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JP2002349818A - Combustible dust injection method for waste melting furnace - Google Patents

Combustible dust injection method for waste melting furnace

Info

Publication number
JP2002349818A
JP2002349818A JP2001163385A JP2001163385A JP2002349818A JP 2002349818 A JP2002349818 A JP 2002349818A JP 2001163385 A JP2001163385 A JP 2001163385A JP 2001163385 A JP2001163385 A JP 2001163385A JP 2002349818 A JP2002349818 A JP 2002349818A
Authority
JP
Japan
Prior art keywords
temperature
furnace
combustible dust
tuyere
melting furnace
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
JP2001163385A
Other languages
Japanese (ja)
Inventor
Hirokazu Tanaka
宏和 田中
Hideji Shibaike
秀治 芝池
Yoshiharu Ueno
義治 上野
Ryohei Kosaka
良平 小阪
Yoshinobu Nishida
義信 西田
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.)
IBARAKISHI
Nippon Steel Corp
Original Assignee
IBARAKISHI
Nippon Steel Corp
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 IBARAKISHI, Nippon Steel Corp filed Critical IBARAKISHI
Priority to JP2001163385A priority Critical patent/JP2002349818A/en
Publication of JP2002349818A publication Critical patent/JP2002349818A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/34Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Incineration Of Waste (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Vertical, Hearth, Or Arc Furnaces (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)

Abstract

(57)【要約】 【課題】 乾留残渣の断面方向における通気抵抗の差の
生じ易い部位近傍の温度を直接測定して、早期に発生箇
所を特定するとともに、その発生箇所近傍への可燃性ダ
ストの吹込み量を制御(増量)することにより、乾留残
渣の断面方向における通気抵抗の差が大きくならない内
に早期に解消する。 【解決手段】 廃棄物溶融炉1の炉頂から飛散した可燃
性ダストを捕集し、捕集した可燃性ダストを廃棄物溶融
炉1の送風羽口10からコークスベッドヘ常温の酸素富
化空気又は高温空気とともに吹き込む方法において、廃
棄物溶融炉1の可燃性ダストを吹き込む羽口10よりも
上部であって、且つ、被処理物が充填されている炉本体
の横断面方向に間隔をおいて設置された複数の温度計1
2で炉内の温度を測定し、測定された温度が事前に設定
された温度以上になった時に、該測定点に近い羽口から
の可燃性ダストの吹込み量を制御する。
(57) [Summary] [PROBLEMS] To directly measure the temperature in the vicinity of a portion where a difference in airflow resistance in the cross-sectional direction of a dry distillation residue is likely to occur, identify the generation location early, and combustible dust to the vicinity of the generation location. By controlling (increasing) the amount of air blown, the difference in the ventilation resistance in the cross-sectional direction of the dry distillation residue is eliminated early without increasing. SOLUTION: The combustible dust scattered from the furnace top of the waste melting furnace 1 is collected, and the collected combustible dust is sent from a blowing tuyere 10 of the waste melting furnace 1 to a coke bed at room temperature oxygen-enriched air. Alternatively, in the method of blowing together with the high-temperature air, a space is provided above the tuyere 10 for blowing the combustible dust of the waste melting furnace 1 and in the cross-sectional direction of the furnace body filled with the object to be treated. Multiple thermometers 1 installed
The temperature in the furnace is measured in 2, and when the measured temperature becomes equal to or higher than a preset temperature, the amount of combustible dust blown from the tuyere close to the measurement point is controlled.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、一般廃棄物、産業
廃棄物等の廃棄物を熱分解溶融処理する廃棄物溶融炉の
可燃性ダストの吹き込み方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method of blowing combustible dust into a waste melting furnace for thermally decomposing and melting waste such as general waste and industrial waste.

【0002】[0002]

【従来の技術】一般廃棄物、産業廃棄物等の廃棄物の処
理方法として、廃棄物をシャフト炉式の廃棄物溶融炉に
装入し、廃棄物を乾燥、予熱、熱分解、燃焼、溶融し、
スラグやメタルとして取り出す熱分解溶融処理方法が知
られている。
2. Description of the Related Art As a method of treating general waste and industrial waste, waste is charged into a shaft furnace type waste melting furnace, and the waste is dried, preheated, pyrolyzed, burned, and melted. And
There is known a thermal decomposition / melting method for extracting slag or metal.

