Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP4038536B2 - Reduction melting furnace and high temperature reducing gas recovery method using the same - Google Patents
[go: Go Back, main page]

JP4038536B2 - Reduction melting furnace and high temperature reducing gas recovery method using the same - Google Patents

Reduction melting furnace and high temperature reducing gas recovery method using the same Download PDF

Info

Publication number
JP4038536B2
JP4038536B2 JP2002299134A JP2002299134A JP4038536B2 JP 4038536 B2 JP4038536 B2 JP 4038536B2 JP 2002299134 A JP2002299134 A JP 2002299134A JP 2002299134 A JP2002299134 A JP 2002299134A JP 4038536 B2 JP4038536 B2 JP 4038536B2
Authority
JP
Japan
Prior art keywords
waste
melting furnace
reducing gas
temperature reducing
gas
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.)
Expired - Fee Related
Application number
JP2002299134A
Other languages
Japanese (ja)
Other versions
JP2004132655A (en
Inventor
正一 久米
Original Assignee
株式会社還元溶融技術研究所
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 株式会社還元溶融技術研究所 filed Critical 株式会社還元溶融技術研究所
Priority to JP2002299134A priority Critical patent/JP4038536B2/en
Publication of JP2004132655A publication Critical patent/JP2004132655A/en
Application granted granted Critical
Publication of JP4038536B2 publication Critical patent/JP4038536B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

