JPH07280240A - Incinerating furnace - Google Patents

Incinerating furnace

Info

Publication number
JPH07280240A
JPH07280240A JP10892494A JP10892494A JPH07280240A JP H07280240 A JPH07280240 A JP H07280240A JP 10892494 A JP10892494 A JP 10892494A JP 10892494 A JP10892494 A JP 10892494A JP H07280240 A JPH07280240 A JP H07280240A
Authority
JP
Japan
Prior art keywords
furnace
ash
melting
sand
residue
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10892494A
Other languages
Japanese (ja)
Inventor
Kiyoshi Shimizu
清 清水
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.)
Taisei Kogyo KK
Original Assignee
Taisei Kogyo KK
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 Taisei Kogyo KK filed Critical Taisei Kogyo KK
Priority to JP10892494A priority Critical patent/JPH07280240A/en
Publication of JPH07280240A publication Critical patent/JPH07280240A/en
Pending legal-status Critical Current

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  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Apparatus For Disinfection Or Sterilisation (AREA)

Abstract

PURPOSE:To fully automatically incinerate infective medical waste and to recycle to use ash, residual metals by forming a fluidized bed for a matter to be incinerated, a melting unit, a pulverizer of melt, harmful gas removing unit by corona discharge, etc., as an integral unit. CONSTITUTION:A part corresponding to furnace afterburning is formed as a fluidized bed with high-temperature sand, and unburnt matter, incinerated liquefied polymer, liquids, etc., from an upper fire grate are completely incinerated. Ash, residue exhaust pusher exhausts light ash, bottle, generated clinker, etc., to a conveyor out of the furnace. Melt is supplied to a melting furnace body 14 by horizontally moving an upper cover 34 of the furnace, opening an upper part of the furnace, and charging preheated residue. Ash, residue 30 are heated in a melting vessel 29, discharged from a melt overflow outlet 32, quenched and pulverized by injection from a quenching nozzle 33 on the way, and collected to a sludge storage box. Exhaust gas passing a flue is passed through a corona discharge zone, and generated charged particles are directed toward a reaction chamber.

Description

【発明の詳細な説明】Detailed Description of the Invention

【産業上の利用分野】本発明は病院から出る感染性医療
廃棄物と一般ゴミの同時焼却システムに関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a system for simultaneous incineration of infectious medical waste and general waste discharged from hospitals.

【従来の技術】[Prior art]

【0003】請求1.2.4について従来の専用感染性
医療廃棄物専用炉は、炉内温度が800〜900℃で燃
焼するので包帯、塩ビチューブ類の焼却は十分されるが
注射針、金属類及びビン類はそのまま灰と共に残る。
又、小型炉は全て水平固定火格子上での燃焼である為、
焼却物が動かされる事が無いので燃焼条件が悪い時は助
燃バーナーを使っても火が十分にまわりきれない。焼却
したとは言え注射針、ビン類の中に感染性ウイルス類が
残ったままの状況も生じる。この場合減菌となっただけ
で滅菌とはならない。この灰及び残渣をスコップなどを
使い人力で炉下部から灰出し作業一般廃棄物として処理
している。感染性医療廃棄物処理としては、不完全その
ものと言える。厨芥などの一般ごみと医療廃棄物とは発
生する塩化水素、手術後臓器の油脂、血液等の液体類対
策など焼却物の物性が大巾に異なる故、根本的に炉の構
造が異なり同時に燃焼出来ないのが現状である。又、医
療廃棄物専用炉を使う時でさえ炉内に投入する場合、作
業者が焼却物の中身をそのつど確かめた後、炉内に分散
させながら焼却している。装置の劣っている分だけ専任
作業者に対し余分の作業時間と燃焼の技術を必要とせざ
るを得ない。請求項3について従来の鋳鋼、ステンレス
等の耐熱金属を使った火格子でも、上下から同時に助燃
バーナーで熱せられると軟化劣化してしまい、長期の使
用に耐えられない。同じ条件で不定形耐火物製の物は高
温に耐えられるがバーナー炎直射の急激な温度上昇によ
る熱衝撃には弱く、折れて落下する事故が発生しやすく
信頼性に劣るのが現状である。請求項4について従来の
もののこの部分は灰溜まりであり未燃のものは、未燃の
まま炉外に排出されるだけであった。
Claim 1.2.4 Since the conventional furnace for exclusive use of infectious medical waste burns at an internal temperature of 800 to 900 ° C., it is sufficient to incinerate bandages and PVC tubes, but injection needles and metals. And bottles remain with the ash.
Also, since all small furnaces burn on a fixed horizontal grate,
Since the incinerated material is not moved, even if the combustion condition is bad, the fire will not be able to fully go around even if the auxiliary burner is used. Although incinerated, infectious viruses may remain in the injection needles and bottles. In this case, the bacteria are sterilized but not sterilized. The ash and the residue are ashed from the lower part of the furnace manually using a scoop and treated as general waste. It can be said that the treatment of infectious medical waste is incomplete. General garbage such as kitchen waste and medical waste generate hydrogen chloride, oil and fat of organs after surgery, measures against liquids such as blood, etc. The physical properties of the incinerator are largely different, so the structure of the furnace is fundamentally different and it burns at the same time. The current situation is that it cannot be done. In addition, even when using a medical waste dedicated furnace, when the operator incinerates the contents of the incinerator in each case, he incinerates it while dispersing it in the furnace. Due to the inferiority of the equipment, it is inevitable that a dedicated worker requires extra working time and combustion technology. Claim 3 Even a conventional grate made of heat-resistant metal such as cast steel or stainless steel cannot be used for a long period of time because it is softened and deteriorated when heated by an auxiliary combustion burner from above and below at the same time. Under the same conditions, amorphous refractory materials can withstand high temperatures, but are vulnerable to thermal shock due to the rapid rise in the temperature of burner flames, and are liable to break and fall, resulting in poor reliability. Regarding Claim 4, this portion of the conventional one is an ash pool, and unburned ones are only discharged outside the furnace as unburned ones.

【0004】請求項5について従来の排出プッシャーは
力の方向が一方向に押すだけのもので、灰、残渣が相互
に食い込んだ時及びブリッヂが出来た排出機能を満足出
来るものではなかった。請求項6について、灰溶融炉の
数トンの大型のものは炭素電極棒、プラズマ発生等の電
力を使ったものや、灰を金属と分別した後、LPG、重
油をエネルギーとするものがある。電力を使った場合、
消費電力が大きく残渣20kg/バッチ能力と小型のも
のでも20kWの電力を新たに用意する必要が有るし、
又、灰ビン、金属の分別は本件の様な小型の場合処理量
が少ないのに比べ設備が不必要に大きいものになる欠点
が有る。請求項7について再燃室及びサイクロンを従来
の小型炉に内蔵させた場合再燃室とサイクロンは排ガス
の流れが上下逆となる為、納まりがつかず再燃室の次に
サイクロンが来る好ましい型に設置する事が出来なかっ
た。この為再燃室を内蔵した時は2ケ所の再燃室とな
り、サイクロンの場合もダブルサイクロンとなってい
た。請求項8、9、10、11、について塩化水素、S
Ox、NOx、微粒ダスト除去には、水を使い洗煙する
湿式、排ガス中に水酸化カルシウムを吹き込み反応させ
る乾式塩化水素除去方法、脱硫、脱硝、電気集塵器らが
有るが、火格子面積2m未満の小型炉には法的規制も
無い為、有害と理解されていても、炉本体の数倍のコス
トがかかる事で設置されないのが普通とされてきた。小
型炉に固形化させた水酸化カルシウムを煙道内に置き、
自然通風反応させる方法は有るが効率が悪く、又、反応
が進行するに従い圧損が増える等で燃焼物中に塩素分が
が5%以上の比率になると処理不能となる。又、取替え
は人手による高所作業を必要とし、高温度状態に有る為
の稼動中は取替え出来ず、休止後半日程度の冷却時間が
必要とするなど問題が有る。
According to claim 5, the conventional discharge pusher pushes the force in one direction only, and cannot satisfy the discharge function when ash and residue bite into each other and when the bridge is formed. With respect to claim 6, the ash melting furnace having a large capacity of several tons includes one using electric power such as a carbon electrode rod and plasma generation, and one using LPG and heavy oil as energy after separating ash from metal. When using electricity,
Power consumption is large, 20 kg residue / batch capacity, and even small ones, it is necessary to newly prepare 20 kW of power.
In addition, the separation of ash bottles and metals has the disadvantage that the equipment is unnecessarily large compared to the small processing amount in the case of a small size as in the present case. Regarding claim 7, when the reburn chamber and the cyclone are built in a conventional small-scale furnace, the exhaust gas flows upside down in the reburn chamber and the cyclone. Therefore, the reburn chamber does not fit and the cyclone is installed next to the preferred type. I couldn't do it. Therefore, when the reburn chamber was built in, there were two reburn chambers, and even in the case of a cyclone, it was a double cyclone. Hydrogen chloride and S for claims 8, 9, 10, and 11.
To remove Ox, NOx, and fine dust, there are wet type that uses water to wash smoke, dry hydrogen chloride removal method that blows calcium hydroxide into exhaust gas for reaction, desulfurization, denitration, and electrostatic precipitator. Since there is no legal regulation for small furnaces with a size of less than 2 m 2, even if it is understood to be harmful, it has been generally considered that it will not be installed because it costs several times as much as the furnace itself. Place calcium hydroxide solidified in a small furnace in the flue,
Although there is a method of causing a natural ventilation reaction, it is not efficient, and if the chlorine content in the combustion product is 5% or more due to an increase in pressure loss as the reaction proceeds, the treatment becomes impossible. Further, replacement requires manual work at a high place, cannot be replaced during operation due to high temperature, and requires cooling time for the second half of rest.

【0005】[0005]

【発明が解決しようとする問題点】感染性医療廃棄物は
従来注射針、手術後臓器等各種類別に分けてそれぞれの
専門業者に処理させていた。これを病院敷地内で一般ご
みも含め無人で安全に処理出来る溶融装置を組込んだ焼
却設備を使う事により焼却後の灰、ガラスビン、金属類
等、残渣を完全滅菌した後再資源として利用しようとす
るものである。請求項2でダンボール箱に入れ投入コン
ベヤ上に並べた燃焼物を逐次自動的に供給するには、炉
内状況の把握が必要である。一般ごみのみ、又は同一把
握出来る焼却物だけであるならば、炉内温度下降をもっ
て燃焼完了と判断できる。しかし、本設備の運転条件に
ダイオキシンの発生を抑制させる為、炉内温度を助燃バ
ーナーと連動させ常時800℃以下にならない様に温度
抑制させている理由でこの手段は使えない問題が有る。
温度によらない確実な炉内状況の把握が必要となる。請
求項3は火格子からの助燃バーナーと下からの火床助燃
バーナーで過熱させる為、普通の焼却炉の様に下からの
燃焼空気により冷却される事なく高温となり、ステンレ
ス系耐熱鋼でも耐久性に難点が生じる。又、不定形耐火
材料をつかってもバーナー直熱による熱衝撃により亀裂
が生じ、中心部まで進みついに折れる問題が生じる。こ
こには耐熱性と強靭性を兼備えた火格子が必要とされ
る。請求項4で従来の炉の灰溜まりであるこのカ所に未
燃の液体や流動化した高分子樹脂類、臓器油脂類が前接
上部火格子から垂れてくる。隙間を通り抜けた物は未燃
のまま灰と共に底に溜まり炉外に排出されてしまい、感
染性医療廃棄物の完全滅菌出来ない問題が生じる。又こ
の未燃残渣量が増えたのちに助燃バーナーで加熱しても
残渣表面のみの加熱にしかならず、特に残渣層が厚くな
った後の底に溜まった液体類の焼却は困難となる問題が
生じる。請求項5についてプッシャーと灰出口間に金
属、ガラス類が相互にからみ合った場合、一方向からの
静的力では食い込むだけで動きが取れなくなる問題が生
じる。
[Problems to be Solved by the Invention] Conventionally, infectious medical wastes have been treated by respective specialists by dividing them into various types such as injection needles and post-operative organs. Let's use this as a resource after completely sterilizing the residue such as ash, glass bottles, metals, etc. after incineration by using an incinerator that incorporates a melting device that can safely and unmannedly handle general waste in the hospital premises. It is what In order to sequentially and automatically supply the combustion products placed in the cardboard box and arranged on the charging conveyor in claim 2, it is necessary to grasp the situation inside the furnace. If only general waste, or only incinerated materials that can be identified as the same, is burned, it can be determined that the temperature inside the furnace has decreased. However, in order to suppress the generation of dioxin in the operating conditions of this equipment, there is a problem that this means cannot be used because the temperature inside the furnace is controlled so that it does not always fall below 800 ° C. by interlocking with the auxiliary combustion burner.
It is necessary to grasp the situation inside the furnace reliably regardless of temperature. According to claim 3, since it is overheated by the auxiliary burner from the grate and the auxiliary burner from the bottom of the bed, the temperature becomes high without being cooled by the combustion air from below like a normal incinerator, and it is durable even with stainless steel heat-resistant steel. There are difficulties in sex. Further, even if an amorphous refractory material is used, a crack may occur due to thermal shock due to direct heat of the burner, and the crack may progress to the central portion and finally break. A grate with both heat resistance and toughness is required here. In Claim 4, unburned liquid, fluidized polymer resins, and organ fats and oils hang down from the front upper grate at this location, which is the ash pool of the conventional furnace. The matter that has passed through the gap remains unburned together with the ash at the bottom and is discharged to the outside of the furnace, causing a problem that the infectious medical waste cannot be completely sterilized. Further, even if the amount of unburned residue is increased and then heated by the auxiliary burner, only the surface of the residue is heated, and it is particularly difficult to incinerate the liquids accumulated at the bottom after the residue layer is thickened. . According to claim 5, when metal and glass are intertwined with each other between the pusher and the ash outlet, there is a problem in that the static force from one direction only bites into the metal and the glass cannot be moved.