【0003】図4はシャフト炉型の廃棄物溶融炉を備え
た廃棄物溶融設備の説明図で、廃棄物溶融炉1には、廃
棄物、副資材であるコークス、石灰石を炉上部から2重
シール弁機構の装入装置2を介して装入し、乾燥、熱分
解、燃焼、溶融する。一方、炉内からの可燃分は、熱分
解ガスとして炉上部のダクト3から排出され、燃焼室4
で燃焼後、ボイラ5、タービン発電機などの付帯設備に
より熱及び電気エネルギーとして利用される。その後、
排ガスは、ガス冷却器6で冷却され、集じん装置7を経
た後、誘引送風機8により煙突9から放出する。
FIG. 4 is an explanatory view of a waste melting facility provided with a shaft furnace type waste melting furnace. In the waste melting furnace 1, waste, coke as a secondary material, and limestone are doubled from the furnace upper part. It is charged through the charging device 2 of the seal valve mechanism, and dried, thermally decomposed, burned, and melted. On the other hand, combustible components from the furnace are discharged from the duct 3 in the upper part of the furnace as pyrolysis gas,
After the combustion, the heat is used as heat and electric energy by auxiliary equipment such as the boiler 5 and the turbine generator. afterwards,
The exhaust gas is cooled by a gas cooler 6, passes through a dust collecting device 7, and is discharged from a chimney 9 by an induced blower 8.

【0004】廃棄物溶融炉の下部には空気と酸素を混合
した酸素富化空気を吹き込む複数の送風羽口10が設け
られ、灰分はスラグ及びメタルとして出滓口11から取
り出す。送風羽口10から吹き込んだ酸素富化空気は炉
内のコークス及び熱分解で発生したチャーを燃焼させ、
その燃焼熱は炉内に投入された廃棄物の乾燥、熱分解、
及び不燃物の溶融に利用される。
[0004] At the lower part of the waste melting furnace, there are provided a plurality of blowing tuyeres 10 for blowing oxygen-enriched air in which air and oxygen are mixed, and ash is taken out from the slag port 11 as slag and metal. The oxygen-enriched air blown from the tuyere 10 burns coke in the furnace and char generated by pyrolysis,
The heat of combustion is used for drying, pyrolysis,
And used for melting incombustibles.

【0005】前記廃棄物溶融炉の操業では、廃棄物溶融
炉内の下部には、装入物中の可燃分が熱分解して乾留残
渣が発生する。発生した残渣は羽口から送られてきた空
気によって燃焼するかあるいは炉内に堆積していくが、
微細なものは、羽口から送られてきた空気によって燃焼
されることなく、気流に乗って炉から可燃性ダストとし
て飛散する。この炉頂から飛散した可燃性ダストを捕集
し再度、炉本体に設けられた羽口から炉内に吹き込むこ
とにより、コークス比を低減するという効果を有する。
[0005] In the operation of the waste melting furnace, the combustible components in the charge are thermally decomposed at the lower portion in the waste melting furnace to generate dry distillation residues. The generated residue is burned by the air sent from the tuyere or deposited in the furnace.
Fines are scattered as combustible dust from the furnace in the air stream without being burned by the air sent from the tuyere. The combustible dust scattered from the furnace top is collected and blown into the furnace again through a tuyere provided in the furnace main body, which has the effect of reducing the coke ratio.