  • Vertical, Hearth, Or Arc Furnaces (AREA)
  • Gasification And Melting Of Waste (AREA)
  • Coke Industry (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、一般廃棄物並びに産業廃棄物などを、処理する過程で発生する熱分解したガスを回収する位置を、充填高さレベルより低位にすることによりダイオキシンの発生を抑制し、かつ還元ガスのエネルギーを回収する還元溶融炉およびそれを用いた高温還元ガス回収方法に関するものである。
【0002】
【従来の技術】
近年、一般廃棄物、いわゆる都市ごみの排出量が増大し、これらの廃棄物(以下、一般廃棄物、産業廃棄物、焼却灰、不燃物等を言う)の殆どが焼却処理により減量化され焼却灰もしくは不燃物として最終処分場に埋め立てられている。しかし、都市ごみの排出量の増加は、この都市ごみの焼却残渣等の最終処分場の不足問題として発展している。これらに対処するために、廃棄物直接溶融方式が提案されている。その一例として特許文献1に開示されているような製鉄技術を応用した廃棄物直接溶融炉によって一般廃棄物をスラグ等の有用物に資源化させようとするものである。この廃棄物直接溶融炉の場合には、酸素雰囲気が3〜21%の雰囲気で、かつ100〜1200℃での焼却がなされ、その結果、焼却灰や未燃物となっているのが実状である。
【0003】
図4は、従来の堅型炉方式の廃棄物溶融炉の全体概略図である。この図に示すように、還元溶融炉1はシャフト部5、朝顔部6および炉底部7から構成され、朝顔部の周辺に設けられた上段羽口3および炉下部の周辺に設けられた下段羽口4から空気が供給される。このような構成における還元溶融炉1の炉上部から、廃棄物および副原料としてコークスおよび石灰石が装入装置2から装入される。装入された廃棄物およびコークス等は炉内で充填層を形成し、上段羽口3および下段羽口4から吹き込まれた空気により、廃棄物の可燃分およびコークスが還元燃焼する。この燃焼ガスは溶融炉内を炉下部から上昇し、廃棄物を予熱、乾燥、熱分解する。廃棄物を予熱、乾燥、熱分解の過程で発生した水蒸気、熱分解ガス等は還元溶融炉1の炉上部に設けたガス排出管8から排出される。一方、熱分解残渣は溶融状態となってスラグ排出孔9から炉外へ排出される。
【0004】
上述した一般廃棄物や産業廃棄物を処理するシャフト炉方式、堅型炉方式では、溶融炉上部から石灰石、コークスと共に供給されたごみは、予熱乾燥帯において水分を蒸発させる。乾燥したごみは降下し、熱分解帯で可燃性ガスと可燃性物に熱分解され、可燃性物は燃焼帯で燃焼する。高温の可燃性物燃焼残渣は、予め供給されたコークスと共に、さらに溶融帯に降下する。炉底部には空気供給羽口が設けられ、この空気供給羽口から供給された酸素富化空気により、コークスを高温燃焼させ、可燃性物燃焼残渣を完全に溶融する。溶融物は予め供給された石灰石により塩基度を調整され、適度な流動性を保持しながら、出湯孔から排出されるものである。この方法は溶融物の性状が安定かつ均質で、各種資材として利用価値が高く、最終処分量が極少化される優れたものである。
【0005】
【引用文献】
(1)特許文献1(特開2002−48321号公報)
【0006】
【発明が解決しようとする課題】
しかしながら、上述したシャフト炉方式、堅型炉方式では、溶融炉上部から廃棄物および石灰石やコークスを投入して、炉の上部より排ガスを排出する方式であって、この排ガスの温度は廃棄物の投入された充填廃棄物レベルより、上部より排出されるために、この排ガス中に投入された廃棄物の水分をそのまま含んでいたり、O2が残存する酸性の排ガスであり、かつ、この投入される常温の廃棄物やそれに含まれる水分によって、常に低温化され、この排ガスの温度は常温から100℃程度と低く、さらには、排ガスの組成は投入された廃棄物中の水分によって大きく変化し、排ガスの組成は投入された廃棄物中の空気によってN2やO2やCO2も含まれる。
【0007】
上述したように、従来の溶融炉は上部より排ガスを排出する方式であるために、一般廃棄物や産業廃棄物を処理することにより発生する排ガスの温度が低下し、ダイオキシンが発生するという問題点があった。一方、排ガスの温度が下がるため、次工程の2次燃焼でバーナーにより助燃せざるを得ないという問題があった。そのために、排ガスはそのまま廃棄される廃棄ガスでしかなかったのが現状である。
【0008】
【発明が解決しようとする手段】
上述したような問題を解消するため、発明者らは鋭意開発を進めた結果、溶融炉内より発生する炉内の高温ガスを溶融炉内で投入された廃棄物の充填高さレベルとコークスの充填高さレベルよりも低い位置に上昇管を持つ還元溶融炉およびそれを用いた方法を提供するものである。その発明に要旨とするところは、
(1)廃棄物の還元溶融炉において、廃棄物の投入する投入口下端に配設した投入ダンパー仕切弁より下部位置で、かつ溶融炉内に投入された廃棄物とコークスの充填高さレベルより排ガス高さレベルの距離を3m以上の低い位置に上昇管を配設し、該上昇管より高温還元ガスを回収可能としたことを特徴とする還元溶融炉。
【0009】
)廃棄物の溶融炉内より発生する高温ガス排出において、廃棄物の投入する投入口下端に配設した投入ダンパー仕切弁より下部位置で、かつ溶融炉内に投入された廃棄物とコークスの充填高さレベルより排ガス高さレベルの距離を3m以上の低い位置に、高温還元ガスを排出することのできる上昇管を有し、投入された廃棄物を溶融処理し廃棄中の水分を過熱蒸気とし、廃棄物を320℃以上の高温還元ガスに熱分解させ、残存酸素量0.5%以下の高温還元ガスに変換させた後、該高温還元ガスを上記上昇管から排出させてエネギーとして回収することを特徴とする高温還元ガス回収方法。
)前記()記載の廃棄物の溶融炉にて1000〜2600℃での高温溶融させ、上昇管より排出する残存酸素量が0.5%以下の高温還元ガス温度および濃度に制御することを特徴とする高温還元ガス回収方法にある。
【0010】
【発明の実施の形態】
以下、本発明について図面に従って詳細に説明する。
図1は、本発明に係る還元溶融炉の全体概略図である。この図1に示すように、還元溶融炉1上部に設けられた装入装置2から投入ダンパー仕切弁10が開かれ石灰石、コークスと共に供給された廃棄物は、徐々に降下し、廃棄物とコークスの充填高さレベル11以降に達し、廃棄物と燃料コークスの充填層12での熱分解帯で可燃性ガスと可燃性物に熱分解され、可燃性物は燃焼帯で燃焼する。高温の可燃性物燃焼残渣は、予め供給されたコークスと共に、さらに溶融帯13に降下する。炉底部7には上段羽口3、中段羽口17および下段羽口4が設けられ、この空気供給羽口から供給された酸素富化空気により、コークスを高温燃焼させ、可燃性物燃焼残渣14を完全に溶融する。溶融物は予め供給された石灰石により塩基度を調整され、適度な流動性を保持しながら、スラグ排出孔9から排出されるものである。なお、符号16は溶融滴下帯を示す。
【0011】
一方、ガスの排出口12は廃棄物の投入する投入口2下端に配設した投入ダンパー仕切弁10より下部位置で、かつ溶融炉内に投入された廃棄物とコークスの充填高さレベル11より低い位置に、高温還元ガスを排出することのできる上昇管15を設ける。この上昇管15の位置は出来るだけ廃棄物が溶融状態で存在する直上に設けるのが望ましく、溶融体の影響のない、しかもO2 含有量が急激に低下し高温還元ガスのリッチな箇所に設ける必要がある。そのためには、具体的なものとしては、充填高さレベルの3mより低い位置に設けのが最適である。これによって、高温還元ガスとして回収することが出来るものである。
【0012】
図2は、充填高さレベルと排ガス高さレベルの距離とH2 ガス濃度との関係を示す図である。この図に示すように、充填高さレベルと排ガス高さレベルとの距離が3mを超えると急激にH2 ガス濃度の上昇が行われることが判る。また、図3は、充填高さレベルと排ガス高さレベルの距離と残存O2 濃度との関係を示す図である。この図に示すように、充填高さレベルと排ガス高さレベルの距離がH2 ガス濃度の場合と同じように、充填高さレベルと排ガス高さレベルの距離が3mを超えると急激に残存O2 濃度の低下することが判る。これから判るように、充填高さレベルと排ガス高さレベルの距離を3m以上に設計すれば、残存O2 濃度を含まないH2 ガス濃度の高いガスを回収することが出来ることが判る。
【0013】
上記したような溶融炉内より発生する炉内の高温ガスを溶融炉内で投入された廃棄物の充填高さレベルおよびコークスの充填高さレベルよりも低い位置に上昇管を持つ構造の還元溶融炉にしたことから、排ガスの温度は廃棄物およびコークスの充填高さレベルより低くなっているため、炉下部1300〜2400℃の赤熱コークスに近づき、その排ガス温度は800〜2000℃の高温となり、ダイオキシンの発生を抑え、また、H2OはH2に分解され、他の廃棄物も高温熱分解するため、H2やCOガスなどの還元性ガスとなって排出される。しかも、高温の還元性のガスに制御ができる還元溶融炉である。従って、このガスは廃棄ガスではなくエネルギーガスとして回収することが可能である。
【0014】
以下、本発明について実施例によって具体的に説明する。
【実施例】
