2)となり、ダイオ
キシンの原因となる塩化水素を発生することはなく、排
ガス及び残渣の無害化が実現できる。
Therefore, the harmful chlorine components are sodium chloride (NaCl) and potassium chloride (K
Cl), water (H 2 O), and gas (CO 2 ), do not generate hydrogen chloride that causes dioxin, and can achieve harmlessness of exhaust gas and residues.

【0081】(B)、SOxの反応の場合 有害なSOxが無害な亜硫酸塩に置換生成される理由は
下記のように反応していることから明らかとなった。
(B) In the case of SOx reaction The reason why the harmful SOx is replaced with a harmless sulfite is evident from the following reaction.

【0082】炭酸水素ナトリウム (NaHCO3)→(NaOH)+(CO2) (2NaOH)+(SO2)→(Na2SO3)+(H
2O) 炭酸水素カリウム (KHCO3)→(KOH)+(CO2) (2KOH)+(SO2)→(K2SO3)+(H2O) 水酸化ナトリウム (2NaOH)+(SO2)→Na2SO3)+(2H
2O) 水酸化カリウム (2KOH)+(SO2)→(K2SO3)+(H2O) 炭酸ナトリウムカリウム (Na2HCO3+K2CO3)+(2SO2)→(Na2
3)+(K2SO3)+(2CO2) 特に炭酸水素系の場合の効果が顕著であるが、これは、
硫化ガス(SO2)が分解析出する温度(300℃以
上)以下の温度でまず、CO2が分離することで、残り
のアルカリ金属水酸化物(NaOH,KOH)と発生し
たSO2との反応がスムーズに行える雰囲気状態となっ
ているものと考えられる。
Sodium hydrogen carbonate (NaHCO 3 ) → (NaOH) + (CO 2 ) (2NaOH) + (SO 2 ) → (Na 2 SO 3 ) + (H
2 O) Potassium hydrogen carbonate (KHCO 3 ) → (KOH) + (CO 2 ) (2KOH) + (SO 2 ) → (K 2 SO 3 ) + (H 2 O) Sodium hydroxide (2NaOH) + (SO 2 ) → Na 2 SO 3 ) + (2H
2 O) potassium hydroxide (2KOH) + (SO 2) → (K 2 SO 3) + (H 2 O) potassium sodium carbonate (Na 2 HCO 3 + K 2 CO 3) + (2SO 2) → (Na 2 S
O 3 ) + (K 2 SO 3 ) + (2CO 2 ) In particular, the effect is remarkable in the case of a hydrogen carbonate system.
First, CO 2 is separated at a temperature lower than the temperature (300 ° C. or higher) at which the sulfurized gas (SO 2 ) decomposes and precipitates, so that the remaining alkali metal hydroxide (NaOH, KOH) and the generated SO 2 It is considered that the atmosphere was such that the reaction could be performed smoothly.

【0083】すなわち、反応状態は、 炭酸水素ナトリウムの場合 (NaHCO3)→(NaOH)+(CO2) (2NaOH)+(SO2)→(Na2SO3)+(H
2O) 炭酸水素カリウム (KHCO3)→(KOH)+(CO2) (2KOH)+(SO2)→(K2SO3)+(H2O) となり、NaOH、KOHとSO2とが迅速に反応して
無害な塩化物(Na2SO3、K2SO3)を新たに生成す
るものである。上記のように生成した、Na2SO3(亜
硫酸ナトリウム)、K2SO3(亜硫酸カリウム)は無害
な亜硫酸塩であり、上記物質以外にも、同様に、Na2
SO3、K2SO3を生成するナトリウム系、カリウム系
の下記の物質があり、同様の効果が得られる。
That is, when the reaction state is sodium hydrogen carbonate, (NaHCO 3 ) → (NaOH) + (CO 2 ) (2NaOH) + (SO 2 ) → (Na 2 SO 3 ) + (H
2 O) Potassium hydrogen carbonate (KHCO 3 ) → (KOH) + (CO 2 ) (2KOH) + (SO 2 ) → (K 2 SO 3 ) + (H 2 O), and NaOH, KOH and SO 2 It reacts quickly to produce harmless chlorides (Na 2 SO 3 , K 2 SO 3 ). Was produced as described above, Na 2 SO 3 (sodium sulfite), K 2 SO 3 (potassium sulfite) is a harmless sulfite, in addition to the above substances, likewise, Na 2
There are the following sodium-based and potassium-based substances that generate SO 3 and K 2 SO 3 , and similar effects can be obtained.

【0084】炭酸ナトリウム、炭酸カリウム、炭酸ナト
リウムカリウム、炭酸ナトリウム水和物、セスキ炭酸ナ
トリウム、天然ソーダ。
Sodium carbonate, potassium carbonate, sodium potassium carbonate, sodium carbonate hydrate, sodium sesquicarbonate, natural soda.

