JP2008049207A - Heat treatment apparatus of contaminant - Google Patents

Heat treatment apparatus of contaminant Download PDF

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JP2008049207A
JP2008049207A JP2006096856A JP2006096856A JP2008049207A JP 2008049207 A JP2008049207 A JP 2008049207A JP 2006096856 A JP2006096856 A JP 2006096856A JP 2006096856 A JP2006096856 A JP 2006096856A JP 2008049207 A JP2008049207 A JP 2008049207A
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heat treatment
exhaust gas
outer cylinder
cylinder
inner cylinder
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Masato Fujita
理人 藤田
Taiichi Okumura
泰一 奥村
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Mitsui Engineering and Shipbuilding Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a heat treatment apparatus of contaminants which is excellent in a decompositional function of organic chlorine compounds such as dioxin contained in contaminants and which prevents the condensation of moisture, tar and the like contained in circulation gas. <P>SOLUTION: The heat treatment apparatus of contaminants is provided with a double tubular rotor 10 comprised of an inner tube 11 and an outer tube 12, an introduction device 21 of the material to be treated having a primary air introduction part 20 at the front end part of the inner tube 11 and a spiral plate 22 for transferring the material to be treated in the inner wall surface of the inner tube, a material to be treated discharge hood 17 at the front end part of the outer tube 12 and an exhaust gas discharge hood 18 at the rear end part of the outer tube and further provided with a secondary air introduction part 24 and a material to be treated discharge part 25 at the material to be treated discharge hood 17, and an exhaust gas discharge part 26 at the exhaust gas discharge hood. Further, the double tubular rotor 10 is inclined forward so that the front end is lower than the rear end and a heating means 16 is installed at the outside of the double tubular rotor. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、ダイオキシン(DXNs)やPCBなどの有機塩素化合物に汚染された土壌やヘドロ(以下、底質という。)などの汚染物質を無害化する汚染物質の加熱処理装置に関する。   The present invention relates to a heat treatment apparatus for pollutants that detoxifies pollutants such as soil and sludge (hereinafter referred to as sediment) contaminated with organic chlorine compounds such as dioxins (DXNs) and PCBs.

従来、図4に示すように、2基の加熱装置51,52を上下2段に設置すると共に、上段加熱装置51の出口53と下段加熱装置52の入口54とを略垂直な連結ダクト55によって連結した加熱処理装置50を用いてダイオキシン(DXNs)やPCBなどの有機塩素化合物に汚染された汚染物質mを無害化する汚染物質の加熱処理方法が提案されている(例えば、特許文献1参照。)。   Conventionally, as shown in FIG. 4, two heating devices 51 and 52 are installed in two upper and lower stages, and an outlet 53 of the upper heating device 51 and an inlet 54 of the lower heating device 52 are connected by a substantially vertical connecting duct 55. There has been proposed a heat treatment method for pollutants that renders the pollutants m contaminated with organic chlorine compounds such as dioxins (DXNs) and PCBs harmless using the connected heat treatment apparatus 50 (see, for example, Patent Document 1). ).

この加熱処理方法では、上段加熱装置51で加熱した汚染物質mを連結ダクト55を経て下段加熱装置52に供給するようにしているが、連結ダクト55を通過する間に上段加熱装置51によって加熱された汚染物質mが大幅に温度低下(例えば、150〜200℃程度低下)することが分かった。この温度低下を補うには、下段加熱装置52の長さを長くしたり、或いは、下段加熱装置52に設けた電熱ヒーター(図示せず)の容量や灯油バーナ(図示せず)を増加することが必要であるが、その場合、下段加熱装置52が長大になる一方、電熱ヒーターの消費電力や灯油バーナの灯油の消費量が増加すると言う問題がある。   In this heat treatment method, the contaminant m heated by the upper heating device 51 is supplied to the lower heating device 52 through the connecting duct 55, but is heated by the upper heating device 51 while passing through the connecting duct 55. It has been found that the pollutant m significantly decreases in temperature (for example, about 150 to 200 ° C.). In order to compensate for this temperature decrease, the length of the lower heating device 52 is increased, or the capacity of an electric heater (not shown) provided in the lower heating device 52 or a kerosene burner (not shown) is increased. However, in this case, there is a problem that the power consumption of the electric heater and the amount of kerosene consumed by the kerosene burner increase while the lower heating device 52 becomes long.

