JP2000193229A - Incinerator - Google Patents

Incinerator

Info

Publication number
JP2000193229A
JP2000193229A JP10368605A JP36860598A JP2000193229A JP 2000193229 A JP2000193229 A JP 2000193229A JP 10368605 A JP10368605 A JP 10368605A JP 36860598 A JP36860598 A JP 36860598A JP 2000193229 A JP2000193229 A JP 2000193229A
Authority
JP
Japan
Prior art keywords
incinerator
waste
furnace body
gas flow
flow path
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.)
Granted
Application number
JP10368605A
Other languages
Japanese (ja)
Other versions
JP3993329B2 (en
Inventor
Yasuo Miyamoto
康男 宮本
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.)
Nippon Yuka Kogyo Co Ltd
Original Assignee
Nippon Yuka Kogyo 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 Nippon Yuka Kogyo Co Ltd filed Critical Nippon Yuka Kogyo Co Ltd
Priority to JP36860598A priority Critical patent/JP3993329B2/en
Publication of JP2000193229A publication Critical patent/JP2000193229A/en
Application granted granted Critical
Publication of JP3993329B2 publication Critical patent/JP3993329B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide an incinerator which can continuously and efficiently incinerate waste composed of a high polymer material without generating any hazardous substance by completely burning the waste through secondary combustion after the waste is melted into a gas with radiant heat. SOLUTION: A rotary incinerator 1, a secondary incinerator 2, a connecting section 3, and a residue post-incineration section 19 are heated by means of a primary burner 9, a secondary burner 18, and a post-incinerator burner 28. In this case, molten glass and an auxiliary, such as the calcium carbonate, quick lime, etc., are housed in advance in an ash melting vessel 29. In the rotary incinerator 1, such a temperature gradient that the temperature becomes higher as going toward the waste charging side from the waste discharging side is formed by utilizing the radiant heat from the secondary incinerator 2. Waste housed in a hopper 7 is fed to the rotary incinerator 1 by means of a segmenting screw 6 and melted and gasified by utilizing the radiant heat from the secondary incinerator 2. Then part of the gas moves toward the connecting section 3 while burning and the burned gas is mixed with an unburned gas. The mixed gas moves to the secondary incinerator 2 and is burned completely.

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、廃棄物を焼却処理
するための焼却炉に関するものであり、特に高分子物質
からなる廃棄物および/または高分子物質からなる構成
部材を包含する廃棄物を、ダイオキシンその他の有害物
質を発生することなく、連続して効率よく焼却処理する
ことができる焼却炉に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an incinerator for incinerating waste materials, and more particularly to a waste material containing a polymer material and / or a waste material containing a component member made of a polymer material. The present invention relates to an incinerator that can continuously and efficiently incinerate without generating dioxins and other harmful substances.

【0002】[0002]

【従来の技術】近年におけるプラスチック材料の改良お
よびプラスチック成形技術の向上により、産業用機器お
よび生活用機器を構成する部材にプラスチック材料から
なる部材を使用するものが急増しており、産業廃棄物お
よび生活廃棄物中にもプラスチック材料が多量に混入さ
れるようになってきている。上記のような廃棄物は、可
燃物として焼却炉により焼却処理されるのが通常であ
る。
2. Description of the Related Art In recent years, plastic materials and plastic molding techniques have been improved, and the use of plastic materials for industrial equipment and household equipment has been increasing rapidly. A large amount of plastic materials are also being mixed into household waste. The wastes as described above are usually incinerated as combustibles by an incinerator.

【0003】この場合、従来の焼却炉では、炉内の火格
子上に廃棄物を載置して、この廃棄物に着火し、炉外か
らの空気供給によって燃焼を継続させる直接燃焼方式が
最も一般的であり、家庭用の小型焼却炉としても多用さ
れてきた。
[0003] In this case, in the conventional incinerator, a direct combustion method in which waste is placed on a grate in the furnace, the waste is ignited, and combustion is continued by supplying air from outside the furnace is most used. It is common and has been widely used as small incinerators for home use.

【0004】また、上記のような廃棄物を空気から遮断
し、直接燃焼を避けた状態で高温加熱によって乾留し、
この乾留によって発生する可燃性のガスを燃焼させるガ
ス化燃焼方式も採用されている。
Further, the above-mentioned waste is shielded from the air, and is subjected to dry distillation by high-temperature heating while avoiding direct combustion,
A gasification combustion system that burns combustible gas generated by the carbonization is also employed.

【0005】[0005]

【発明が解決しようとする課題】まず前者の直接燃焼方
式においては、プラスチック材料から遊離カーボンを多
量に排出し、黒煙および刺戟臭を発生するため焼却炉近
傍の環境を汚染するという問題点がある。特に近年にお
いては、焼却に伴なってダイオキシンをはじめとして有
害物質を排出するため、家庭用等の小規模炉の使用が規
制されるに至っている。また上記の煤煙、有害物質の排
出を抑制するために、二次燃焼のための工夫が必要とな
り、補助燃料の併用、設備の大型化、複雑化を招来し、
初期投資コストのみならず、運転コストをも高騰させる
という問題点も併有する。
First, in the former direct combustion method, a large amount of free carbon is discharged from a plastic material, and black smoke and an irritating odor are generated, thereby polluting the environment near the incinerator. is there. Particularly in recent years, the use of small-scale furnaces for home use and the like has been regulated in order to discharge dioxins and other harmful substances with incineration. In addition, in order to suppress the emission of soot and harmful substances described above, it is necessary to devise measures for secondary combustion, which leads to the combined use of auxiliary fuel, large-sized equipment, and complicated equipment.
There is also a problem that not only initial investment costs but also operating costs rise.