図1に基づく還元溶融炉を用いて、還元溶融炉1の上部から廃棄物および副原料としてコークスおよび石灰石が還元溶融炉1に装入される。廃棄物として都市ごみを処理した。その都市ごみの性状は、灰物8.2%、水分18.5%、可燃物73.3%のものを使用し、還元溶融炉1の下部周辺に設けられた上段羽口3、中段羽口17および下段羽口4から空気および酸素が供給される。廃棄物の処理量は395kg/h、コークスおよび石灰石は廃棄物の約27%、空気は12Nm3 /hであり、その空気および酸素量は上段羽口3Nm3 /h、中段羽口3Nm3 /h、下段羽口6Nm3 /h、の条件で吹き込んだ。還元溶融炉に装入された廃棄物およびコークス等は炉内で充填層を形成し、上段羽口3、中段羽口17および下段羽口4から吹き込まれた空気および酸素により、廃棄物を溶融処理し廃棄中の水分を過熱蒸気とし、廃棄物を320℃以上、2000℃以下の高温還元ガスに熱分解させ、残存酸素量0.5%以下の高温還元ガスに変換させる。
【0015】
この燃焼ガスは還元溶融炉内を炉下部から上昇し、溶融炉内に投入された廃棄物とコークスの充填高さレベルより低い位置に、高温還元ガスを排出することのできる上昇管15から排出させてエネギーとして回収する。排出されたガスの温度およびダイオキシン濃度は従来の場合は、ガス温度が98〜220℃であるに対し、本発明の場合は875℃〜2000℃と高く、また、ダイオキシン濃度は従来0.42ng−TEQ/Nm3 に対し、0.002ng−TEQ/Nm3 と激減していることが判る。また、排出されたガス温度が従来よりも高く回収可能となったことから、高温ガスを活用した発電力も大幅に高くなりエネルギー回収率が高くなった。
【0016】
【発明の効果】
以上述べたように、本発明により排出されるガス温度は従来方式よりも320℃〜2000℃と高温となり、ダイオキシン濃度が大幅に低下し、かつ高温ガスを活用した発電力も大幅に高くなりエネルギー回収率が高くなる一方、COリッチ状態となり、発生した還元ガスを燃料として利用できる等極めて優れた効果を奏するものである。
【図面の簡単な説明】
【図1】本発明に係る還元溶融炉の全体概略図である。
【図2】充填高さレベルと排ガス高さレベルとの距離(△h)とH2 ガス濃度との関係を示す図である。
【図3】充填高さレベルと排ガス高さレベルとの距離(△h)と残存O2 濃度との関係を示す図である。
【図4】従来の堅型炉方式の廃棄物溶融炉の全体概略図である
【符号の説明】
1 還元溶融炉
2 装入装置
3 上段羽口
4 下段羽口
5 シャフト部
6 朝顔部
7 炉下部
8 ガス排出管
9 スラグ排出孔
10 投入ダンパー仕切弁
11 充填高さレベル
12 充填層
13 溶融帯
14 可燃性物燃焼残渣
15 上昇管
16 溶融滴下帯
17 中段羽口
18 排ガス高さレベル
19 △h(充填高さレベル−排ガス高さレベル)
[0001]
BACKGROUND OF THE INVENTION
The present invention suppresses the generation of dioxins by reducing the position where the pyrolyzed gas generated in the process of treating general waste and industrial waste, etc., in the process of processing is lower than the filling height level, and reducing gas. The present invention relates to a reduction melting furnace that recovers the energy of the gas and a high-temperature reducing gas recovery method using the same.
[0002]
[Prior art]
In recent years, the amount of general waste, so-called municipal waste, has increased, and most of these waste (hereinafter referred to as general waste, industrial waste, incinerated ash, incombustibles, etc.) has been reduced by incineration and incinerated. Landfilled in landfill as ash or incombustible. However, the increase in the amount of municipal waste generated is developing as a problem of shortage of final disposal sites such as incineration residue of municipal waste. In order to cope with these, a waste direct melting method has been proposed. As an example, general waste is made to be useful resources such as slag by a waste direct melting furnace to which iron manufacturing technology as disclosed in Patent Document 1 is applied. In the case of this waste direct melting furnace, the oxygen atmosphere is in an atmosphere of 3 to 21% and incineration is performed at 100 to 1200 ° C. As a result, incineration ash and unburned substances are actually obtained. is there.
[0003]
FIG. 4 is an overall schematic view of a conventional solid furnace type waste melting furnace. As shown in this figure, the reduction melting furnace 1 is composed of a shaft part 5, a morning glory part 6 and a furnace bottom part 7, and an upper tuyere 3 provided around the morning glory part and a lower stage feather provided around the lower part of the furnace. Air is supplied from the mouth 4. Coke and limestone are charged from the charging device 2 as waste and auxiliary materials from the upper part of the reduction melting furnace 1 having such a configuration. The charged waste and coke form a packed bed in the furnace, and the combustible waste and coke are reduced and burned by the air blown from the upper tuyere 3 and the lower tuyere 4. This combustion gas rises in the melting furnace from the lower part of the furnace and preheats, dries, and thermally decomposes the waste. Water vapor, pyrolysis gas, etc. generated in the process of preheating, drying and pyrolysis of the waste are discharged from a gas discharge pipe 8 provided in the upper part of the reduction melting furnace 1. On the other hand, the pyrolysis residue is in a molten state and discharged from the slag discharge hole 9 to the outside of the furnace.
[0004]
