JPH0531475A - Treatment of ash - Google Patents
Treatment of ashInfo
- Publication number
- JPH0531475A JPH0531475A JP3194283A JP19428391A JPH0531475A JP H0531475 A JPH0531475 A JP H0531475A JP 3194283 A JP3194283 A JP 3194283A JP 19428391 A JP19428391 A JP 19428391A JP H0531475 A JPH0531475 A JP H0531475A
- Authority
- JP
- Japan
- Prior art keywords
- fly ash
- ash
- exhaust gas
- dust collector
- incinerator
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Landscapes
- Fire-Extinguishing Compositions (AREA)
- Chimneys And Flues (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
(57)【要約】
【目的】焼却炉からの排ガス中に含まれる飛灰中の微量
有機塩素化合物を分解除去する灰処理方法を提供する。
【構成】焼却炉11からの排ガス中に含まれる飛灰は第
1の集塵機14で捕集される。上記飛灰は焼却炉11か
らの400℃以上の高温排ガスと共に流され、その熱に
より上記飛灰中の微量有機塩素化合物が分解される。上
記高温排ガス中の上記飛灰は第2の集塵機19で再捕集
される。
(57) [Summary] [Purpose] To provide an ash treatment method for decomposing and removing trace organic chlorine compounds in fly ash contained in exhaust gas from an incinerator. [Structure] Fly ash contained in the exhaust gas from the incinerator 11 is collected by a first dust collector 14. The fly ash is caused to flow together with the high-temperature exhaust gas of 400 ° C. or higher from the incinerator 11, and the heat decomposes the trace amount of organic chlorine compounds in the fly ash. The fly ash in the high-temperature exhaust gas is recollected by the second dust collector 19.
Description
【0001】[0001]
【産業上の利用分野】本発明は、清掃工場から排出され
る飛灰中に含まれるダイオキシン類等の微量有機塩素化
合物の分解除去を行うための灰処理方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an ash treatment method for decomposing and removing trace amounts of organic chlorine compounds such as dioxins contained in fly ash discharged from a cleaning plant.
【0002】[0002]
【従来の技術】ごみ焼却プラントにおいて、ガスクーラ
または反応塔から捕集される灰(以下、総称してGC灰
と記す)、電気集塵機またはバグフィルタから捕集され
る灰(以下、総称してEP灰と記す)には、有害物質で
あるダイオキシン等の塩素系化合物が微量ではあるが含
有されていることが近年明らかになった。上記有害物質
の除去方法は、ごみ焼却プラントにおいていまだ無く、
早期に上記有害物質除去装置の開発が望まれている。2. Description of the Related Art In a refuse incineration plant, ash collected from a gas cooler or a reaction tower (hereinafter collectively referred to as GC ash), ash collected from an electrostatic precipitator or a bag filter (hereinafter collectively referred to as EP) It has recently been revealed that ash) contains a small amount of chlorinated compounds such as dioxin, which is a harmful substance. There is still no method of removing the above-mentioned harmful substances in the refuse incineration plant,
Development of the above-mentioned harmful substance removing device is desired at an early stage.
【0003】EP灰に含まれているダイオキシン等の従
来の除去技術としては、図2に示すようなものがある。
EP灰1は、図2の矢印Aの方向から処理装置に導入さ
れ、ヒータにより400〜600℃に加熱されたスクリ
ューコンベア3により搬送され、矢印Bの方向に排出さ
れる。この結果、EP灰中に含まれる有機塩素系化合物
であるポリ塩化ジベンゾダイオキシン(以下、PCDD
sと記す)、ポリ塩化ジベンゾフラン(以下、PCDF
sと記す)は分解され、590℃以上の時、PCDD
s、PCDFsは99%を超える除去率となる。なお図
中、符号5はコントローラ、7はモータ、9は回収部
(例えば缶詰)を夫々示す。(G. OK. Y. Hanal, Y. La
tou, "Dechlorination Techniques of PCDDs and PCDFs
in Fly Ashfrom Municipal Refuse Incineration Plant
s", 10th The International Conference on Organohal
ogen Compounds (1990), ps. 393-396. )A conventional technique for removing dioxins and the like contained in EP ash is shown in FIG.