【0006】本出願人は、飛散する可燃性ダストの処理
技術として、特願平11−217997号で燃料を送風
羽口からコークスベッドへ吹き込む方法を出願した(な
お、該出願にあっては、羽口から吹込むものは捕集ダス
トに限らず一般的な燃料としている。)。この方法は、
図4に示すように、廃棄物溶融炉に廃棄物をコークス、
石灰石とともに装入し、乾燥、熱分解、燃焼、溶融して
排出する際に、廃棄物溶融炉の送風羽口からコークスベ
ッドヘ常温の酸素富化空気又は高温空気とともに、燃料
をコークスベッドヘ吹き込む方法において、廃棄物溶融
炉の炉頂ガス温度を検出し、炉頂ガス温度が設定値を超
えた場合、炉頂ガス温度が所定の炉頂ガス温度範囲に入
るように燃料吹込量を制御したり、あるいは廃棄物溶融
炉の炉頂ガス中のCO濃度(%)及びCO濃度(%)
を測定してηCO=CO/(CO+CO)を演算
し、演算されたηCOが設定値を超えた場合、所定の範
囲に入るように燃料吹込量を制御するものである。
[0006] The applicant of the present application has filed a method of blowing fuel from a tuyere into a coke bed in Japanese Patent Application No. 11-217997 as a technique for treating flammable dust that has been scattered. What is blown from the tuyere is not limited to collected dust, but is used as general fuel.) This method
As shown in FIG. 4, coke wastes into a waste melting furnace,
When charged with limestone and dried, pyrolyzed, burned, melted and discharged, fuel is blown into the coke bed together with oxygen-enriched air at normal temperature or high-temperature air from the blast tuyere of the waste melting furnace into the coke bed. In the method, the top gas temperature of the waste melting furnace is detected, and when the top gas temperature exceeds a set value, the fuel injection amount is controlled so that the top gas temperature falls within a predetermined top gas temperature range. Or CO concentration (%) and CO 2 concentration (%) in the top gas of waste melting furnace
Is calculated to calculate ηCO = CO 2 / (CO 2 + CO), and when the calculated ηCO exceeds a set value, the fuel injection amount is controlled so as to fall within a predetermined range.

【0007】溶融処理対象物として、一般の都市ごみだ
けでなく、高水分ごみや異形ごみ等の変動の大きい様々
なごみを処理する場合に、ごみの熱分解が完了しないま
ま炉底部へ降下する場合がある。コークスベッド充填層
内に吹き込まれた可燃性ダストは、コークスベッド充填
層内で適当に混合され、吹き込んだ可燃性ダストとコー
クスが優先的に羽口を介して吹き込んだ酸素富化空気も
しくは高温空気と反応し燃焼するが、余剰の酸素は熱分
解未完了ごみを羽口前で直接燃焼させる。熱分解未完了
ごみが直接燃焼すると、体積縮小が大きいために空間部
が生じ、断面方向における通気抵抗の差が生じ、熱交換
効率が低下することがある。
[0007] In the case of processing various kinds of refuse having large fluctuations such as high-moisture refuse and irregular refuse, as well as general municipal refuse, the refuse falls to the furnace bottom without completing thermal decomposition of the refuse. There is. The combustible dust blown into the coke bed packed bed is appropriately mixed in the coke bed packed bed, and the blown combustible dust and coke are preferentially blown through the tuyere by oxygen-enriched air or hot air. The excess oxygen burns the incompletely pyrolyzed refuse directly in front of the tuyere. When the pyrolysis-incomplete refuse is directly burned, a space portion is generated due to a large volume reduction, a difference in ventilation resistance in a cross-sectional direction is generated, and the heat exchange efficiency may decrease.

【0008】この出願の発明は、この空間部を早期に解
消することを課題としており、その手段として、炉頂ガ
スの温度、炉頂ガス中のCO及びCO濃度を測定し、
この値によりその空間部の発生を知り、その情報を基に
してシャフト炉の羽口から燃料を制御することにより空
間部を解消せんとするものである。しかし、前記した乾
留残渣の断面方向における通気抵抗の差(空間部)は、
一般的には、炉内でも羽口前に発生しやすい。ところ
が、前述した如く、炉頂ガスの情報(温度、濃度)を基
にしているため、発生箇所とは距離的ギャップがあるた
め空間部の発見が遅れ、また、炉頂ガスの温度は炉内各
部位の平均された温度であるため、断面方向のどの部位
に空間部が発生しているのか特定ができないため、その
現象の解消に時間がかかるという問題を有していた。ま
た、空間部のない方向にもダストを吹き込む必要がある
ため、多量の可燃性ダストのストックが必要であり、大
きなホッパが必要となる。
The object of the invention of this application is to eliminate this space portion at an early stage. As means for this purpose, the temperature of the furnace top gas, the concentration of CO and CO 2 in the furnace top gas are measured,
The occurrence of the space is known from this value, and the space is eliminated by controlling the fuel from the tuyere of the shaft furnace based on the information. However, the difference in the ventilation resistance in the cross-sectional direction of the dry distillation residue (space) is as follows.
Generally, it is likely to occur before the tuyere even in a furnace. However, as described above, since it is based on the information (temperature and concentration) of the top gas, there is a distance gap from the generation point, so that the discovery of the space is delayed, and the temperature of the top gas is Since the average temperature of each part is used, it is not possible to specify at which part in the cross-sectional direction the space part is generated. Therefore, there is a problem that it takes time to eliminate the phenomenon. Further, since it is necessary to blow dust in a direction where there is no space, a large amount of combustible dust stock is required, and a large hopper is required.