In the shaft furnace method and the solid furnace method for treating general waste and industrial waste described above, the waste supplied together with limestone and coke from the upper part of the melting furnace evaporates moisture in the preheating drying zone. The dried waste falls and is pyrolyzed into combustible gas and combustible material in the pyrolysis zone, and the combustible material burns in the combustion zone. The high-temperature combustible material combustion residue further falls to the melting zone together with the coke supplied in advance. An air supply tuyere is provided at the bottom of the furnace, and coke is burned at a high temperature by the oxygen-enriched air fed from the air feed tuyere and the combustible combustion residue is completely melted. The basicity of the melt is adjusted by limestone supplied in advance, and the melt is discharged from the tapping hole while maintaining appropriate fluidity. This method is excellent in that the property of the melt is stable and homogeneous, the utility value as various materials is high, and the final disposal amount is minimized.
[0005]
[Cited document]
(1) Patent Document 1 (Japanese Patent Laid-Open No. 2002-48321)
[0006]
[Problems to be solved by the invention]
However, in the shaft furnace method and the solid furnace method described above, waste and limestone or coke are introduced from the upper part of the melting furnace, and exhaust gas is discharged from the upper part of the furnace. Since it is discharged from the upper part from the level of the charged waste that has been input, it is an acidic exhaust gas that contains the moisture of the input waste in the exhaust gas as it is or has O 2 remaining, and this input The temperature of the exhaust gas is constantly lowered from room temperature to about 100 ° C., and the composition of the exhaust gas varies greatly depending on the water in the waste that has been input, The composition of the exhaust gas includes N 2 , O 2, and CO 2 depending on the air in the input waste.
[0007]
As described above, since the conventional melting furnace is a method of exhausting exhaust gas from the top, the temperature of exhaust gas generated by processing general waste and industrial waste is lowered, and dioxins are generated. was there. On the other hand, since the temperature of the exhaust gas is lowered, there is a problem that the burner must be assisted by the secondary combustion in the next step. Therefore, the present situation is that the exhaust gas is only a waste gas that is discarded as it is.
[0008]
Means to be Solved by the Invention
In order to solve the above-mentioned problems, the inventors have made extensive developments. As a result, the high temperature gas generated in the melting furnace and the filling height level of the waste charged in the melting furnace and the coke A reduction melting furnace having a riser at a position lower than a filling height level and a method using the same are provided. The gist of the invention is that
(1) In a reduction melting furnace for waste, at a lower position than a charging damper gate valve disposed at the lower end of the charging inlet, and from a filling height level of waste and coke charged in the melting furnace. A reductive melting furnace characterized in that a riser pipe is disposed at a position where the exhaust gas height level is as low as 3 m or more , and high temperature reducing gas can be recovered from the riser pipe.
[0009]
( 2 ) When discharging high-temperature gas generated from the melting furnace of waste, the waste and coke put into the melting furnace at a position lower than the charging damper gate valve disposed at the lower end of the charging inlet. It has a riser pipe that can discharge high-temperature reducing gas at a position 3m or more lower than the filling height level of the exhaust gas, and melts the input waste to overheat the waste water. Steam, waste is thermally decomposed into a high-temperature reducing gas of 320 ° C. or higher and converted into a high-temperature reducing gas having a residual oxygen content of 0.5% or less, and then the high-temperature reducing gas is discharged from the riser as energy. A high temperature reducing gas recovery method characterized by recovering.