【0006】請求項6の残渣溶融炉で最後に残る金属類
をA重油、又はLPG燃料を使い溶融するには、約15
50℃まで溶融物温度を上げる必要が有る。しかし、こ
れまでの高温に耐えられる耐火物は熱衝撃に弱く、温度
コントロールプログラムにより徐々に温度上昇を計らな
ければならない。最短でも10〜20時間バーナーを焚
き続ける事になり燃料コストが非常にかかる問題があ
る。又、ルツボの様な間接加熱では中の溶融物温度を1
200℃までにしか上昇させられない。本件の場合直接
火炎をぶっつけると灰などの軽量残渣が飛び散ってしま
う問題が生じる。又、灰、ビン、金属類を混ぜたまま溶
融した場合、灰が1200℃で最初に融けるが、このま
ま温度を上げて行き金属と共に溶融させると混合溶融物
の粘性が極端に増大し、出口からの流失が困難となる問
題が生じる。灰残渣を溶融炉に自動投入させるには炉の
空、満杯検知が必要である。空の状態は炉内温度が最後
の炭素鋼が溶け出す1550℃になった事により知れ
る。しかし、満杯感知は残渣見掛け比重がそのつど灰の
多い場合、金属が多い場合等の例の様にその都度異なり
同時に高温雰囲気もあって検知出来ない問題が生じる。
請求項7で小型焼却炉に再燃室とサイクロンを同時に組
み込むのは理想的であるが、排ガスの流れる出口と入口
が水平に接続出来ない問題が有る。又、再燃室、サイク
ロンそれぞれ底に沈降したダストを衛生面からその都度
人手によりかき出す必要ない機能が求められる。
In order to melt the last-remaining metals in the residue melting furnace of claim 6 using heavy fuel oil A or LPG fuel, about 15
It is necessary to raise the melt temperature to 50 ° C. However, conventional refractories that can withstand high temperatures are vulnerable to thermal shock, and a temperature control program must gradually increase the temperature. Since the burner will continue to be burned for 10 to 20 hours at the shortest, the fuel cost will be very high. In addition, in the case of indirect heating such as in a crucible, the temperature of the melt inside is set to 1
It can only be raised to 200 ° C. In this case, if the flame is directly hit, a problem arises in which lightweight residue such as ash is scattered. Also, if ash, bottle, and metal are melted while being mixed, the ash first melts at 1200 ° C, but if the temperature is raised as it is and melted together with the metal, the viscosity of the mixed melt increases extremely, and There is a problem that it becomes difficult to wash away the water. In order to automatically put the ash residue into the melting furnace, it is necessary to detect whether the furnace is empty or full. The empty state is known because the temperature inside the furnace reached 1550 ° C at which the last carbon steel melted out. However, the full detection has a problem in that the apparent specific gravity of the residue is different in each case, such as when there is a lot of ash and when there is a lot of metal, and at the same time, there is a high temperature atmosphere and the detection is impossible.
In claim 7, it is ideal to incorporate the reburn chamber and the cyclone into the small incinerator at the same time, but there is a problem that the outlet and the inlet through which the exhaust gas flows cannot be connected horizontally. In addition, it is required that the dust settled on the bottom of each of the reburn chamber and the cyclone is not required to be manually scraped from the sanitary side each time.

【0007】[0007]

【課題点を解決する為の手段】請求項2で炉内焼却物は
投入された当初傾斜固定ロストル等の上に留まっている
が、焼却物送りプッシャーの作動と燃焼が進行するに従
い下部に落とされていく。プッシャーの送り速度は火格
子燃焼率及び炉負荷率と炉の基本性能から決定されてい
るが燃焼速度は押込空気温度、含有水分、燃焼物発熱量
等でその時々により異なる。故に、コンベア上の次の焼
却物を目視によらず自動で投入するには炉内の燃焼進捗
状態センサーにより、投入可能な空の確認信号を受けた
後、炉扉を開きコンベアを満杯感知信号を受けるまで1
バッチ分動かす事が必要である。図1、7にもとづいて
説明すると6傾斜固定ロストルの両側にマイクロ波の発
信、5受信装置1セットを満空センサーとして設置する
事で炉内の焼却物の減少状況を感知可能となり、自動投
入と炉内燃焼進行自動制御が実現した。請求項3で図2
により説明すると、上から落ちて来る焼却物による衝撃
に対ては、十分耐えられる断面形状を考慮すると同時に
耐荷重条件の厳しくなる中間部で、隣と連結部を持たせ
る事でさらに機械的強度の向上を計る。熱衝撃に対応し
て不定型耐火物は低熱膨張特性を持ったものに、直径が
0.2m/mφのステンレスワイヤーを混入させて表面
の細かい亀裂の発生を防ぐ。又、火格子の内部長手及び
これと直角方向に複数のステンレスの補強材を入れる事
で、火格子折事故の場合でも、これらの補強材により欠
落を防止する事で後接の排出プッシャー、溶融装置等へ
の破片混入によるトラブルの発生が無くなる事で無人自
動運転が可能となった。
According to a second aspect of the present invention, the incinerator in the furnace stays on the initially fixed slanted rostrut or the like, but it drops to the lower portion as the operation and combustion of the incinerator feed pusher progress. Will be done. The pusher feed rate is determined from the grate burning rate, the furnace load rate, and the basic performance of the furnace, but the burning rate varies depending on the intruding air temperature, the water content, the calorific value of the combustion products, etc. Therefore, in order to automatically load the next incinerated material on the conveyor without visual inspection, the combustion progress status sensor in the furnace receives a confirmation signal that the furnace is ready to be charged, then opens the furnace door and detects the conveyor full condition. 1 to receive
It is necessary to move by batch. Explaining with reference to Figs. 1 and 7, by installing 1 set of microwave transmitting and 5 receiving devices as full-space sensors on both sides of a 6-tilt fixed rostrur, it becomes possible to detect the state of reduction of incinerator in the furnace and automatically insert it. And automatic control of combustion progress in the furnace was realized. FIG. 2 in claim 3
In terms of the impact from incineration falling from above, considering the cross-sectional shape that can withstand enough, at the same time, the middle part where the load bearing condition becomes strict, the adjoining and connecting parts have more mechanical strength. To improve. Corresponding to thermal shock, the amorphous refractory has low thermal expansion characteristics and stainless steel wire with a diameter of 0.2 m / mφ is mixed in to prevent generation of fine cracks on the surface. Also, by inserting multiple stainless steel reinforcements in the inner longitudinal direction of the grate and in the direction perpendicular to this, even in the event of a grate break, these reinforcements prevent the chips from falling out, and the discharge pusher at the rear contact, Unattended automatic operation is possible because troubles due to debris mixing into the melting device are eliminated.

【0008】請求項4、5について図面1、10に基づ
いて説明すると、炉後燃に相当する部分を高温畜熱した
砂による流動床とし、8上部火格子からの未燃焼物、液
状化した高分子焼却物、液体類を完全焼却させる。温度
を27熱電対と48助燃バーナの組合せで800℃〜9
00℃にするべく制御設定しておく。10a流動床部の
底は9a排出プッシャー進行方向に対し水平であるが、
進行方向左右には傾斜をつけ舟底のごとく形状を持たせ
る事で対流している砂の大部分が常時中央に集まる。砂
中の注射針等の不燃物を9bラチェット櫛刃に9a灰、
残渣排出プッシャーと共に振動を加え前進させる事で床
前方に砂中から鋤集められる。9a灰、残渣排出プッシ
ャーは9dプッシャーガイドレールに乗っている事で砂
中に埋もれず砂の対流を乱す事なく、砂の上面を前進し
上層の吹き上げられた軽い灰やバースクリーン上のビ
ン、発生クリンカー等を排出口迄押し集め、連動する1
0b排出扉を開け炉外のコンベアに排出する。櫛目にか
からない砂の粒径0.5〜1.0m/mφより小さい灰
の多くは砂上層に吹上られプッシャーにて排出される
が、砂中に混入した細い灰は櫛分けられる事なく逐次累
積し10a流動床部から砂をオーバーフローさせたり、
砂をひんぱんに新しく交換せざるを得ない事態が生じ
る。9a灰、残渣排出プッシャーに10d砂中ダスト吸
引管を取り付ける事により砂中ダストをサイクロン迄マ
イナス圧力で吸引させる、網目スクリーのごとく目ずま
りを生じさせない捕捉手段が実現した。これにより前燃
焼を行なうストーカー式炉とのジョイントで焼却物を予
備破砕したり、砂を一度炉外に搬出してからの篩作業、
リターンバケットコンベアによる不燃物分離を必要とせ
ず炉内で砂と不燃物を分離出来る流動床式後燃部を持っ
た高燃焼効率の炉が実現した。
The fourth and fifth aspects will be described with reference to FIGS. 1 and 10. A portion corresponding to afterburning of the furnace is a fluidized bed of sand that has been subjected to high temperature heat storage, and 8 unburned matter from the upper grate and liquefaction. Complete incineration of polymer incineration materials and liquids. The temperature is 800 ° C to 9 with a combination of 27 thermocouples and 48 auxiliary burners.
The control is set so that the temperature is set to 00 ° C. Although the bottom of the fluidized bed section 10a is horizontal with respect to the traveling direction of the 9a discharge pusher,
Most of the convective sand is always gathered in the center by sloping to the left and right in the direction of travel to give it a shape like a boat bottom. Injectable materials such as injection needles in the sand on the 9b ratchet comb blade 9a ash,
By applying vibration with the residue discharge pusher and moving it forward, the plow is collected from the sand in front of the floor. The 9a ash and residue discharge pusher are not buried in the sand because they are on the 9d pusher guide rail, and do not disturb the convection of the sand. Collecting generated clinker etc. up to the discharge port and interlocking 1
0b Open the discharge door and discharge to the conveyor outside the furnace. Most of the ash particles with a grain size of 0.5-1.0 m / mφ that does not come into contact with the comb are blown up onto the sand layer and discharged by the pusher, but the fine ash particles mixed in the sand are successively accumulated without being combed. 10a, overflow the sand from the fluidized bed,
A situation arises in which the sand must be replaced frequently. By attaching a dust suction pipe in the sand 10d to the 9a ash and residue discharge pusher, dust in the sand is sucked up to the cyclone with a negative pressure, and a trapping means that does not cause clogging like a mesh screen is realized. As a result, the incinerated matter is pre-crushed at the joint with the stalker-type furnace that performs pre-combustion, and the sanding work is carried out after the sand is once carried out of the furnace.
A highly efficient combustion furnace with a fluidized bed type afterburning unit that can separate sand and incombustibles in the furnace without the need to separate incombustibles with a return bucket conveyor has been realized.

【0009】請求項6で図1、3、6で説明すると、1
2灰残渣ホッパーが満杯になり溶融の必要が生じた時点
で、35予熱用排ガスバイパス煙道のダンパーを開け、
約900℃の排ガスを18a本再燃室から17排ガスバ
イパス(出口)、溶融炉、13引出フィダーを経由して
17排ガスバイパス(入口)まで通過させる。ダクト内
は煙突設置の43イヂェクターによりマイナス圧となっ
ている。ここで主排ガス流と再合流となるが、27溶融
炉温度感知用熱電対信号と連動する35炉前ダンパーが
有る事で、温度上昇プログラミングに沿って予熱を利用
するバイパス排ガス流通過量のコントロールが可能とな
る。溶融炉が700〜800℃のピークまで温度上昇な
された時点で35入口ダンパを閉じ、28ヂェットバー
ナーを作動させ1550℃までの温度上昇をはかる。こ
のスタート点でも既設定プログラミングにより急激な温
度上昇がおこらない様、バーナー出力カロリーはコント
ロールされる。14溶融炉本体への溶融物供給は34炉
上部蓋を水平移動させて、炉上部を開け予熱された残渣
を投入する。炉の構造は炉内側壁接線方向に火炎が出せ
る様設置し先端に形成される空気断熱層を破壊させる為
の火炎速度、約100m/secの28ジェットバーナ
ーにより炉内に回転火炎をおこす円筒ルツボ炉タイプを
使う。ただし、ルツボ炉は間接熱射で内部の溶融物を1
200℃程度までしか上昇させられないし、又、たとえ
高質耐火材料を使っても2〜3回程度しかもたない。故
に炉は円筒ルツボ炉タイプを使い中心部にルツボの替り
に下部に複数の切欠き開口を持った不定型耐火物製円筒
を設置し、29溶融容器とする。31炉内部床は耐火物
の上に一定厚の金属を敷いて置く。この上面レベルは溶
融物出口底面と同一平面に設定されている。
The description of claim 6 with reference to FIGS.
2 When the ash residue hopper is full and needs to be melted, open the damper for the 35 preheating exhaust gas bypass flue,
Exhaust gas at about 900 ° C. is passed from the 18a reburn chamber to the 17 exhaust gas bypass (outlet), the melting furnace, and the 13 extraction feeder to the 17 exhaust gas bypass (inlet). The inside of the duct has a negative pressure due to the 43 injectors installed in the chimney. Although it is rejoined with the main exhaust gas flow here, since there is a 35 furnace front damper that works in conjunction with the 27 melting furnace temperature sensing thermocouple signal, it is possible to control the bypass exhaust gas flow passage rate using preheating along with the temperature rise programming. It will be possible. When the temperature of the melting furnace is raised to the peak of 700 to 800 ° C, the 35 inlet damper is closed and the 28 jet burner is operated to raise the temperature to 1550 ° C. Even at this starting point, the burner output calorie is controlled so that the preset temperature does not cause a sudden temperature rise. To supply the molten material to the 14 melting furnace main body, the 34 upper furnace lid is moved horizontally, the upper furnace is opened, and the preheated residue is charged. The structure of the furnace is a cylindrical crucible that is installed so that the flame can be emitted in the tangential direction of the inner wall of the furnace and has a flame velocity for destroying the air insulating layer formed at the tip, with a 28 jet burner of about 100 m / sec to generate a rotating flame in the furnace. Use furnace type. However, the crucible furnace uses indirect thermal spray to remove the melt inside
It can be raised only up to about 200 ° C, and even if a high quality refractory material is used, it only takes about 2 to 3 times. Therefore, as the furnace, a cylindrical crucible furnace type is used, and instead of the crucible in the center, an indeterminate refractory cylinder having a plurality of notch openings is installed in the lower part to form a 29 melting vessel. 31 The inner floor of the furnace is laid with a certain thickness of metal on the refractory. This top level is set flush with the bottom of the melt outlet.