【0009】そこで、本発明は、乾留残渣の断面方向に
おける通気抵抗の差の生じ易い部位近傍の温度を直接測
定して、早期に発生箇所を特定するとともに、その発生
箇所近傍への可燃性ダストの吹込み量を制御(増量)す
ることにより、乾留残渣の断面方向における通気抵抗の
差が大きくならない内に早期に解消せんとするものであ
る。
Accordingly, the present invention is to directly measure the temperature in the vicinity of a portion where a difference in airflow resistance in the cross-sectional direction of the dry distillation residue is likely to occur, to identify the generation location at an early stage, and to detect the flammable dust near the generation location. By controlling (increasing) the amount of air blown, the difference in gas flow resistance in the cross-sectional direction of the dry distillation residue is not eliminated as soon as possible.

【0010】[0010]

【課題を解決するための手段】本発明の廃棄物溶融炉の
可燃性ダストの吹込み方法は、廃棄物溶融炉に廃棄物を
コークス、石灰石とともに装入し、乾燥、熱分解、燃
焼、溶融して排出する際に、廃棄物溶融炉の炉頂から飛
散した可燃性ダストを捕集し、捕集した可燃性ダストを
廃棄物溶融炉の送風羽口からコークスベッドヘ常温の酸
素富化空気又は高温空気とともに吹き込む方法におい
て、廃棄物溶融炉の可燃性ダストを吹き込む羽口よりも
上部であって、且つ、被処理物が充填されている炉本体
の横断面方向に間隔をおいて設置された複数の温度計で
炉内の温度を測定し、測定された温度が事前に設定され
た温度以上になった時に、該測定点に近い羽口からの可
燃性ダストの吹込み量を制御することを特徴とする。
According to the present invention, a method for injecting combustible dust into a waste melting furnace comprises charging waste together with coke and limestone into a waste melting furnace, drying, pyrolyzing, burning and melting. Combustible dust scattered from the top of the waste melting furnace and collect the combustible dust from the blast tuyere of the waste melting furnace to the coke bed at room temperature. Alternatively, in the method of blowing together with high-temperature air, the furnace is disposed above the tuyere of the waste melting furnace at which the combustible dust is blown, and is disposed at intervals in the cross-sectional direction of the furnace body filled with the object to be treated. The temperature in the furnace is measured with a plurality of thermometers, and when the measured temperature is equal to or higher than a preset temperature, the amount of combustible dust blown from the tuyere close to the measurement point is controlled. It is characterized by the following.

【0011】[0011]

【発明の実施形態】図1(a)は、本発明の廃棄物溶融
炉のダストの吹込み方法を実施するための設備の要部を
示す図、(b)は吹込み方法の制御の説明図である。図
4に示す従来の廃棄物溶融設備と同一の構成について
は、同一符号を付しその説明は省略する。15は、炉頂
から飛散したダストを捕集する除じん器で、16は、そ
の捕集したダストを羽口10を介して吹き込むための吹
込み装置である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 (a) shows a main part of equipment for carrying out a method for injecting dust in a waste melting furnace according to the present invention, and FIG. 1 (b) explains control of the injecting method. FIG. The same components as those of the conventional waste melting facility shown in FIG. 4 are denoted by the same reference numerals, and description thereof is omitted. Reference numeral 15 denotes a dust remover that collects dust scattered from the furnace top, and 16 denotes a blowing device that blows the collected dust through the tuyere 10.