【0006】一方、後者の乾留によるガス化燃焼方式に
おいては、遊離カーボンの発生は少ないものの、乾留の
ための加熱と、乾留後のガスの燃焼とを必要とする二段
階燃焼方式となるため、設備が複雑化し、コスト高とな
るという問題点がある。また、この方式はバッチ処理方
式のものであるため、連続処理が困難であり、処理能力
が低く、かつ発生ガスの制御がむずかしく、可燃性のガ
スが爆発する危険性が高い等の問題点もある。
On the other hand, in the latter gasification combustion system by dry distillation, although the generation of free carbon is small, it is a two-stage combustion system which requires heating for dry distillation and combustion of gas after dry distillation. There is a problem that equipment becomes complicated and cost increases. In addition, since this method is a batch processing method, there are also problems such as difficulty in continuous processing, low processing capacity, difficulty in controlling generated gas, and high risk of explosion of combustible gas. is there.

【0007】本発明は、上記従来技術に存在する問題点
を解決し、高分子物質からなる廃棄物および/または高
分子物質からなる構成部材を包含する廃棄物を、有害物
質を発生することなく、連続して効率よく焼却処理する
ことができる焼却炉を提供することを課題とする。
SUMMARY OF THE INVENTION The present invention solves the above-mentioned problems in the prior art, and eliminates waste containing polymer substances and / or waste containing constituent members made of polymer substances without generating harmful substances. It is an object of the present invention to provide an incinerator that can continuously and efficiently incinerate.

【0008】[0008]

【課題を解決するための手段】上記の課題を解決するた
めに、本発明においては、中空筒状に形成され、かつそ
の軸線の回りに回転可能に支持された炉体と、この炉体
の一方の開口部を閉塞するように設けられた装入側部材
と、この装入側部材を前記炉体の軸線に沿って貫通する
ように設けられ、かつ廃棄物を収容するホッパーと接続
された切出スクリュウとを備えてなる回転燃焼炉と、中
空筒状に形成され、かつその軸線に沿う方向にガス流路
が形成された炉体と、この炉体内に前記ガス流路を横断
し、かつその一部を遮断するように設けられた複数列の
障壁と、これらの障壁間に設けられ、かつ前記ガス流路
と直交する方向に空気を吹出す複数個の給気ノズルとを
備えてなる二次燃焼炉と、中空短筒状に形成され、かつ
前記回転燃焼炉の他方の開口部と二次燃焼炉のガス流路
の上流側とを各炉体の軸線方向に無隔壁状態で連結する
連結部と、によって構成する、という技術的手段を採用
した。
In order to solve the above-mentioned problems, according to the present invention, a furnace body formed in a hollow cylindrical shape and rotatably supported around its axis is provided. A charging-side member provided to close one opening, and a charging-side member was provided so as to penetrate the charging-side member along the axis of the furnace body, and was connected to a hopper for storing waste. A rotary combustion furnace comprising a cutting screw, a furnace body formed in a hollow cylindrical shape, and having a gas flow path formed in a direction along the axis thereof, and traversing the gas flow path in the furnace body; And a plurality of rows of barriers provided so as to block a part thereof, and a plurality of air supply nozzles provided between these barriers and blowing air in a direction orthogonal to the gas flow path. Secondary combustion furnace, and formed in a hollow short cylindrical shape, and the rotary combustion furnace A connecting portion which square the upstream side of the gas passage opening and the secondary combustion furnace is connected by noncompartmental state in the axial direction of the furnace body, constituted by, employing the technical means that.

【0009】本発明において、障壁を直立する複数個の
角柱によって形成することができる。
In the present invention, the barrier can be formed by a plurality of upright prisms.

【0010】また、上記の発明において、角柱をガス流
路に沿って千鳥状に配設することができる。
In the above invention, the prisms can be arranged in a staggered manner along the gas flow path.

【0011】更に、上記の発明において、角柱を高アル
ミナ質耐火物からなるれんがの積層によって形成するこ
とができる。
Further, in the above invention, the prism can be formed by stacking bricks made of high alumina refractory.