【0010】請求項7で図6により説明すると18a本
再燃室と20aサイクロンを小型焼却炉内に同時に組込
むには炉からの排ガスを上部から18a本再燃室に入れ
流速を落としダストを沈降させてから下部から抜けた排
ガスを新たに設けた18b副再燃室に入れる。18b副
再燃室は18a本再燃室と逆で下部に入口があり、18
a本再燃室出口と接続する。同様に出口は上部に付けサ
イクロン入口と接続取付ける。又、沈降ダクトは47ゲ
ート開閉ロット又は気密ロータリーバルブにより13引
き出しフィダーに排出する機構である。請求項8で図
1、4、9にて説明すると、煙道に空隙を無くす為に正
六角形とした55コロナ放電プラス電極と各正六角形に
対応し中心部に54コロナ放電マイナス電極の放電極を
57、58支持より取付ける。正、負極間距離を50m
/m、12kv、1m/mAとしコロナ放電を開始させ
る。電極部に水滴微粒子を吹きつけ発生したイオン、電
子と衝突させ通過する排ガス中に帯電粒子流を作る。プ
ラスに帯電した逆帯電粒子は、負極後方に取り付けた5
6逆帯電粒子吸収翼で電気的に中和させて帯電粒子流に
はマイナス粒子のみが残る様にする。反応湿には載台に
乗せた41消石灰中空円筒ブロックを常時表面を湿ら
し,尚かつ40プラス電極集電子でプラスに電圧を加え
た状態にしてセットする。クーロン力によりマイナス帯
電水滴微粒子及びダスト粒子を捕促し、消石灰と反応さ
せ酸を塩基固定させる事が実現した。請求項9で耐熱バ
インダーを使い内外周の長手にV型溝の切込みを持ち中
空円筒状に成形した事で接触面積が単純に円筒型か四角
に穴を空けた時と比較し表面積が4倍になり、尚かつ微
量電解質を含入させる事で湿潤化により通電可能な水酸
化カルシウム円筒ブロックが実現した。
Referring to FIG. 6 in claim 7, in order to simultaneously incorporate the 18a main reburn chamber and the 20a cyclone into the small incinerator, the exhaust gas from the furnace is introduced into the 18a main reburn chamber from the upper part to reduce the flow rate and settle dust. The exhaust gas discharged from the lower part of the above is put into a newly provided 18b sub-reburning chamber. The 18b sub-reburn chamber has an inlet at the lower part, which is the reverse of the 18a main reburn chamber.
a Connect to the outlet of the reburn chamber. Similarly, the outlet is attached to the top and connected to the cyclone inlet. The settling duct is a mechanism that discharges to a 13-drawer feeder using a 47-gate open / close lot or an airtight rotary valve. Explaining in FIGS. 1, 4 and 9 in claim 8, 55 corona discharge plus electrodes which are hexagonal in order to eliminate voids in the flue and 54 corona discharge minus electrodes in the center corresponding to each hexagon. 57, 58 from the support. Distance between positive and negative electrodes is 50m
/ M, 12 kv, 1 m / mA to start corona discharge. A stream of charged particles is created in the exhaust gas passing through by colliding with the ions and electrons generated by spraying water droplets on the electrodes. The positively charged oppositely charged particles were attached to the rear of the negative electrode.
6. The negatively charged particle absorbing blade electrically neutralizes so that only negative particles remain in the charged particle flow. For the reaction humidity, a 41 slaked lime hollow cylindrical block placed on a mounting table is set by always moistening the surface and applying a positive voltage with a 40 positive electrode current collector. By the Coulomb force, it was possible to capture negatively charged water droplets and dust particles and to react with slaked lime to fix the acid as a base. In claim 9, the heat-resistant binder is used to form a hollow cylindrical shape with V-shaped groove notches on the inner and outer circumferences, so that the contact area is four times as large as that of a cylindrical type or a square hole. In addition, the inclusion of a trace amount of electrolyte has realized a calcium hydroxide cylindrical block that can be energized by moistening.

【0011】請求項10で図4を説明すると、36載台
は載台床と反応済消石灰受け皿で組み立てられ受け皿の
上を4つの52碍子脚が載台床を支えている構造をして
いる。この41消石灰中空円筒を乗せる載台床は丸棒材
でグレーチング状に加工し、下から上昇する帯電粒子流
が抜け易くしていると同時に、反応後のはがれ落ちた塩
基が載台の外部に零れる事なく、下部受け皿に落ちやす
い構造とする。36載台が21載台自動取替装置によ
り、42反応室に送られ設置された状態は38載台受棹
及び40プラス電極集電子の上に乗る事により全体がプ
ラスに電圧を加えられている。4つの碍子脚により電気
的に載台床と受け皿は縁が切られている。52碍子脚は
49帯電水滴粒子附着防止カバーで直接帯電粒子流にさ
らすのを防ぐ構造をしている。51ノズルを49帯電水
滴粒子附着防止カバー内にリークして附着した帯電水滴
粒子清掃の為に各ケースに取り付ける。請求項11で図
1、4で説明すると、排ガス中の主なる有害ガスである
塩化水素が水酸化カルシウムとの反応を終え生成した塩
化カルシウムは、元の水酸化カルシウムより50%重量
が増加する。塩化カルシウムは反応後、自重落下と上部
の51スプレーでかき落とされ全て載台受け皿に溜ま
る。この重量変化を22ロードセルで常時計量する事で
反応終了を感知出来、この時点で21自動取替装置本体
を作動させる事により新規と交換するシステムが実現し
た。
Referring to FIG. 4 in claim 10, the 36 mount is constructed of a mount base and a reacted slaked lime saucer, and four 52 insulator legs support the mount base on the saucer. . The 41 platform on which this slaked lime hollow cylinder is placed is processed with a round bar material into a grating shape to facilitate the escape of the charged particle flow rising from the bottom, and at the same time, the base that has peeled off after the reaction is placed outside the platform. The structure is such that it will not fall and will easily fall into the lower tray. The 36 platform is sent to the 42 reaction chamber by the 21 platform automatic changer, and the installed state is that the entire platform is positively charged by riding on the 38 platform and 40 positive electrode current collector. There is. The pedestal floor and the saucer are electrically cut off by four insulator legs. The 52 insulator leg has a structure for preventing direct exposure to the flow of charged particles by a cover 49 for preventing attachment of charged water particles. The 51 nozzle is attached to each case for cleaning the charged water droplet particles attached by leaking into the 49 charged water droplet particle attachment prevention cover. To explain with reference to FIGS. 1 and 4 in claim 11, calcium chloride produced by the reaction of hydrogen chloride, which is a main harmful gas in exhaust gas, with calcium hydroxide is increased in weight by 50% as compared with the original calcium hydroxide. . After the reaction, the calcium chloride was dropped by its own weight and scraped off by the 51 spray on the top, and all was collected in the platform tray. By measuring this weight change with 22 load cells at all times, the end of the reaction can be detected, and at this point, a system for exchanging a new one was realized by activating the 21 automatic changer body.

【0012】[0012]

【作用】請求項2について、図7にて説明すると波長2
4.15GHのマイクロ波はアイソトープのごとく専
門管理技術者を必要とせず、人体に無害で比較的安価で
あり、壁面の耐火物を透過する事が出来ると同時に、灼
熱の影響を全く受けない特質を持つ。以上の理由によ
り、不特定多数の人が炉に近づいても危険がなく、5受
信部に鋼板製フードを取り付け4発信器からのマイクロ
波をあたかもビーム光束のごとく使用する事により炉内
部焼却物の有無を連続的に監視するセンサーとして焼却
物自動投入装置作動するのに有効に作用する。請求項3
について、図2にて説明すると前記のごとく細かいステ
ンレスワイヤーを不定形耐火物への混入は細かい亀裂の
発生を防ぐのに有効に作用する。B部詳細のごとく8不
定形火格子の主筋となるステンレス補強材不定形耐火物
との間に約0.03m/m程度のクリアランスを予め設
ける。これにより炉稼動による加熱時にステンレスの熱
膨張を吸収すると共に、クリアランスがほぼゼロになる
事で不定形耐火物に亀裂を入れる内部発生応力を無くし
火格子の破壊を防ぐのに有効に作用する。クリアランス
を作るにはステンレスの補強材に火燃性塗料を希望設計
厚みに塗り、これに型枠を組んだ後不定形耐火物を流し
込む。後ほどの焼結加熱により塗料は燃焼してしまい、
補強材と不定形耐火物間にクリアランスが出来る。又、
8火格子の隣合った連結部突起構造は相互に補い強度を
高めるだけでなく、火格子と直角方向にほぐし押されて
来る焼却物を未燃のまま火格子間隙から落ちるのを最少
限にし、焼却物がストーカーの上を移動する様に円滑に
進めるのに有効に作用する。請求項4、5について図
8、10にて説明すると9cエアー吹き出し口からの予
熱エアーを舟形の10a流動床部直角方向に吹き出す事
により、砂に底部から傾斜に沿って上昇し、上層部で水
平に中心部に戻る流れが生じる。舟形の10a流動床部
は背骨のごとく中心部にある9dプッシャーガイドレー
ルにより前方D部を除き左右に仕切られているので、中
心部に戻った砂は一度9dプッシャーガイドレールにぶ
つかり、それに沿って下方に流れる。このように左右独
立したあばら骨方向での対流を発生する。この砂の対流
は注射針等小さい不燃物のみ共に流動させるがビン、発
生クリンカー類等大きい不燃物に対して9eバースクリ
ンはこれ等を砂の中に埋もれさす事なく表面に浮かんだ
状態で中央に集めるのに有効に作用をする。9eバース
クリンには砂の対流に乗って中央部に集められた、ビ
ン、鉄片、上部燃焼部での発生クリンカーが10a流動
床部底部まで飲み込まれ9cエアー吹き出し口をふさい
だり、吹き出し口に引っ掛かり対流を妨げる等流動床部
機能を落とす事態の発生を防ぐ作用と19熱交換器で3
00℃まで加熱されたエアーと48助燃バーナーの働き
で灼熱されたこれ等ビン、金属類を砂上層部に保持させ
る作用をする。これにより上部火格子から垂れて来る液
状焼却物を砂に達する前にこの上で燃焼するか、又はす
り抜ける間に燃焼を進行させる等、砂との共役の役目を
する事で流動床部の燃焼効率上昇に対し有効に作用す
る。9a灰、残渣排出プッシャーは、砂上層部を9dプ
ッシャーガイドレールに乗り一定時間毎に前進、後退し
9eバースクリーン上の大きい不燃物及び軽い灰を前方
D部砂上に押し集める。又、9a灰、残渣排出プッシャ
ー下に取り付けられている9bラチット櫛刃は、砂中の
注射針等小さい不燃物を61振動発生機からの振動を砂
に与えながら小さい未燃物を前方D部に鋤集める。戻る
時は砂の抵抗により支持ビンを中心として砂上部に持ち
上げられた状態となり鋤の働はしない。ストロークは連
続作動でない為、次の開始時には9bラチェット櫛刃は
自重、砂の流動、振動等により進行方向と直角定位置に
ついて戻る。D部は9Cエアー吹き出し口を配置してな
いので、砂の対流が発生せず前回の9a灰、残渣プッシ
ャーのストローク作動で集められた大小不燃物が再拡散
する事はない。
The operation of claim 2 will be described with reference to FIG.
Microwave 4.15GH z does not need professional management technician as of isotope, are relatively inexpensive and harmless to the human body, and at the same time can be transmitted through the refractory wall, not affected by the scorching It has characteristics. For the above reasons, there is no danger even if an unspecified number of people approach the furnace. (5) A steel plate hood is attached to the receiving part. (4) Microwave from the transmitter is used as if it were a beam of light. As a sensor that continuously monitors the presence or absence of the incinerator, it is effective in operating the automatic incinerator charging device. Claim 3
With reference to FIG. 2, mixing the fine stainless wire into the amorphous refractory as described above effectively acts to prevent the generation of fine cracks. As described in detail in section B, a clearance of about 0.03 m / m is provided in advance between the stainless reinforcing material and the amorphous refractory, which are the main bars of the 8 amorphous grate. This absorbs the thermal expansion of stainless during heating by operating the furnace, and eliminates the internally generated stress that causes cracks in the amorphous refractory because the clearance becomes almost zero, and effectively acts to prevent the destruction of the grate. To make clearance, apply a flame retardant paint to the stainless steel reinforcement material to the desired design thickness, assemble a formwork on this, and pour in an irregular refractory material. The paint burns due to later sintering heating,
Clearance can be created between the reinforcing material and the irregular shaped refractory. or,
8 The adjacent connecting protrusions of the grate not only complement each other and increase the strength, but also minimize the incineration of the grate that is disentangled and pushed in the direction perpendicular to the grate from falling out of the grate gap without burning. , The incineration works effectively to move smoothly on the stalker. When claims 4 and 5 are described with reference to FIGS. 8 and 10, preheated air from a 9c air outlet is blown out in a direction perpendicular to the boat-shaped 10a fluidized bed section, so that the sand rises along the slope from the bottom to the upper layer. There is a horizontal flow back to the center. The boat-shaped 10a fluidized bed is partitioned left and right by the 9d pusher guide rail in the center like the spine except for the front part D, so the sand returning to the center once hits the 9d pusher guide rail, and along it It flows down. In this way, left and right independent convection in the direction of the ribs is generated. This convection of sand causes only small incombustibles such as injection needles to flow together, but for large incombustibles such as bottles and clinker, 9e Versculin floats on the surface without being buried in the sand. It works effectively to collect in. On the 9e bar screen, bottles, iron pieces, and clinker generated in the upper combustion part gathered in the center part due to the convection of sand were swallowed to the bottom part of the fluidized bed part at 10a, and the air outlet of 9c was blocked and caught in the outlet. 3 functions with 19 heat exchangers that prevent the occurrence of situations in which the function of the fluidized bed is impaired, such as blocking convection
The air heated to 00 ° C. and the 48 auxiliary burners work to retain these burned bottles and metals in the upper layer of sand. As a result, the liquid incineration dripping from the upper grate is burned on the sand before it reaches the sand, or the combustion progresses while slipping through the sand, etc. Effectively increases efficiency. The 9a ash / residue discharge pusher rides on the sand upper layer on the 9d pusher guide rail and advances and retreats at regular intervals, and collects large incombustibles and light ash on the 9e bar screen on the front D sand. Also, 9a ash, 9b ratchet comb blade installed under the residue discharge pusher, small non-combustible material such as an injection needle in sand is applied to the sand by the vibration from the 61 vibration generator to the front D part. Collect plows. At the time of returning, it is in a state of being lifted to the upper part of the sand around the support bottle due to the resistance of the sand and the plow does not work. Since the stroke is not continuous operation, at the next start, the 9b ratchet comb blade returns at a fixed position perpendicular to the traveling direction due to its own weight, sand flow, vibration, and the like. Since the 9C air blowout port is not arranged in the D part, the convection of sand does not occur and the large and small incombustibles collected by the previous stroke operation of the 9a ash and the residue pusher do not re-diffuse.