他方、下段加熱装置52に供給した2次空気jは、連結ダクト55を経てその上部に設置した高温分離装置56に流入するため、連結ダクト55内を落下する汚染物質mに付随する粉塵を大量に噴き上げることになる。このため、高温分離装置56内に設けた高温バグフィルタやセラミックフィルタなどのフィルタが目詰まりする虞れがある。なお、符号iは、下段加熱装置51に供給した1次空気である。更に、上記のように、2基の加熱装置51,52を上下2段に設置すると、加熱処理装置50の高さが必然的に高くなり、加熱処理装置50のメンテナンスが高所作業になるなどの問題があった。   On the other hand, since the secondary air j supplied to the lower stage heating device 52 flows into the high-temperature separator 56 installed on the upper portion thereof via the connection duct 55, a large amount of dust accompanying the contaminant m falling in the connection duct 55 is produced. Will be blown up. For this reason, there is a possibility that a filter such as a high temperature bag filter or a ceramic filter provided in the high temperature separator 56 may be clogged. The symbol i is primary air supplied to the lower stage heating device 51. Further, as described above, when the two heating devices 51 and 52 are installed in two upper and lower stages, the height of the heat treatment device 50 is inevitably high, and the maintenance of the heat treatment device 50 becomes a work at a high place. There was a problem.

このような問題を解消するため、内筒と外筒よりなる2重筒形状の加熱処理装置を考案するに至ったが、図5に示すように、内筒61と外筒62とからなる2重筒形状の加熱処理装置60があることが分かった(例えば、特許文献2参照。)。   In order to solve such a problem, a double cylinder-shaped heat treatment apparatus composed of an inner cylinder and an outer cylinder has been devised, but as shown in FIG. It has been found that there is a heavy cylindrical heat treatment apparatus 60 (see, for example, Patent Document 2).

しかし、従来の加熱処理装置60は、導入口63から内筒61と外筒62との間隙を通って外筒62の奥に焼却灰nを移送するため、図6に示すように、小径管部64の外周面にスクリュー状の羽根65を設けると共に、内筒61の外周面に軸線に平行な複数の仕切羽根66や螺旋状の多数のガイド羽根67a,67bを設けているので、構造が複雑なものになっている。その上、内筒61と外筒62との回転が異なるように、それぞれ、独立した回転機構68,69を備えているので、回転機構などが複雑になる問題がある。従って、建設コストやメンテナンスコストが嵩むことになる。   However, since the conventional heat treatment apparatus 60 transfers the incineration ash n from the inlet 63 through the gap between the inner cylinder 61 and the outer cylinder 62 to the back of the outer cylinder 62, as shown in FIG. Since the screw-like blade 65 is provided on the outer peripheral surface of the portion 64 and the plurality of partition blades 66 and the spiral guide blades 67a and 67b parallel to the axis are provided on the outer peripheral surface of the inner cylinder 61, the structure is improved. It is complicated. In addition, since the independent rotation mechanisms 68 and 69 are provided so that the rotation of the inner cylinder 61 and the outer cylinder 62 is different, there is a problem that the rotation mechanism is complicated. Therefore, construction costs and maintenance costs increase.

また、従来の加熱処理装置60は、外筒62の奥側において、外筒62内の焼却灰nを重力に逆らって内筒61内にかき上げるため、内筒61内に仕切壁70を設けると共に、その側面に傾斜した多数のガイド板71,72を設けている。更に、上記小径管部64内に焼却灰払い出し用のスクリュー羽根73を設けているので、構造が非常に複雑なものになっている。   Further, in the conventional heat treatment apparatus 60, a partition wall 70 is provided in the inner cylinder 61 in order to scrape the incinerated ash n in the outer cylinder 62 into the inner cylinder 61 against the gravity on the back side of the outer cylinder 62. In addition, a large number of inclined guide plates 71 and 72 are provided on the side surfaces. Further, since the screw blades 73 for discharging the incineration ash are provided in the small diameter pipe portion 64, the structure is very complicated.