【0012】次に、上記の発明において、連結部の下方
に残渣後燃部を設け、この残渣後燃部の底部を段差を有
する上段部と下段部とによって形成すると共に、各段部
に各々灰出プッシャーを設け、前記下段部の端部近傍に
後燃バーナーと、溶剤を収容した灰溶融容器とを設け、
回転燃焼炉からの残渣を前記上段部および/または下段
部において燃焼させ、かつ燃焼後の灰を前記灰溶融容器
内で溶融させることができる。
Next, in the above invention, a residue afterburning portion is provided below the connecting portion, and a bottom portion of the residue afterburning portion is formed by an upper step portion and a lower step portion having a step, and each of the step portions has a lower portion. Provide an ash pusher, afterburner near the end of the lower portion, and an ash melting container containing a solvent,
Residue from a rotary combustion furnace can be burned in the upper part and / or the lower part, and the burned ash can be melted in the ash melting vessel.

【0013】[0013]

【発明の実施の形態】図1は本発明の実施の形態を示す
要部縦断面説明図である。図1において、1は回転燃焼
炉、2は二次燃焼炉であり、各々後述するように構成さ
れ、後述するように構成された連結部3により無隔壁状
態で一体にかつ気密に連結される。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is an explanatory longitudinal sectional view of a main part showing an embodiment of the present invention. In FIG. 1, reference numeral 1 denotes a rotary combustion furnace, and 2 denotes a secondary combustion furnace, each of which is configured as described below, and which are integrally and airtightly connected in a partition-free state by a connecting portion 3 configured as described below. .

【0014】まず回転燃焼炉1の構成について記述す
る。4は炉体であり、例えば中空円筒状に形成され、軸
線の回りに回転可能に支持されている。すなわち、炉体
1は両端に開口部を有する例えば鉄板からなる炉殻内面
に耐火材層が設けられ、例えばローラ上に支持され、適
宜の駆動手段(何れも図示省略)によって回転駆動され
得るように形成される。
First, the configuration of the rotary combustion furnace 1 will be described. Reference numeral 4 denotes a furnace body, which is formed, for example, in a hollow cylindrical shape and is rotatably supported around an axis. That is, the furnace body 1 is provided with a refractory material layer on the inner surface of a furnace shell made of, for example, an iron plate having openings at both ends, is supported on, for example, a roller, and can be rotationally driven by an appropriate driving means (all not shown). Formed.

【0015】なお炉体1は、例えば等径の中空円筒状に
形成して、その軸線が水平面に対して傾斜するように、
連結部3側が下位になるように支持するか、内周面を連
結部3側が大径となる円錐面に形成することにより、炉
体1の回転により、炉体1内に装入された廃棄物が、連
結部3側に移動し得るように構成する。炉体1の内面
は、その横断面を多角形状に形成してもよい。
The furnace body 1 is formed, for example, in the shape of a hollow cylinder having the same diameter, and its axis is inclined with respect to the horizontal plane.
By supporting the connecting portion 3 so as to be lower, or forming the inner peripheral surface as a conical surface having a large diameter on the connecting portion 3 side, the rotation of the furnace body 1 causes the waste charged in the furnace body 1 to be disposed. An object is configured to be able to move to the connecting portion 3 side. The inner surface of the furnace body 1 may have a polygonal cross section.

【0016】次に5は装入側部材であり、炉体1の一方
の開口部(図1においては左側)を閉塞するように設け
られる。6は切出スクリュウであり、装入側部材5を前
記炉体1の軸線に沿って貫通するように設けられると共
に、切出スクリュウ6は廃棄物を収容するホッパー7の
下端部と接続される。なお炉体1の両端部は、装入側部
材5および連結部3とシール部材8を介して相対回能可
能かつ気密可能に接続される。9は一次バーナーであ
り、装入側部材に設けられる。
Next, 5 is a charging side member, which is provided so as to close one opening (left side in FIG. 1) of the furnace body 1. Reference numeral 6 denotes a cut-out screw, which is provided so as to penetrate the charging member 5 along the axis of the furnace body 1, and the cut-out screw 6 is connected to a lower end of a hopper 7 for storing waste. . Both ends of the furnace body 1 are connected to the charging-side member 5 and the connecting portion 3 via a sealing member 8 so as to be relatively reversible and airtight. Reference numeral 9 denotes a primary burner, which is provided on the charging side member.

【0017】二次燃焼炉2の構成については後に詳細に
説明するが、二次燃焼炉2は、中空筒状に形成され、か
つその軸線に沿う方向にガス流路10が形成された炉体
11と、この炉体11内に前記ガス流路10を横断し、
かつガス流路10の一部を遮断するように設けられた複
数列の障壁12と、これら障壁12,12間に設けら
れ、かつ前記ガス流路10と直交する方向(図1におい
ては上下方向)に空気を吹出す複数個の給気ノズル13
とを備えて構成される。14は給気管であり、給気ノズ
ル13と接続される。15は給気管14に介装された調
節弁、16は二次送風機であり、給気本管17を介して
給気管14に二次空気を供給するためのものである。
The structure of the secondary combustion furnace 2 will be described later in detail, but the secondary combustion furnace 2 is formed in a hollow cylindrical shape and has a gas passage 10 formed in a direction along an axis thereof. 11 and traverse the gas flow path 10 in the furnace body 11,
And a plurality of rows of barriers 12 provided so as to block a part of the gas flow path 10, and a direction provided between the barriers 12 and 12 and perpendicular to the gas flow path 10 (the vertical direction in FIG. 1). ) A plurality of air supply nozzles 13 for blowing air
And is provided. An air supply pipe 14 is connected to the air supply nozzle 13. Reference numeral 15 denotes a control valve provided in the air supply pipe 14, and reference numeral 16 denotes a secondary blower, which supplies secondary air to the air supply pipe 14 through the air supply main pipe 17.