【0013】10b排出扉は10cプッシャー連動扉ロ
ットにより9a灰、残渣排出プッシャーと連動して開閉
する。逐次後から押し出された状態で大、小不燃物は炉
外コンベアに押し出される。この時加えられる振動は大
小不燃物から砂を篩い落とすのに有効に作用する。9e
バースクリーンを10a流動床部側面いっぱいに取り付
けず、中央部のみとする事より隙間から砂の対流により
底部に一度取り込まれた大きい不燃物も対流に乗り傾斜
に沿って上層部に向かい、再度9eバースクリーン上に
戻す事が可能となる。又,10a流動床部下部において
上部砂層を押上ようとする9cエアー吹出し口押し込み
エアーの圧力と、それを砂押える上部砂層の自重による
圧力で拮抗しつつエアーが上部に抜けている状態の所へ
弱い20aサイクロンからの吸引力が作用している10
d砂中ダスト吸引管口が前進移動して来る事により61
振動発生機による振動効果も加わり拮抗バランスが崩れ
る。押し込みエアーがあたかもガス抜きされた状態とな
り砂及びダストはやや浮遊した状態で10d砂中ダスト
吸引管口へ流れる。図10、E部詳細のごとく吸引管入
口はラッパ状に開いている事により入口部速度Vは吸
引管上部速度Vより大巾に遅く吸引力も弱い。これに
よりダストより10〜30倍以上重い砂は吸引管入口で
管内に吸い上げられる事はなくダストのみがV速度で
吸引され17サイクロン入口へ送られる。吸引管入口を
直管のまま速度Vで吸引した場合多少の炉内条件変動
で砂を吸引する事態が発生する。以上述べたごとく10
d砂中ダスト吸引管のラッパ形状は砂、ダストの分離に
有効に作用する。又10d砂中ダスト吸引管によるダス
ト分離は10a流動床部の砂を炉外にオーバーフローさ
せる事なく、又砂を絶えず新しい状態で使用する為有効
に作用する。微量の砂は不燃物に附着して14溶融炉で
30灰、残渣と共に溶融されるが、他の溶融物に取り込
まれ炉外に流出する。
The 10b discharge door is opened and closed in conjunction with the 9a ash and residue discharge pusher by the lot of the 10c pusher interlocking doors. Large and small incombustibles are extruded to the out-of-furnace conveyor while being extruded one after another. The vibration applied at this time effectively acts to remove sand from large and small incombustibles. 9e
The bar screen is not attached to the side surface of the fluidized bed 10a, and only the central part is provided. Large incombustibles once taken in by the convection of sand from the gap to the bottom also ride on the convection and head for the upper layer along the slope, and again 9e It is possible to return to the bar screen. In addition, to the place where the air escapes to the upper part while competing with the pressure of the 9c air outlet pushing air that tries to push up the upper sand layer in the lower part of the fluidized bed part 10a and the pressure due to the own weight of the upper sand layer that presses the sand. Weak suction force from 20a cyclone is acting 10
d As the dust suction port in the sand moves forward, 61
The vibration effect of the vibration generator is also added and the antagonistic balance is lost. The forced air becomes as if it were degassed, and the sand and dust flow in a slightly floating state to the dust suction port in the sand for 10d. Since the suction pipe inlet is opened in a trumpet shape as shown in detail in FIG. 10 and E, the inlet velocity V 2 is much slower than the suction pipe upper velocity V 1 and the suction force is weak. As a result, sand that is 10 to 30 times heavier than dust is not sucked up into the pipe at the suction pipe inlet, and only dust is sucked at the V 1 speed and sent to the 17 cyclone inlet. When the suction pipe inlet is sucked at a velocity V 1 with a straight pipe, sand may be sucked due to a slight change in the furnace condition. As mentioned above, 10
d The trumpet shape of the dust suction pipe in sand effectively acts to separate sand and dust. Further, the dust separation by the dust suction pipe in the sand 10d is effective because the sand in the fluidized bed 10a does not overflow outside the furnace and the sand is constantly used in a new state. A small amount of sand adheres to the incombustible material and is melted together with 30 ash and residue in the 14 melting furnace, but is taken in by other melting materials and flows out of the furnace.

【0014】請求項6で図3で説明すると過度な熱衝撃
を炉に与えない為、温度上昇プログラミングされたジェ
トバーナー火炎を29溶融容器外壁と14溶融炉内壁の
間の空間を31金属底床部とは水平で炉内壁に対し接線
方向に沿って回す事は29溶融容器下部開口からの30
灰、残渣溶融物をふき上げ、吸引圧力力か生ぜず圧力バ
ランスを保ち炉を高温に持って行くのに有効に作用す
る。又、火炎は幾回か廻り29溶融容器及び31金属底
床加熱して、天上蓋穴からサイクロンに排気される。溶
融容器内灰残渣は31金属底床からの熱伝導、容器側壁
副射、天上蓋からの火炎及び副射で加熱される。又、2
9溶融容器下部に開口部を設けてあるが、容器厚みを溶
融物の安息角で出来る裾野より大巾に大きく設定してあ
るので、29溶融容器外の火炎の通る隙間に出る事はな
い。以上で述べた理由により、30灰、残渣には直接火
炎がぶつからない為飛散する事はなく溶融点まで温度を
高められる。31金属底床部の熱伝導により炉内温度が
上昇するに従い、まず灰が溶融し金属床表面を溶融容器
下部開口から流れ出て、炉内壁に達し溶融物出口を経て
炉外へ出る。金属床はまだ溶融していない為、灰の溶融
した物と混合する事はない。同様にガラス類も炉外へ流
れ出る。温度上昇に伴い溶融容器外の31金属底床が、
バーナー火炎により溶かされ始め熱伝導により徐々に内
側も溶融され、最後に内部金属も溶融し炉外に流れ出
す。又、灰、ガラス、金属の溶融温度は200〜300
℃差が有る。この温度差を捕え27熱電対センサーと1
6bスラッヂ仕分コンベアと連動させる事で分別仕分回
収が可能となる。炉が空になった状況を炉内熱電対で感
知し炉蓋を水平に移動し、灰、残渣ホッパー下13引き
出しフィダーが作動し新たな灰、残渣を投入する。残渣
はその都度見掛比重が異なるのでロードセルによる重量
チェックでは感知出来ない。満杯感知は溶融炉側面から
前接炉内感知センサーと同仕様の4、5マイクロ波利用
レベル計を使う。5受信部に最少寸法20m/mφの金
属フードをかける細かい光束ビームのごとくマイクロ波
は灰、残渣により出来る安息角項上部を精度良く感知す
るのに有効に作用する。請求項7について図6にて説明
すると、18a本再燃室と同様に18b副再燃室は排ガ
ス速度は押え酸素との燃焼をさらに十分に行ない、圧損
の少ない煙道の役目も持たせる。これにより排ガス出口
はサイクロン入口とスムーズに接続出来る位置関係が可
能となり、18a本再燃室と20サイクロンが小型 焼
却炉に同時に納める為に有効に作用する。又、ここで発
生する圧損は後接の43エヂェクター吸引力で十分カバ
ー出来切るものである。請求項9で図4にて説明する
と、反応が進行するに従い外及び中空部表面が剥離し、
下の受け皿部に落下させる事により排ガスの通る断面積
が増加し圧損を減少させる。又、接続表面積の増大は4
2反応室、36載台、21自動供給、排出装置のコンパ
クト化に対し有効に作用する。
As will be described with reference to FIG. 3 in claim 6, a temperature rising programmed jet burner flame is provided in the space between the outer wall of the melting vessel 29 and the inner wall of the melting vessel 31 to prevent excessive thermal shock to the furnace. It is possible to rotate it along the tangential direction to the inner wall of the furnace, which is horizontal with the part
It wipes up ash and residual melt, and acts effectively to bring the furnace to high temperature while maintaining pressure balance without generating suction pressure force. Also, the flame is heated several times, 29 melting vessel and 31 metal bottom floor heating, and exhausted to the cyclone through the top lid hole. The ash residue in the melting vessel is heated by heat conduction from the 31 metal bottom floor, by-side injection from the side wall of the vessel, and by flame and side-injection from the top cover. Again 2
Although there is an opening at the bottom of the melting vessel 9, since the thickness of the vessel is set to be much larger than the skirt formed by the angle of repose of the molten material, it does not appear in the gap through which the flame passes outside the melting vessel 29. For the reasons described above, since the flame does not directly hit the 30 ash and the residue, it does not scatter and the temperature can be raised to the melting point. 31 As the temperature inside the furnace rises due to the heat conduction of the metal bottom floor, the ash first melts and flows out of the lower surface of the melting vessel on the surface of the metal floor, reaches the inner wall of the furnace, and exits the furnace through the melt outlet. Since the metal bed is not yet molten, it will not mix with the molten ash. Similarly, glasses also flow out of the furnace. 31 metal bottom floor outside the melting vessel due to temperature rise,
It begins to be melted by the burner flame and gradually melts the inner side by heat conduction, and finally the inner metal also melts and flows out of the furnace. The melting temperature of ash, glass and metal is 200-300.
There is a difference of ℃. Catch this temperature difference and set it to 27 thermocouple sensor
By linking with the 6b sludge sorting conveyor, sorting sorting can be performed. When the furnace is empty, the thermocouple in the furnace detects the situation and the furnace lid is moved horizontally, and the ash / residue hopper bottom 13 drawer feeder operates to insert new ash and residue. Since the apparent specific gravity of the residue is different each time, it cannot be detected by the weight check with the load cell. For full detection, a level meter using 4, 5 microwaves with the same specifications as the in-front detection sensor is used from the side of the melting furnace. 5 Microwaves that act as a fine beam of light by applying a metal hood with a minimum size of 20 m / mφ to the receiving section are effective in accurately sensing the upper part of the repose angle term formed by ash and residues. When the seventh aspect is described with reference to FIG. 6, the 18b sub-reburning chamber as well as the 18a main reburning chamber allows the exhaust gas velocity to more sufficiently combust with the holding oxygen and also serves as a flue with less pressure loss. As a result, the exhaust gas outlet can be placed in a position where it can be smoothly connected to the cyclone inlet, and the 18a main reburn chamber and 20 cyclones can be effectively put into a small incinerator at the same time. Further, the pressure loss generated here can be sufficiently covered by the suction force of the 43-educator at the rear side. Explaining with reference to FIG. 4 in claim 9, as the reaction progresses, the outer surface and the hollow surface are peeled off,
By dropping it on the lower tray, the cross-sectional area through which exhaust gas passes increases and the pressure loss is reduced. Also, the increase in connection surface area is 4
It works effectively for downsizing of 2 reaction chambers, 36 pedestals, 21 automatic supply and discharge device.

【0015】請求項8について図1、4、9で説明する
と、コロナ放電を開始すると排ガス中のイオンや電子は
放電極近傍の強い電界により加速されるので、充分な運
動エネルギーを持って排ガス中の分子と衝突し、これを
電離し更に多くのイオンや電子が急激に発生する。ここ
の60コロナ放電帯部に51アトマイヂングノズルによ
り、空気と水とを混合して作られた水滴微粒子を吹き込
む。60放電帯部で発生したイオン電子等は、ガス中を
熱運動しながらイオン濃度差に従って拡散しており、こ
の拡散によりり水滴微粒子及びダスト微粒子に衝突し電
荷を与える。しかし、時間と共にこれらはクーロン力に
より相互に引合い電気的に中和するのでこれを避ける
為、54コロナ放電極である負電極後方(排ガスの進む
方向)に電極と平行で同数の6枚の翼のある56逆帯電
粒子吸収翼を取り付ける。この翼に正イオン及び正逆帯
電粒子をクーロン力で吸着する事でガス中には負イオ
ン、負帯電水滴微粒子、負帯電でダスト粒子、未帯電水
滴微粒子等からなる帯電粒子流が生成される。吹き込ま
れた水滴微粒子は排ガス中くまなく霧のごとく拡がり、
帯電すると同時に塩化水素、亜鉛酸ガス、二酸化窒素等
の水溶性有害ガスを瞬時に液中に溶解拡散させ、酸性水
溶液で出来た帯電水敵微粒子となる。酸性水溶液となり
水滴の電気抵抗が小さくなる事で、帯電した場合イオン
が離れてしまう逆電離現象は生じない。又、煙道内が高
温の為、一部の水滴微粒子は水蒸気となるが、水蒸気飽
和点以下であっても排ガス中の未衝突イオン及び、帯電
ダスト粒子が水分凝結核の働きをなし、再び可逆的に5
9帯電水滴微粒子となる作用をする。帯電粒子流煙道は
こ、で排ガス速度を落とす事により、帯電水滴微粒子に
未吸着の塩化水素、SO,NO、ダスト粒子等を取
り込むべく有効に作用する。42反応室の41消石灰中
空円筒ブロックそれ自体は導伝体ではないが、清掃役目
も持った上部ノズルからの水噴射により、表面が常時水
の薄膜で温潤された状態となっており、含入された塩化
ナトリウム等微量電解液膜の生成の効果により載台に電
圧を加える事で電気集塵機の集塵極(プラス極)の働き
をしマイナス帯電の水滴微粒子、ダスト粒子をクーロン
力により吸着する。又、酸性水溶液化した帯電水滴微粒
子の取り込みにより、消石灰中空円筒ブロック表面は未
反応の酸性水溶液薄膜に覆われる状態となり一肩全体に
クーロン力が働きやすくなり、集塵極としての捕捉、吸
着効率の上昇と共に消石灰ブロックの細かい亀裂にも酸
性化水溶液が浸み込み、表面だけでなく内部でも反応を
起こし、単時間で効率よく有害ガスを塩基として固定さ
せる事を可能とした。
When claim 8 is described with reference to FIGS. 1, 4, and 9, when the corona discharge is started, the ions and electrons in the exhaust gas are accelerated by the strong electric field near the discharge electrode, so that sufficient kinetic energy is exerted in the exhaust gas. Collide with the molecules of and ionize them, and more ions and electrons are rapidly generated. The 51 atomizing nozzle blows fine particles of water droplets prepared by mixing air and water into the 60 corona discharge zone. Ion electrons and the like generated in the 60th discharge zone are diffused according to the difference in ion concentration while thermally moving in the gas, and due to this diffusion, they collide with water droplet fine particles and dust fine particles to give an electric charge. However, over time, these attract each other due to Coulomb force and electrically neutralize, so to avoid this, in order to avoid this, behind the negative electrode which is the 54 corona discharge electrode (direction in which the exhaust gas advances), the same number of six blades parallel to the electrode. Attach a reverse charged particle absorption blade with 56. By adsorbing positive ions and positive and negative charged particles by Coulomb force to this blade, a charged particle flow composed of negative ions, negatively charged water droplets particles, dust particles, uncharged water droplets particles, etc. is generated in the gas. . The water droplets that have been blown in spread like mist throughout the exhaust gas,
At the same time as being charged, water-soluble harmful gas such as hydrogen chloride, zinc acid gas, and nitrogen dioxide is instantly dissolved and diffused in the liquid, and becomes charged water enemy fine particles made of acidic aqueous solution. Since it becomes an acidic aqueous solution and the electrical resistance of the water droplets becomes small, the reverse ionization phenomenon in which ions are separated when charged is not caused. Also, because of the high temperature inside the flue, some of the water droplets become water vapor, but even below the water vapor saturation point, uncollided ions in the exhaust gas and charged dust particles act as water condensation nuclei and are reversible again. To 5
9 Charged water drops act as fine particles. By reducing the velocity of the exhaust gas with the charged particle flow flue, it effectively acts to take in unadsorbed hydrogen chloride, SO x , NO x , dust particles and the like into the charged water droplet fine particles. Although the 41 slaked lime hollow cylindrical block of the 42 reaction chamber itself is not a conductor, the surface is always warmed with a thin film of water by the water jet from the upper nozzle that also has a cleaning function. By applying a voltage to the mounting table due to the effect of forming a small amount of electrolyte membrane such as sodium chloride that has entered, it works as a dust collecting electrode (plus electrode) of the electrostatic precipitator and adsorbs negatively charged water droplets and dust particles by Coulomb force. To do. In addition, the surface of the slaked lime hollow cylindrical block becomes covered with unreacted acidic aqueous solution thin film due to the incorporation of charged water droplets that have been converted to acidic aqueous solution, and Coulomb force easily acts on the entire shoulder, trapping and adsorbing efficiency as a dust collecting electrode. As the temperature rises, the acidified aqueous solution penetrates even into the fine cracks of the slaked lime block, causing a reaction not only on the surface but also inside, making it possible to efficiently fix harmful gas as a base in a single hour.

