JP3511609B2 - Melt processing method of mixture of incineration ash and fly ash - Google Patents

Melt processing method of mixture of incineration ash and fly ash

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Publication number
JP3511609B2
JP3511609B2 JP12833594A JP12833594A JP3511609B2 JP 3511609 B2 JP3511609 B2 JP 3511609B2 JP 12833594 A JP12833594 A JP 12833594A JP 12833594 A JP12833594 A JP 12833594A JP 3511609 B2 JP3511609 B2 JP 3511609B2
Authority
JP
Japan
Prior art keywords
ash
fly ash
mixture
incinerated
melting
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 - Lifetime
Application number
JP12833594A
Other languages
Japanese (ja)
Other versions
JPH07308650A (en
Inventor
▲紘▼一郎 金藤
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.)
Daido Steel Co Ltd
Original Assignee
Daido Steel Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Daido Steel Co Ltd filed Critical Daido Steel Co Ltd
Priority to JP12833594A priority Critical patent/JP3511609B2/en
Priority to US08/436,731 priority patent/US5511495A/en
Priority to DE69501426T priority patent/DE69501426T2/en
Priority to EP95303202A priority patent/EP0683140B1/en
Publication of JPH07308650A publication Critical patent/JPH07308650A/en
Application granted granted Critical
Publication of JP3511609B2 publication Critical patent/JP3511609B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は焼却灰と飛灰との混合物
の溶融処理方法に関する。都市ごみや産業廃棄物等の焼
却灰、これらを焼却処理する際に発生する飛灰をアーク
炉、プラズマアーク炉、抵抗炉、誘導炉又はバーナ炉等
の溶融炉で溶融処理して、減容化及び無害化することが
行なわれる。本発明は上記のような焼却灰と飛灰との混
合物を溶融炉で溶融処理する方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a melt processing method for a mixture of incinerated ash and fly ash. Incineration ash of municipal waste and industrial waste, fly ash generated when incinerating these is melted in a melting furnace such as an arc furnace, plasma arc furnace, resistance furnace, induction furnace or burner furnace to reduce the volume. It is made to be harmless and harmless. The present invention relates to a method for melting and treating a mixture of incinerated ash and fly ash as described above in a melting furnace.

【0002】[0002]

【従来の技術】従来、焼却灰と飛灰との混合物の溶融処
理方法として、それぞれホッパに貯留しておいた焼却灰
と飛灰とをプッシャやロータリバルブで切り出してコン
ベア上に落下させ、双方を該コンベアで溶融炉へ搬送し
て投入することが行なわれている。ところが、かかる従
来法には次のような欠点がある。1)焼却灰はその飛散
や再燃焼を防止して取扱い易くするため、散水等で加湿
処理されるので、相当の水分を含有している。かかる焼
却灰は粘着性が強く、その安息角も大きいため、ホッパ
やコンベア等に付着し易く、ホッパ内でブリッジ現象を
生じて、しばしば目詰まりを引き起こす。また焼却灰の
水分が多いと、該焼却灰中のナトリウム成分から水酸化
ナトリウムを生じ、かかる焼却灰と飛灰とを混合する
と、水酸化ナトリウムが飛灰中の金属アルミニウムや亜
鉛等と反応して水素ガスを発生するので、誠に危険であ
る。2)それぞれホッパに貯留しておいた焼却灰と飛灰
とをプッシャやロータリバルブで切り出す従来法はホッ
パからその下部の一定空間に落下した焼却灰や飛灰を切
り出す所謂定容積方式によるものであるため、焼却灰や
飛灰の嵩比重が変わったり、或はホッパ内におけるそれ
らのレベルが変わったりすると、双方の切り出し重量が
変化し、溶融炉への投入重量も変化する。その結果、溶
融炉における溶融温度が変動し、生成する溶融スラグの
排出が不安定になる。3)切り出した焼却灰と飛灰とを
単にコンベア上へ落下させるだけであり、双方が充分に
混合されていないため、溶融炉へ投入する廃棄物の組成
が不均一であることに起因して、溶融炉内において一時
的に揮散分が多くなったり、或は部分的に未溶融の焼却
灰や飛灰が残ってこれらが溶融スラグと共に排出されて
しまう。
2. Description of the Related Art Conventionally, as a method for melting a mixture of incinerated ash and fly ash, the incinerated ash and fly ash stored in a hopper are cut out by a pusher or a rotary valve and dropped on a conveyor. Is carried to the melting furnace by the conveyor and charged. However, the conventional method has the following drawbacks. 1) The incinerated ash contains a considerable amount of water because it is humidified by sprinkling water or the like in order to prevent the incineration ash from scattering and reburning and making it easy to handle. Since such incinerated ash has a strong adhesiveness and a large angle of repose, it easily adheres to a hopper, a conveyor, etc., and a bridge phenomenon occurs in the hopper, often causing clogging. When the incinerated ash has a high water content, sodium hydroxide is produced from the sodium component in the incinerated ash, and when the incinerated ash and fly ash are mixed, sodium hydroxide reacts with metallic aluminum or zinc in the fly ash. Since it produces hydrogen gas, it is extremely dangerous. 2) The conventional method of cutting out the incineration ash and fly ash stored in the hopper with a pusher or a rotary valve is a so-called constant volume method in which the incineration ash and fly ash that have fallen from the hopper into a certain space below the hopper are cut out. Therefore, when the bulk specific gravity of incinerated ash or fly ash changes, or their level in the hopper changes, the cut-out weight of both changes, and the input weight to the melting furnace also changes. As a result, the melting temperature in the melting furnace fluctuates, and the discharge of the generated molten slag becomes unstable. 3) Because the incinerated ash and the fly ash that have been cut out are simply dropped onto the conveyor and both are not sufficiently mixed, this is because the composition of the waste to be put into the melting furnace is uneven. In the melting furnace, the amount of volatilization increases temporarily, or partially unmelted incinerated ash or fly ash remains and these are discharged together with the molten slag.