【0085】次に、処理後の硫化物の確認を行った。Next, the sulfide after the treatment was confirmed.

【0086】得られた残渣を分析した結果、有害なSO
xガス成分は検出されず、無害な亜硫酸塩であるカリウ
ム金属塩(Na2SO3,K2SO3)が検出された。
As a result of analyzing the obtained residue, harmful SO was detected.
No x gas component was detected, and potassium metal salts (Na 2 SO 3 , K 2 SO 3 ), which are harmless sulfites, were detected.

【0087】更に残渣を10分間撹拌して水洗浄するこ
とにより、亜硫酸塩のアルカリ金属塩は水に溶けやす
く、加水分解してアルカリ性を呈し、 (Na2SO3)+(2H2O)→(2NaOH)+(H2
SO3) (K2SO3)+(2H2O)→(2KOH)+(H2SO
3) これらの物質は水に溶解し、炭化物が残存するが、この
炭化物中にも有害なSOxガス成分は検出されなかっ
た。
Further, by stirring the residue for 10 minutes and washing with water, the alkali metal salt of sulfite is easily dissolved in water, hydrolyzed to exhibit alkalinity, and (Na 2 SO 3 ) + (2H 2 O) → (2NaOH) + (H 2
SO 3 ) (K 2 SO 3 ) + (2H 2 O) → (2KOH) + (H 2 SO
3 ) These substances were dissolved in water and carbide remained, but no harmful SOx gas component was detected in the carbide.

【0088】従って、有害なSOx成分は、残渣の一部
となる、亜硫酸ナトリウム(粉末)(Na2SO3)、亜
硫酸カリウム(粉末)(K2SO3)、水分(H2O)、
気体(CO2)となり、SOxガスの発生は防止され、
分解ガス及び残渣からSOxガスの無害化が実現できる
ことが確認できた。
Therefore, the harmful SOx components become a part of the residue, such as sodium sulfite (powder) (Na 2 SO 3 ), potassium sulfite (powder) (K 2 SO 3 ), moisture (H 2 O),
Gas (CO 2 ), preventing the generation of SOx gas,
It was confirmed that the detoxification of SOx gas can be realized from the decomposition gas and the residue.

【0089】このような、有害成分処理に使用する処理
剤としては、 (1)アルカリ金属化合物の単体、複数種の混合 (2)アルカリ金属化合物は、水酸化物、炭酸化物の物
質 (3)水酸化物、炭酸化物は、ナトリウム系、カリウム
系の物質 (4)脱硫剤は、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、複
数種の混合が適合することも判明した。
The treating agents used for treating harmful components include: (1) a simple substance of an alkali metal compound, a mixture of plural kinds thereof, (2) the alkali metal compound is a substance of hydroxide or carbonate, and (3) Hydroxides and carbonates are sodium-based and potassium-based substances. (4) The desulfurizing agent is sodium bicarbonate, sodium carbonate, sodium sesquicarbonate, natural soda, potassium carbonate, potassium bicarbonate, sodium potassium carbonate, sodium hydroxide. It has also been found that a single substance selected from the group consisting of, potassium hydroxide, and a mixture of plural kinds are suitable.

【0090】従って、発生する分解ガス中の有害成分
(塩素系ガス及び硫黄酸化物系ガス)と加えた処理剤と
の接触反応により、有害成分が無害な塩化ナトリウム
(NaCl、KCl)及び亜硫酸塩(Na2SO3、K2
SO3)に置換生成されるので、分解ガスおよび残渣か
ら有害な成分(塩素系ガス及び硫黄酸化物系ガス)を無
くすることができ、無害な分解ガスおよび無害な残渣と
することができる。
Therefore, the contact reaction between the harmful components (chlorine gas and sulfur oxide gas) in the generated decomposition gas and the added treating agent causes the harmful components to be harmless sodium chloride (NaCl, KCl) and sulfite. (Na 2 SO 3 , K 2
Since SO 3 is replaced and generated, harmful components (chlorine-based gas and sulfur oxide-based gas) can be eliminated from the decomposition gas and the residue, and harmless decomposition gas and harmless residue can be obtained.

【0091】この無害化された残渣(被処理物)は、第
2の加熱処理炉20で炭化等による減容化が行われ、反
応生成物の無害な塩化ナトリウム、亜硫酸塩とともに溶
解槽34に取り出される。この塩化ナトリウム、亜硫酸
塩は水などの溶液で洗浄することにより、効果的に除去
できる。
The detoxified residue (substance to be treated) is reduced in volume by carbonization or the like in the second heat treatment furnace 20, and is transferred to the dissolution tank 34 together with the harmless sodium chloride and sulfite of the reaction product. Taken out. The sodium chloride and the sulfite can be effectively removed by washing with a solution such as water.

