JP3084731B2 - Decomposition method of halogenated dioxins in incineration ash - Google Patents

Decomposition method of halogenated dioxins in incineration ash

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Publication number
JP3084731B2
JP3084731B2 JP02198720A JP19872090A JP3084731B2 JP 3084731 B2 JP3084731 B2 JP 3084731B2 JP 02198720 A JP02198720 A JP 02198720A JP 19872090 A JP19872090 A JP 19872090A JP 3084731 B2 JP3084731 B2 JP 3084731B2
Authority
JP
Japan
Prior art keywords
heating
dioxins
incinerated ash
halogenated dioxins
halogenated
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
JP02198720A
Other languages
Japanese (ja)
Other versions
JPH0484977A (en
Inventor
真積 板谷
裕昭 原田
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.)
Mitsui Engineering and Shipbuilding Co Ltd
Original Assignee
Mitsui Engineering and Shipbuilding 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 Mitsui Engineering and Shipbuilding Co Ltd filed Critical Mitsui Engineering and Shipbuilding Co Ltd
Priority to JP02198720A priority Critical patent/JP3084731B2/en
Publication of JPH0484977A publication Critical patent/JPH0484977A/en
Application granted granted Critical
Publication of JP3084731B2 publication Critical patent/JP3084731B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は焼却灰中のハロゲン化ダイオキシン類の分解
方法に係り、特に焼却灰中のポリ塩化ダイオキシン等の
ハロゲン化ダイオキシン類を低い処理温度で分解するこ
とができる焼却灰中のハロゲン化ダイオキシン類の分解
方法に関する。
Description: TECHNICAL FIELD The present invention relates to a method for decomposing halogenated dioxins in incinerated ash, and more particularly to a method for treating halogenated dioxins such as polychlorinated dioxin in incinerated ash at a low treatment temperature. The present invention relates to a method for decomposing halogenated dioxins in incinerated ash that can be decomposed.

[従来の技術] ダイオキシンとは、2つのベンゼン核を2つの酸素原
子で橋渡しした骨格を持つ化合物で、物質名はディペン
ゾパラダイオキシンという。その化学構造式は下記
[I]に示す通りであり、〜及び〜の位置のH
がClで置換された化合物が塩化ダイオキシンで、Clの数
と位置により多数の異性体がある。これらの異性体はポ
リ塩化ダイオキシン(PCDDs)と総称される。
[Prior Art] Dioxin is a compound having a skeleton in which two benzene nuclei are bridged by two oxygen atoms, and the substance name is dipenso paradioxin. Its chemical structural formula is as shown in the following [I].
The compound in which is substituted by Cl is dioxin chloride, and there are many isomers depending on the number and position of Cl. These isomers are collectively referred to as polychlorinated dioxins (PCDDs).

ポリ塩化ダイオキシン(PPDDs)は、いずれも発ガン
性や催奇性等の毒性が強く、特に、PCDDsのうち両方の
ベンゼン核に2つずつの塩素を有するもの、とりわけ、
前記[I]式中、、、、の位置に塩素を有する
2、3、7、8−四塩化ダイオキシン(TCDDs)は最も
毒性が強く、この物質が単にダイオキシンと呼ばれる場
合もある。
Polychlorinated dioxins (PPDDs) are highly toxic, such as carcinogenic and teratogenic. In particular, PCDDs having two chlorine atoms in both benzene nuclei, especially
In the above formula [I], 2,3,7,8-tetrachlorinated dioxins (TCDDs) having chlorine at the positions of,, and are the most toxic, and this substance is sometimes simply referred to as dioxin.

また、ダイオキシンに類似した化学構造を有する化合
物には、下記[II]に示すような2つのベンゼン核が1
つの酸素原子で橋渡しされ、他方は直接結合したディベ
ンゾフラン、下記[III]に示すような直接2つのベン
ゼン核が結合したビフェニールなどがある。
Further, a compound having a chemical structure similar to dioxin has two benzene nuclei as shown in the following [II].
There are dibenzofuran which is bridged by one oxygen atom and the other is directly bonded, and biphenyl which is directly bonded to two benzene nuclei as shown in the following [III].