【0003】[0003]

【発明が解決しようとする課題】本発明が解決しようと
する課題は、従来法には前述したような1)〜3)の欠
点があり、つまるところ従来法では、焼却灰と飛灰とを
継続的に安定して溶融処理できない点である。
The problem to be solved by the present invention is that the conventional method has the drawbacks of 1) to 3) as described above, and in the end, in the conventional method, incineration ash and fly ash are continuously produced. The point is that the melt processing cannot be performed stably.

【0004】[0004]

【課題を解決するための手段】しかして本発明は、焼却
灰を乾燥処理して水分12重量%以下にしたものと飛灰
とを別々に切り出し、各々の重量を秤量した後、双方を
混合機で混合して、組成を均一化した混合物を溶融炉へ
投入することを特徴とする焼却灰と飛灰との混合物の溶
融処理方法に係る。
SUMMARY OF THE INVENTION In the present invention, however, incinerated ash that has been dried to a water content of 12% by weight or less and fly ash are cut out separately, and the respective weights are weighed and then both are mixed. The present invention relates to a melting treatment method for a mixture of incinerated ash and fly ash, which is characterized in that a mixture having a uniform composition is charged into a melting furnace by mixing with a machine.

【0005】本発明において溶融処理の対象となる焼却
灰は都市ごみや産業廃棄物等の焼却残渣である。前述し
たようにかかる焼却灰は通常、取扱い易くするため、加
湿処理されている。また飛灰は上記の都市ごみ等を焼却
処理する際、排ガスと共に揮散して集塵装置で捕捉され
る捕捉物である。かかる飛灰はその捕捉時の水分が殆ど
0%で、非常に小さい粒度(1〜数十μm)を有し、再
加熱により有害物質を再揮散させ易い性質を持ってお
り、通常は焼却処理の際に発生する塩酸ガスを中和する
ため、水酸化カルシウムや炭酸カルシウム等の中和剤が
添加されている。本発明では上記のような焼却灰と飛灰
とを同時に溶融炉で溶融処理する。溶融処理に用いる溶
融炉はアーク炉、プラズマアーク炉、抵抗炉、誘導炉、
バーナ炉等である。
The incineration ash to be subjected to the melting treatment in the present invention is an incineration residue such as municipal waste or industrial waste. As described above, such incinerated ash is usually humidified for easy handling. Further, fly ash is a trapped substance that is volatilized together with the exhaust gas and captured by the dust collector when the above-mentioned municipal waste is incinerated. Such fly ash has a moisture content of almost 0% at the time of capture, has a very small particle size (1 to several tens of μm), and has the property of easily re-evaporating harmful substances by reheating, and is usually incinerated. A neutralizing agent such as calcium hydroxide or calcium carbonate is added to neutralize the hydrochloric acid gas generated at the time. In the present invention, the incineration ash and the fly ash as described above are simultaneously melt-processed in the melting furnace. The melting furnace used for the melting process is an arc furnace, a plasma arc furnace, a resistance furnace, an induction furnace,
For example, a burner furnace.