【0012】前記したように、溶融処理対象物として、
一般の都市ごみだけでなく、高水分ごみや異形ごみ等の
変動の大きい様々なごみを処理する場合に、ごみの熱分
解が完了しないまま炉底部へ降下する場合がある。コー
クスベッド充填層内に吹き込まれた可燃性ダストは、コ
ークスベッド充填層内で適当に混合され、吹き込んだ可
燃性ダストとコークスが優先的に羽口を介して吹き込ん
だ酸素富化空気もしくは高温空気と反応し燃焼するが、
余剰の酸素は熱分解未完了ごみを羽口前で直接燃焼させ
る。熱分解未完了ごみが直接燃焼すると、体積縮小が大
きいために空間部が生じ、断面方向における通気抵抗の
差が生じ、熱交換効率が低下することがある。従って、
通気抵抗の差(空間部)を特定するための温度測定個所
は、少なくとも可燃性ダストを吹き込む羽口よりも上方
である必要があり、出来る限り可燃性ダストを吹き込む
羽口近傍が好ましいが、少なくとも被処理物の充填層内
の温度が測定できれば、空間部の発生は容易に把握する
ことができる。
As described above, as an object to be melted,
When treating not only general municipal waste but also various refuse with large fluctuations, such as high-moisture refuse and deformed refuse, the refuse may fall to the furnace bottom without being completely pyrolyzed. The combustible dust blown into the coke bed packed bed is appropriately mixed in the coke bed packed bed, and the blown combustible dust and coke are preferentially blown through the tuyere by oxygen-enriched air or hot air. Reacts with and burns,
Excess oxygen burns the incompletely pyrolyzed waste directly in front of the tuyere. When the incompletely pyrolyzed refuse is directly burned, a space portion is generated due to a large volume reduction, a difference in ventilation resistance occurs in a cross-sectional direction, and the heat exchange efficiency may be reduced. Therefore,
The temperature measurement point for specifying the difference (space portion) of the ventilation resistance needs to be at least above the tuyere that blows combustible dust, and is preferably as close as possible to the tuyere that blows combustible dust. If the temperature in the packed bed of the object to be treated can be measured, the occurrence of the space can be easily grasped.

【0013】図1(a)において、廃棄物溶融炉1の可
燃性ダストを吹き込む羽口よりも上部であって、且つ、
被処理物が充填されている炉本休の横断面方向に間隔を
おいて複数の温度計12を設置する。乾留残渣に通気抵
抗の差(空間部)が生じると、その部分での熱交換効率
が低下して、ガス温度が上昇するので、上昇した温度を
計測した温度計12の設置個所から発生した空間部を特
定することが出来る。
In FIG. 1 (a), it is above the tuyere of the waste melting furnace 1 for blowing combustible dust, and
A plurality of thermometers 12 are installed at intervals in the direction of the cross section of the furnace that is filled with the workpiece. If a difference in ventilation resistance (space part) occurs in the carbonization residue, the heat exchange efficiency in that part decreases, and the gas temperature rises. Therefore, the space generated from the installation place of the thermometer 12 that measures the risen temperature. The part can be specified.

【0014】各温度計12の計測信号は空間部を特定す
る空間部特定演算部13に入力され、各温度計の計測温
度が事前に設定した温度より上昇しているか否かが判定
され、判定結果から空間部の発生、発生箇所が特定され
る。
The measurement signal of each thermometer 12 is input to a space specifying operation unit 13 for specifying a space, and it is determined whether or not the temperature measured by each thermometer is higher than a preset temperature. From the result, the occurrence and location of the space part are specified.

【0015】空間部特定演算部13から空間部発生箇
所、温度情報が可燃性ダスト吹込み量演算部14に入力
され、増量すべき羽口が特定され、その羽口への可燃性
ダストの吹込み量が演算される。
Information on the location and temperature at which the space is generated from the space specifying operation unit 13 is input to the combustible dust blowing amount calculation unit 14 to identify the tuyere to be increased, and to blow the combustible dust to the tuyere. The inset amount is calculated.

【0016】演算結果の信号は、特定された羽口の可燃
性ダスト吹込み装置に設けられた流量調節計(FIC)
に送られて、羽口に吹き込む可燃性ダスト量が調節され
る。図2は、本発明の可燃性ダストの吹き込み例とシャ
フト部炉内の温度変化を示すグラフである。
The signal of the operation result is supplied to a flow controller (FIC) provided in the combustible dust blowing device of the specified tuyere.
And the amount of combustible dust blown into the tuyere is adjusted. FIG. 2 is a graph showing an example of injectable combustible dust of the present invention and a temperature change in a shaft part furnace.

