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JP3148705B2 - Fly ash treatment method for waste treatment equipment - Google Patents
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JP3148705B2 - Fly ash treatment method for waste treatment equipment - Google Patents

Fly ash treatment method for waste treatment equipment

Info

Publication number
JP3148705B2
JP3148705B2 JP35919697A JP35919697A JP3148705B2 JP 3148705 B2 JP3148705 B2 JP 3148705B2 JP 35919697 A JP35919697 A JP 35919697A JP 35919697 A JP35919697 A JP 35919697A JP 3148705 B2 JP3148705 B2 JP 3148705B2
Authority
JP
Japan
Prior art keywords
fly ash
dioxin
waste treatment
furnace
treatment facility
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
JP35919697A
Other languages
Japanese (ja)
Other versions
JPH11188330A (en
Inventor
直克 毛利
隆 卯津江
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP35919697A priority Critical patent/JP3148705B2/en
Publication of JPH11188330A publication Critical patent/JPH11188330A/en
Application granted granted Critical
Publication of JP3148705B2 publication Critical patent/JP3148705B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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

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、ごみ処理場のよう
な廃棄物処理設備から発生する飛灰の処理方法に関する
ものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating fly ash generated from a waste treatment facility such as a refuse treatment plant.

【0002】[0002]

【従来の技術】ごみ処理場のような廃棄物処理設備で
は、焼却工程などからダイオキシンが発生し、社会問題
となっている。このため、ごみを熱分解したうえ130
0℃以上の高温で溶融することによりダイオキシンの絶
対発生量を抑制し、それによって飛灰中のダイオキシン
残留量も減少させる方法が注目されている。この方法は
ダイオキシン対策として有効な方法であるが、飛灰中の
ダイオキシンを完全になくすことは容易ではないという
問題がある。
2. Description of the Related Art In a waste treatment facility such as a refuse treatment plant, dioxin is generated from an incineration process or the like, which is a social problem. For this reason, garbage is thermally decomposed and 130
Attention has been paid to a method of suppressing the absolute amount of dioxin generated by melting at a high temperature of 0 ° C. or higher, thereby reducing the amount of dioxin remaining in fly ash. Although this method is an effective method as a measure against dioxin, there is a problem that it is not easy to completely eliminate dioxin in fly ash.

【0003】また、焼却工程や溶融工程からの排ガスを
活性炭により処理し、ダイオキシンを吸着させる方法も
あるが、この活性炭吸着法は排ガス中のダイオキシンは
除去できるものの、飛灰中のダイオキシンを除去する効
果はないという問題がある。さらに、焼却工程や溶融工
程から排出された飛灰を外部加熱することにより飛灰中
のダイオキシンを分解させる方法もあるが、新たに外部
エネルギーが必要となり、経済的でないという問題があ
る。
There is also a method of treating exhaust gas from an incineration process and a melting process with activated carbon to adsorb dioxin. This activated carbon adsorption method can remove dioxin in exhaust gas but removes dioxin in fly ash. There is a problem that it is not effective. Furthermore, there is a method of decomposing dioxin in fly ash by externally heating the fly ash discharged from the incineration step or the melting step, but it requires new external energy and is not economical.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決し、外部エネルギーを必要とせずに、廃
棄物処理設備から生じた飛灰中のダイオキシンを確実に
除去することができる廃棄物処理設備の飛灰処理方法を
提供するためになされたものである。
SUMMARY OF THE INVENTION The present invention solves the above-mentioned conventional problems and can reliably remove dioxin in fly ash generated from waste treatment equipment without requiring external energy. The purpose of the present invention is to provide a fly ash treatment method for a waste treatment facility.

【0005】[0005]

【課題を解決するための手段】上記の課題を解決するた
めになされた本発明は、廃棄物処理設備で発生した飛灰
をダイオキシン分解炉に入れ、廃棄物処理設備の熱分解
部または抑制燃焼部で発生した未燃ガスと分解炉内で接
触させて250℃以上に加熱したうえ、急冷して取り出
すことを特徴とするものである。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention is directed to a method in which fly ash generated in a waste treatment facility is introduced into a dioxin decomposition furnace, and a thermal decomposition section or a suppressed combustion of the waste treatment facility is provided. It is characterized in that it is brought into contact with the unburned gas generated in the section in a decomposition furnace, heated to 250 ° C. or higher, and then rapidly cooled and taken out.