( 3 ) The waste melting furnace described in ( 2 ) is melted at a high temperature of 1000 to 2600 ° C., and the amount of residual oxygen discharged from the riser is controlled to a high temperature reducing gas temperature and concentration of 0.5% or less. It is in the high temperature reducing gas recovery method characterized by this.
[0010]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the present invention will be described in detail with reference to the drawings.
FIG. 1 is an overall schematic view of a reductive melting furnace according to the present invention. As shown in FIG. 1, the waste damper gate valve 10 is opened from the charging device 2 provided in the upper part of the reduction melting furnace 1 and the waste supplied together with limestone and coke is gradually lowered, and the waste and coke. Is reached, and is pyrolyzed into combustible gas and combustible material in the pyrolysis zone of the waste and fuel coke packed bed 12, and the combustible material burns in the combustion zone. The high-temperature combustible material combustion residue further falls to the melting zone 13 together with the coke supplied in advance. The upper bottom tuyere 3, the middle tuyere tuyere 17 and the lower tuyere tuyere 4 are provided in the furnace bottom 7, and the coke is burned at a high temperature by the oxygen-enriched air supplied from the air supply tuyere, and the combustible combustion residue 14 To completely melt. The melt is discharged from the slag discharge hole 9 while the basicity is adjusted by the limestone supplied in advance and the appropriate fluidity is maintained. Reference numeral 16 denotes a melt dripping zone.
[0011]
On the other hand, the gas discharge port 12 is at a lower position than the input damper gate valve 10 disposed at the lower end of the input port 2 into which the waste is input, and from the filling level 11 of the waste and coke charged into the melting furnace. A rising pipe 15 capable of discharging the high temperature reducing gas is provided at a low position. The position of the riser 15 is preferably provided immediately above the waste in a molten state as much as possible. The riser 15 is provided at a location where there is no influence of the melt, and the O 2 content is drastically reduced and the hot reducing gas is rich. There is a need. For that purpose, it is optimal to provide at a position lower than the filling height level of 3 m. Thereby, it can be recovered as a high-temperature reducing gas.
[0012]
FIG. 2 is a diagram showing the relationship between the distance between the filling height level and the exhaust gas height level and the H 2 gas concentration. As shown in this figure, it can be seen that when the distance between the filling height level and the exhaust gas height level exceeds 3 m, the H 2 gas concentration is rapidly increased. FIG. 3 is a graph showing the relationship between the distance between the filling height level, the exhaust gas height level, and the residual O 2 concentration. As shown in this figure, as in the case where the distance between the filling height level and the exhaust gas height level is H 2 gas concentration, when the distance between the filling height level and the exhaust gas height level exceeds 3 m, the residual O 2 It can be seen that the concentration decreases. As can be seen, it can be seen that if the distance between the filling height level and the exhaust gas height level is designed to be 3 m or more, a gas having a high H 2 gas concentration that does not contain the residual O 2 concentration can be recovered.
[0013]