【0016】請求項10で図4にて説明すると、載台は
4ヶの52碍子により、電気的に上部の円筒消石灰ブロ
ック載台床と反応済塩基受け皿とに縁切りされている。
電気的に接続していると表面積の大きい受け皿に多くの
帯電水滴粒子がクーロン力により吸着してしまい、目的
としている酸性帯電水滴微粒子と41水酸化カルシウム
との反応による塩基固定が出来ず、多くは反応すること
無く再度有害ガスとなり煙突より大気中に拡散し、捕集
効率のダウンとなる。排ガス流中にある支持碍子表面に
酸性帯電水滴粒子が附着をさせるべく碍子に接触しない
様配慮した49円筒カバーで囲い、飛来した帯電水滴粒
子が直接52碍子に衝突するのを防ぎ、なおかつ一定時
間毎に側面穴から51ノズルで清浄水水滴を円筒ガバー
中に吹き込み、清掃を行う機能は碍子の絶縁に対し有効
に作用をする。請求項11で図1、4、にて説明する
と、有害ガスのほとんどは塩化水素であり 載台上で、水酸化カルシウムが塩化カルシウムに反応が
終えた時、正確に50%増の重量になる。一方がピン支
持になっている38受棹から伝達された負荷変化量を反
応進行のパラメーターとして捕えるのに22ロードセル
は有効に作用する。22ロードセルの替りにバネとリミ
ットスイッチの組合せも有る。図4のB〜断面で取替え
時、21載台自動取替装置の腕が39上昇、下降シリン
ダーの上昇により36載台を持ち上げると36載台は4
0プラス電極集電子から離れ電気的にOFFとなる。下
降は逆に電気的にONとなる。この様に単純な作動をス
イッチ機能として使うのは上記と同様、条件が悪い場所
では有効である。
To explain with reference to FIG. 4 in claim 10, the mounting table is electrically cut by four 52 insulators into the upper cylindrical slaked lime block mounting bed and the reacted base tray.
When electrically connected, many charged water droplet particles are adsorbed by the Coulomb force on the large surface area of the saucer, and the desired acid-based water droplet fine particles cannot be fixed with the base due to the reaction between 41 calcium hydroxide. Does not react and becomes harmful gas again and diffuses into the atmosphere from the chimney, reducing the collection efficiency. Enclosed with a 49-cylindrical cover designed to prevent acid charged water droplet particles from adhering to the surface of the supporting insulator in the exhaust gas flow, to prevent the charged water droplet particles from directly colliding with 52 insulators and for a certain period of time. The function of performing cleaning by injecting clean water droplets into the cylindrical gabber from the side holes with 51 nozzles each time effectively acts on the insulation of the insulator. Explaining in claim 11 with reference to FIGS. 1 and 4, most of harmful gas is hydrogen chloride. On the table, when the calcium hydroxide has finished reacting with the calcium chloride, the weight increases by exactly 50%. The 22 load cell effectively acts to capture the load change amount transmitted from the 38 rods, one of which is a pin support, as a parameter of reaction progress. There is also a combination of spring and limit switch instead of 22 load cell. In the section B to B of FIG. 4, the arm of the 21-table automatic changing device is raised by 39, and when the 36-cylinder is lifted by raising the descending cylinder, the 36-cable is 4
0 Positive electrode Separated from the current collector and turned off electrically. Conversely, the descent is electrically turned on. The use of such a simple operation as the switch function is effective in a place where the conditions are bad, as in the above.

【0017】[0017]

【実施例】請求項1、2について図1にて説明する。ダ
ンボールに入れられた1焼却物は2投入コンベア上のマ
ーキングされた位置に置かれる。25燃焼室の燃焼物残
量は4、5マイクロ波受発信センサーにより、監視し把
握されている。24.15GHのマイクロ波は、数枚
のシャモット系煉瓦なら透過出来、又、高周波の灼炎の
影響は受けないが、波の広がり角度が大きくビーム状に
絞る事が出来ない為、本装置の様な状況では使えなかっ
た。しかし、図7のごとく炉の左右に4、5受発器を設
置すると共に図3のC部 詳細図の様に、前面に20m
/mφの開口を持った鋼板製フードを受信器に取り付
け、あたかもビーム状にしたごとく、波の指向性を強め
る事で利用が可能となり、燃焼状況監視による自動投入
が実現した。3炉自動扉は2投入コンベアと連動する
が、システムが故障の時レール上のローラーを滑らせ手
動でも作動が出来る。6傾斜固定火格子はダクタイル鋳
鋼製で複数に分割する事で焼却物がずり落ち易くすると
同時に、焼却物の裏側にも燃焼空気が回り易い構造とし
ている。7焼却物押しプッシャーはタイマー作動し、ほ
ぐし効果と共に逐次焼却物を前方に送る。請求項3の8
不定形耐火物製火格子は図2のすでに述べたごとく、耐
火物とステンレス補助材の間に、熱膨張吸収用クリアラ
ンスを持たせており、又、長手方向の太い背骨主補強材
に対し、直角方向にある細い補強材はフープ節の役目を
し、剪断力を高めると同時に亀裂の入った場合の耐火物
を落下させずに保持する役目をする。尚、更に細かい亀
裂に対し25m/m長さ、0.2m/mφのステンレス
ワイヤーを混入し発生を防と同時に発生した場合欠落を
防ぐ効果を目的とする。これら効果により耐熱衝撃性を
持ち、高温での使用にも耐えられる不定形耐火物製火格
子が実現した。又、一本づつ段を付け設置する事で逐次
後から押されて来る焼却物をほぐし、落下させ流れを円
滑にさせる効果を生んでいる。中央部の連絡部も強度的
に相互保管的役割をすると同時に上記と同様な役目を果
たす。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Claims 1 and 2 will be described with reference to FIG. One incineration product placed in the corrugated cardboard is placed at the marked position on the two loading conveyor. The remaining amount of burned material in the 25 combustion chambers is monitored and grasped by 4, 5 microwave sensor. Microwave 24.15GH z is, can be transparent if several sheets of chamotte-based brick, also, is not affected by the high frequency of灼炎, because that can not be squeezed to spread angle of the wave is large beam-like, the apparatus It couldn't be used in situations like. However, as shown in Fig. 7, 4 and 5 receivers are installed on the left and right sides of the furnace, and 20m in front of
By attaching a steel plate hood with an opening of / mφ to the receiver and strengthening the directivity of the wave as if it were in the shape of a beam, it can be used, and automatic injection by monitoring the combustion situation has been realized. The automatic door of the 3rd furnace works in conjunction with the 2nd feeding conveyor, but when the system fails, it can be operated manually by sliding the rollers on the rails. The 6-slope fixed grate is made of ductile cast steel, and is divided into multiple pieces to make it easier for the incinerated material to slide down, and at the same time to make it easier for the combustion air to flow behind the incinerated material. 7 The incinerator pusher operates with a timer to send incinerators forward one by one with a loosening effect. Claim 8
As described above with reference to FIG. 2, the irregular-shaped refractory grate has a clearance for thermal expansion absorption between the refractory and the stainless steel auxiliary material, and also for the thick backbone main reinforcement in the longitudinal direction, The thin reinforcements at right angles act as hoop joints, increasing shear and at the same time holding the refractory in case of cracks without falling. It should be noted that the purpose of the present invention is to prevent the occurrence of cracks when fine cracks are mixed with a stainless wire having a length of 25 m / m and a diameter of 0.2 m / mφ to prevent the occurrence of cracks. Due to these effects, we have realized an irregular-shaped refractory grate that has thermal shock resistance and can withstand use at high temperatures. In addition, the installation of one step at a time creates the effect of loosening and dropping the incinerated materials that are pushed later one after another and smoothing the flow. The central communication part also plays a similar role to the above while playing a strong mutual storage role.

【0018】請求項4、5について図8、10で10a
流動床部の砂中の小さい不燃物を鋤き出す役目の9bラ
チェット櫛刃は9a灰、残渣排出プッシャー前方下側に
取り付けられており前進する時は、砂の抵抗で下に食い
込む力が働き進行方向と直角になり小さい不燃物をD部
傾斜に押し上げる。逆に戻る時は同じく砂の抵抗によ
り、砂上面を浮上がった状態となり鋤く働きはしない。
9eバースクリーンは砂中上層に埋もれた状態で9dプ
ッシャーガイドレールに先端及び尾部で固定取り付けら
れている。10d砂中ダスト吸引管は9a灰、残渣排出
プッシャー先端部に取付け各9cエアー吹出口の側を通
過させる。9aプッシャー内を通る通路はダストの沈降
を防ぐ為傾斜を持たせる。配管は図6、17(入口)に
接続する事で43イヂェクター吸引力の作用で一定マス
ナス圧力に保たれる。ダストは20aサイクロン下ダス
トボックスを経て46ダスト排出管を通り13引出しフ
ィダーに送る。47ゲート開閉ロットは全自動仕様の時
はロータリーバルブを使用する。炉内の焼却条件につい
て図1で説明すると、不完全燃焼防止及び温度制御は、
25燃焼室の出口にある27熱電対が上限900℃を感
知した時、26温度調節用水スプレーノズルが作動し、
水噴霧により温度を下げる。温度降下により25燃焼室
内の燃焼物のガス化進行が減少し、必要酸素量が24押
込み送風機の設定能力以内で納まり、酸素不足よる不完
全燃焼を防げる。主に作動させる48助燃バーナーには
10a流動床部の物を使う。この部分では燃焼はほとん
ど済んでおり、供給された燃焼用酸素は大部分消費され
ず上部燃焼帯で使われる。又、炉内温度を900℃〜8
00℃にコントロールする事はダイオキシン及びNO
の発生を押える。43イヂェクターにより炉内、煙道を
常時マイナス圧に保ち24押込み送風機とのバランスを
とる平衡通風方式としている。
Regarding Claims 4 and 5, 10a in FIGS.
The 9b ratchet comb blade, which works to plow out small incombustibles in the sand of the fluidized bed, is attached to the 9a ash, residue discharge pusher front lower side, and when moving forward, the force of the sand to cut in works It becomes perpendicular to the direction of travel and pushes up small incombustibles to the D section inclination. On the contrary, when returning, the resistance of the sand causes the surface of the sand to float and does not work as a plow.
The 9e bar screen is fixedly attached to the 9d pusher guide rail at the tip and the tail while being buried in the upper layer of sand. The 10d sand dust suction pipe is attached to the tip of the 9a ash and residue discharge pusher, and is passed through the 9c air outlet side. The passage passing through the 9a pusher has an inclination to prevent sedimentation of dust. By connecting the piping to the inlets shown in FIGS. 6 and 17, the pressure of 43 ejectors can be maintained so that the pressure is constant. The dust passes through the dust box under the 20a cyclone, passes through the 46 dust discharge pipe, and is sent to the 13-drawer feeder. A rotary valve is used for a 47-gate open / close lot when fully automatic. Explaining the incineration conditions in the furnace with reference to FIG. 1, incomplete combustion prevention and temperature control are
When the thermocouple 27 at the exit of the 25 combustion chamber senses the upper limit of 900 ° C, the water spray nozzle 26 for temperature control operates,
Lower the temperature by spraying with water. Due to the temperature drop, the progress of gasification of the combustion products in the 25 combustion chambers is reduced, and the required oxygen amount is kept within the set capacity of the 24 insufflation blower, which prevents incomplete combustion due to lack of oxygen. For the 48 auxiliary combustion burners which are mainly operated, the thing of 10a fluidized bed is used. Most of the combustion is completed in this part, and most of the supplied combustion oxygen is not consumed and is used in the upper combustion zone. Moreover, the temperature in the furnace is 900 ° C to 8
Controlling the temperature to 00 ℃ is dioxin and NO x
Suppress the occurrence of. A 43-injector keeps the flue inside the furnace at a negative pressure all the time, and uses a balanced ventilation system that balances with a 24 pusher fan.

【0019】請求項6について図3、6にて説明する
と、14溶融炉の排ガスを使った予熱は、17排ガスバ
イパス(出口)からダンパを開いた35予熱用排ガスバ
イパス(入口)に戻す。14溶融炉への30灰、残渣投
入は34溶融炉投入蓋シリンダーで、炉扉を開け13引
出しフィダーを4、5マイクロ波受発信機の上限レベル
満杯信号が出る迄作動させる。ただし、13引出しフィ
ダーの作動は上限信号感知可能とする為、30灰、残渣
の落下を連続させないタクト運転とする。このレベルセ
ンサーとしての使用も炉自動投入と同様に5マイクロ波
受信部に鋼板製フードを付け、波の指向性を高める事で
可能となった温度プログラミングされた28ヂェットバ
ーナー火炎は、29溶融容器と14溶融炉内壁との空間
を31金属底床のみを直接加熱し、同時に他ヶ所は間接
加熱して複数回廻り閉じられた投入蓋中心出口から13
引出しフィダーに残されている31灰残渣を予備加熱
し、サイクロンの17排バイパス(入口)へ抜けてい
く。31金属底床はバーナー火炎で直接加熱されてお
り、これに29溶融容器内で乗っている30灰、残渣の
内で加熱され、融点に達したものは31金属底床上を経
て32溶融物オーバフロー出口から流出する。途中、溶
融物は33急冷用ノズルからの噴射により急冷粉砕され
て図1の15スラッヂ搬送コンベアにて、16スラッヂ
溜箱に集められる。最後に、金属類が流出し元の31金
属底床だけが残る空状態の炉温(1550℃以上)を2
7熱電対が感知して、再度30灰、残渣投入の動作を1
2灰、残渣溜ホッパーが空になる迄繰り返す。請求項7
について排ガスの流れは図6で説明すると25燃焼室か
ら18a本再燃室に入り、18b副再燃室、20aサイ
クロンを経由して図1、4の53コロナ放電排ガスイオ
ン化装置に行く。再燃室の飛散ダストは重力沈降により
44再燃室沈降ダストに戻し管入口部に集積される。こ
れとサイクロンダストボックス下部に集積されたダスト
を炉停止時に45ダストシールゲート、46ダスト排出
管を経て13引出しフィダーに行き溶融される。47ゲ
ート開閉ロットはエアーシール電動バルブにより自動化
も可能である。
When claim 6 is described with reference to FIGS. 3 and 6, the preheating using the exhaust gas of the 14 melting furnace is returned from the 17 exhaust gas bypass (outlet) to the 35 preheating exhaust gas bypass (inlet) where the damper is opened. In order to load 30 ash and residue into 14 melting furnaces, use the 34 melting furnace charging lid cylinder, open the furnace door, and operate 13 drawer feeder until the upper level full signal of 4,5 microwave receiver / transmitter is output. However, since the operation of the 13-drawer feeder can detect the upper limit signal, the tact operation is performed so as not to continuously drop the 30 ash and residue. As with the automatic furnace charging, this level sensor is also equipped with a steel plate hood at the 5 microwave receiving part, and the temperature programmed 28 jet burner flame made possible by increasing the directivity of the wave is melted 29 times. The space between the vessel and the inner wall of the melting furnace 14 is heated directly at the metal bottom floor 31 at the same time as the other floor is indirectly heated at the same time.
The 31 ash residue remaining in the drawer feeder is preheated and discharged to the cyclone 17 exhaust bypass (inlet). 31 The metal bottom bed is directly heated by the burner flame, 29 is heated in the melting vessel, 29 ash and residue, and the one reaching the melting point passes through 31 metal bottom bed and 32 melt overflows Outflow from the exit. On the way, the melt is rapidly cooled and pulverized by the injection from the 33 quenching nozzle, and is collected in the 16 sludge storage box by the 15 sludge transfer conveyor in FIG. Finally, the furnace temperature (1550 ° C or higher) in an empty state in which the metals flow out and only the original 31 metal bottom floor remains
7 thermocouple senses again, 30 ash, 1 operation of residue input
2 Repeat until the ash and residue reservoir hoppers are empty. Claim 7
The flow of the exhaust gas will be explained with reference to FIG. 6 from the 25th combustion chamber to the 18a main reburning chamber, then to the 53b corona discharge exhaust gas ionizer of FIGS. 1 and 4 via the 18b sub-reburning chamber and the 20a cyclone. The scattered dust in the reburn chamber is accumulated at the inlet of the return pipe into the settled dust in the 44 reburn chamber by gravity settling. This and the dust accumulated in the lower part of the cyclone dust box are melted by going to the 13 drawer feeder through the 45 dust seal gate and the 46 dust discharge pipe when the furnace is stopped. The 47-gate open / close lot can be automated with an air-sealed electric valve.