また、この加熱処理装置60は、流通ガスpを灰温度の低い外筒62の前端部から排出する構造になっているため、灰に比べて水分や可燃分を多く含む土壌や底質などの汚染物質を加熱処理する場合は、加熱処理により蒸発した水分や可燃分の燃焼によって生じたタール分が流通ガスに多量に含まれ、流通ガスp中の含まれる水分やタール分の凝縮によってホッパ74と外筒62とを連通する配管75の閉塞や、フィルター76の目詰まりが発生する虞れがある。更に、この加熱処理装置60は、流通ガスpの取入口が一つであるからダイオキシンやPCBなどの有機塩素化合物を分解に使用する酸素量が不足気味となり、有害な有機塩素化合物の分解機能が必ずしも充分とは言い難い。
特開2005−152882号公報 特開2003−126802号公報
In addition, since the heat treatment apparatus 60 has a structure in which the circulation gas p is discharged from the front end portion of the outer cylinder 62 having a low ash temperature, soil, sediment, etc. that contain more moisture and combustible components than ash. In the case where the pollutant is heat-treated, the circulation gas contains a large amount of moisture evaporated by the heat treatment and combustion of combustible matter, and the hopper 74 is condensed by condensation of moisture and tar content contained in the circulation gas p. There is a possibility that the pipe 75 communicating with the outer cylinder 62 may be blocked or the filter 76 may be clogged. Further, since the heat treatment apparatus 60 has one inlet for the circulating gas p, the amount of oxygen used for decomposing organic chlorine compounds such as dioxins and PCBs is insufficient, and has a function of decomposing harmful organic chlorine compounds. It's not always enough.
JP 2005-152882 A JP 2003-126802 A

本発明は、上記のような問題を改善するためになされたものであり、第1の目的は、汚染物質に含まれているダイオキシンやPCBなどの有機塩素化合物の分解機能に優れると共に、流通ガス中に含まれる水分やタール分などの凝縮防止を図ることができる汚染物質の加熱処理装置を提供することにある。更に、第2の目的は、従来の2重筒形状の加熱処理装置に比較して被処理物送り手段や回転機構などが簡単な汚染物質の加熱処理装置を提供することにある。   The present invention has been made in order to improve the above-mentioned problems, and a first object is to provide an excellent decomposition function of organic chlorine compounds such as dioxins and PCBs contained in pollutants, and a circulating gas. It is an object of the present invention to provide a heat treatment apparatus for pollutants that can prevent condensation of moisture and tar contained therein. Furthermore, the second object is to provide a contaminant heat treatment apparatus with a simple workpiece feed means, a rotation mechanism, and the like, as compared with a conventional double cylinder heat treatment apparatus.

係る目的を達成するため、請求項1に記載の発明に係る汚染物質の加熱処理装置は、ダイオキシンやPCB等の有機塩素化合物に汚染された土壌や底質などの汚染物質を無害化する汚染物質の加熱処理装置において、内筒と外筒により2重筒形回転体を形成し、前記内筒の前端部に1次空気導入部を有する被処理物導入装置を設けると共に、前記内筒の内壁面に被処理物移送用の螺旋板を設け、更に、前記外筒の前端部に被処理物排出フードを設けると共に、前記外筒の後端部に排ガス排出フードを設け、更に、前記被処理物排出フードに2次空気導入部と被処理物排出部とを設けると共に、前記排ガス排出フードに排ガス排出部を設け、かつ、前記2重筒形回転体を前端部が後端部よりも低くなるように前傾させると共に、前記2重筒形回転体の外側に加熱手段を設けたことを特徴とする。   In order to achieve such an object, the heat treatment apparatus for pollutants according to the invention described in claim 1 is a pollutant that renders pollutants such as soil and sediment contaminated with organic chlorine compounds such as dioxin and PCB harmless. In this heat treatment apparatus, a double cylinder-shaped rotating body is formed by an inner cylinder and an outer cylinder, a workpiece introduction apparatus having a primary air introduction portion is provided at the front end of the inner cylinder, and an inner portion of the inner cylinder is provided. A spiral plate for transferring an object to be processed is provided on the wall surface, an object discharge hood is provided at the front end of the outer cylinder, and an exhaust gas discharge hood is provided at the rear end of the outer cylinder. A secondary air introduction part and an object discharge part are provided in the waste discharge hood, a waste gas discharge part is provided in the exhaust gas discharge hood, and the front end of the double cylindrical rotating body is lower than the rear end. In addition to tilting forward, the double cylinder Characterized in that a heating means on the outside of the body.

請求項2に記載の発明は、請求項1記載の汚染物質の加熱処理装置において、前記内筒と前記外筒との間隙に接続リブを設けて前記内筒と前記外筒とを一体化したことを特徴とする。   According to a second aspect of the present invention, in the contaminant heat treatment apparatus according to the first aspect, a connection rib is provided in a gap between the inner cylinder and the outer cylinder to integrate the inner cylinder and the outer cylinder. It is characterized by that.