【0018】なお二次燃焼炉2のガス流路10の下流側
は、図示省略した例えばサイクロン、ガススクラバー等
から構成される廃ガス処理系と接続される。またこの廃
ガス処理系においては、廃ガス中に含有される飛灰、塵
埃その他の異物を分離除去するために、大量の洗浄用水
を使用するが、この洗浄用水は別途水処理系によって異
物からなる汚泥を分離除去されると共に、分離除去され
た汚泥もまた本発明の焼却炉によって焼却処理され得
る。
The downstream side of the gas passage 10 of the secondary combustion furnace 2 is connected to a waste gas treatment system which is not shown and includes, for example, a cyclone and a gas scrubber. In this waste gas treatment system, a large amount of cleaning water is used to separate and remove fly ash, dust, and other foreign substances contained in the waste gas. The separated sludge can be separated and removed, and the separated sludge can also be incinerated by the incinerator of the present invention.

【0019】次に18は二次バーナーであり、接続部3
の上部に例えば対向して2基設けられている。19は残
渣後燃部であり、連結部3の下方に連通して設けられ、
その底部を段差を有する上段部20と下段部21とによ
って形成する。これらの上段部20と下段部21とに
は、各々灰出プッシャー22,23を水平方向摺動可能
に設ける。24,25は各々油圧シリンダーであり、灰
出プッシャー22,23と接続されると共に、油圧ポン
プ26を備えた油圧ユニット27によって駆動される。
なお上記段部を3段以上の複数段に形成し、夫々対応す
る複数個の灰出プッシャーを設けてもよい。
Reference numeral 18 denotes a secondary burner.
For example, two units are provided to face each other. Reference numeral 19 denotes a residue afterburning portion, which is provided below the connecting portion 3 and communicates therewith.
The bottom is formed by an upper portion 20 and a lower portion 21 having a step. Ashing pushers 22 and 23 are provided on the upper section 20 and the lower section 21 slidably in the horizontal direction, respectively. Hydraulic cylinders 24 and 25 are connected to the ash extraction pushers 22 and 23 and driven by a hydraulic unit 27 having a hydraulic pump 26.
The step portion may be formed in three or more steps, and a plurality of ash extraction pushers may be provided corresponding to the steps.

【0020】28は後燃バーナー、29は灰溶融容器で
あり、各々前記残渣後燃部19の下段部21の端部近傍
に設けられる。30は水封コンベアであり、灰溶融容器
29の下方に接続筒31を介して設けられ、水中で生成
されたスラグを搬出可能に形成される。32は排出コン
ベア、33はコンテナである。
Reference numeral 28 denotes a post-burning burner, and 29 denotes an ash melting container, each of which is provided near an end of the lower portion 21 of the residue after-heating portion 19. Reference numeral 30 denotes a water-sealed conveyor, which is provided below the ash melting container 29 via a connection tube 31, and is formed so that slag generated in water can be carried out. 32 is a discharge conveyor, and 33 is a container.

【0021】図2および図3は各々前記図1における二
次燃焼炉2を示す要部断面拡大平面図および要部縦断面
拡大側面図、図4は図3におけるA−A線断面図であ
り、同一部分は前記図1と同一の参照符号で示す。図2
ないし図4において、炉体11は例えば中空角筒状に形
成されて、床面上に固定される。
FIGS. 2 and 3 are an enlarged plan view and an enlarged sectional side view, respectively, of a main part of the secondary combustion furnace 2 shown in FIG. 1, and FIG. 4 is a cross-sectional view taken along line AA in FIG. , The same parts are indicated by the same reference numerals as in FIG. FIG.
In FIG. 4 to FIG. 4, the furnace body 11 is formed, for example, in the shape of a hollow square tube and fixed on the floor.

【0022】障壁12は、例えば横断面形状が長方形の
直立する複数個の角柱によって形成すると共に、ガス流
路10に沿って千鳥状、またはチェッカー状の多列に配
置する。このような構成により、ガス流路10は障壁1
2によってその一部が遮断され、いわゆるジグザグ状と
なり、上流側から下流側に直線状となることが回避され
る。この障壁12は、例えばアルミナ(Al2 3 )の
含有量が55%以上の高アルミナ質耐火物からなるれん
がの積層によって形成することができる。34は炉体1
1の側面下部に設けられた灰出口である。
The barriers 12 are formed, for example, by a plurality of upright prisms having a rectangular cross section and arranged in a staggered or checkered multi-row along the gas flow path 10. With such a configuration, the gas flow path 10 is formed by the barrier 1
A part thereof is cut off by 2 to form a so-called zigzag shape, and a straight line from the upstream side to the downstream side is avoided. The barrier 12 can be formed, for example, by stacking bricks made of a high alumina refractory having an alumina (Al 2 O 3 ) content of 55% or more. 34 is the furnace body 1
1 is an ash outlet provided at the lower part of the side surface.