【0006】上記のように、ダイオキシンを含む飛灰を
熱分解部または抑制燃焼部で発生した未燃ガスと接触さ
せ250℃以上に保つと、飛灰中のダイオキシンは抑制
雰囲気下で効率よく分解される。その後、飛灰を急冷す
ればダイオキシンが再合成されることはない。しかもこ
の未燃ガスは廃棄物処理設備から発生するものであるか
ら外部エネルギーは不要である。その後この未燃ガスは
廃棄物処理設備中で完全燃焼されるため、ガス中のダイ
オキシンが外部に漏れるおそれはない。なお、本発明の
適用範囲は熱分解部または抑制燃焼部を備えた廃棄物処
理設備に限定される。しかし現在新設されている廃棄物
処理設備の多くは熱分解部または抑制燃焼部を備えてい
るため、実質的な適用範囲はさほど限定されるものでは
ない。以下に本発明の好ましい実施の形態を示す。
As described above, when the fly ash containing dioxin is brought into contact with the unburned gas generated in the thermal decomposition section or the suppression combustion section and kept at a temperature of 250 ° C. or more, the dioxin in the fly ash is efficiently decomposed under the suppression atmosphere. Is done. Thereafter, if fly ash is quenched, dioxin will not be resynthesized. Moreover, since the unburned gas is generated from the waste treatment facility, no external energy is required. Thereafter, the unburned gas is completely burned in the waste treatment facility, so that dioxin in the gas does not leak to the outside. In addition, the applicable range of the present invention is limited to a waste treatment facility provided with a pyrolysis section or a suppression combustion section. However, since many of the newly installed waste treatment facilities are provided with a pyrolysis section or a suppression combustion section, the practical application range is not so limited. Hereinafter, preferred embodiments of the present invention will be described.

【0007】[0007]

【発明の実施の形態】〔第1の実施形態〕図1は本発明
の第1の実施形態を示すものであり、この廃棄物処理設
備は熱分解部である熱分解炉1と、溶融炉2と、排ガス
処理装置3とを備えている。熱分解炉1はごみ等の廃棄
物を抑制雰囲気下で熱分解し、COその他の可燃分を含
んだ未燃ガスと、チャーと呼ばれる熱分解残査とする。
これらは溶融炉2に送られ未燃ガスは燃料として燃焼さ
れ、熱分解残査は溶融スラグとなる。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS [First Embodiment] FIG. 1 shows a first embodiment of the present invention. This waste treatment equipment includes a pyrolysis furnace 1 as a pyrolysis section, and a melting furnace. 2 and an exhaust gas treatment device 3. The thermal decomposition furnace 1 thermally decomposes waste such as refuse under a suppressed atmosphere to produce unburned gas containing CO and other combustibles and pyrolysis residue called char.
These are sent to the melting furnace 2 and the unburned gas is burned as fuel, and the pyrolysis residue becomes molten slag.

【0008】この溶融炉2では溶融飛灰が発生し、排ガ
ス処理装置3の集塵機により回収される。前記したよう
に、溶融型の廃棄物処理設備ではダイオキシンの発生量
は焼却型に比較して少ないが、回収された飛灰中に微量
のダイオキシンが含まれる。そこでこの飛灰をダイオキ
シン分解炉4に入れ、熱分解炉1で発生した未燃ガスを
ダイオキシン分解炉4内に導いて、250℃以上、より
好ましくは250〜400℃の温度域で接触させる。
In the melting furnace 2, molten fly ash is generated and collected by a dust collector of the exhaust gas treatment device 3. As described above, the amount of generated dioxin in the molten waste treatment facility is smaller than that in the incineration type, but a small amount of dioxin is contained in the collected fly ash. Then, the fly ash is put into the dioxin decomposition furnace 4, and the unburned gas generated in the pyrolysis furnace 1 is guided into the dioxin decomposition furnace 4, and is brought into contact at a temperature of 250 ° C. or more, more preferably 250 to 400 ° C.

【0009】ダイオキシン分解炉4は、飛灰と未燃ガス
との接触が十分に行われる構造であればよく、例えば図
2に示すような流動床型の炉が用いられる。この図2で
は未燃ガスが炉体5の下部から供給され、炉体5の上部
から投入される飛灰を流動させながら、飛灰と未燃ガス
とを十分に接触させる。また炉体5の下部にバーナ6を
設けておき、飛灰と未燃ガスの保有熱のみではダイオキ
シン分解炉4内の温度が250℃に達しない場合には、
少量の空気を供給しながら未燃ガスを燃焼させてもよ
い。
The dioxin decomposing furnace 4 may have any structure as long as the contact between the fly ash and the unburned gas is sufficiently performed. For example, a fluidized bed type furnace as shown in FIG. 2 is used. In FIG. 2, the unburned gas is supplied from the lower part of the furnace body 5, and while the fly ash supplied from the upper part of the furnace body 5 flows, the fly ash and the unburned gas are sufficiently contacted. Further, a burner 6 is provided at the lower part of the furnace body 5, and when the temperature in the dioxin cracking furnace 4 does not reach 250 ° C. by only the retained heat of fly ash and unburned gas,
The unburned gas may be burned while supplying a small amount of air.