【0017】図に見る如く、シャフト炉の断面にあっ
て、周方向に適宜間隔をおいて4個の温度計(12−
1、12−2、12−3、12−4)を設けている。即
ち、測定点は4ケ所(a)、(b)、(c)、(d)で
ある。
As shown in the figure, four thermometers (12-
1, 12-2, 12-3, 12-4). That is, there are four measurement points (a), (b), (c), and (d).

【0018】しかして、該図にあって、x時刻までは、
可燃性ダストの吹き込み量は、各羽口とも100kgで
一定しており、x時刻以降は設定温度に対応した吹き込
み量制御(増量)行った状態を示す。
In the figure, up to the time x,
The blowing amount of the combustible dust is constant at 100 kg for each tuyere, and shows a state in which the blowing amount control (increase) corresponding to the set temperature has been performed after time x.

【0019】ところで、この図にあって、(c)(12
−3)の位置の温度変化を見るに、初期に急激な温度上
昇が見られるが、この部位近傍で空間部が発生し、熱交
換効率が低下していることが判断される。ただ、この例
に見るように、時間経過と共に、自然解消することもあ
るが、一般的には、長期にわたり空間部が残存し、スラ
グ温度の低下や、ゴミ処理量の低下ということになる。
By the way, in this figure, (c) (12)
Looking at the temperature change at the position of -3), a sharp temperature rise is observed at the beginning, but it is determined that a space portion is generated near this portion and the heat exchange efficiency is reduced. However, as can be seen from this example, there is a case where the space is naturally resolved with the passage of time. However, in general, the space remains for a long period of time, resulting in a decrease in slag temperature and a decrease in the amount of waste disposal.

【0020】そこで、本発朋にあっては、あらかじめ、
形成される空間部と炉内温度との相関を把握し、この温
度経緯から空間部の出来始める温度域を想定(設定)
し、この設定温度域になった時に吹き込むダスト量を増
量せんとするものである。
Therefore, in the present invention,
Comprehend the correlation between the space formed and the furnace temperature, and assume the temperature range where the space starts to be formed from this temperature process (setting)
The amount of dust blown when the temperature reaches the set temperature range is increased.

【0021】この設定温度は、シャフト温度計の高さ方
向位置関係等により経験的に決定する必要があるが、本
実施例では400℃とした。
The set temperature must be empirically determined based on the positional relationship of the shaft thermometer in the height direction and the like. In this embodiment, the set temperature is 400 ° C.

【0022】しかして、図2にあって、(c)(12−
3)の温度は、時間経過の8時以降に、炉内測定温度が
設定温度の400℃を越えたので、その近傍の乾留残さ
部に空間部が発生したと判断、その近傍に位置する羽口
からの可燃性ダストの吹き込み量を制御(増加)させた
ことにより、その後、その部位の温度は上昇せず、40
0℃前後で推移した後、約300℃程度の温度まで降下
した。
In FIG. 2, (c) (12-
In the temperature of 3), since the measured temperature in the furnace exceeded the set temperature of 400 ° C. after 8:00 of the elapse of time, it was determined that a space portion was generated in the dry distillation residue in the vicinity, and the blade located in the vicinity was determined. By controlling (increasing) the amount of flammable dust blown from the mouth, the temperature of the portion does not rise thereafter,
After changing around 0 ° C., the temperature dropped to a temperature of about 300 ° C.

【0023】図3は、炉頂ガス温度の測定結果と、シャ
フト部内のガス温度の測定結果を対比したものである。
FIG. 3 compares the measurement result of the furnace top gas temperature with the measurement result of the gas temperature in the shaft portion.

【0024】前述した如く、従来は、炉頂ガス温度の変
化を見ながら空間部の発生を把握し、全羽口からの可燃
性ダストの吹き込み量を増量していたが、本発明は、シ
ャフト部内のガス温度の変化から空間部の発生を把握
し、その近傍の羽口からの可燃性ダストの吹き込み量の
みを増量せんとするものであるが、図に見る如く、炉頂
ガス温度は、炉内各部位の平均されたものになっている
ため非常に緩やかな変化を示しているが、本発明のよう
に、シャフト部内を測定した温度経緯は、ひじように敏
感に反応し、又、温度上昇の見られるタイミングも早
い。このことは、本発明の方が空間部の出来始めを早く
知ることが出来、又、明確に知り得ることが出来る、と
いうことを意味している。
As described above, conventionally, the generation of the space was grasped while observing the change in the furnace gas temperature, and the amount of flammable dust blown from all tuyeres was increased. The generation of the space is grasped from the change in the gas temperature in the section, and only the amount of flammable dust blown from the tuyere in the vicinity is to be increased, but as shown in the figure, the furnace top gas temperature is Although it shows an extremely gradual change because it has been averaged for each part in the furnace, as in the present invention, the temperature history measured inside the shaft part reacts sensitively like an elbow, The timing of the temperature rise is also early. This means that the present invention makes it possible to know the beginning of the space portion sooner and to know it more clearly.