【0020】請求項8を図9で説明すると、20サイク
ロンからの排ガスは53コロナ放電排ガスイオン化装置
の60コロナ放電帯を通過する。コロナ放電装置の構造
は、複数の55正六角形正電極の組合せにより電極を煙
道に隙間なく配置出来、又それらの中心に六角形各辺に
正対した六っの刃物状平板を持った54負放電極を設け
る事で煙道断面にくまなく広がる60放電帯を作るのを
可能とした。これにより煙道を通る排ガスは洩れなく6
0コロナ放電帯を通り発生した帯電粒子を取り込み、5
9帯電粒子流煙道を経て反応室に向かう。57,58は
負正電極の支持材である。51アトマイヂングノズルに
よる水滴微粒子直径を10〜40μmの大きさに作る。
理由の第1は水滴微粒子が10μmを超えると急激にイ
オンとの衝突機構による荷電数μが増加し後接の41消
石灰中空ブロックへの被クーロン力吸着が増す。第2は
帯電微粒子が55正電極へ引かれる移動速度をこれに直
角に煙道に沿い移動する排ガス速度より大巾に遅くする
事により、正六角筒形状長さを最小限にした55正電極
により生成したマイナス帯電粒子の55正電極へのクー
ロン力吸着を避けられる。これにより、発生したほとん
どの帯電粒子を排ガス中帯電粒子流に取り込み使える事
になる。実際にコロナ放電帯で帯電した粒子について、
コロナ放電マイナス極から正電極までの速度を計算す
る。粒子は平均大きさをとり25μmとする。 排ガス速度を1m/secとし51アトマイジングノズ
ルにより水滴粒子に加えられる加速度を条件に入れない
で合成速度ベクトル(V′)で表わしたのが図9、C〜
C断面上部である。55正電極の正六角筒L寸法がV′
との比例極数で十分に長いと、帯電粒子はEP集塵装置
の集塵極のごとく作用し正電極に全て吸着されてしまう
不都合が生じる。53コロナ放電装置に入る時の排ガス
温度は図6サイクロン出口20b空気取り入口からの空
気で約600℃に下げられ、更に図9、51アトマイヂ
ングノズル噴射一部水滴気化熱により200〜300℃
になるが、高温ほど発生条件が良いコロナ放電によるイ
オン化は既に熱運動が十分激しい状態でガスのイオン化
が著しく促進されており、51アトマイヂングノズル噴
射での温度低下によりイオンの発生が減少する事は無
い。ダイオキシンは600℃前後で最も発生しやすく又
排ガス中ダストに附着する。一時排ガス温度を600℃
にして発生を防げなかったダイオキシンがダストに附着
させ後接装置で捕集するダストに附着させる効果を目的
としている。又、51アトマイヂングノズルと20b空
気取り入から供給酸素は、コロナ放電部で積極的にオゾ
ン発生させNO除却に使う目的である。4押込送風気
での酸素は既に燃焼用として使用されて排ガス中には少
なくなっている理由による。オゾンの役目はNO中の
水に溶けない一酸化窒素(NO)を水溶性の二酸化窒素
に酸化させる事にある。焼却炉及び溶融炉排ガス中の9
0〜95%はNOであり、残り5〜10%はNOであ
る。NO、N、Nはほとんど無い。 NO+O →NO+O NOが59帯電粒子流煙道で帯電水滴微粒子と衝突し
易く帯電水溶液粒子となる。これが反応室に入り、41
消石灰中空円筒にクーロン力により吸着され、反応して 2Ca(OH)+4NO→2Ca(NO+2
O+O 塩基として固定され36消石灰中空円筒載台の受け皿に
落下する。同様に亜硫酸ガスは帯電硫酸水滴微粒子とな
り反応室で Ca(OH)+HSO→CaSO+2HO 石膏のかたちで塩基固定される。消石灰と反応前の電解
液で温潤されている41消石灰中空円筒表面には、一時
的に消石灰と未反応のHSOが有る。これとN
が反応する。 HSO+N(NO+NO)→2NOHSO
+HO ニトロシル硫酸として固定される。有害ガスの大部分は
塩化水素であり Ca(OH)+2HCl→CaCl+2HO 塩化カルシウムで塩基固定される。反応後の塩化カルシ
ウムは自重と上部51スプレーノズルにより掻き落とさ
れ、36載台の受け皿に溜まる。新規取替え時の50%
重量増になった時、22ロードセルは38載台受棹を通
して重量変化を感知する。図4で炉が稼動中であって
も、22ロードセルより反応終了の信号が出ると37反
応室扉が開き、21自動取替装置本体の爪が50反応室
出入りシリンダー作動により最大ストロークまで42反
応室内に伸ばす。この時点で40b移載コンベア上には
何も無い。次に39上昇、下降シリンダーの上昇作動に
より21自動取替装置本体の爪が36載台を持ち上げ
る。これにより36載台は38載台受棹及び40プラス
電極集電子上方に離れ、電気接続が0FFとなると同時
に22ロードセル感知も無負荷となる。50反応室出入
シリンダーの縮作動と39上昇、下降シリンダーの下降
により36載台は40b移載コンベア上に乗り、21自
動取替装置本体からはフリー状態となる。40a反応前
消石灰ストレージコンベア、40b移載コンベアと40
c反応済消石灰ストレージコンベアを同時に矢印方向へ
作動させる事で、反応済消石灰の36載台は40c反応
済消石灰ストレージに移動し、反応前の41消石灰中空
円を乗せた36載台40b移載コンベアに呼び込まれ
る。次に39上昇、下降シリンダーの上昇作動と50反
応室出入シリンダーの伸作動により36載台は40b移
載コンベア上から42反応室に移動させられる。39上
昇、下降シリンダーの下降作動で41消石灰中空円筒、
36載台は40プラス電極集電子、38載台受棹に移載
される事で電気接続ONとなると同時に22ロードセル
にも感知される。50反応室出入シリンダーが縮み作動
し、37反応室扉が閉じて取替作動が完了する。40
a,40cの角ストージコンベアは、予めセットしてお
くストレージ載台の数に沿って任意の長さにする事が可
能である。上部と側面に取り付けられている51反応室
ノズルは3つの役目を持つ。第1は、加圧水滴を41消
石灰中空円筒の表面及び内面にぶつける事で、既に反応
済の塩基を下部受け皿に強制的に掻き落とし、絶えず未
反応面をさらさせ、反応効率を上げる事にある。第2は
41消石灰中空円筒と36載台を絶えず温潤状態にさせ
ておき40プラス電極集電子から電圧を加えられて、絶
縁されている受け皿を除き全体をプラス電極化させる事
にある。41消石灰中空円筒ブロックに含入された微量
塩化ナトリウムは湿潤により電解液となり表面を覆う事
となり、同時に帯電酸性水滴粒子の衝突は通電を更にし
易くし電極としての機能が高まり更に多くの帯電酸性微
粒子を吸着し、反応効率を高める事になる。第3は51
ノズル水滴と吸着された帯電酸性水滴粒子により出来る
湿潤膜は41消石灰中空円筒に発生している細かい亀裂
の内部に浸透し、表面だけでなく内部での反応もする事
になり、反応効率を高める事になる。
Explaining claim 8 with reference to FIG. 9, the exhaust gas from the 20 cyclone passes through the 60 corona discharge zone of the 53 corona discharge exhaust gas ionizer. The structure of the corona discharger is such that the electrodes can be arranged in the flue without gaps by combining a plurality of 55 regular hexagonal positive electrodes, and at the center of them, there are six blade-shaped flat plates facing each side of the hexagon. By providing a negative discharge electrode, it became possible to create a 60 discharge band that spreads all over the flue cross section. As a result, the exhaust gas passing through the flue will not leak 6
Incorporates charged particles generated through 0 corona discharge zone, 5
9 Toward the reaction chamber via the charged particle flow flue. Reference numerals 57 and 58 are support materials for the negative and positive electrodes. 51 Atomizing nozzle is used to make the diameter of water droplets to be 10-40 μm.
The first reason is that when the water-droplet fine particles exceed 10 μm, the number of charges μ due to the collision mechanism with ions rapidly increases, and the adsorption of Coulomb force on the post-contact 41 slaked lime hollow block increases. The second is 55 positive electrode in which the length of the regular hexagonal cylinder is minimized by making the moving speed of the charged fine particles drawn to the 55 positive electrode much slower than the exhaust gas speed moving along the flue at right angles to the 55 positive electrode. It is possible to avoid the adsorption of Coulomb force of the negatively charged particles generated by the method onto the 55 positive electrode. As a result, most of the generated charged particles can be taken in and used in the flow of charged particles in the exhaust gas. For particles actually charged in the corona discharge band,
Calculate the velocity from the negative pole to the positive electrode of the corona discharge. The particles have an average size of 25 μm. The exhaust gas velocity is set to 1 m / sec, and the acceleration applied to the water droplet particles by the 51 atomizing nozzle is represented by the synthetic velocity vector (V ') without considering the conditions in FIGS.
It is the upper part of C section. 55 Regular electrode hexagonal cylinder L dimension is V '
If the number of poles proportional to is sufficiently long, the charged particles act like dust collecting electrodes of the EP dust collector and are all adsorbed to the positive electrode. 53 The temperature of the exhaust gas when entering the corona discharge device is lowered to about 600 ° C. by the air from the cyclone outlet 20b air intake port in FIG.
However, the higher the temperature is, the better the generation condition is. The ionization by corona discharge has already promoted the ionization of gas significantly in the state where the thermal motion is already vigorous, and the generation of ions is reduced due to the temperature drop at 51 atomizing nozzle injection There is nothing. Dioxins are most likely to be generated at around 600 ° C and adhere to dust in exhaust gas. Temporary exhaust gas temperature of 600 ℃
The purpose is to attach dioxin, which could not be prevented from being generated in the above manner, to the dust and to the dust collected by the post-contact device. Further, the oxygen supplied from the 51 atomizing nozzle and the air intake of 20b is for the purpose of positively generating ozone in the corona discharge part and using it for NO x removal. 4 Oxygen in forced air is already used for combustion and is reduced in exhaust gas. The role of ozone is to oxidize water-insoluble nitric oxide (NO) in NO x to water-soluble nitrogen dioxide. 9 in incinerator and melting furnace exhaust gas
0 to 95% is NO, and the remaining 5 to 10% is NO 2 . NO 3, N 2 O 4, N 2 O 5 is little. NO + O 3 → NO 2 + O 2 NO 2 easily collides with charged water droplet fine particles in the 59 charged particle flow flue to become charged aqueous solution particles. This enters the reaction chamber, 41
It is adsorbed by the Coulomb force to the slaked lime hollow cylinder and reacts to react with 2Ca (OH) 2 + 4NO 2 → 2Ca (NO 2 ) 2 +2
It is fixed as H 2 O + O 2 base and falls onto the saucer of the 36 slaked lime hollow cylinder mount. Similarly, sulfurous acid gas becomes charged sulfuric acid water droplets and is fixed in the reaction chamber in the form of Ca (OH) 2 + H 2 SO 4 → CaSO 4 + 2H 2 O gypsum. On the surface of the 41 slaked lime hollow cylinder that has been warmed with the slaked lime and the electrolytic solution before the reaction, there is temporarily H 2 SO 4 that has not reacted with the slaked lime. This and N 2 O
3 reacts. H 2 SO 4 + N 2 O 3 (NO + NO 2 ) → 2NOHSO
It is fixed as 4 + H 2 O nitrosyl sulfate. Most of the harmful gas is hydrogen chloride, and Ca (OH) 2 + 2HCl → CaCl 2 + 2H 2 O calcium chloride is base-fixed. The calcium chloride after the reaction is scraped off by its own weight and the upper 51 spray nozzles, and is collected in the receiving tray of 36 mounts. 50% of new replacement
As the weight increases, the 22 load cell senses the weight change through the 38 platform support. Even if the furnace is operating in Fig. 4, when the reaction completion signal is output from the 22 load cell, the 37 reaction chamber door opens, and 21 the claw of the automatic changer body moves in and out of the 50 reaction chamber, and 42 reactions up to the maximum stroke due to cylinder operation. Extend it indoors. At this point, there is nothing on the 40b transfer conveyor. Next, the pawls of the main body of the automatic replacement device 21 lift up the mounting table by the raising operation of the raising and lowering cylinder 39. As a result, the 36 mount is separated above the 38 mount receiver and the 40 plus electrode current collector, and the electrical connection becomes 0FF, and at the same time, the 22 load cell sensing becomes unloaded. By the contraction operation of the reaction chamber inlet / outlet cylinder 50, the ascent of 39, and the lowering of the descending cylinder, the 36 platform is placed on the 40b transfer conveyor, and the 21 automatic changer main body becomes free. 40a pre-reaction slaked lime storage conveyor, 40b transfer conveyor and 40
By simultaneously operating the c-reacted slaked lime storage conveyor in the direction of the arrow, the 36-placed table of the reacted slaked lime moves to the 40c-reacted slaked lime storage, and the 36-placed table 40b transfer conveyor on which the 41 slaked lime hollow circle before the reaction is placed Be called into. Next, the 36 platform is moved from the 40b transfer conveyor to the 42 reaction chamber by the raising operation of the 39 raising / lowering cylinder and the extending operation of the 50 reaction chamber loading / unloading cylinder. 39 Ascending / descending cylinder descending operation 41 slaked lime hollow cylinder,
The 36 platform is transferred to the 40 electrode collector and the 38 platform receiver, so that the electrical connection is turned on and at the same time, the 22 load cell senses it. The 50 reaction chamber inlet / outlet cylinder contracts, the 37 reaction chamber door closes, and the replacement operation is completed. 40
The square storage conveyors a and 40c can be set to an arbitrary length according to the number of storage stands to be set in advance. The 51 reaction chamber nozzles mounted on the top and sides serve three functions. The first is to hit the surface and the inner surface of the 41 slaked lime hollow cylinder with a pressurized water drop to forcibly scrape the already-reacted base onto the lower tray to constantly expose the unreacted surface and improve the reaction efficiency. . Secondly, the 41 slaked lime hollow cylinder and 36 mounting table are kept in a constantly warmed state, and a voltage is applied from the 40 positive electrode current collector to make the whole positive electrode except for the insulated saucer. 41 A small amount of sodium chloride contained in the slaked lime hollow cylindrical block becomes an electrolytic solution by wetting and covers the surface, and at the same time, the collision of charged acidic water droplet particles makes it easier to conduct electricity and enhances the function as an electrode. Adsorbs fine particles and enhances reaction efficiency. Third is 51
The wet film formed by the nozzle water droplets and the charged acidic water droplet particles adsorbed penetrates into the fine cracks generated in the 41 slaked lime hollow cylinder and causes not only the reaction on the surface but also on the inside, increasing the reaction efficiency. It will be a matter.