【0010】このように、飛灰を未燃ガスによる抑制雰
囲気下で250℃以上に加熱すると、飛灰中のダイオキ
シンは分解される。そこでダイオキシン分解炉4で処理
された飛灰を急冷装置7に入れ、ダイオキシンの再合成
を防止しつつ取り出せばよい。急冷装置7は例えば冷却
水を飛灰と混練する装置であり、同時にセメントを投入
してコンクリートを製造するようにしてもよい。このよ
うにしてダイオキシンが分解された処理灰が取り出され
る。またこのダイオキシン分解炉4の排ガスは図1に示
すように溶融炉2に返送すればよい。
As described above, when the fly ash is heated to 250 ° C. or more in an atmosphere suppressed by unburned gas, dioxin in the fly ash is decomposed. Therefore, the fly ash treated in the dioxin decomposition furnace 4 may be put into the rapid cooling device 7 and taken out while preventing resynthesis of dioxin. The quenching device 7 is, for example, a device for kneading cooling water with fly ash, and may be configured to simultaneously put cement and produce concrete. The treated ash from which the dioxin has been decomposed is taken out. Further, the exhaust gas from the dioxin decomposition furnace 4 may be returned to the melting furnace 2 as shown in FIG.

【0011】図3はダイオキシン分解炉4の他の例を示
すもので、ロータリーキルンタイプのものである。この
ダイオキシン分解炉4は炉体5を回転させながら、飛灰
と未燃ガスとを接触させる。この場合にもバーナ6によ
り未燃ガスを燃焼させてもよい。
FIG. 3 shows another example of the dioxin cracking furnace 4, which is of a rotary kiln type. The dioxin cracking furnace 4 brings fly ash into contact with unburned gas while rotating the furnace body 5. Also in this case, the unburned gas may be burned by the burner 6.

【0012】上記したように、本発明によれば飛灰を抑
制雰囲気下で250℃以上に保つことにより、ダイオキ
シンを分解する。このため、処理灰はダイオキシンを全
く含まず、最終処分が容易となる。しかも外部エネルギ
ーを全く要しないので、経済的である。
As described above, according to the present invention, dioxin is decomposed by maintaining fly ash at a temperature of 250 ° C. or more in a suppressed atmosphere. For this reason, the treated ash does not contain any dioxin, and the final disposal is easy. Moreover, since no external energy is required, it is economical.

【0013】〔第2の実施形態〕図4に示す第2の実施
形態では、廃棄物処理設備が焼却炉8と排ガス処理装置
9とから構成されている。この焼却炉8は例えばごみ焼
却用の流動床焼却炉であり、その下部の砂層部の直上は
空気比の低い熱分解部または抑制燃焼部となっている。
そしてこの部分から抜き出された未燃ガスをダイオキシ
ン分解炉4に導き、第1の実施形態と同様に飛灰中のダ
イオキシンを分解させる。ダイオキシン分解炉4の排ガ
スは再び焼却炉8に送られる。
[Second Embodiment] In a second embodiment shown in FIG. 4, a waste treatment facility includes an incinerator 8 and an exhaust gas treatment device 9. The incinerator 8 is, for example, a fluidized bed incinerator for incineration of refuse, and a thermal decomposition section or a suppression combustion section having a low air ratio is provided immediately above a sand layer section below the incinerator.
Then, the unburned gas extracted from this portion is led to the dioxin decomposing furnace 4 to decompose the dioxin in the fly ash as in the first embodiment. The exhaust gas from the dioxin decomposition furnace 4 is sent to the incinerator 8 again.

【0014】[0014]

【発明の効果】以上に説明したように、本発明によれば
外部エネルギーを必要とせずに、廃棄物処理設備から生
じた飛灰中のダイオキシンを確実に除去することができ
る利点がある。
As described above, according to the present invention, there is an advantage that dioxin in fly ash generated from waste treatment equipment can be reliably removed without requiring external energy.

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

【図1】第1の実施形態を示すブロック図である。FIG. 1 is a block diagram showing a first embodiment.

【図2】ダイオキシン分解炉の模式的な断面図である。FIG. 2 is a schematic sectional view of a dioxin decomposition furnace.