これらの化合物の塩素置換体もまた、ダイオキシンと
同様の激しい毒性を有し、特にポリ塩化ビフェニール
(PCB)は10年余り前から、その顕著な被害実績により
厳重な使用及び排出の規制が行なわれている。
Chlorinated products of these compounds also have the same severe toxicity as dioxin. In particular, polychlorinated biphenyls (PCBs) have been strictly regulated for use and emissions for more than 10 years due to their remarkable damage record. ing.

近年、これらハロゲン化ダイオキシン類が、ごみ焼却
施設の集塵ダストや焼却灰の中から検出されたことか
ら、その分解除去技術の確立が重要視されている。
In recent years, since these halogenated dioxins have been detected in dust collected from incineration facilities and incinerated ash, establishment of a technology for decomposing and removing these has been regarded as important.

これらのハロゲン化ダイオキシン類は、加熱により分
解する。例えばTCDDsは滞留1秒間では約700℃の高温で
分解する。そして、灰中のハロゲン化ダイオキシン類
は、酸素を制限した状態で加熱すると通常の加熱の場合
よりも低い温度で分解することが知られている。
These halogenated dioxins are decomposed by heating. For example, TCDDs decompose at a high temperature of about 700 ° C. for 1 second. It is known that halogenated dioxins in ash decompose at a lower temperature when heated in a state where oxygen is restricted, than in normal heating.

[発明が解決しようとする課題] しかしながら、酸素を制限した状態で加熱した場合に
おいても、ハロゲン化ダイオキシン類の分解には600℃
近い高温が必要であり、このような高温分解の必要性が
実用化の難点となっている。
[Problems to be Solved by the Invention] However, even when heating is performed in a state where oxygen is restricted, 600 ° C. is required for decomposition of halogenated dioxins.
Nearly high temperatures are required, and the necessity of such high-temperature decomposition is a difficult point for practical use.

本発明は上記従来の実情に鑑みて、焼却灰中のハロゲ
ン化ダイオキシン類をより低温度で分解することができ
る焼却灰中のハロゲン化ダイオキシン類の分解方法を提
供することを目的とする。
An object of the present invention is to provide a method for decomposing halogenated dioxins in incinerated ash, which can decompose halogenated dioxins in incinerated ash at a lower temperature in view of the above-mentioned conventional circumstances.

[課題を解決するための手段] 本発明の焼却灰中のハロゲン化ダイオキシン類の分解
方法は、焼却灰を酸素を制限しつつ加熱することによ
り、含有されるハロゲン化ダイオキシン類を分解する方
法であって、焼却灰を200〜300kg/cm2の加圧下で400〜4
50℃に加熱する。
[Means for Solving the Problems] The method for decomposing halogenated dioxins in incinerated ash of the present invention is a method for decomposing halogenated dioxins contained by heating incinerated ash while limiting oxygen. there is, the incinerator ash under pressure of 200~300kg / cm 2 400~4
Heat to 50 ° C.

なお、本発明において、ハロゲン化ダイオキシン類と
しては、前述のTCDDs等のPCDDsをはじめとするディベン
ゾパラダイオキシンの塩化物、フッ化物等のハロゲン化
ダイオキシンの他、ディベンゾパラダイオキシンの塩化
物等のハロゲン化物、例えばポリ塩化ジベンゾフラン
(PCDFs)、PCB等のハロゲン化ビフェニール等の、2個
のベンゼン核が酸素を介して或いは介さずに連結された
芳香族化合物のハロゲン置換化合物が包含される。
In the present invention, examples of the halogenated dioxins include chlorides of dibenzoparadioxin including PCDDs such as the above-mentioned TCDDs, halogenated dioxins such as fluoride, and chlorides of dibenzoparadioxin such as fluoride. Halogenated compounds, such as halogenated biphenyls such as polychlorinated dibenzofurans (PCDFs) and PCBs, and halogen-substituted compounds of aromatic compounds in which two benzene nuclei are linked with or without oxygen are included.

以下に本発明を詳細に説明する。 Hereinafter, the present invention will be described in detail.