The EP ash 1 is introduced into the processing apparatus from the direction of arrow A in FIG. 2, conveyed by the screw conveyor 3 heated to 400 to 600 ° C. by the heater, and discharged in the direction of arrow B. As a result, polychlorinated dibenzodioxin (hereinafter referred to as PCDD) which is an organic chlorine compound contained in EP ash.
s), polychlorinated dibenzofuran (hereinafter PCDF
s) is decomposed and PCDD
The removal rate of s and PCDFs exceeds 99%. In the figure, reference numeral 5 is a controller, 7 is a motor, and 9 is a recovery unit (for example, canned food). (G. OK. Y. Hanal, Y. La
tou, "Dechlorination Techniques of PCDDs and PCDFs
in Fly Ashfrom Municipal Refuse Incineration Plant
s ", 10th The International Conference on Organohal
ogen Compounds (1990), ps. 393-396.)
【0004】[0004]
【発明が解決しようとする課題】しかし、上記従来技術
では、GC灰やEP灰処理のために外部からヒータ等で
エネルギーを供給するため、ランニングコストが大きく
掛る。また、590℃を下回る温度ではダイオキシン等
の除去率が低下するが、原因は、灰温度にばらつきがあ
り、平均灰温度はより低い状態にあるためであると考え
られる。従って本発明は、灰中のダイオキシン類等の微
量有機塩素化合物を完全に分解除去しうる灰処理方法を
提供することを目的とする。However, in the above-mentioned prior art, since energy is externally supplied by a heater or the like for the treatment of GC ash and EP ash, the running cost is high. Further, the removal rate of dioxins and the like decreases at a temperature lower than 590 ° C., but it is considered that the cause is that the ash temperature varies and the average ash temperature is lower. Therefore, an object of the present invention is to provide an ash treatment method capable of completely decomposing and removing trace organic chlorine compounds such as dioxins in ash.
【0005】[0005]
【課題を解決するための手段】上記目的を達成するた
め、本発明の処理方法にあっては、焼却炉からの排ガス
中に含まれる飛灰を第1の集塵機で捕集する工程と、上
記飛灰を上記焼却炉からの400℃以上の高温排ガスと
共に流しながら、該高温排ガスが有する熱により上記飛
灰中の微量有機塩素化合物を分解する工程と、上記高温
排ガス中の上記飛灰を第2の集塵機で再捕集する工程
と、を具備することを特徴とする。To achieve the above object, in the treatment method of the present invention, a step of collecting fly ash contained in the exhaust gas from the incinerator by a first dust collector, A step of decomposing trace organic chlorine compounds in the fly ash by the heat of the high temperature exhaust gas while flowing the fly ash together with the high temperature exhaust gas of 400 ° C. or higher from the incinerator; And a step of re-collecting with a second dust collector.
【0006】[0006]
【作用】第1集塵機で捕集した飛灰中のダイオキシン等
の微量有機塩素化合物は、400℃以上の高温排ガスが
有する熱により分解される。上記飛灰は高温用の第2集
塵機で再捕集される。望ましくは、高温排ガスは第1集
塵機前のラインに戻される。The trace amount of organic chlorine compounds such as dioxins in the fly ash collected by the first dust collector is decomposed by the heat of the high temperature exhaust gas at 400 ° C or higher. The fly ash is recollected by the second dust collector for high temperature. Desirably, the hot exhaust gas is returned to the line in front of the first dust collector.
【0007】[0007]
【実施例】図1は本発明に係る灰処理方法を応用したシ
ステムの一実施例を示す図である。DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is a diagram showing an embodiment of a system to which the ash processing method according to the present invention is applied.