【0006】本発明では先ず、焼却灰を乾燥処理してそ
の水分を12重量%以下にする。水分が12重量%を超
えると、焼却灰の粘着性が急激に強くなり、安息角も急
激に大きくなって、それだけホッパやコンベア等に付着
し易くなり、投入工程の各所で目詰まりする頻度が高く
なるからである。また水分が多くなると、前述したよう
にそれだけ水素ガスを発生する危険が増すからである。
乾燥処理には回転形、ベルト形、トンネル形等、各種の
乾燥機を用いることができるが、熱風式ロータリードラ
イヤを用いるのが好ましい。焼却灰を飛灰と混合した後
に乾燥処理することも考えられるが、このようにする
と、乾燥時の加熱及び撹拌により微細な飛灰が乾燥排ガ
スに同伴して再飛散したり、またたとへ飛灰を造粒して
おいたとしてもかかる飛灰から乾燥時の加熱により有害
な低沸点物質が揮散して、結果的に後の溶融処理におけ
るスラグ化効率を低下させ、また有害物質無害化の目的
を阻害することになるので、不都合である。
In the present invention, first, the incinerated ash is dried to reduce its water content to 12% by weight or less. If the water content exceeds 12% by weight, the stickiness of the incineration ash will suddenly become strong and the angle of repose will also suddenly increase, making it easier to adhere to hoppers, conveyors, etc., and to cause clogging at various places during the loading process. Because it will be higher. Moreover, as the water content increases, the risk of generating hydrogen gas increases as described above.
Various types of dryers such as rotary type, belt type and tunnel type can be used for the drying treatment, but it is preferable to use a hot air rotary dryer. It is possible to mix the incinerated ash with the fly ash and then dry it.However, in this case, fine fly ash is entrained in the dry exhaust gas due to heating and agitation during drying, and is scattered again or again. Even if ash is granulated, harmful low-boiling-point substances are volatilized from the fly ash by heating at the time of drying, and as a result, the slag-forming efficiency in the subsequent melting process is reduced, and the harmful substances are rendered harmless. This is an inconvenience because it hinders the purpose.

【0007】乾燥処理に先立って焼却灰を篩分け処理
し、目開き25mm以下の篩を通過したものを乾燥処理す
るのが有利である。通常、焼却灰を破砕処理した後に篩
分け処理するが、破砕及び篩分け処理を同時に行なうこ
ともできる。いずれの場合も、破砕及び篩分け処理の経
済性を考慮しつつ、焼却灰の粒径を細かくし、その比表
面積を大きくすることによって、乾燥処理を効率的に行
ない、また後述する飛灰との混合をより均一に行なっ
て、更にその混合物の溶融処理をも効率的に行なうこと
ができるからである。破砕処理には各種のクラッシャや
ミルを用いることができるが、横形衝撃剪断併用式のハ
ンマーミルを用いるのが好ましく、また篩分け処理には
回転形、振動形、揺動形等、各種の篩を用いることがで
きるが、回転形篩を用いるのが好ましい。
It is advantageous that the incinerated ash is subjected to a sieving treatment prior to the drying treatment, and that which has passed through a sieve having an opening of 25 mm or less is dried. Usually, the incinerated ash is crushed and then sieved, but crushing and sieving can be performed simultaneously. In any case, while considering the economics of crushing and sieving treatment, the particle size of the incinerated ash is made finer, and by increasing the specific surface area, the drying treatment is efficiently performed, and the fly ash described later is also used. This is because the mixing can be performed more uniformly, and the melting treatment of the mixture can be efficiently performed. Various crushers and mills can be used for the crushing treatment, but it is preferable to use a hammer mill with a combination of horizontal impact shearing, and for the sieving treatment, various types of sieves such as a rotary type, a vibration type and a swing type are used. Can be used, but it is preferable to use a rotary sieve.