【0092】以上のように、被処理物の含有する有害成
分を分解析出させると同時にアルカリ金属化合物と反応
させる分解反応手段と、その後の被処理物を加熱して減
容化する手段とを別の加熱処理炉で行うと、 (1)実験の結果から明らかなように、塩素成分及び硫
黄成分を含有する廃棄物等の被処理物を加熱処理した場
合には、有害な塩素系ガスおよび硫黄酸化物系ガスが分
解析出するが、アルカリ金属化合物と、発生した有害成
分とが反応して無害な塩類を置換生成するので、分解ガ
スと残渣の両方の無害化が実現でき、しかも、残渣中の
生成した塩類は、水などの溶液によって除去でき、除去
溶液中にも有害成分は析出しないので、安全に廃棄物を
処理できる。
As described above, the decomposition reaction means for decomposing and depositing the harmful components contained in the object to be treated and reacting with the alkali metal compound at the same time, and the means for heating and reducing the volume of the object to be treated thereafter. When performed in another heat treatment furnace, (1) As is clear from the results of the experiment, when the object to be treated such as waste containing chlorine component and sulfur component is subjected to heat treatment, harmful chlorine-based gas and The sulfur oxide-based gas is decomposed and precipitated, but the alkali metal compound and the generated harmful component react to produce harmless salts, so that both the decomposed gas and the residue can be made harmless, and The generated salts in the residue can be removed by a solution such as water, and no harmful components are precipitated in the removal solution, so that the waste can be safely treated.

【0093】従って、ダイオキシン類を生成する塩素系
ガスの除去、大気汚染を促進する硫黄酸化物系ガスの除
去を効果的に行うことができる。
Therefore, it is possible to effectively remove chlorine-based gas that generates dioxins and sulfur oxide-based gas that promotes air pollution.

【0094】(2)被処理物の含有する有害物質を分解
析出させる分解反応工程において、被処理物と処理剤の
アルカリ金属化合物とを共に加熱しているので、分解析
出したガスと処理剤との接触反応は迅速に、且つ確実に
行われ、無害な塩類を生成して排ガス中には、有害成分
は存在しない。よって、ダイオキシンの生成は防止され
る。
(2) In the decomposition reaction step of decomposing and separating harmful substances contained in the object to be treated, the object to be treated and the alkali metal compound of the treating agent are both heated, so that the gas decomposed and deposited and The contact reaction with the agent is carried out quickly and reliably, and forms harmless salts, so that no harmful components are present in the exhaust gas. Therefore, generation of dioxin is prevented.

【0095】また、煙道の腐食もなく、高温の排ガス又
は高温にして、熱源、燃料として安全に使用できる。
Further, the flue gas is not corroded and can be safely used as a heat source and a fuel at a high temperature exhaust gas or at a high temperature.

【0096】分解ガスは無害なものであるから、再利用
のため燃料(タービン、ボイラなど)として利用でき
る。
Since the cracked gas is harmless, it can be used as fuel (turbine, boiler, etc.) for reuse.

【0097】(3)塩素系ガスを除去した被処理物を加
熱して減容化する減容化工程は、先の分解反応工程の加
熱処理炉とは別の加熱処理炉で行うので、減容化工程で
は残渣中には有害成分に起因して生成されるダイオキシ
ン類は存在しないので、ダイオキシン類が残渣(炭化
物,灰類)に吸着混入することはなく、残渣の無害化が
実現でき、残渣から金属,炭化物を取り出して再利用で
きる。
(3) The volume reduction step of heating the material from which the chlorine-based gas has been removed to reduce the volume is performed in a heat treatment furnace different from the heat treatment furnace in the decomposition reaction step. In the consolidation step, there is no dioxin generated due to harmful components in the residue, so that the dioxin does not adsorb and mix in the residue (carbide, ash), and the residue can be made harmless. Metals and carbides can be extracted from the residue and reused.

【0098】[0098]

【発明の効果】以上のように本発明は、加熱源としてL
NG燃焼ガスを使用し、更に、この熱ガスを円筒体の外
表面に受熱増加手段を設けて効率よく円筒体に受熱する
ようにしたので、被処理物を効果的に加熱でき、加熱時
間は短縮でき、処理効率が向上する。
As described above, according to the present invention, L is used as a heating source.
Since the NG combustion gas is used, and the heat gas is efficiently received by the cylindrical body by providing a heat receiving increasing means on the outer surface of the cylindrical body, the object to be processed can be effectively heated, and the heating time is reduced. It can be shortened and the processing efficiency is improved.

【0099】従って、被処理物の投入から排出までの全
処理作業時間の短縮ができ、総じて被処理物の処理量の
増加が図れる等の効果を奏する。
Accordingly, it is possible to shorten the entire processing time from the introduction to the discharge of the object to be discharged, and to increase the processing amount of the object as a whole.