Reductive melting of a structure having a riser pipe at a position lower than the filling height level of waste and the filling height level of coke charged in the melting furnace with the high-temperature gas generated in the melting furnace as described above Since the furnace was made into a furnace, the exhaust gas temperature was lower than the waste and coke filling height level, so it approached the red hot coke at the bottom of the furnace 1300-2400 ° C, and the exhaust gas temperature was 800-2000 ° C, Generation of dioxins is suppressed, H 2 O is decomposed into H 2 , and other wastes are also thermally decomposed at high temperature, so that they are discharged as reducing gases such as H 2 and CO gas. Moreover, it is a reducing melting furnace that can be controlled to a high-temperature reducing gas. Therefore, this gas can be recovered not as waste gas but as energy gas.
[0014]
Hereinafter, the present invention will be specifically described with reference to examples.
【Example】
Using the reduction melting furnace based on FIG. 1, coke and limestone are charged into the reduction melting furnace 1 from the top of the reduction melting furnace 1 as waste and auxiliary materials. Municipal waste was treated as waste. The municipal waste is composed of 8.2% ash, 18.5% moisture, and 73.3% combustible material. Air and oxygen are supplied from the mouth 17 and the lower tuyere 4. About 27% of the throughput of waste 395kg / h, coke and limestone waste, air is 12Nm 3 / h, the air and oxygen are upper tuyere 3 Nm 3 / h, middle tuyere 3 Nm 3 / It was blown under the conditions of h, lower tuyere 6 Nm 3 / h. Waste and coke charged in the reduction melting furnace form a packed bed in the furnace, and the waste is melted by air and oxygen blown from the upper tuyere 3, the middle tuyere 17 and the lower tuyere 4 The water in the treated waste is converted into superheated steam, and the waste is thermally decomposed into a high-temperature reducing gas of 320 ° C. or more and 2000 ° C. or less and converted into a high-temperature reducing gas having a residual oxygen content of 0.5% or less.
[0015]
This combustion gas rises in the reduction melting furnace from the lower part of the furnace, and is discharged from the riser 15 which can discharge the high temperature reducing gas at a position lower than the filling height level of waste and coke charged in the melting furnace. And collect it as energy. The temperature of the discharged gas and the dioxin concentration in the conventional case are 98 to 220 ° C., whereas in the present invention, the gas temperature is as high as 875 to 2000 ° C., and the dioxin concentration is 0.42 ng− for TEQ / Nm 3, it can be seen that depleted the 0.002ng-TEQ / Nm 3. In addition, since the discharged gas temperature can be recovered higher than before, the power generation using the high-temperature gas is significantly increased and the energy recovery rate is increased.
[0016]
【The invention's effect】
As described above, the temperature of the gas discharged by the present invention is 320 ° C to 2000 ° C higher than that of the conventional method, the dioxin concentration is greatly reduced, and the power generation utilizing the high temperature gas is also greatly increased, resulting in energy recovery. On the other hand, the rate becomes high, and it becomes a CO-rich state, and there is an extremely excellent effect such that the generated reducing gas can be used as fuel.
[Brief description of the drawings]
FIG. 1 is an overall schematic view of a reduction melting furnace according to the present invention.
FIG. 2 is a diagram showing the relationship between the distance (Δh) between the filling height level and the exhaust gas height level and the H 2 gas concentration.
FIG. 3 is a graph showing a relationship between a distance (Δh) between a filling height level and an exhaust gas height level and a residual O 2 concentration.
FIG. 4 is an overall schematic diagram of a conventional solid furnace type waste melting furnace.
DESCRIPTION OF SYMBOLS 1 Reduction melting furnace 2 Charging apparatus 3 Upper tuyere 4 Lower tuyere 5 Shaft part 6 Morning glory part 7 Furnace lower part 8 Gas discharge pipe 9 Slag discharge hole 10 Input damper gate valve 11 Filling height level 12 Packing bed 13 Melting zone 14 Combustible residue 15 Ascending pipe 16 Melting drip zone 17 Middle tuyere 18 Exhaust gas height level 19 Δh (filling height level minus exhaust gas height level)