【0023】ガス流路10に沿う方向(図2および図3
における左右方向)の障壁12,12間には、複数個の
給気ノズル13を炉体11の上下に対向させて設ける
が、これらを炉体11の左右に対向させて設けてもよ
い。図2において、14a〜14eは、夫々第1給気ノ
ズル列ないし第5給気ノズル列であり、例えば第1給気
ノズル列14aは上方から下方に吹出すエアカーテンと
し、第2給気ノズル列14bと第3給気ノズル列14c
とは、上下両方から吹出して上下衝突流を形成するよう
に、第4給気ノズル列14dは上方からの下方併行流を
および第5給気ノズル列14eは下方からの上方併行流
を形成し、かつ第4給気ノズル列14dと第5給気ノズ
ル列14eとによって上下併行対流を形成するように、
夫々の調節弁15を調節する。
The direction along the gas flow path 10 (FIGS. 2 and 3)
A plurality of air supply nozzles 13 are provided between the barriers 12, 12 (in the left-right direction) so as to face the furnace body 11 up and down, but may be provided so as to face the furnace body 11 left and right. In FIG. 2, reference numerals 14a to 14e denote first to fifth air supply nozzle rows, respectively. For example, the first air supply nozzle row 14a is an air curtain that blows downward from above, and the second air supply nozzle row Row 14b and third air supply nozzle row 14c
Means that the fourth supply nozzle row 14d forms a downward parallel flow from above and the fifth supply nozzle row 14e forms an upward parallel flow from below so as to blow out from both upper and lower sides to form a vertical collision flow. And a vertical convection is formed by the fourth air supply nozzle array 14d and the fifth air supply nozzle array 14e,
Each control valve 15 is adjusted.

【0024】なお、上記障壁12の横断面の形状および
寸法、設置間隔、ならびに給気ノズル13の寸法、間
隔、更には第2給気ノズル列14bないし第5給気ノズ
ル列14e(または第n給気ノズル列14n)における
吹出態様については、廃棄物の物性および処理量によ
り、上記以外の種々の組合せが可能である。
Incidentally, the shape and size of the cross section of the barrier 12, the installation interval, the size and interval of the air supply nozzles 13, and the second to fifth air supply nozzle rows 14b to 14e (or the n-th air supply nozzle row 14e) Various combinations other than those described above are possible for the blowing mode in the air supply nozzle row 14n) depending on the physical properties and the amount of waste.

【0025】上記の構成により、次に作用について説明
する。まず図1において、一次バーナー9、二次バーナ
ー18および後燃バーナー28の作動により、回転燃焼
炉1、二次燃焼炉2、連結部3および残渣後燃部19を
加熱する。この場合、灰溶融容器29内には溶融ガラス
と、例えば炭酸カルシウム、消石灰等の助剤とを収容し
ておく。
Next, the operation of the above configuration will be described. First, in FIG. 1, the rotary burner 1, the secondary burner 2, the connecting portion 3, and the residual afterburning portion 19 are heated by the operation of the primary burner 9, the secondary burner 18, and the afterburning burner 28. In this case, the ash melting container 29 contains molten glass and auxiliary agents such as calcium carbonate and slaked lime.

【0026】図5は本発明の実施の形態における定常状
態の炉内の温度分布の例を示す要部縦断面図である。す
なわち、回転燃焼炉1においては、二次燃焼炉2からの
放射熱によって廃棄物の装入側(左側)から排出側(右
側)に向って高温域となる温度勾配を形成する。
FIG. 5 is a vertical sectional view of a main part showing an example of a temperature distribution in the furnace in a steady state in the embodiment of the present invention. That is, in the rotary combustion furnace 1, a radiant heat from the secondary combustion furnace 2 forms a temperature gradient that becomes a high temperature region from the waste charging side (left side) to the waste side (right side).

【0027】図1において、ホッパー7内に収容された
廃棄物は切出スクリュウ6によって回転燃焼炉1内に装
入され、二次燃焼炉2の放射熱により溶融、ガス化して
その一部が燃焼しつつ、連結部3に向って移動させら
れ、燃焼ガスおよび未燃ガスが混合した状態で二次燃焼
炉2に移動し、後述するように二次燃焼炉2内において
完全燃焼する。なお一次バーナー9および二次バーナー
18は、焼却炉の立上り時においてのみ作動し、前記図
5に示す定常状態が形成された後には作動を停止する。
In FIG. 1, waste stored in a hopper 7 is charged into a rotary combustion furnace 1 by a cutting screw 6, and is melted and gasified by the radiant heat of the secondary combustion furnace 2 and a part thereof. While burning, it is moved toward the connecting portion 3, moves to the secondary combustion furnace 2 in a state where the combustion gas and the unburned gas are mixed, and completely burns in the secondary combustion furnace 2 as described later. The primary burner 9 and the secondary burner 18 operate only when the incinerator starts up, and stop operating after the steady state shown in FIG. 5 is established.