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

【図1】本発明の第1の実施の形態の概念図。FIG. 1 is a conceptual diagram of a first embodiment of the present invention.

【図2】本発明の受熱増加手段の説明図。FIG. 2 is an explanatory view of a heat receiving increasing means of the present invention.

【図3】本発明の第2の実施の形態の廃棄物処理設備の
概念図。
FIG. 3 is a conceptual diagram of a waste treatment facility according to a second embodiment of the present invention.

【符号の説明】[Explanation of symbols]

h…加熱処理炉 1…円筒体 2…加熱筒 3…供給口 4…排出口 5…回転駆動手段 6…供給側ダクト 7…排出側ダクト 8…燃焼装置 Fh : Heat treatment furnace 1: Cylindrical body 2: Heating cylinder 3: Supply port 4: Discharge port 5: Rotary drive means 6: Supply duct 7: Discharge duct 8: Combustion device

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 一端側に被処理物を供給する供給口およ
び他端側にこれを排出する排出口を有し、略水平位置に
配置した回転自在な円筒体と、該円筒体の内部に設けら
れ被処理物を供給口側から排出口側に撹拌しながら移送
させる手段と、この円筒体を外部から加熱する加熱手段
とで加熱処理炉を構成し、前記加熱手段は、円筒体の外
周に加熱筒を設けて該加熱筒と円筒体の外周間に密閉空
間を形成し、この密閉空間内に燃焼装置で得た熱ガスを
導入して被処理物を加熱するとともに、円筒体の外表面
に熱ガスとの接触面積を増大させる受熱増加手段を形成
したことを特徴とする加熱処理装置。
1. A rotatable cylindrical body having a supply port for supplying an object to be processed on one end side and a discharge port for discharging the same on the other end side, and disposed at a substantially horizontal position. A heating treatment furnace is constituted by means for stirring and transferring the object to be treated from the supply port side to the discharge port side, and a heating means for externally heating the cylindrical body, wherein the heating means comprises an outer periphery of the cylindrical body. A heating cylinder is provided to form a sealed space between the heating cylinder and the outer periphery of the cylindrical body, and a heated gas obtained by a combustion device is introduced into the sealed space to heat the object to be processed, and the outside of the cylindrical body is heated. A heat treatment apparatus characterized in that a heat receiving increasing means for increasing a contact area with a hot gas is formed on a surface.
【請求項2】 受熱増加手段は、螺旋状突起、平板状突
起、波状板突起で形成したことを特徴とする請求項1記
載の熱ガスによる加熱処理装置。
2. The heat gas treatment apparatus according to claim 1, wherein the heat receiving increasing means is formed by a spiral projection, a flat projection, or a corrugated projection.
【請求項3】 受熱増加手段は、表面の周方向に所定間
隔をもって複数の凹状又は波状の溝で形成したことを特
徴とする請求項1記載の熱ガスによる加熱処理装置。
3. The heat gas treatment apparatus according to claim 1, wherein the heat reception increasing means is formed by a plurality of concave or wavy grooves at predetermined intervals in a circumferential direction of the surface.
【請求項4】 円筒体は鉄系材料からなることを特徴と
する請求項1ないし3のいずれか1項に記載の熱ガスに
よる加熱処理装置。
4. The heating apparatus according to claim 1, wherein the cylindrical body is made of an iron-based material.
【請求項5】 熱ガスはLNGを燃焼して発生させたガ
スを用いることを特徴とする請求項1記載の熱ガスによ
る加熱処理装置。
5. The heat gas processing apparatus according to claim 1, wherein a gas generated by burning LNG is used as the hot gas.
JP10069622A 1998-03-19 1998-03-19 Apparatus for heat treatment with hot gas Withdrawn JPH11263978A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10069622A JPH11263978A (en) 1998-03-19 1998-03-19 Apparatus for heat treatment with hot gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10069622A JPH11263978A (en) 1998-03-19 1998-03-19 Apparatus for heat treatment with hot gas

Publications (1)

Publication Number Publication Date
JPH11263978A true JPH11263978A (en) 1999-09-28

Family

ID=13408166

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10069622A Withdrawn JPH11263978A (en) 1998-03-19 1998-03-19 Apparatus for heat treatment with hot gas

Country Status (1)

Country Link
JP (1) JPH11263978A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4529230B2 (en) * 2000-02-24 2010-08-25 株式会社Ihi Rotary kiln
CN102199452A (en) * 2011-04-07 2011-09-28 刘靖强 Reaction equipment of biomass engine gas for vehicle

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4529230B2 (en) * 2000-02-24 2010-08-25 株式会社Ihi Rotary kiln
CN102199452A (en) * 2011-04-07 2011-09-28 刘靖强 Reaction equipment of biomass engine gas for vehicle

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