上記のように、請求項1に記載の発明は、汚染物質の加熱処理装置において、内筒の前端部に1次空気導入部を有する処理物導入装置を設けると共に、被処理物排出フードに2次空気導入部を設け、前記1次空気導入部から導入した新鮮な1次空気によって汚染物質に含有されている水分を蒸発し、可燃分を燃焼させた後、前記2次空気導入部から導入した新鮮な2次空気に含まれている豊富な酸素を使用して汚染土に含有されているダイオキシンやPCBなどの有害な有機塩素化合物を確実に分解することが可能になった。   As described above, according to the first aspect of the present invention, in the heat treatment apparatus for pollutants, the processed material introducing device having the primary air introducing portion is provided at the front end portion of the inner cylinder, and the processed material discharge hood has 2 A secondary air introduction part is provided, the moisture contained in the pollutant is evaporated by the fresh primary air introduced from the primary air introduction part, the combustible component is burned, and then introduced from the secondary air introduction part By using abundant oxygen contained in fresh secondary air, harmful organic chlorine compounds such as dioxin and PCB contained in contaminated soil can be reliably decomposed.

また、この発明は、排ガス温度の高い排ガス排出フードの部分、すなわち、被処理物である汚染物質の加熱処理過程の途中から排ガスを排出できる構造になっているため、水分やタール分の凝縮に起因する配管の閉塞を防止することができる。また、高温集塵器を採用することにより、フィルターの目詰まりを起すこと無く、徐じんを行うことができるようになった。   In addition, the present invention has a structure in which exhaust gas can be discharged from the part of the exhaust gas exhaust hood where the exhaust gas temperature is high, that is, in the middle of the heat treatment process of the pollutant that is the object to be treated. The resulting blockage of the piping can be prevented. Moreover, by adopting a high-temperature dust collector, it has become possible to carry out slow dusting without causing clogging of the filter.

また、内筒と外筒とが接続され、内筒と外筒とが一体となって回転するので、従来の2重筒形状の加熱処理装置に比べて構造及び回転機構が簡素化され、構造が極めてシンプルになった。また、仕切り板やガイド羽根なども、内筒の内壁面に設けた半径方向高さ20〜30%程度の螺旋板、或いは、外筒の内壁面に設けた半径方向高さ20〜30%程度の螺旋板や攪拌手段だけで良く、構造がシンプルになった。   In addition, since the inner cylinder and the outer cylinder are connected and the inner cylinder and the outer cylinder rotate together, the structure and the rotation mechanism are simplified and the structure is simplified as compared with the conventional double cylinder-shaped heat treatment apparatus. Became extremely simple. Further, the partition plate, the guide blades, and the like are also a spiral plate having a radial height of about 20 to 30% provided on the inner wall surface of the inner cylinder, or a radial height of about 20 to 30% provided on the inner wall surface of the outer cylinder. Only a spiral plate and stirring means are required, and the structure is simplified.

このため、建設コストを安価に押えることができる。また、不具合も起き難いと予想されるので、メンテナンスコストも軽減することが可能となった。また、この発明は、被処理物としての汚染物質が重力によって内筒から外筒に自然落下するので、従来の2重筒形状の加熱処理装置に比べて構造がシンプルとなった。   For this reason, construction costs can be kept low. In addition, since it is expected that problems will not occur, maintenance costs can be reduced. In addition, this invention has a simpler structure than a conventional double cylinder-shaped heat treatment apparatus because contaminants as an object to be processed naturally fall from the inner cylinder to the outer cylinder by gravity.

また、請求項2に記載の発明は、前記内筒と前記外筒との間隙に接続リブを設けて前記内筒と前記外筒とを一体化したので、従来の2重筒形状の加熱処理装置に比べて構造及び回転機構ともシンプル化することが可能となった。   In the invention according to claim 2, since the inner cylinder and the outer cylinder are integrated by providing a connection rib in the gap between the inner cylinder and the outer cylinder, the conventional double cylinder-shaped heat treatment is performed. Compared to the device, both the structure and the rotation mechanism can be simplified.

以下、本発明の実施の形態を図面を用いて説明する。   Hereinafter, embodiments of the present invention will be described with reference to the drawings.

図1は、本発明に係る汚染物質の加熱処理装置を含む汚染土処理施設の全体構成図であり、ダイオキシン(DXNs)やPCBなどの有機塩素化合物に汚染された土壌やヘドロ(以下、底質という。)などの汚染物質を無害化するようになっている。なお、この実施の形態では、汚染物質として底質を例に採る。   FIG. 1 is an overall configuration diagram of a contaminated soil treatment facility including a heat treatment apparatus for pollutants according to the present invention, and soil and sludge (hereinafter referred to as sediment) contaminated with organic chlorine compounds such as dioxins (DXNs) and PCBs. It is designed to detoxify pollutants. In this embodiment, sediment is taken as an example of the contaminant.