本発明においては、焼却灰を酸素を制限しつつ、200
〜300kg/cm2の加圧下で400〜450℃の温度に加熱する。
この加熱に際し、操作圧力が200kg/cm2未満であると、
十分な低温分解性が得られないため、操作圧力は低温分
解性と装置設定条件とのかね合いから、200〜300kg/cm2
とする。また、加熱温度は400℃未満では分解効率が低
く、450℃を超えると装置材質も制約される上、エネル
ギーコストも増加するため、400〜450℃とする。
In the present invention, while limiting oxygen incinerated ash, 200
Heated to a temperature of 400 to 450 ° C. under a pressure of ~300kg / cm 2.
Upon this heating, the operating pressure is less than 200 kg / cm 2,
Since sufficient low-temperature decomposability cannot be obtained, the operating pressure must be 200 to 300 kg / cm 2 in consideration of low-temperature decomposability and equipment setting conditions.
And If the heating temperature is lower than 400 ° C., the decomposition efficiency is low, and if the heating temperature is higher than 450 ° C., the material of the apparatus is restricted, and the energy cost increases.

なお、焼却灰を反応筒に充填などして加圧状態で加熱
した場合、酸素の供給は殆どなく、自ら酸素供給は制限
された状態となるため、酸素を制限するための操作等が
別途必要となることはない。
When incineration ash is filled into a reaction tube and heated under pressure, there is almost no supply of oxygen, and the supply of oxygen itself is restricted, so an operation to restrict oxygen is required separately. Will not be.

本発明の方法の具体的な実施方法としては、次の〜
等の方法が挙げられるが、これらの方法に限定される
ものではないことは言うまでもない。
Specific methods for carrying out the method of the present invention include the following:
And the like, but it is needless to say that the present invention is not limited to these methods.

焼却灰をピストン等の加圧手段を有する反応筒に充
填し、この反応筒の外からヒータ等で加熱する(外部加
熱方式)。
The incinerated ash is filled in a reaction tube having a pressurizing means such as a piston, and heated from outside the reaction tube by a heater or the like (external heating method).

焼却灰をピストン等の加圧手段を有するセラミック
ス製の反応筒に充填し、ピストン等を電極として高周波
電圧を印加し、焼却灰を高周波誘電加熱する(内部加熱
方式)。
The incinerated ash is filled into a ceramic reaction tube having a pressurizing means such as a piston, and a high frequency voltage is applied using the piston or the like as an electrode to perform high frequency dielectric heating of the incinerated ash (internal heating method).

焼却灰をピストン等の加圧手段を有する反応筒に充
填し、ピストン等を電極として電圧を印加し、焼却灰に
通電して電気抵抗熱で加熱する(内部加熱方式)。
The incineration ash is filled in a reaction tube having a pressurizing means such as a piston, a voltage is applied using the piston or the like as an electrode, and the incineration ash is energized and heated by electric resistance heat (internal heating method).

[作用] 焼却灰を酸素を制限した状態で加圧、加熱することに
より、含有されるハロゲン化ダイオキシン類は、低温度
で効率的に分解される。因みに300kg/cm2加圧下では400
℃の加熱でほぼ100%分解率を得ることができる。
[Action] By pressurizing and heating the incinerated ash while limiting oxygen, the contained halogenated dioxins are efficiently decomposed at a low temperature. 400 kg / cm 2 under pressure
Almost 100% decomposition rate can be obtained by heating at ℃.

しかも、加圧、加熱により、100kg/cm2以上の圧縮強
度の高い固化体が得られ、この固化体は高強度な上に有
害物質を含有しないことから、路盤材等に有効利用する
ことができる。また、このような固化体とすることによ
り、焼却灰の減容化も図れる。
Moreover, pressurization, heating, high solid material of 100 kg / cm 2 or more compression strength is obtained, this solid material because it does not contain harmful substances on a high strength, it is possible to effectively utilize the roadbed material, etc. it can. Further, by using such a solidified body, the volume of incinerated ash can be reduced.

[実施例] 以下に実施例、比較例及び参考例を挙げて本発明をよ
り具体的に説明する。
[Examples] Hereinafter, the present invention will be described more specifically with reference to Examples, Comparative Examples, and Reference Examples.

実施例1 都市ゴミの焼却灰250gを、内径50mm、高さ100mmの鋼
製の反応筒に充填し、上下からピストンで300kg/cm2
加圧した状態にて電気ヒータによる外部加熱方式で第1
表に示す温度に20分加熱し、各々の場合についてPCDDs
又はPCDFsの濃度を調べ、結果を第1表に示した。
Example 1 250 g of municipal waste incineration ash was filled into a steel reaction tube having an inner diameter of 50 mm and a height of 100 mm, and was pressurized with a piston from above and below at 300 kg / cm 2 by an external heating method using an electric heater. 1
Heat to the temperature shown in the table for 20 minutes, in each case PCDDs
Alternatively, the concentration of PCDFs was examined, and the results are shown in Table 1.