【図3】他のダイオキシン分解炉の模式的な断面図であ
る。
FIG. 3 is a schematic sectional view of another dioxin decomposition furnace.

【図4】第4の実施形態を示すブロック図である。FIG. 4 is a block diagram showing a fourth embodiment.

【符号の説明】[Explanation of symbols]

1 熱分解炉、2 溶融炉、3 排ガス処理装置、4
ダイオキシン分解炉、5 炉体、6 バーナ、7 急冷
装置、8 焼却炉、9 排ガス処理装置
1 Pyrolysis furnace, 2 Melting furnace, 3 Exhaust gas treatment device, 4
Dioxin decomposition furnace, 5 furnace body, 6 burner, 7 quenching device, 8 incinerator, 9 exhaust gas treatment device

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平6−15249(JP,A) 特開 平2−78479(JP,A) 特開 平7−108249(JP,A) 特開 平5−223236(JP,A) 特開 平10−227434(JP,A) 特開 平7−155723(JP,A) 特開 平9−57230(JP,A) 特開 平5−154461(JP,A) 特開 平4−98008(JP,A) (58)調査した分野(Int.Cl.7,DB名) B09B 3/00 303 F23J 1/00 ────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-6-15249 (JP, A) JP-A-2-78479 (JP, A) JP-A-7-108249 (JP, A) JP-A-5-108249 223236 (JP, A) JP-A-10-227434 (JP, A) JP-A-7-155723 (JP, A) JP-A-9-57230 (JP, A) JP-A-5-154461 (JP, A) JP-A-4-98008 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B09B 3/00 303 F23J 1/00

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 廃棄物処理設備で発生した飛灰をダイオ
キシン分解炉に入れ、廃棄物処理設備の熱分解部または
抑制燃焼部で発生した未燃ガスと分解炉内で接触させて
250℃以上に加熱したうえ、急冷して取り出すことを
特徴とする廃棄物処理設備の飛灰処理方法。
1. Fly ash generated in a waste treatment facility is introduced into a dioxin decomposition furnace, and is brought into contact with unburned gas generated in a thermal decomposition section or a suppression combustion section of the waste treatment facility in the decomposition furnace to at least 250 ° C. A fly ash treatment method for a waste treatment facility, wherein the fly ash is heated and rapidly cooled and taken out.
【請求項2】 ダイオキシン分解炉において、未燃ガス
を抑制雰囲気下で燃焼させて温度を250℃以上に維持
する請求項1に記載の廃棄物処理設備の飛灰処理方法。
2. The fly ash treatment method for a waste treatment facility according to claim 1, wherein the unburned gas is burned in a suppressed atmosphere in the dioxin decomposition furnace to maintain the temperature at 250 ° C. or higher.
【請求項3】 ダイオキシン分解炉の温度を250〜4
00℃とする請求項1又は2に記載の廃棄物処理設備の
飛灰処理方法。
3. The temperature of the dioxin decomposing furnace is from 250 to 4
The fly ash treatment method for a waste treatment facility according to claim 1 or 2, wherein the temperature is set to 00 ° C.
JP35919697A 1997-12-26 1997-12-26 Fly ash treatment method for waste treatment equipment Expired - Fee Related JP3148705B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP35919697A JP3148705B2 (en) 1997-12-26 1997-12-26 Fly ash treatment method for waste treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP35919697A JP3148705B2 (en) 1997-12-26 1997-12-26 Fly ash treatment method for waste treatment equipment

Publications (2)

Publication Number Publication Date
JPH11188330A JPH11188330A (en) 1999-07-13
JP3148705B2 true JP3148705B2 (en) 2001-03-26

Family

ID=18463252

Family Applications (1)

Application Number Title Priority Date Filing Date
JP35919697A Expired - Fee Related JP3148705B2 (en) 1997-12-26 1997-12-26 Fly ash treatment method for waste treatment equipment

Country Status (1)

Country Link
JP (1) JP3148705B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003507153A (en) 1999-08-17 2003-02-25 ウィスコンシン エレクトリック パワー カンパニー Removal of ammonia from fly ash
JP4524918B2 (en) * 2000-12-28 2010-08-18 栗田工業株式会社 Detoxification method for fly ash
CN105889948A (en) * 2016-06-14 2016-08-24 湖州森诺环境科技有限公司 Device for removing dioxin from flying garbage dust and treatment method of device
CN119642203B (en) * 2025-02-17 2025-06-24 浙江大维高新技术股份有限公司 A system and method for removing dioxins from fly ash

Also Published As

Publication number Publication date
JPH11188330A (en) 1999-07-13

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