【0008】焼却炉11で発生した高温の排ガスはガス
混合室により未燃焼ガスが再燃焼した状態とされ、ボイ
ラ12で約350℃まで冷却される。次に消石灰スラリ
−による有害ガス除去装置13でHCl,SO4 が除去
され、集塵機14に達する。ここで飛灰は捕集され、更
に、集塵機14内のダスト層(未反応消石灰、酸性ガス
との反応生成物、飛灰等を主成分とする)によりダイオ
キシン類等の微量有機塩素化合物が除去される。飛灰が
除去され、クリーンになった排ガスは、IDF(誘引送
風機)15を経て煙突16により大気中に排出される。The high-temperature exhaust gas generated in the incinerator 11 is brought into a state where unburned gas is recombusted in the gas mixing chamber and cooled to about 350 ° C. in the boiler 12. Next, HCl and SO 4 are removed by the harmful gas removing device 13 using the slaked lime slurry, and the dust reaches the dust collector 14. Fly ash is collected here, and a trace amount of organic chlorine compounds such as dioxins is removed by a dust layer (mainly composed of unreacted slaked lime, reaction product with acidic gas, fly ash, etc.) in the dust collector 14. To be done. The exhaust gas that has been cleaned by removing the fly ash passes through the IDF (induction blower) 15 and is discharged into the atmosphere by the chimney 16.
【0009】一方捕集されたダイオキシン等の微量有機
塩素化合物を含む飛灰は、スクリューコンベヤ17を経
てシュ−ト18へ至る。ここにおいて、ダスト23によ
り800℃以上の高温排ガスが燃焼室出口からシュート
18へ流され、飛灰を高温集塵機19へ導く。シュート
18から高温集塵機19までの間でダイオキシン等の微
量有機塩素化合物は完全に分解除去される。高温集塵機
19により集められた飛灰は、スクリューコンベア20
で飛灰ホッパ21に回収される。On the other hand, the fly ash containing a trace amount of organic chlorine compounds such as dioxins, which has been collected, reaches the shoe 18 via the screw conveyor 17. Here, high temperature exhaust gas of 800 ° C. or higher is caused to flow from the combustion chamber outlet to the chute 18 by the dust 23, and guides fly ash to the high temperature dust collector 19. Between the chute 18 and the high-temperature dust collector 19, trace organic chlorine compounds such as dioxins are completely decomposed and removed. The fly ash collected by the high temperature dust collector 19 is transferred to the screw conveyor 20.
It is collected in the fly ash hopper 21.
【0010】ここで、燃焼室出口から導かれる高温排ガ
スの量は800Nm3 /hで、これはボイラ出口ダンパ
24、ダクト22のダンパ25で調整される。この時、
飛灰の排出量は150kg/h程度である。Here, the amount of high temperature exhaust gas introduced from the outlet of the combustion chamber is 800 Nm 3 / H, which is adjusted by the boiler outlet damper 24 and the damper 25 of the duct 22. At this time,
The amount of fly ash discharged is about 150 kg / h.
【0011】高温集塵機19としては、金属製織布、フ
ェルト、たわし状ワイヤによる濾過部材や、セラミック
フィルタによる濾過部材、或いは内面をキャスタブルレ
ンガで被覆したサイクロン等が採用できる。As the high temperature dust collector 19, a woven metal cloth, a felt, a filter member using a brush wire, a filter member using a ceramic filter, or a cyclone whose inner surface is covered with castable bricks can be used.
【0012】表1に図1図示装置における飛灰の分析結
果を示す。この結果に示されるように、本発明の処理方
法を応用したシステムにおいて、ホッパ21では、飛灰
中のPCDDs、PCDFsが殆ど完全に除去されてい
ることが分かる。Table 1 shows the analysis results of fly ash in the apparatus shown in FIG. As shown in this result, in the system to which the treatment method of the present invention is applied, the PCDDs and PCDFs in the fly ash are almost completely removed in the hopper 21.
【0013】[0013]
【表1】 [Table 1]
【0014】[0014]
【発明の効果】本発明に係る灰処理方法によれば、焼却
炉からの排ガス中のダイオキシン類等の微量有機塩素化
合物を、焼却炉自体の高温排ガスの熱を利用し、完全に
分解除去することができるようになる。According to the ash treatment method of the present invention, trace organic chlorine compounds such as dioxins in the exhaust gas from the incinerator are completely decomposed and removed by utilizing the heat of the high temperature exhaust gas of the incinerator itself. Will be able to.
【図1】本発明に係る灰処理方法を応用したシステムの
一実施例を示す図。FIG. 1 is a diagram showing an embodiment of a system to which an ash processing method according to the present invention is applied.