【0028】上記のように、回転燃焼炉1内において
は、装入された廃棄物は、二次燃焼炉2の放射熱によっ
てガス化されるため、理論値に近い過剰空気率を得るこ
とができ、二次燃焼炉2における燃焼制御が容易である
と共に、応答性が高く、完全燃焼が可能となる。また廃
棄物は切出スクリュウ6によって連続的に装入されるた
め、細分化されながら、外気の炉内への吸込が制限さ
れ、部分的燃焼を含むガス化が平均化され得る。
As described above, in the rotary combustion furnace 1, the charged waste is gasified by the radiant heat of the secondary combustion furnace 2, so that an excess air rate close to the theoretical value can be obtained. As a result, the combustion control in the secondary combustion furnace 2 is easy, the responsiveness is high, and complete combustion is possible. In addition, since the waste is continuously charged by the cutting screw 6, while being fragmented, the suction of the outside air into the furnace is limited, and gasification including partial combustion can be averaged.

【0029】回転燃焼炉1における残渣は残渣後燃部1
9に逐次移動させられるが、その底部は段差を有する上
段部20と下段部21とによって形成されており、かつ
これらの段部20,21には灰出プッシャー22,23
が外気と遮断された状態で設けられているため、残渣は
上記段部20,21上で後燃バーナー28によって完全
に燃焼する。なお残渣は灰出プッシャー22,23の交
互の作動を含む制御された作動により、所定の割合で移
動させられ、灰溶融容器29内に落下して溶融する。溶
融状態の灰は灰溶融容器29から逐次溢出して、接続筒
31を経て水封コンベア30に至り、冷却固化後排出コ
ンベア32によりコンテナ33に排出される。
The residue in the rotary combustion furnace 1 is
9, the bottom of which is formed by an upper step 20 and a lower step 21 having a step, and these steps 20, 21 are provided with ash pushers 22, 23.
Is provided in a state where it is shut off from the outside air, so that the residue is completely burned by the afterburner 28 on the steps 20 and 21. The residue is moved at a predetermined rate by a controlled operation including the alternate operation of the ash extraction pushers 22 and 23, and falls into the ash melting container 29 to be melted. The ash in the molten state sequentially overflows from the ash melting container 29, reaches the water sealing conveyor 30 via the connecting tube 31, and is discharged to the container 33 by the discharging conveyor 32 after being cooled and solidified.

【0030】次に二次燃焼炉2における作用について説
明する。二次燃焼炉2のガス流路10の上流側には、図
2に示すように第1給気ノズル列14aにより、上方か
ら下方に吹出すエアカーテンが形成されているため、回
転燃焼炉1から連結部3を経由して移動するガス流中に
含まれる塵埃等の異物が分離させられる。
Next, the operation of the secondary combustion furnace 2 will be described. On the upstream side of the gas flow path 10 of the secondary combustion furnace 2, as shown in FIG. 2, an air curtain that blows from above to below is formed by the first air supply nozzle row 14 a. The foreign matter such as dust contained in the gas flow moving through the connecting portion 3 from the gas is separated.

【0031】二次燃焼炉2内には、複数個の障壁12が
ガス流路10を横断して複数列に亘って例えば千鳥状に
設けられているため、ガス流は直進することなく分断さ
れると共に、障壁12への衝突、迂回、回り込みが強制
され、高熱の障壁12表面との接触機会が増大し、炉内
における滞留時間、反応時間が長くなる。これに加えて
第2給気ノズル列14bないし第5給気ノズル列14e
による上下衝突流、上下方併行流、上下併行対流等によ
ってガスとの混合が急速かつ充分に行なわれ得る。
In the secondary combustion furnace 2, a plurality of barriers 12 are provided, for example, in a staggered manner across a plurality of rows across the gas flow path 10, so that the gas flow is divided without going straight. At the same time, the collision, detour, and wraparound of the barrier 12 are forced, the chance of contact with the high-heat barrier 12 surface is increased, and the residence time and reaction time in the furnace are prolonged. In addition, the second air supply nozzle array 14b to the fifth air supply nozzle array 14e
Mixing with the gas can be rapidly and sufficiently performed by the vertical collision flow, the vertical parallel flow, the vertical parallel convection, and the like.

【0032】このためガス中の未燃ガスの燃焼が供給さ
れた空気量に応じて段階的に進行するので、ダイオキシ
ン規制温度を維持し、かつ異状高温を回避し、持込N2
を抑制しながらNOx の発生が防止される。また反応時
間が長いため、夫々の燃焼域において低残存酸素率の燃
焼が行なわれる。更に高温の障壁12前面へのガス流の
衝突および障壁12後面への誘引渦流により、例えばア
ルミナ触媒の反応と相まって、ガス流中に含まれる微小
飛灰、煤塵等が障壁12の表面に付着するから、これら
の表面に多量に含有されるダイオキシンは完全に焼滅さ
れる。なお上記高温のガスの通過および未燃ガスの完全
燃焼により、障壁12が高温に加熱され、かつ蓄熱され
るから、障壁12からの放射熱が前記回転燃焼炉1内の
廃棄物のガス化に効率よく作用するのである。
Therefore, the combustion of the unburned gas in the gas proceeds stepwise according to the supplied air amount, so that the dioxin regulated temperature is maintained, abnormal high temperature is avoided, and N 2
And generation of NO x is prevented. Further, since the reaction time is long, combustion with a low residual oxygen rate is performed in each combustion zone. Further, due to the collision of the gas flow on the front surface of the high-temperature barrier 12 and the induced vortex on the rear surface of the barrier 12, for example, in combination with the reaction of the alumina catalyst, fine fly ash, dust and the like contained in the gas flow adhere to the surface of the barrier 12. Therefore, dioxins contained in a large amount on these surfaces are completely burned off. Since the high temperature gas passes and the unburned gas is completely burnt, the barrier 12 is heated to a high temperature and heat is stored. It works efficiently.