例えば、ダイオキシンで汚染された底質aは、乾燥手段1によって乾燥された後、その下方のホッパ2に一時的に蓄えられる。ホッパ2に貯蔵された乾燥底質bは、後述する加熱処理装置3によって加熱処理される。加熱処理装置3によって浄化又は無害化された底質cは、その下方に設置した冷却器4によって急冷される(例えば、450〜470℃→80〜100℃程度。)。   For example, the bottom sediment a contaminated with dioxin is temporarily stored in the hopper 2 below after being dried by the drying means 1. The dried sediment b stored in the hopper 2 is subjected to heat treatment by a heat treatment device 3 described later. The bottom sediment c purified or detoxified by the heat treatment apparatus 3 is rapidly cooled by the cooler 4 installed therebelow (for example, about 450 to 470 ° C. → 80 to 100 ° C.).

他方、加熱処理装置3より排出された排ガスdは、高温集塵器5に導入され、当該高温集塵器5内の高温バグフィルタ、セラミックフィルタなどのフィルタ6によって濾過される。フィルタ6によって除じんされた粉塵eは、前記ホッパ2に戻される。フィルタ6を通過した排ガスdは、排ガス加熱処理装置7によって加熱され、CO(一酸化炭素)、タール分、ダイオキシン(DXNs)が熱分解される。この排ガス加熱処理装置7には、燃料f及び燃焼用空気gが供給される。排ガス加熱処理装置7で処理された排ガスdは、更に、排ガス処理系活性炭素吸着法や湿式洗煙法などを適用した後処理装置8によって後処理した後、大気中に放出される。   On the other hand, the exhaust gas d discharged from the heat treatment apparatus 3 is introduced into the high temperature dust collector 5 and filtered by a filter 6 such as a high temperature bag filter or a ceramic filter in the high temperature dust collector 5. The dust e removed by the filter 6 is returned to the hopper 2. The exhaust gas d that has passed through the filter 6 is heated by the exhaust gas heat treatment device 7, and CO (carbon monoxide), tar content, and dioxins (DXNs) are thermally decomposed. The exhaust gas heat treatment device 7 is supplied with fuel f and combustion air g. The exhaust gas d processed by the exhaust gas heat treatment device 7 is further post-treated by a post-treatment device 8 to which an exhaust gas treatment activated carbon adsorption method, a wet smoke cleaning method, or the like is applied, and then released into the atmosphere.

上記加熱処理装置3は、図2に示すように、内筒11と外筒12からなる2重筒形回転体10を有している。この2重筒形回転体10は、前後二ヶ所の部分において、内筒11と外筒12との間に複数の支持体13を放射状に設けて両者を一体化している。その上、2重筒形回転体10は、前端部が後端部よりも、若干、低くなるように前傾している。また、外筒12の前後二ヶ所に円環状のタイヤ14を設けると共に、これらのタイヤ14を駆動ローラ15によって支持して2重筒形回転体10が所定の速度(例えば、1〜10rpm程度)で回転するようにしている。また、外筒12の外側に電熱ヒーター16を設けている。この電熱ヒーター16の加熱温度は、500〜550℃に設定されている。その上、この電熱ヒーター16は、500〜550℃の範囲内で10℃ずつ温度調整できるようになっている。   As shown in FIG. 2, the heat treatment apparatus 3 includes a double cylindrical rotating body 10 including an inner cylinder 11 and an outer cylinder 12. In the double cylindrical rotating body 10, a plurality of support bodies 13 are provided radially between the inner cylinder 11 and the outer cylinder 12 at two front and rear portions to integrate the two. In addition, the double cylindrical rotating body 10 is inclined forward so that the front end is slightly lower than the rear end. In addition, annular tires 14 are provided at two positions before and after the outer cylinder 12, and these tires 14 are supported by a driving roller 15 so that the double cylindrical rotating body 10 has a predetermined speed (for example, about 1 to 10 rpm). Rotate with. An electric heater 16 is provided outside the outer cylinder 12. The heating temperature of the electric heater 16 is set to 500 to 550 ° C. In addition, the temperature of the electric heater 16 can be adjusted by 10 ° C. within a range of 500 to 550 ° C.