【0025】[0025]

【発明の効果】本発明によれば、乾留残渣断面方向に於
ける通気抵抗の差(空間部)の生じ易い羽口部近傍から
その上方の被処理物充填層内のガス温度を複数箇所測定
することにより、空間部の発生をより早く、且つ、明確
に把握することが出来、又、その発生した近傍への可燃
性ダストの吹き込み量を増量することにより、空間部の
発生を早期に解消することが出来る。その結果、常に安
定した操業が維持出来る。
According to the present invention, the gas temperature is measured at a plurality of locations from the vicinity of the tuyere where the difference in air flow resistance (space portion) in the cross-sectional direction of the dry distillation residue is likely to occur, and in the material-filled layer above the tuyere. By doing so, it is possible to quickly and clearly grasp the occurrence of the space, and to eliminate the occurrence of the space early by increasing the amount of combustible dust blown into the vicinity of the occurrence You can do it. As a result, stable operation can always be maintained.

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

【図1】本発明の方法を実施するための設備の要部を示
す図である。
FIG. 1 is a diagram showing a main part of equipment for implementing a method of the present invention.

【図2】本発明の可燃性ダスト吹込み例を示すグラフで
ある。
FIG. 2 is a graph showing an example of flammable dust injection according to the present invention.

【図3】本発明と比較例の温度測定結果を示すグラフで
ある。
FIG. 3 is a graph showing temperature measurement results of the present invention and a comparative example.

【図4】シャフト炉型の廃棄物溶融炉を備えた廃棄物溶
融設備の説明図である。
FIG. 4 is an explanatory view of a waste melting facility provided with a shaft furnace type waste melting furnace.

【符号の説明】[Explanation of symbols]

1:廃棄物溶融炉 2:装入装置 3:ダクト
4:燃焼室 5:ボイラ 6:ガス冷却器 7:集じん装置 8:誘引送風機
9:煙突 10:送風羽口 11:出滓口 12:
温度計 13:空間部特定演算部 14:可燃性ダスト
吹き込み量演算部 15:除じん器 16:吹き込み装
1: Waste melting furnace 2: Charging device 3: Duct
4: Combustion chamber 5: Boiler 6: Gas cooler 7: Dust collector 8: Induction blower 9: Chimney 10: Blower tuyere 11: Slag outlet 12:
Thermometer 13: Space part specific calculation part 14: Combustible dust blowing amount calculation part 15: Dust remover 16: Blowing device

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F27B 1/28 F27D 19/00 A F27D 19/00 B09B 3/00 303K (72)発明者 芝池 秀治 北九州市戸畑区大字中原46−59 新日本製 鐵株式会社エンジニアリング事業本部内 (72)発明者 上野 義治 大阪府茨木市東野々宮町14番1号 茨木市 環境衛生センター内 (72)発明者 小阪 良平 大阪府茨木市東野々宮町14番1号 茨木市 環境衛生センター内 (72)発明者 西田 義信 大阪府茨木市東野々宮町14番1号 茨木市 環境衛生センター内 Fターム(参考) 3K061 AA16 AB02 AB03 AC01 BA04 CA07 DB16 3K062 AA16 AB02 AB03 AC01 BA02 CA01 CB04 DA01 DA32 DB01 4D004 AA46 BA03 CA24 CA29 CA42 CB04 CC02 CC11 DA01 DA02 DA06 DA10 4K045 AA01 BA10 DA02 DA04 GB11 NA01 4K056 BB01 CA20 FA03 FA13 Continuation of the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (reference) F27B 1/28 F27D 19/00 A F27D 19/00 B09B 3/00 303K (72) Inventor Hideharu Shibaike Tobata-ku, Kitakyushu Nakahara 46-59 Nippon Steel Corporation Engineering Business Headquarters (72) Inventor Yoshiharu Ueno 14-1 Higashinonomiyacho, Ibaraki City, Osaka Prefecture Ibaraki City Environmental Sanitation Center (72) Inventor Ryohei Kosaka Higashinonomiyamachi, Ibaraki City, Osaka Prefecture No. 14-1 Ibaraki City Environmental Health Center (72) Inventor Yoshinobu Nishida 14-1 Higashinonomiyamachi, Ibaraki City, Osaka Prefecture F-term in Ibaraki City Environmental Health Center 3K061 AA16 AB02 AB03 AC01 BA04 CA07 DB16 3K062 AA16 AB02 AB03 AC01 BA02 CA01 CB04 DA01 DA32 DB01 4D004 AA46 BA03 CA24 CA29 CA42 CB04 CC02 CC11 DA01 DA02 DA06 DA10 4K045 AA01 BA10 DA02 DA04 GB11 NA01 4K056 BB01 CA20 FA03 FA13