【0033】二次燃焼炉2から排出されたガスは、その
後前述のように廃ガス処理系において冷却、除塵されて
大気中に排出される。なお上記廃ガス処理系において使
用された洗浄用水中の異物、中和剤、高分子剤等は、所
定の水処理系によって汚泥ケーキとして分離除去される
が、この汚泥ケーキを再び図1に示すホッパー7に装入
し、前記廃棄物と共に焼却処理することができる。
The gas discharged from the secondary combustion furnace 2 is then cooled and dust-removed in the waste gas treatment system and discharged to the atmosphere as described above. Foreign substances, neutralizing agents, polymer agents and the like in the cleaning water used in the waste gas treatment system are separated and removed as a sludge cake by a predetermined water treatment system, and the sludge cake is shown in FIG. 1 again. It can be charged in the hopper 7 and incinerated together with the waste.

【0034】[0034]

【発明の効果】本発明は、以上記述のような構成および
作用であるから、下記の効果を奏し得る。 (1)廃棄物を放射熱によって溶融ガス化した後、二次
燃焼によって完全燃焼させるため、理論値に近い過剰空
気率が得られ、燃焼制御が容易であると共に応答性が高
い。 (2)残存酸素量が8%位で運転できるためCOの発生
が抑制され、かつ低温部が縮小され、ダイオキシン、N
x 等の有害物質の発生が極めて小である。 (3)蓄熱式触媒反応によって二次燃焼を行ない、放射
熱を利用するため、バーナーは立上り時に使用するのみ
で足り、高効率かつ低コストの焼却が可能である。 (4)廃棄物を連続的に、かつ外気の吸込を抑制した状
態で装入できるため、高効率かつ安定した焼却処理がで
きる。 (5)残渣灰を灰溶融容器内で溶融処理できるため、残
渣灰の処理が容易である。
Since the present invention has the above-described configuration and operation, the following effects can be obtained. (1) Since waste is melted and gasified by radiant heat and completely burned by secondary combustion, an excess air ratio close to a theoretical value is obtained, and combustion control is easy and responsiveness is high. (2) Since the operation can be performed with the residual oxygen amount of about 8%, the generation of CO is suppressed, the low-temperature part is reduced, and dioxin, N
Generation of harmful substances such as O x is extremely small. (3) Since secondary combustion is performed by a regenerative catalytic reaction and radiant heat is used, the burner only needs to be used at the time of start-up, and high-efficiency and low-cost incineration is possible. (4) Since waste can be charged continuously and in a state where the intake of outside air is suppressed, high efficiency and stable incineration can be performed. (5) Since the residual ash can be melted in the ash melting container, the processing of the residual ash is easy.

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

【図1】本発明の実施の形態を示す要部縦断面説明図で
ある。
FIG. 1 is an explanatory view of a main part longitudinal section showing an embodiment of the present invention.

【図2】図1における二次燃焼炉2を示す要部断面拡大
平面図である。
FIG. 2 is an enlarged sectional plan view of a main part showing a secondary combustion furnace 2 in FIG.

【図3】図1における二次燃焼炉2を示す要部縦断面拡
大側面図である。
FIG. 3 is an enlarged vertical cross-sectional side view of a main part showing the secondary combustion furnace 2 in FIG.

【図4】図3におけるA−A線断面図である。FIG. 4 is a sectional view taken along line AA in FIG.

【図5】本発明の実施の形態における定常状態の炉内の
温度分布の例を示す要部縦断面図である。
FIG. 5 is a vertical sectional view of a main part showing an example of a temperature distribution in a furnace in a steady state according to the embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 回転燃焼炉 2 二次燃焼炉 3 連結部 19 残渣後燃部 DESCRIPTION OF SYMBOLS 1 Rotary combustion furnace 2 Secondary combustion furnace 3 Connecting part 19 Residual afterburning part

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 3K061 AA07 AB03 AC01 AC19 CA01 FA03 FA10 FA13 FA21 FA23 FA24 KA02 KA15 KA21 KA23 3K078 BA03 BA13 BA22 BA24 BA26 CA02 CA04 CA09 CA12  ────────────────────────────────────────────────── ─── Continued on the front page F term (reference) 3K061 AA07 AB03 AC01 AC19 CA01 FA03 FA10 FA13 FA21 FA23 FA24 KA02 KA15 KA21 KA23 3K078 BA03 BA13 BA22 BA24 BA26 CA02 CA04 CA09 CA12