更に、上記外筒12の前端部に被処理物排出フード17を設けると共に、外筒12の後端部に排ガス排出フード18を設けている。更に、前記内筒11の前端部に1次空気導入部20を有する被処理物導入装置21を設けると共に、内筒11の内壁面に被処理物移送用の螺旋板22を設けている。この被処理物導入装置21としては、スクリューフィーダー、シュート、プッシャーなどがある。また、螺旋板22の高さとしては、内筒11の半径の20〜30%程度が好ましい。20%未満の場合は、被処理物の移送が不足する。尚、所望により、外筒12には、ヒータ16から外れた内壁部分に螺旋板(図示せず)を設け、ヒータ部分には、リフターを設けても良い。   Further, a workpiece discharge hood 17 is provided at the front end of the outer cylinder 12, and an exhaust gas discharge hood 18 is provided at the rear end of the outer cylinder 12. Further, a workpiece introduction device 21 having a primary air introduction section 20 is provided at the front end of the inner cylinder 11, and a spiral plate 22 for transferring the workpiece is provided on the inner wall surface of the inner cylinder 11. Examples of the workpiece introduction device 21 include a screw feeder, a chute, and a pusher. Further, the height of the spiral plate 22 is preferably about 20 to 30% of the radius of the inner cylinder 11. If it is less than 20%, the transfer of the workpiece is insufficient. If desired, the outer cylinder 12 may be provided with a spiral plate (not shown) on the inner wall portion removed from the heater 16, and the heater portion may be provided with a lifter.

更に、被処理物排出フード17の上部に2次空気導入部24を設けると共に、被処理物排出フード17の下部に処理物排出部25を設けている。更に、排ガス排出フード18の上部に排ガス排出部26を設けている。また、所望により、外筒12の内壁面に攪拌手段として良い。更に、外筒12の外側に付着防止用のハンマリング装置を設けても良い。   Further, a secondary air introduction unit 24 is provided at the upper portion of the workpiece discharge hood 17, and a workpiece discharge portion 25 is provided at the lower portion of the workpiece discharge hood 17. Further, an exhaust gas discharge part 26 is provided on the upper part of the exhaust gas discharge hood 18. Further, if desired, the inner wall surface of the outer cylinder 12 may be used as a stirring means. Further, a hammering device for preventing adhesion may be provided outside the outer cylinder 12.

次に、上記加熱処理装置の作用について説明する。   Next, the effect | action of the said heat processing apparatus is demonstrated.

乾燥器1によって乾燥された底質bは、図2に示すように、被処理物導入装置21によって2重筒形回転体10の内筒11内に供給される。2重筒形回転体10の内筒11に供給された底質bは、2重筒形回転体10の回転に伴い、内筒11の内壁面に設けた螺旋板22によって排ガス排出フード18の方向に連続的に移送される。内筒11内を移動中の底質bは、外筒12の外側に設けた電熱ヒーター16によって加熱される。その際、上記被処理物導入装置21のケーシング23に設けた1次空気導入部20から内筒11内に新鮮な1次空気iが供給されるので、底質bに含まれている水分が蒸発し、可燃分が燃焼する。その間、1次空気hは、底質bと並行に流れる。内筒11内で発生した排ガスdは、排ガス排出フード18の上部に設けた排ガス排出部26を通って高温集塵器5に供給される。   The bottom sediment b dried by the dryer 1 is supplied into the inner cylinder 11 of the double cylindrical rotator 10 by the workpiece introduction apparatus 21 as shown in FIG. The bottom material b supplied to the inner cylinder 11 of the double cylindrical rotator 10 is generated by the spiral plate 22 provided on the inner wall surface of the inner cylinder 11 as the double cylindrical rotator 10 rotates. Continuously transferred in the direction. The bottom sediment b moving in the inner cylinder 11 is heated by an electric heater 16 provided outside the outer cylinder 12. At that time, fresh primary air i is supplied into the inner cylinder 11 from the primary air introduction section 20 provided in the casing 23 of the workpiece introduction apparatus 21, so that moisture contained in the bottom material b is present. Evaporates and combustibles burn. Meanwhile, the primary air h flows in parallel with the sediment b. The exhaust gas d generated in the inner cylinder 11 is supplied to the high-temperature dust collector 5 through the exhaust gas discharge part 26 provided in the upper part of the exhaust gas exhaust hood 18.