Claims (3)

廃棄物の還元溶融炉において、廃棄物の投入する投入口下端に配設した投入ダンパー仕切弁より下部位置で、かつ溶融炉内に投入された廃棄物とコークスの充填高さレベルより排ガス高さレベルの距離を3m以上の低い位置に上昇管を配設し、該上昇管より高温還元ガスを回収可能としたことを特徴とする還元溶融炉。In a reductive melting furnace for waste, the exhaust gas height is lower than the input damper gate valve disposed at the lower end of the charging inlet and the exhaust gas height is higher than the filling height level of waste and coke charged in the melting furnace. A reductive melting furnace characterized in that a riser pipe is arranged at a low position with a level distance of 3 m or more , and high temperature reducing gas can be recovered from the riser pipe. 廃棄物の溶融炉内より発生する高温ガス排出において、廃棄物の投入する投入口下端に配設した投入ダンパー仕切弁より下部位置で、かつ溶融炉内に投入された廃棄物とコークスの充填高さレベルより排ガス高さレベルの距離を3m以上の低い位置に、高温還元ガスを排出することのできる上昇管を有し、投入された廃棄物を溶融処理し廃棄中の水分を過熱蒸気とし、廃棄物を320℃以上の高温還元ガスに熱分解させ、残存酸素量0.5%以下の高温還元ガスに変換させた後、該高温還元ガスを上記上昇管から排出させてエネギーとして回収することを特徴とする高温還元ガス回収方法。When discharging high-temperature gas from the waste melting furnace, the filling height of the waste and coke charged into the melting furnace is lower than the charging damper gate valve disposed at the lower end of the charging inlet. It has a riser pipe that can discharge high-temperature reducing gas at a position where the distance of the exhaust gas height level is 3 m or more lower than the height level, melts the waste that has been thrown in, and makes the water in waste superheated steam, The waste is thermally decomposed into a high-temperature reducing gas of 320 ° C. or higher and converted into a high-temperature reducing gas having a residual oxygen content of 0.5% or less, and then the high-temperature reducing gas is discharged from the riser and recovered as energy. A high-temperature reducing gas recovery method characterized by the above. 請求項記載の廃棄物の溶融炉にて1000〜2600℃での高温溶融させ、上昇管より排出する残存酸素量が0.5%以下の高温還元ガス温度および濃度に制御することを特徴とする高温還元ガス回収方法。A waste melting furnace according to claim 2, wherein the waste is melted at a high temperature of 1000 to 2600 ° C, and the amount of residual oxygen discharged from the riser is controlled to a high temperature reducing gas temperature and concentration of 0.5% or less. High temperature reducing gas recovery method.
JP2002299134A 2002-10-11 2002-10-11 Reduction melting furnace and high temperature reducing gas recovery method using the same Expired - Fee Related JP4038536B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2002299134A JP4038536B2 (en) 2002-10-11 2002-10-11 Reduction melting furnace and high temperature reducing gas recovery method using the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2002299134A JP4038536B2 (en) 2002-10-11 2002-10-11 Reduction melting furnace and high temperature reducing gas recovery method using the same