第1表より明らかなように加圧下で加熱することによ
り、低温度でハロゲン化ダイオキシン類を分解すること
ができる。
As is clear from Table 1, by heating under pressure, halogenated dioxins can be decomposed at a low temperature.

なお、実施例1において、加圧力を300kg/cm2又は200
kg/cm2とし、100、200又は300℃で20分加熱処理して得
られた固化体の圧縮強度を調べ、結果を第1図に示し
た。
In Example 1, the pressing force was set to 300 kg / cm 2 or 200 kg / cm 2.
kg / cm 2, and the heat treatment at 100, 200 or 300 ° C. for 20 minutes was conducted to examine the compressive strength of the solidified product. The results are shown in FIG.

第1図より、反応温度が高い程高強度の固化体が得ら
れることが明らかである。
From FIG. 1, it is clear that the higher the reaction temperature, the higher the strength of the solidified body can be obtained.

比較例1 第2表に示すハロゲン化ダイオキシン類含有率の焼却
灰No.1〜5を加圧することなく、常圧下にて、酸素を制
限した状態で第2表に示す温度で加熱し、各々の場合に
ついてPCDDs及びPCDFsの濃度を調べ結果を第2表に示し
た。
Comparative Example 1 The incinerated ash Nos. 1 to 5 having the halogenated dioxins content shown in Table 2 were heated at the temperature shown in Table 2 in a state where oxygen was restricted under normal pressure without pressurization. In the case of (1), the concentrations of PCDDs and PCDFs were examined, and the results are shown in Table 2.

第2表より明らかなように、加圧を行なわない状態で
加熱することによりハロゲン化ダイオキシン類を分解さ
せるには、590〜600℃の高温加熱が必要である。
As is apparent from Table 2, high-temperature heating at 590 to 600 ° C. is required to decompose halogenated dioxins by heating without applying pressure.

[発明の効果] 以上詳述した通り、本発明の焼却灰中のハロゲン化ダ
イオキシン類の分解方法によれば、焼却灰中のハロゲン
化ダイオキシン類を、従来に比べて低い加熱温度で分解
することができ、工業的に極めて有利である。しかも、
加圧、加熱により焼却灰の減容化が図れると共に、高強
度の固化体が得られるため、焼却灰の有効利用が可能と
なる。
[Effects of the Invention] As described in detail above, according to the method for decomposing halogenated dioxins in incineration ash of the present invention, halogenated dioxins in incineration ash are decomposed at a lower heating temperature than before. Which is extremely industrially advantageous. Moreover,
Pressurization and heating can reduce the volume of the incinerated ash, and a high-strength solidified body can be obtained, so that the incinerated ash can be effectively used.

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

第1図は参考例1の結果を示すグラフである。 FIG. 1 is a graph showing the results of Reference Example 1.

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】焼却灰を酸素を制限しつつ加熱することに
より、該焼却灰中に含有されるハロゲン化ダイオキシン
類を分解する方法であって、焼却灰を200〜300kg/cm2
加圧下で400〜450℃に加熱することを特徴とする焼却灰
中のハロゲン化ダイオキシン類の分解方法。
1. A method for decomposing halogenated dioxins contained in incinerated ash by heating the incinerated ash while limiting oxygen, wherein the incinerated ash is heated under a pressure of 200 to 300 kg / cm 2 . A method for decomposing halogenated dioxins in incinerated ash, wherein the method comprises heating to 400 to 450 ° C.
JP02198720A 1990-07-26 1990-07-26 Decomposition method of halogenated dioxins in incineration ash Expired - Fee Related JP3084731B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP02198720A JP3084731B2 (en) 1990-07-26 1990-07-26 Decomposition method of halogenated dioxins in incineration ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP02198720A JP3084731B2 (en) 1990-07-26 1990-07-26 Decomposition method of halogenated dioxins in incineration ash

Publications (2)

Publication Number Publication Date
JPH0484977A JPH0484977A (en) 1992-03-18
JP3084731B2 true JP3084731B2 (en) 2000-09-04

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ID=16395884

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3084731B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2706634B2 (en) * 1995-05-25 1998-01-28 株式会社テクノフロンティア Recycling method of main ash of stalker type incinerator

Also Published As

Publication number Publication date
JPH0484977A (en) 1992-03-18

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