内筒11の出口に達した底質bは、内筒11から外筒12内に自然落下する。内筒11の出口温度は、300〜400℃程度になっている。外筒12内に落下した底質bは、2重筒形回転体10の前傾姿勢と2重筒形回転体10の回転により、排ガス排出フード18側から被処理物排出フード17側の方向に移送される。その際、外筒12内にリフター(図示せず)を設けることにより、底質bの攪拌を促進することができる。その間、外筒12内の底質bは、電熱ヒーター16によって所定の温度(例えば、450〜470℃程度)に加熱される。その際、被処理物排出フード17に設けた2次空気導入部24から新鮮な2次空気jが供給されるので、底質bに含まれているダイオキシン(DXNs)やPCBなどの有機塩素化合物が2次空気j中の酸素によって酸化分解され、無害な底質cとなる。この際、2次空気jは、被処理物排出フード17から排ガス排出フード18の方向に流動するため、2次空気jと底質b又はcは、対向流となる。この2次空気jは、排ガス排出フード18の排ガス排出部26より高温集塵器5に供給される。他方、無害化した底質cは、処理物排出部26から冷却器4に供給される。   The bottom sediment b that has reached the outlet of the inner cylinder 11 naturally falls from the inner cylinder 11 into the outer cylinder 12. The outlet temperature of the inner cylinder 11 is about 300 to 400 ° C. The bottom sediment b that has fallen into the outer cylinder 12 is moved in the direction from the exhaust gas exhaust hood 18 side to the workpiece exhaust hood 17 side by the forward inclined posture of the double cylindrical rotor 10 and the rotation of the double cylindrical rotor 10. It is transferred to. At that time, by providing a lifter (not shown) in the outer cylinder 12, stirring of the bottom material b can be promoted. Meanwhile, the sediment b in the outer cylinder 12 is heated to a predetermined temperature (for example, about 450 to 470 ° C.) by the electric heater 16. At that time, since fresh secondary air j is supplied from the secondary air introduction part 24 provided in the workpiece discharge hood 17, organochlorine compounds such as dioxins (DXNs) and PCB contained in the bottom sediment b Is oxidatively decomposed by oxygen in the secondary air j and becomes harmless bottom sediment c. At this time, since the secondary air j flows in the direction from the workpiece discharge hood 17 to the exhaust gas discharge hood 18, the secondary air j and the bottom material b or c are in a counterflow. The secondary air j is supplied to the high-temperature dust collector 5 from the exhaust gas discharge part 26 of the exhaust gas exhaust hood 18. On the other hand, the detoxified bottom sediment c is supplied to the cooler 4 from the processed product discharge section 26.

尚、図3の汚染物質の加熱処理装置は、排ガス排出フード18をダクト型に変更した点が図2の汚染物質の加熱処理装置と相違するだけであるから、同じ部品に同じ符号を付与して詳細な説明を省略する。また、加熱手段としては、電熱ヒータ以外に灯油バーナなどを適用することができる。   3 is different from the contaminant heat treatment apparatus of FIG. 2 only in that the exhaust gas exhaust hood 18 is changed to a duct type, the same reference numerals are given to the same parts. Detailed description is omitted. In addition to the electric heater, a kerosene burner or the like can be applied as the heating means.

本発明に係る汚染物質の加熱処理装置を含む加熱処理設備の全体構成図である。It is a whole block diagram of the heat processing equipment containing the heat processing apparatus of the contaminant which concerns on this invention. 本発明に係る汚染物質の加熱処理装置の断面図である。It is sectional drawing of the heat processing apparatus of the contaminant which concerns on this invention. 本発明に係る汚染物質の加熱処理装置の他の実施態様を示す断面図である。It is sectional drawing which shows the other embodiment of the heat processing apparatus of the contaminant which concerns on this invention. 従来の上下2段式の加熱処理装置の概略構成図である。It is a schematic block diagram of the conventional upper and lower two-stage type heat treatment apparatus. 従来の2重管式の加熱処理装置の概略構成図である。It is a schematic block diagram of the conventional double tube | pipe type heat processing apparatus. 従来の2重管式の加熱処理装置の要部断面図である。It is principal part sectional drawing of the conventional double pipe | tube type heat processing apparatus.