【0021】[0021]

【発明の効果】請求項1でセンサーによる全自動焼却シ
ステムは、専門担当が不要で運転出来、投入コンベア上
の印された荷位置にダンボールに入れた焼却物を置くだ
けで焼却は進行する故、看護婦、厨房の調理担当等の人
で容易に稼動出来る効果がある。又、有害ガス、ダスト
を除去出来る為、都市密集地での使用に耐えられる効果
がある。請求項2でマイクロ波センサーと熱電対で常時
炉を管理する機能は、炉内をプロブラミング条件に沿っ
て焼却物を安定燃焼させるが、これは人による目視と違
いロスが無い。常時炉の100%能力の稼動効果と、焼
却物発熱カロリー変化に追従してスイッチの切り、入れ
をする事で助燃バーナーの無駄炊きを無くした省エネル
ギー効果を生む。請求項3について、この火格子が使わ
れる場所は前段階で燃焼しきれず、ほぐしながら炉内燃
焼物送りプッシャーにより押されて来た注射針、ビン内
血液、オムツ等の燃焼しにくい焼却物を受ける、最も高
温を必要とする本燃焼部である。本発明火格子により
上、下からの助燃バーナーにより必要とする、高温で長
時間の使用する事が可能となった。請求項4、5につい
て本発明の灼熱したビン、発生クリンカー等不燃物をバ
ースクリーンにより、砂上層に浮かす構造の流動床部を
炉後燃として設置する事により、前の火格子隙間から落
下した未燃の臓器油脂、軟化及び融けて垂れ落ちた高分
子樹脂類、血液等の液体類の完全燃焼を効率良く進める
効果がある。又、進行方向に振動を与える機能を持った
プッシャーにより、静的荷重では食い込んだ状態になっ
てしまうからみ合った残渣でも容易に破砕し排出出来る
効果がある。砂中に入った櫛刃は振動が加えられる事に
より、押込みエアーで浮動している砂を更に櫛刃の間か
ら通り抜け易くし不燃物を鋤き分ける効果が上がる。砂
層の上に浮いた細かい灰は、灰残渣プッシャーにより、
又砂中の細かい灰は砂中ダスト吸引管と同時に二つの手
段で砂から分離される事でこれらは篩いと全く同一の機
能を持つ事となり従来の流動床炉の様に炉外にコンベア
と篩いを設置する必要はなくなり、コストの安い流動床
の実現となった。又、流動床部設置による燃焼効率の上
昇は灰、残渣に耐高温性ウイルスの残存する可能性の未
燃の固まりが残る事なく灰残渣溶融前で既に感染性医療
廃棄物を完全滅菌する効果を生む。請求項6の本発明に
よる灰残渣溶融炉は、灰、ビン、金属類を事前に分別す
る事なしに同時に溶融が可能であり、又自動運転での融
点温度管理により、ガラス類(900〜1100℃)、
灰(1200℃)、注射針等ステンレス(1400〜1
450℃)、刃物類炭素鋼(1500〜1550℃)等
の種類ごとに建材用スラッヂ、金属材料等として容易に
取り出せる効果がある。この種類別に灰、残渣をスラッ
ヂ化するのは、資源の再利用であると共に感染性医療廃
棄物の完全滅菌効果を目的としたものである。請求項7
についての説明は再燃室とサイクロンを同時内蔵させる
事で装置全体を小型に出来、又、沈降ダストを人が直接
手に触れる事無く溶融処理出来る効果がある。又サイク
ロンによるダスト一次捕捉は後接のコロナ放電への負荷
を減じる効果もある。
According to the first aspect of the invention, the fully automatic incineration system using the sensor can be operated without the need for a specialized person, and the incineration progresses only by placing the incinerated matter in the cardboard at the marked load position on the input conveyor. , A nurse, a person in charge of cooking in the kitchen, etc. can easily operate. In addition, since it can remove harmful gases and dust, it has the effect of withstanding use in dense urban areas. In the second aspect, the function of constantly controlling the furnace with the microwave sensor and the thermocouple burns the incinerator in a stable manner in the furnace according to the programming condition, but this does not cause a loss unlike the human visual inspection. The operation effect of 100% capacity of the furnace at all times and the energy saving effect by eliminating the waste cooking of the auxiliary combustion burner are produced by switching on and off according to the change in calorific value of the incinerated material. According to claim 3, the place where this grate is used cannot be completely burned in the previous stage, and the incinerated substances such as the injection needle, the blood in the bottle, and the diaper, which are pushed by the in-furnace combustion product feeding pusher while being loosened, are difficult to burn. This is the main combustion unit that receives the highest temperature. The grate of the present invention makes it possible to use it at a high temperature for a long time, which is required by an auxiliary burner from above and below. Claims 4 and 5: The burning bed of the present invention, the non-combustible material such as the generated clinker, were dropped by the bar screen from the front grate gap by installing the fluidized bed part of the structure floating on the sand upper layer as the post combustion furnace. It has an effect of efficiently promoting complete combustion of unburned organ oils and fats, polymer resins softened and melted, and liquids such as blood. Further, the pusher having a function of giving vibration in the traveling direction has an effect that it can be easily crushed and discharged even if the residue is entangled with static load. By vibrating the comb blade that has entered the sand, the sand that is floating by the pushing air can more easily pass through between the comb blades, and the effect of separating the incombustibles with the plow is improved. Fine ash floating on the sand layer is removed by the ash residue pusher.
Also, fine ash in the sand is separated from the sand by two means at the same time as the dust suction pipe in the sand, so that these have exactly the same function as the sieve, and as in the conventional fluidized bed furnace, they are used outside the furnace as a conveyor. It became unnecessary to install a sieve, and a low cost fluidized bed was realized. In addition, the increase in combustion efficiency due to the installation of the fluidized bed part is the effect of completely sterilizing infectious medical waste before melting the ash residue without leaving unburned lumps that may leave high temperature resistant virus in the ash and residue. Give birth. In the ash residue melting furnace according to the present invention of claim 6, ash, bottles and metals can be melted at the same time without prior separation, and glass (900-1100) can be controlled by melting point temperature control by automatic operation. ℃),
Ash (1200 ℃), injection needle stainless steel (1400-1
450 ° C.), cutlery carbon steel (1500 to 1550 ° C.), and the like have the effect that they can be easily taken out as building material sludge, metal materials, and the like. Sludge of ash and residue by type is to reuse resources and to completely sterilize infectious medical waste. Claim 7
As for the explanation, there is an effect that the whole equipment can be made compact by incorporating the reburn chamber and the cyclone at the same time, and the sedimentation dust can be melted without human touch. The primary capture of dust by a cyclone also has the effect of reducing the load on the corona discharge at the rear.

【0022】請求項8についてすでに説明して来たよう
に、塩化水素には洗煙水処理装置、及び微紛消石灰吹込
み装置、ダスト粒子にはバックフィルター装置、EP集
塵装置、SOには脱硫装置、NOには脱硝装置と除
去を目的とする装置を設置せざるを得なかった。本発明
によりこれ等機能を一つの装置に収斂させる事が可能と
なった為、従来大型炉専用設備であったこれ等を低コス
ト化が実現した事により小型炉にも容易に取り付けられ
る効果を生んだ。同様に中型都市ごみ焼却炉にもスケー
ルアップした場合でも低コストにより容易に適用出来る
排ガス処理装置が実現した。又、有害ガスの捕促効率が
大巾に高くなった事により、塩化ビニール専用炉にも水
処理装置と組合わさなくとも使える効果がある。請求項
9について本発明はV字形溝を円筒内外面に設けた事に
より、重量当たりの表面積が大きく、自動取替装置反応
室容積を大巾に小型にする事が可能となった。微量塩化
ナトリウムの含入と湿潤効果により、本来電気を通さな
い消石灰ブロックをあたかも導体のごとく作用させて電
極の機能を持たせ、又、同じ酸とアルカリとの反応で塩
基生成させる手段であっても、従来設備とは異いバクフ
ィルター、EP集塵機、水処理装置が不要にする効果も
ある。請求項10についてすでに述べた様に表面の湿潤
電解溶液の効果より上に乗っている消石灰中空円筒ブロ
ックと電気的に接続させる事で、載台は消石灰中空円筒
ブロック全体をブラス電極にさせる効果がある。又、電
気的に碍子で絶縁されている下部受け皿は反応済塩基を
こぼさず保持する事で、反応進歩状況を正確にロードセ
ルに感知させる効果がある。請求項11ですでに述べた
通り、反応進行状況を常時ロードセルにより捕えている
構造により、反応済消石灰を炉の稼動中でも冷却を必要
とせず新規のものと交換出来る効果がある。この冷却を
必要とせず瞬時に自動取替えする機能は、前記の機能と
組合させて消石灰の消費が激しい塩化ビニール専用炉に
も導入出来る効果がある。以上述べて来た様に本発明の
効果は小型炉に限らず都市ごみ焼却炉等の中大型焼却炉
にも適用できる。
As has already been described for claim 8, a smoke-washing water treatment device and a fine lime blowing device for hydrogen chloride, a back filter device for dust particles, an EP dust collector, and SO x . Had to install a desulfurization device, and a NOx removal device for NO x and a device for removal. Since the present invention makes it possible to converge these functions into a single device, it is possible to easily attach them to a small-sized furnace by realizing the cost reduction of the conventional large-scale furnace dedicated equipment. Born Similarly, an exhaust gas treatment device has been realized that can be easily applied at low cost even when scaled up to a medium-sized municipal solid waste incinerator. In addition, since the efficiency of trapping harmful gases is greatly increased, it is possible to use it in a vinyl chloride furnace without combining it with a water treatment device. Claim 9 In the present invention, since the V-shaped groove is provided on the inner and outer surfaces of the cylinder, the surface area per weight is large, and the reaction chamber volume of the automatic replacement device can be greatly reduced. Due to the inclusion of a trace amount of sodium chloride and the wetting effect, a slaked lime block, which originally does not conduct electricity, acts as if it were a conductor and has the function of an electrode, and it is a means to generate a base by the reaction between the same acid and alkali. However, unlike the conventional equipment, it also has the effect of eliminating the need for a tap filter, an EP dust collector, and a water treatment device. As already described in claim 10, by electrically connecting with the hydrated lime hollow cylindrical block that is above the effect of the wet electrolytic solution on the surface, the mounting table has the effect of making the entire hydrated lime hollow cylindrical block the brass electrode. is there. In addition, the lower tray, which is electrically insulated by the insulator, holds the reacted base without spilling it, so that the load cell can accurately detect the progress of the reaction. As already described in claim 11, due to the structure in which the progress of the reaction is always captured by the load cell, there is an effect that the reacted slaked lime can be replaced with a new one without cooling even during the operation of the furnace. This automatic automatic replacement function without the need for cooling has the effect of being combined with the above-mentioned functions and can be introduced into a furnace for exclusive use of vinyl chloride, which consumes a lot of slaked lime. As described above, the effects of the present invention can be applied not only to small-sized furnaces but also to medium-sized and large-sized incinerators such as municipal solid waste incinerators.

【0023】[0023]

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

【図1】 図1は焼却システムの全体配置図である。FIG. 1 is an overall layout of an incineration system.

【図2】 図2は不定型耐火物製火格子の組立図であ
る。
FIG. 2 is an assembly drawing of an irregular refractory grate.

【図3】 図3は灰、残渣溶融炉装置及びマイクロ波
レベル計配置図である。
FIG. 3 is a layout view of an ash, a residue melting furnace device and a microwave level meter.

【図4】 図4はコロナ放電装置、反応室、消石灰中
空円筒載台自動取替装置の配置図である。
FIG. 4 is a layout view of a corona discharge device, a reaction chamber, and a slaked lime hollow cylindrical platform automatic replacement device.

【図5】 図5は消石灰中空円筒ブロック全体図であ
る。
FIG. 5 is an overall view of a slaked lime hollow cylindrical block.

【図6】 図6は本再燃室、副再燃室、サイクロン、
沈降ダストリターン、及び排ガスバイパスダクト等の組
立図である。
FIG. 6 is a main reburn chamber, a sub-reburn chamber, a cyclone,
It is an assembly drawing of a settling dust return, an exhaust gas bypass duct, and the like.

【図7】 図7はマイクロ波センサーによる炉内焼却
物検出の配置図である。
FIG. 7 is a layout view of incinerator detection by a microwave sensor.

【図8】 図8は灰残渣押プッシャー設置図である。FIG. 8 is an installation view of an ash residue pushing pusher.

【図9】 図9はコロナ放電による帯電粒子発生装置
である。
FIG. 9 shows a charged particle generation device by corona discharge.

【図10】 図10は灰、残渣排出プッシャー及び流動
床部配置図である。
FIG. 10 is a layout of ash, residue discharge pusher and fluidized bed section.