【図2】灰に含まれているダイオキシン等の従来の除去
技術を示す図。FIG. 2 is a view showing a conventional technology for removing dioxin contained in ash.
11…焼却炉、12…ボイラ、14…集塵機、16…煙
突、17…スクリューコンベヤ、19…高温集塵機、2
0…スクリューコンベア、21…ホッパ。11 ... incinerator, 12 ... boiler, 14 ... dust collector, 16 ... chimney, 17 ... screw conveyor, 19 ... high temperature dust collector, 2
0 ... Screw conveyor, 21 ... Hopper.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 森重 敦 東京都千代田区丸の内一丁目1番2号 日 本鋼管株式会社内 (72)発明者 伊藤 健太郎 東京都千代田区丸の内一丁目1番2号 日 本鋼管株式会社内 ─────────────────────────────────────────────────── (72) Inventor Atsushi Morishige Atsushi Marunouchi 1-2-2 Marunouchi, Chiyoda-ku, Tokyo Japan Steel Pipe Co., Ltd. (72) Kentaro Ito 1-2-1 Marunouchi Chiyoda-ku, Tokyo Inside the steel pipe company
Claims (1)
第1の集塵機で捕集する工程と、上記飛灰を上記焼却炉
からの400℃以上の高温排ガスと共に流しながら、該
高温排ガスが有する熱により上記飛灰中の微量有機塩素
化合物を分解する工程と、上記高温排ガス中の上記飛灰
を第2の集塵機で再捕集する工程と、を具備することを
特徴とする灰処理方法。Claims: 1. A step of collecting fly ash contained in exhaust gas from an incinerator with a first dust collector, and the fly ash together with high-temperature exhaust gas of 400 ° C or higher from the incinerator. While flowing, a step of decomposing a trace amount of organic chlorine compounds in the fly ash by the heat of the high temperature exhaust gas, and a step of re-collecting the fly ash in the high temperature exhaust gas with a second dust collector An ash treatment method characterized by.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3194283A JP2570012B2 (en) | 1991-08-02 | 1991-08-02 | Ash treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3194283A JP2570012B2 (en) | 1991-08-02 | 1991-08-02 | Ash treatment method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0531475A true JPH0531475A (en) | 1993-02-09 |
| JP2570012B2 JP2570012B2 (en) | 1997-01-08 |
Family
ID=16322028
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3194283A Expired - Lifetime JP2570012B2 (en) | 1991-08-02 | 1991-08-02 | Ash treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2570012B2 (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0796268A (en) * | 1993-06-17 | 1995-04-11 | Von Roll Ag | Method for heat treatment of solids generated during flue gas cleaning |
| WO2018101029A1 (en) * | 2016-12-02 | 2018-06-07 | 日立造船株式会社 | Exhaust gas treatment device and incineration facility |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5736420U (en) * | 1980-08-07 | 1982-02-26 |
-
1991
- 1991-08-02 JP JP3194283A patent/JP2570012B2/en not_active Expired - Lifetime
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5736420U (en) * | 1980-08-07 | 1982-02-26 |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0796268A (en) * | 1993-06-17 | 1995-04-11 | Von Roll Ag | Method for heat treatment of solids generated during flue gas cleaning |
| WO2018101029A1 (en) * | 2016-12-02 | 2018-06-07 | 日立造船株式会社 | Exhaust gas treatment device and incineration facility |
| CN110036240A (en) * | 2016-12-02 | 2019-07-19 | 日立造船株式会社 | Exhaust gas treatment device and incineration equipment |
| JPWO2018101029A1 (en) * | 2016-12-02 | 2019-10-17 | 日立造船株式会社 | Exhaust gas treatment equipment and incineration equipment |
| CN113477047A (en) * | 2016-12-02 | 2021-10-08 | 日立造船株式会社 | Exhaust gas treatment device and incineration equipment |
| CN113477047B (en) * | 2016-12-02 | 2023-05-16 | 日立造船株式会社 | Exhaust gas treatment device and incineration equipment |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2570012B2 (en) | 1997-01-08 |
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