符号の説明Explanation of symbols

10 2重筒形回転体
11 内筒
12 外筒
16 加熱手段
17 被処理物排出フード
18 排ガス排出フード
20 1次空気導入部
21 被処理物導入装置
22 螺旋板
24 2次空気導入部
25 被処理物排出部
26 排ガス排出部
DESCRIPTION OF SYMBOLS 10 Double cylinder-shaped rotary body 11 Inner cylinder 12 Outer cylinder 16 Heating means 17 To-be-processed object discharge | emission hood 18 Exhaust gas discharge | emission hood 20 Primary air introduction part 21 To-be-processed object introduction apparatus 22 Spiral plate 24 Secondary air introduction part 25 To-be-processed Waste discharge part 26 Exhaust gas discharge part

Claims (2)

ダイオキシンやPCB等の有機塩素化合物に汚染された土壌や底質などの汚染物質を無害化する汚染物質の加熱処理装置において、内筒と外筒により2重筒形回転体を形成し、前記内筒の前端部に1次空気導入部を有する被処理物導入装置を設けると共に、前記内筒の内壁面に被処理物移送用の螺旋板を設け、更に、前記外筒の前端部に被処理物排出フードを設けると共に、前記外筒の後端部に排ガス排出フードを設け、更に、前記被処理物排出フードに2次空気導入部と被処理物排出部とを設けると共に、前記排ガス排出フードに排ガス排出部を設け、かつ、前記2重筒形回転体を前端部が後端部よりも低くなるように前傾させると共に、前記2重筒形回転体の外側に加熱手段を設けたことを特徴とする汚染物質の加熱処理装置。 In a pollutant heat treatment device that detoxifies pollutants such as soil and sediment contaminated with organic chlorine compounds such as dioxin and PCB, a double cylinder rotating body is formed by an inner cylinder and an outer cylinder, A processing object introduction device having a primary air introduction unit is provided at the front end of the cylinder, a spiral plate for transferring a processing object is provided on the inner wall surface of the inner cylinder, and further, a processing object is provided at the front end of the outer cylinder. In addition to providing an exhaust hood, an exhaust gas hood is provided at the rear end of the outer cylinder, and further, a secondary air introduction part and an object discharge part are provided in the object exhaust hood, and the exhaust gas exhaust hood Provided with an exhaust gas discharge part, and the double cylindrical rotator is tilted forward so that the front end is lower than the rear end, and a heating means is provided outside the double cylindrical rotator. Contaminant heat treatment device characterized by. 前記内筒と前記外筒との間隙に接続リブを設けて前記内筒と前記外筒とを一体化したことを特徴とする請求項1記載の汚染物質の加熱処理装置。
The contaminant heat treatment apparatus according to claim 1, wherein a connecting rib is provided in a gap between the inner cylinder and the outer cylinder to integrate the inner cylinder and the outer cylinder.
JP2006096856A 2006-03-31 2006-03-31 Heat treatment apparatus of contaminant Withdrawn JP2008049207A (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103978027A (en) * 2014-05-06 2014-08-13 南京大学 Spiral recursive discharge plasma soil purifying apparatus
CN107695090A (en) * 2017-11-07 2018-02-16 中科鼎实环境工程股份有限公司 Double-layer barrel type thermal desorption System and method for
CN108262354A (en) * 2018-04-09 2018-07-10 赵海平 A kind of engagement type dystopy soil remediation improvement is pulverized and mixed device with soil
CN111250523A (en) * 2020-01-15 2020-06-09 北京石油化工学院 Gas thermal desorption heating well with longitudinal soil heated uniformly
CN112893432A (en) * 2021-03-04 2021-06-04 东南大学 Vertical internal circulation soil thermal desorption device
CN113182342A (en) * 2021-05-19 2021-07-30 山西八建集团有限公司 Thermal desorption prosthetic devices who pollutes soil

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103978027A (en) * 2014-05-06 2014-08-13 南京大学 Spiral recursive discharge plasma soil purifying apparatus
CN107695090A (en) * 2017-11-07 2018-02-16 中科鼎实环境工程股份有限公司 Double-layer barrel type thermal desorption System and method for
CN108262354A (en) * 2018-04-09 2018-07-10 赵海平 A kind of engagement type dystopy soil remediation improvement is pulverized and mixed device with soil
CN111250523A (en) * 2020-01-15 2020-06-09 北京石油化工学院 Gas thermal desorption heating well with longitudinal soil heated uniformly
CN112893432A (en) * 2021-03-04 2021-06-04 东南大学 Vertical internal circulation soil thermal desorption device
CN113182342A (en) * 2021-05-19 2021-07-30 山西八建集团有限公司 Thermal desorption prosthetic devices who pollutes soil
CN113182342B (en) * 2021-05-19 2022-07-19 山西八建集团有限公司 Thermal desorption prosthetic devices who pollutes soil

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