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 中空筒状に形成され、かつその軸線の回
りに回転可能に支持された炉体と、この炉体の一方の開
口部を閉塞するように設けられた装入側部材と、この装
入側部材を前記炉体の軸線に沿って貫通するように設け
られ、かつ廃棄物を収容するホッパーと接続された切出
スクリュウとを備えてなる回転燃焼炉と、 中空筒状に形成され、かつその軸線に沿う方向にガス流
路が形成された炉体と、この炉体内に前記ガス流路を横
断し、かつその一部を遮断するように設けられた複数列
の障壁と、これらの障壁間に設けられ、かつ前記ガス流
路と直交する方向に空気を吹出す複数個の給気ノズルと
を備えてなる二次燃焼炉と、 中空短筒状に形成され、かつ前記回転燃焼炉の他方の開
口部と二次燃焼炉のガス流路の上流側とを各炉体の軸線
方向に無隔壁状態で連結する連結部と、 によって構成したことを特徴とする焼却炉。
1. A furnace body formed in a hollow cylindrical shape and rotatably supported around its axis, a charging side member provided to close one opening of the furnace body, A rotary combustion furnace, which is provided so as to penetrate the charging side member along the axis of the furnace body, and includes a cut-out screw connected to a hopper for storing waste, and a hollow cylindrical shape. A furnace body in which a gas flow path is formed in a direction along the axis thereof, and a plurality of rows of barriers provided so as to cross the gas flow path in the furnace body and block a part thereof, A secondary combustion furnace provided between the barriers and comprising a plurality of air supply nozzles for blowing air in a direction orthogonal to the gas flow path; and a hollow short cylindrical shape, The other opening of the combustion furnace and the upstream side of the gas flow path of the secondary combustion furnace are aligned with the axis of each furnace body. Incinerator, characterized by being configured into a connecting portion for connecting with no partition wall state, by.
【請求項2】 障壁を直立する複数個の角柱によって形
成したことを特徴とする請求項1記載の焼却炉。
2. The incinerator according to claim 1, wherein the barrier is formed by a plurality of upright prisms.
【請求項3】 角柱をガス流路に沿って千鳥状に配設し
たことを特徴とする請求項2記載の焼却炉。
3. The incinerator according to claim 2, wherein the prisms are arranged in a staggered manner along the gas flow path.
【請求項4】 角柱を高アルミナ質耐火物からなるれん
がの積層によって形成したことを特徴とする請求項2ま
たは3記載の焼却炉。
4. The incinerator according to claim 2, wherein the prisms are formed by stacking bricks made of high alumina refractories.
【請求項5】 連結部の下方に残渣後燃部を設け、この
残渣後燃部の底部を段差を有する上段部と下段部とによ
って形成すると共に、各段部に各々灰出プッシャーを設
け、前記下段部の端部近傍に後燃バーナーと、溶剤を収
容した灰溶融容器とを設け、回転燃焼炉からの残渣を前
記上段部および/または下段部において燃焼させ、かつ
燃焼後の灰を前記灰溶融容器内で溶融させることを特徴
とする請求項1ないし4何れかに記載の焼却炉。
5. A residue afterburning portion is provided below the connecting portion, and a bottom portion of the residue afterburning portion is formed by an upper portion and a lower portion having a step, and ash extraction pushers are provided at each of the steps, A post-burning burner and an ash melting container containing a solvent are provided near the end of the lower section, and a residue from a rotary combustion furnace is burned in the upper section and / or the lower section, and the burnt ash is removed. The incinerator according to any one of claims 1 to 4, wherein the incinerator is melted in an ash melting vessel.
JP36860598A 1998-12-25 1998-12-25 Incinerator Expired - Fee Related JP3993329B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP36860598A JP3993329B2 (en) 1998-12-25 1998-12-25 Incinerator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP36860598A JP3993329B2 (en) 1998-12-25 1998-12-25 Incinerator

Publications (2)

Publication Number Publication Date
JP2000193229A true JP2000193229A (en) 2000-07-14
JP3993329B2 JP3993329B2 (en) 2007-10-17

Family

ID=18492266

Family Applications (1)

Application Number Title Priority Date Filing Date
JP36860598A Expired - Fee Related JP3993329B2 (en) 1998-12-25 1998-12-25 Incinerator

Country Status (1)

Country Link
JP (1) JP3993329B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111848261A (en) * 2020-08-20 2020-10-30 郎建华 Nitrified waste acid biomass absorption method and hydrolysis device
CN111848261B (en) * 2020-08-20 2024-04-26 郎建华 Nitrifying waste acid biomass absorption method and hydrolysis device

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111848261A (en) * 2020-08-20 2020-10-30 郎建华 Nitrified waste acid biomass absorption method and hydrolysis device
CN111848261B (en) * 2020-08-20 2024-04-26 郎建华 Nitrifying waste acid biomass absorption method and hydrolysis device

Also Published As

Publication number Publication date
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