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 廃棄物溶融炉に廃棄物をコークス、石灰
石とともに装入し、乾燥、熱分解、燃焼、溶融して排出
する際に、廃棄物溶融炉の炉頂から飛散した可燃性ダス
トを捕集し、捕集した可燃性ダストを廃棄物溶融炉の送
風羽口からコークスベッドヘ常温の酸素富化空気又は高
温空気とともに吹き込む方法において、 廃棄物溶融炉
の可燃性ダストを吹き込む羽口よりも上部であって、且
つ、被処理物が充填されている炉本体の横断面方向に間
隔をおいて設置された複数の温度計で炉内の温度を測定
し、測定された温度が事前に設定された温度以上になっ
た時に、該測定点に近い羽口からの可燃性ダストの吹込
み量を制御することを特徴とする廃棄物溶融炉の可燃性
ダストの吹込み方法。
When the waste is charged together with coke and limestone into a waste melting furnace, and dried, thermally decomposed, burned, melted and discharged, combustible dust scattered from the top of the waste melting furnace is discharged. In the method in which combustible dust is collected and collected and blown into the coke bed together with the oxygen-enriched air at room temperature or high-temperature air through the tuyere of the waste melting furnace, Is also at the top, and the temperature in the furnace is measured with a plurality of thermometers installed at intervals in the cross-sectional direction of the furnace body filled with the object to be processed, and the measured temperature is determined in advance. A method for injecting combustible dust into a waste melting furnace, comprising controlling an amount of combustible dust to be blown from a tuyere close to the measurement point when the temperature reaches or exceeds a set temperature.
JP2001163385A 2001-05-30 2001-05-30 Combustible dust injection method for waste melting furnace Pending JP2002349818A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001163385A JP2002349818A (en) 2001-05-30 2001-05-30 Combustible dust injection method for waste melting furnace

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001163385A JP2002349818A (en) 2001-05-30 2001-05-30 Combustible dust injection method for waste melting furnace

Publications (1)

Publication Number Publication Date
JP2002349818A true JP2002349818A (en) 2002-12-04

Family

ID=19006367

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001163385A Pending JP2002349818A (en) 2001-05-30 2001-05-30 Combustible dust injection method for waste melting furnace

Country Status (1)

Country Link
JP (1) JP2002349818A (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS55102811A (en) * 1979-02-01 1980-08-06 Takuma Co Ltd Hollow cavity preventing and fire extinguishing device for vertical type refuse melting and gasifying furnace
JPH109554A (en) * 1996-06-24 1998-01-16 Kamaishishi Control method of upper tuyere air blowing amount of waste melting furnace
JP2001108212A (en) * 1999-07-30 2001-04-20 Nippon Steel Corp Operating method of waste melting furnace

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS55102811A (en) * 1979-02-01 1980-08-06 Takuma Co Ltd Hollow cavity preventing and fire extinguishing device for vertical type refuse melting and gasifying furnace
JPH109554A (en) * 1996-06-24 1998-01-16 Kamaishishi Control method of upper tuyere air blowing amount of waste melting furnace
JP2001108212A (en) * 1999-07-30 2001-04-20 Nippon Steel Corp Operating method of waste melting furnace

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