Publications (2)

Publication Number Publication Date
JP2004132655A JP2004132655A (en) 2004-04-30
JP4038536B2 true JP4038536B2 (en) 2008-01-30

Family

ID=32288359

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2002299134A Expired - Fee Related JP4038536B2 (en) 2002-10-11 2002-10-11 Reduction melting furnace and high temperature reducing gas recovery method using the same

Country Status (1)

Country Link
JP (1) JP4038536B2 (en)

Also Published As

Publication number Publication date
JP2004132655A (en) 2004-04-30

Similar Documents

Publication Publication Date Title
JP5180917B2 (en) Waste melting treatment method and waste melting treatment apparatus
KR100513932B1 (en) A pyrolyser heating wastes directly by exhaust gas of a melting furnace and the pyrolysis process using the pyroser
CN1506613A (en) Domestic garbage gasification melting self-incineration treatment method
JP4038536B2 (en) Reduction melting furnace and high temperature reducing gas recovery method using the same
JP4734776B2 (en) Organic or hydrocarbon waste recycling method and blast furnace equipment suitable for recycling
CN209909919U (en) Integrated plasma grate furnace
JP2001227713A (en) Melting furnace for refuse
JPH10169944A (en) Fluidized layer control method in waste thermal decomposition furnace
CN117663148B (en) Two-stage type plasma gasification and melting medical waste treatment device and process
JP3791853B2 (en) Gasification of solid waste and gasification combustion method
JP4520673B2 (en) Method of injecting combustible dust into a waste melting furnace
KR20060017963A (en) Second gas reflux system of waste incinerator
JP2629117B2 (en) Waste melting furnace
JP3732013B2 (en) Waste plastic injection into waste melting furnace
JP4336743B2 (en) High-temperature smelting reduction gasification method for waste livestock products and their discharge
JP3015266B2 (en) Waste melting equipment
JP3759200B2 (en) Thermal decomposition / melting method and apparatus for waste
JPH06129618A (en) Melt treatment method for waste
CN2628884Y (en) Solid garbage incinerator
JP2006170609A (en) Gasification of solid waste and gasification combustion method
JP3071172B2 (en) Waste melting equipment
JP2823978B2 (en) Waste melting furnace
JP4336226B2 (en) Waste melting treatment method
JP2001280621A (en) Waste treatment method
JPH0894037A (en) Waste melting furnace

Legal Events

Date Code Title Description
A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20050511

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20070522

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20070717

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20070814

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20070815

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20071109

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101116

Year of fee payment: 3

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101116

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101116

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101116

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101116

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20101116

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20111116

Year of fee payment: 4

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20121116

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20131116

Year of fee payment: 6

LAPS Cancellation because of no payment of annual fees