【0008】本発明では次に、水分12重量%以下に乾
燥した焼却灰と、飛灰とを別々に切り出し、各々の重量
を秤量する。焼却灰及び飛灰の各重量を秤量することに
より双方の切り出し重量及び結果的にその混合物の溶融
炉への投入重量を均一安定化して、溶融炉における溶融
温度及び生成する溶融スラグの排出を安定化させること
ができるからである。秤量手段それ自体は特に制限され
ないが、例えば焼却灰又は飛灰をスクレーパ付きのコン
ベアで搬送してロードセルで受けた容器に投入し、その
投入量が一定量になったときにロードセルから発せられ
る信号でコンベアとの間において容器の上方に設けた遮
断弁を閉じることにより、容器に一定量の焼却灰又は飛
灰を秤量することができる。
In the present invention, next, the incinerated ash and the fly ash which have been dried to a water content of 12% by weight or less are cut out separately and the respective weights are weighed. By weighing the weight of each of the incinerated ash and the fly ash, the cut-out weight of both and as a result, the weight of the mixture charged to the melting furnace is uniformly stabilized, and the melting temperature in the melting furnace and the discharge of the generated molten slag are stabilized. It is because it can be made into. Although the weighing means itself is not particularly limited, for example, a signal emitted from the load cell when the incinerated ash or the fly ash is conveyed by a conveyor with a scraper and put into the container received by the load cell, and the input amount becomes a constant amount. By closing the shutoff valve provided above the container between the container and the conveyor, a certain amount of incinerated ash or fly ash can be weighed in the container.

【0009】本発明では最後に、秤量した焼却灰と飛灰
とを混合する。混合によりその混合物の組成を均一化し
て、溶融炉において一時的に揮散分が多くなったり或は
部分的に未溶融の焼却灰や飛灰が残ったりするのを防止
できるからである。混合には回転形、振動形、揺動形
等、各種の混合機を用いることができるが、回転ドラム
式混合機を用いるのが好ましい。
In the present invention, finally, the weighed incinerated ash and fly ash are mixed. This is because the composition of the mixture can be made uniform by mixing, and it is possible to prevent a temporary increase in the amount of volatilization in the melting furnace or a part of unmelted incinerated ash or fly ash remaining. Various types of mixers such as a rotary type, a vibration type, and an oscillating type can be used for mixing, but it is preferable to use a rotating drum type mixer.

【0010】かくして焼却灰と飛灰とを混合した後、そ
の混合物を溶融炉へ投入する。投入に先立って混合物の
重量を再秤量することもできる。
After the incineration ash and the fly ash are mixed in this way, the mixture is put into a melting furnace. It is also possible to reweigh the mixture prior to dosing.

【0011】[0011]

【実施例】図1は本発明の一実施状態を示す工程図であ
る。焼却炉で発生した焼却灰を破砕し、篩分けして、そ
の通過物を乾燥している。そして乾燥した焼却灰と上記
焼却炉で発生した飛灰とを別々に切り出し、各々の重量
を秤量した後、双方を混合し、その混合物の重量を再秤
量して、溶融している。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is a process diagram showing an embodiment of the present invention. The incineration ash generated in the incinerator is crushed, sieved, and the passing material is dried. Then, the dried incinerated ash and the fly ash generated in the incinerator are cut out separately, the respective weights are weighed, both are mixed, and the weight of the mixture is re-weighed and melted.