【0024】[0024]

【符号の簡単な説明】[Simple explanation of symbols]

1.ダンボールに入れられた焼却物 2.自動投入コン
ベア 3.炉自動扉 4.マイクロ波発
信器 5.フード付マイクロ波受信器 6.傾斜固定火格
子 7.焼却物押プッシャー 8.不定型耐火物
火格子 9a.灰、残渣排出プッシャー 9d.プッシャガ
イドレール 9b.ラチェット櫛刃 9e.バースクリ
ーン 9c.エアー吹出し口 10a.流動床部 10b.排出扉 10c.プッシャ
ー連動扉ロット 10d.砂中ダスト吸引管 11.灰、残渣コ
ンベア 12.灰、残渣溜ホッパー 13.引出しフィ
ダー 14.溶融炉 15.スラッヂ搬
送コンベア 16a.スラッヂ溜箱 16b.スラッヂ
仕分用コンベア 17.排ガスバイパス 18a.本再燃室 18b.副再燃室 19.熱交換器 20a.サイクロン集塵装置 20b.空気取入
口 21.自動取替装置本体 22.塩化水素反
応済検出用ロードセル 23.煙突 24.押込送風機 25.燃焼室 26.温度調整用
水スプレーノズル 27.熱電対 28.ヂェットバ
ーナ 29.溶融容器 30.灰、残渣 31.金属底床部 32.溶融物オーバーフロー出口(掃除 33.急冷用ノズル 口兼用) 34.溶融炉投入蓋シリンダー 35.予熱用排ガ
スバイパス煙道 36.載台 37.反応室扉 38.載台受棹 39.上昇、下降
シリンダー 40.プラス電極集電子 40a.反応前消
石灰ストレージコンベア 40b.移載コンベア 40c.反応済消
石灰ストレーヂコンベア 41.消石灰中空円筒 42.反応室 43.イヂェクター 44.再燃室沈
降ダスト戻し管 45.ダストシールゲート 46.ダスト排
出管 47.ゲート開閉ロット 48.助燃バー
ナ 49.帯電水滴粒子附着防止カバー 50.反応室出
入シリンダー 51.アトマイヂングノズル 52.碍子脚 53.コロナ放電排ガスイオン化装置 54.コロナ放
電 マイナス電極 55.コロナ放電 プラス電極 56.逆帯電粒
子吸収翼 57.マイナス電極支持材 58.プラス電
極支持材 59.帯電粒子流煙道 60.コロナ放
電帯 61.振動発生機
1. Incinerated matter in cardboard 2. Automatic loading conveyor 3. Automatic furnace door 4. Microwave transmitter 5. Microwave receiver with hood 6. Fixed fixed grate 7. Incinerated matter pusher 8. Atypical refractory grate 9a. Ash, residue discharge pusher 9d. Pusher guide rail 9b. Ratchet comb blade 9e. Bar screen 9c. Air outlet 10a. Fluidized bed 10b. Discharge door 10c. Pusher interlocking door lot 10d. Dust suction tube in sand 11. Ash, residue conveyor 12. Ash, residue reservoir hopper 13. Drawer feeder 14. Melting furnace 15. Sludge conveyor 16a. Sludge storage box 16b. Sludge sorting conveyor 17. Exhaust gas bypass 18a. This reburn chamber 18b. Secondary reburn chamber 19. Heat exchanger 20a. Cyclone dust collector 20b. Air intake 21. Automatic replacement device body 22. Hydrogen chloride reacted detection load cell 23. Chimney 24. Push blower 25. Combustion chamber 26. Water spray nozzle for temperature adjustment 27. Thermocouple 28. Jet Burner 29. Melting container 30. Ash, residue 31. Metal bottom floor 32. Melt overflow outlet (cleaning 33. Rapid cooling nozzle also serves as outlet) 34. Melting furnace charging lid cylinder 35. Exhaust gas bypass flue for preheating 36. Stand 37. Reaction chamber door 38. Mounting stand 39. Ascending and descending cylinder 40. Positive electrode current collector 40a. Pre-reaction slaked lime storage conveyor 40b. Transfer conveyor 40c. Reacted slaked lime storage conveyor 41. Slaked lime hollow cylinder 42. Reaction chamber 43. Ejector 44. Reburning chamber Settling dust return pipe 45. Dust seal gate 46. Dust discharge pipe 47. Gate opening / closing lot 48. Burning burner 49. Cover for preventing attachment of charged water droplets 50. Reaction chamber entry / exit cylinder 51. Atomizing nozzle 52. Insulator leg 53. Corona discharge exhaust gas ionizer 54. Corona discharge negative electrode 55. Corona discharge plus electrode 56. Reversely charged particle absorbing blade 57. Negative electrode support material 58. Positive electrode support material 59. Charged particle flow flue 60. Corona discharge zone 61. Vibration generator

Claims (11)

【特許請求の範囲】 【0001】[Claims] [0001] 【請求項1】病院のガラスビン、注射針等を含めた感染
性医療廃棄物を単独及び一般ごみと同時に焼却出来、
又、灰、残渣、金属類を溶融し完全滅菌した後急冷微粉
砕化により建材、金属材料としてリサイクル使用を可能
とする焼却炉。その為に焼却物自動投入装置、炉内焼却
物送りプッシャー、未燃及び液状化焼却物用流動床部、
焼却後残屑押し出しプッシャー、溶融装置、溶融物微粉
砕、コロナ放電による有害ガス除去装置、反応室載台自
動供給排出装置機能等を一体型として組込んだのを特長
とする高温完全滅菌型全自動焼却炉システム。
1. Infectious medical waste including glass bottles, injection needles, etc. of hospitals can be incinerated alone and at the same time with general waste,
An incinerator that can be reused as a building material or metal material by melting and completely sterilizing ash, residues, and metals, then quenching and pulverizing. For that purpose, automatic incinerator charging device, incinerator feed pusher, fluidized bed for unburned and liquefied incinerator,
Complete high-temperature sterilization type that features integrated push-out pusher after incineration, melting device, fine pulverization of molten material, harmful gas removal device by corona discharge, automatic supply and discharge device of reaction chamber platform, etc. Automatic incinerator system.
【請求項2】焼却炉内が燃焼進行により再び投入出来る
状態になったのをマイクロ波センサーで感知し、投入扉
及び投入コンベアを連動させ上に置かれた焼却物を炉内
に満るまで供給するのを特長とする請求項1の焼却物燃
焼状況監視センサーと連動する自動投入装置。
2. A microwave sensor detects that the inside of the incinerator is ready to be charged again due to the progress of combustion, and the charging door and the charging conveyor are interlocked until the incinerator placed on the furnace is filled up. An automatic charging device that operates in conjunction with the incinerator combustion condition monitoring sensor according to claim 1, characterized by being supplied.
【請求項3】上、下から助燃バーナーを使った場合、金
属製火格子は連続高温で使用出来ない為、2本相互に連
結部を持ち1組とする事で隣の火格子と強度を補い合う
構造を持ち、又内部に熱膨張吸収用クリアランスを設け
たステンレス補強材を入れる事で耐熱衝撃性及び燃焼物
落下時にも耐えられる耐衝撃荷重性を持たせ、欠点であ
った「火格子の割れ」による欠落発生を無くした事を特
長とする請求項1の不定形耐火物製火格子。
3. When an auxiliary burner is used from above and below, the metal grate cannot be used at a continuous high temperature, so two girders are connected to each other to form a set, so that the strength of the adjacent grate can be increased. It has a structure that complements each other, and by incorporating a stainless steel reinforcing material with a clearance for absorbing thermal expansion inside, it has thermal shock resistance and shock load resistance that can withstand the fall of combustion products, which was a drawback. The irregular-shaped refractory grate according to claim 1, characterized in that the occurrence of chipping due to "cracking" is eliminated.
【請求項4】砂上層部に集められた灰、残渣、ビン、金
属類を砂と共役の役目をさせる為灼熱状態にしておく事
により上部火格子からの未燃物、液状化した高分子焼却
物、液体類を完全焼却させ、又、砂を炉外に出さず灰、
残渣を分離する機能を持つのを特長とする、請求項1の
流動床式後燃部。
4. Ashes, residues, bottles, and metals collected in the upper layer of sand are kept in a burning state so as to have a function of conjugating with sand, so that unburned substances from the upper grate and liquefied polymer Completely incinerates incineration materials and liquids, and does not remove sand from the furnace to remove ash,
The fluidized bed after-combustion unit according to claim 1, which has a function of separating a residue.
【請求項5】流動床部で砂のみを残し灰、ビン、金属類
残渣を炉外に排出来る機能を持ち、ブリッジ防止、閉塞
防止、砂未燃物分離用篩い機能等の為の振動部を組み込
んだ機構を持ち、炉排出扉と連動するのを特長とする請
求項1の灰 ビン、金属類炉外排出プッシャー装置。 【0002】
5. A vibrating part having a function of leaving only sand in the fluidized bed part and discharging ash, bottles, and metal residues to the outside of the furnace, for preventing bridge, blocking, and sieving function for separating unburned sand. The ash bottle according to claim 1, wherein the ash bin and the metal-external pusher device are connected to the furnace discharge door. [0002]
【請求項6】灰を飛散させずに金属溶融点まで温度上昇
出来る構造で、灰、ガラスビン、金属類等それぞれの溶
融点に達したものは留まる事なく溶融炉外に自然流出さ
せる機能を持ち、又、熱電対センサーで溶融温度を感知
し仕分装置を作動させる事で溶融物毎に分別し回収が可
能な溶融炉。炉本体の排熱を利用し溶融炉を予熱するた
め温度上昇プログラムに沿い排ガスを導入して溶融炉と
灰残渣を熱する機能を持つ。又、溶融炉の満空の状態を
請求項2と同仕様の受信部フードをしぼったマイクロ波
利用レベル装置及び熱電対を使い検知し、自動運転する
等のを特長を持った請求項1の灰残渣溶融炉。
6. A structure that can raise the temperature to the metal melting point without scattering ash, and has the function of allowing ash, glass bottles, metals, etc. that have reached their melting points to spontaneously flow out of the melting furnace without remaining. Also, a melting furnace that can detect and collect the melting temperature by detecting the melting temperature with a thermocouple sensor and operating the sorting device. In order to preheat the melting furnace by using the exhaust heat of the furnace body, it has the function to heat the melting furnace and ash residue by introducing exhaust gas according to the temperature rise program. Further, the full state of the melting furnace is detected by using a microwave utilization level device and a thermocouple having a receiving hood having the same specifications as those of claim 2, and is automatically operated. Ash residue melting furnace.
【請求項7】燃焼室出口とサイクロン集塵装置の間に本
再燃室及びこれと空気予熱管壁により仕切られ煙道機能
を兼ねている副再燃室を組込む事で、再燃室とサイクロ
ンが同時に並置して内蔵出来、又、沈降ダスト及び流動
床部の砂中分離ダストを溶融炉フィダーに排出する構造
を持つのを特長とする請求項1の小型炉内同時内蔵型再
燃室及びサイクロン排ガス処理装置。
7. A reburn chamber and a cyclone are installed at the same time by incorporating a main reburn chamber and a sub-reburn chamber, which is partitioned by the reburn chamber and an air preheating pipe wall and has a flue function, between the outlet of the combustion chamber and the cyclone dust collector. 2. The simultaneous built-in reburn chamber in the small furnace and the cyclone exhaust gas treatment according to claim 1, which can be installed side by side and have a structure for discharging settling dust and dust separated in sand from the fluidized bed to a melting furnace feeder. apparatus.
【請求項8】排ガス中の塩化水素、SOx、NOx等の
有害ガス及びサイクロンで捕集出来なかった微粒ダスト
を同時に除去する目的で、イオン、オゾンを発生させる
コロナ放電部分と水滴微粒子を作るアトマイヂングノズ
ル部との組合せにより、マイナス帯電水滴微粒子を作
り、これに煙道中で有害ガスを取り込ませ後接のプラス
極に加電させた消石灰中空円筒にクーロン力を使い吸
着、反応、塩基固定させるのを特長とする請求項1の有
害ガス及び、微粒ダスト除去装置。
8. A corona discharge portion for generating ions and ozone and water droplet fine particles for the purpose of simultaneously removing harmful gases such as hydrogen chloride, SOx, NOx and the like in exhaust gas and fine dust which could not be collected by a cyclone. By combining with a miding nozzle, negatively charged water droplets are made into fine particles, and harmful gas is taken into the flue, and the slaked lime hollow cylinder charged with the positive electrode of the subsequent contact is adsorbed, reacted, and fixed with a base. A device for removing harmful gas and fine dust according to claim 1, characterized in that
【請求項9】円筒表面及び内側中空部の長手方向にV型
溝を持ち、排ガス中の酸との反応で生成する塩基層が閉
塞せずに自重で剥離落下すると同時にノズル水噴射で易
く欠き落とされる構造を持つ事で、有害ガスとの接触面
積が大きく、反応室での圧損が増える事なく、常時未反
応の新しい表面を持つ事が出来る。又、微量塩化のナト
リウム等電解物質を含入させておく事によりノズル等の
水分が加わって湿潤化され表面が電解質薄膜で覆われた
状態の通電可能な消石灰ブロックとなる。これ等を特長
とする請求項8の中空円筒成形の水酸化カルシウム。
9. A V-shaped groove is formed in the cylindrical surface and in the longitudinal direction of the inner hollow portion, and the base layer formed by the reaction with the acid in the exhaust gas is not clogged and peels and falls by its own weight, and at the same time it is easily chipped by a nozzle water jet. By having a structure that is dropped, the contact area with harmful gas is large, and the pressure loss in the reaction chamber does not increase, and it is possible to have a new surface that is always unreacted. In addition, by containing a slight amount of electrolytic substance such as sodium chloride, the hydrated lime block which can be energized in the state where the water is moistened by the addition of water from the nozzle and the surface is covered with the electrolyte thin film. The hollow cylindrical molded calcium hydroxide according to claim 8, which is characterized by these.
【請求項10】反応室内で集塵極(プラス極)となる消
石灰中空円筒ブロックを載せる台であり、下部の反応後
落下塩基受け皿に帯電粒子が電気的に吸着するのを防ぐ
目的で、粒子付着防止と清掃機能を持つカバーに納めら
れた4つの碍子脚により載台床部と、受け皿とを電気的
に縁切りさせた構造を特長とする請求項1の消石灰中空
円筒載台。
10. A table on which a slaked lime hollow cylindrical block serving as a dust collecting electrode (plus electrode) is placed in the reaction chamber, and particles for the purpose of preventing the charged particles from being electrically adsorbed on the falling base tray after the reaction. 2. The slaked lime hollow cylindrical mount according to claim 1, characterized in that the mount floor and the pan are electrically cut off by four insulator legs housed in a cover having an adhesion preventing and cleaning function.
【請求項11】消石灰中空円筒成型と、有害ガスとの反
応進捗を重量変化量としてロードセルで感知し、反応が
終えた時点で炉の稼動中でもコンベア上にストレージさ
れている新規の消石灰中空円筒と自動交換する機能を持
つ事を特長とする請求項1の反応室載台自動取替装置。
11. A slaked lime hollow cylinder, and a new slaked lime hollow cylinder which is stored on a conveyor when the reaction progresses with a harmful gas as a weight change amount is sensed by a load cell and the reaction is completed and the furnace is in operation. The reaction chamber table automatic replacement device according to claim 1, which has a function of automatically exchanging.
JP10892494A 1994-04-12 1994-04-12 Incinerating furnace Pending JPH07280240A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10892494A JPH07280240A (en) 1994-04-12 1994-04-12 Incinerating furnace

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10892494A JPH07280240A (en) 1994-04-12 1994-04-12 Incinerating furnace

Publications (1)

Publication Number Publication Date
JPH07280240A true JPH07280240A (en) 1995-10-27

Family

ID=14497110

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10892494A Pending JPH07280240A (en) 1994-04-12 1994-04-12 Incinerating furnace

Country Status (1)

Country Link
JP (1) JPH07280240A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106594758A (en) * 2016-12-12 2017-04-26 上海市特种设备监督检验技术研究院 Method for rapidly processing residual liquid/residual gas in liquefied gas steel cylinder
CN116357982A (en) * 2023-01-31 2023-06-30 江苏立宇环境科技有限公司 Incineration treatment system for treating fluorine-containing chlorine-containing salt-containing waste liquid and use method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106594758A (en) * 2016-12-12 2017-04-26 上海市特种设备监督检验技术研究院 Method for rapidly processing residual liquid/residual gas in liquefied gas steel cylinder
CN116357982A (en) * 2023-01-31 2023-06-30 江苏立宇环境科技有限公司 Incineration treatment system for treating fluorine-containing chlorine-containing salt-containing waste liquid and use method thereof
CN116357982B (en) * 2023-01-31 2023-10-03 江苏立宇环境科技有限公司 Incineration treatment system for treating fluorine-containing chlorine-containing salt-containing waste liquid and use method thereof

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