【0012】図1について前述した工程図にしたがい、
都市ごみ焼却灰とその飛灰との混合物を溶融した。焼却
灰は横形衝撃剪断併用式のハンマーミルで破砕し、その
破砕物を回転形篩で篩分けして、目開き25mmの篩を通
過したものを熱風式ロータリードライヤで水分11重量
%に乾燥した。水分は赤外線式水分計で測定した。かく
して乾燥した焼却灰と、飛灰とを別々に切り出し、各々
の重量を前述したロードセルを用いた秤量手段で秤量し
て、焼却灰60重量部に対して飛灰40重量部の割合で
双方を回転ドラム式混合機により混合した。混合物の重
量を同様に再秤量した後、アーク炉へ投入した。かかる
操作を連続して一週間行なったところ、その間、投入工
程における焼却灰の付着や目詰まりは殆ど生ぜず、溶融
温度は1200±50℃で安定しており、溶融スラグの
排出も円滑であって、溶融スラグと共に未溶融の焼却灰
や飛灰が排出されるようなことはなかった。
According to the process diagram described above with reference to FIG.
A mixture of municipal waste incineration ash and its fly ash was melted. The incinerated ash was crushed with a horizontal impact shearing type hammer mill, the crushed material was sieved with a rotary sieve, and the material that passed through a sieve with an opening of 25 mm was dried to a water content of 11% by weight with a hot air rotary dryer. . The water content was measured with an infrared moisture meter. The incinerated ash thus dried and the fly ash are cut out separately, and the respective weights are weighed by the weighing means using the load cell described above, and both are in a ratio of 40 parts by weight of fly ash to 60 parts by weight of incinerated ash. Mix with a rotating drum mixer. The weight of the mixture was similarly re-weighed and then charged into an arc furnace. When such an operation was continuously carried out for one week, during that period, incineration ash was hardly attached or clogged in the charging process, the melting temperature was stable at 1200 ± 50 ° C, and the molten slag was discharged smoothly. As a result, unmelted incinerated ash and fly ash were not discharged together with the molten slag.

【0013】[0013]

【発明の効果】既に明らかなように、以上説明した本発
明には、焼却灰と飛灰とを継続的に安定して溶融処理で
きるという効果がある。
As is apparent from the above, the present invention described above has an effect that the incineration ash and the fly ash can be continuously and stably melt-processed.

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

【図1】本発明の一実施状態を示す工程図。FIG. 1 is a process drawing showing an embodiment of the present invention.

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B09B 3/00 - 5/00 F23G 5/00 F23G 7/00 F23J 1/00 ─────────────────────────────────────────────────── ─── Continuation of the front page (58) Fields surveyed (Int.Cl. 7 , DB name) B09B 3/00-5/00 F23G 5/00 F23G 7/00 F23J 1/00

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 焼却灰を乾燥処理して水分12重量%以
下にしたものと飛灰とを別々に切り出し、各々の重量を
秤量した後、双方を混合機で混合して、組成を均一化し
た混合物を溶融炉へ投入することを特徴とする焼却灰と
飛灰との混合物の溶融処理方法。
1. An incinerator ash that has been dried to a water content of 12% by weight or less and fly ash are cut out separately, each weight is weighed, and then both are mixed with a mixer to homogenize the composition.
A method for melting a mixture of incinerated ash and fly ash, which comprises charging the mixture into a melting furnace.
【請求項2】 焼却灰を篩分け処理して目開き25mm以
下の篩を通過したものを乾燥処理する請求項1記載の焼
却灰と飛灰との混合物の溶融処理方法。
2. The melting treatment method for a mixture of incinerated ash and fly ash according to claim 1, wherein the incinerated ash is subjected to a sieving treatment and passed through a sieve having an opening of 25 mm or less and dried.
JP12833594A 1994-05-17 1994-05-17 Melt processing method of mixture of incineration ash and fly ash Expired - Lifetime JP3511609B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP12833594A JP3511609B2 (en) 1994-05-17 1994-05-17 Melt processing method of mixture of incineration ash and fly ash
US08/436,731 US5511495A (en) 1994-05-17 1995-05-08 Method of processing a mixture of bottom ash and fly ash
DE69501426T DE69501426T2 (en) 1994-05-17 1995-05-12 Process for preparing a mixture of bottom ash and fly ash
EP95303202A EP0683140B1 (en) 1994-05-17 1995-05-12 Method of processing a mixture of bottom ash and fly ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12833594A JP3511609B2 (en) 1994-05-17 1994-05-17 Melt processing method of mixture of incineration ash and fly ash

Publications (2)

Publication Number Publication Date
JPH07308650A JPH07308650A (en) 1995-11-28
JP3511609B2 true JP3511609B2 (en) 2004-03-29

Family

ID=14982254

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