JPH07155731A - Heating dechlorination treatment for collected dust and ash - Google Patents

Heating dechlorination treatment for collected dust and ash

Info

Publication number
JPH07155731A
JPH07155731A JP5309491A JP30949193A JPH07155731A JP H07155731 A JPH07155731 A JP H07155731A JP 5309491 A JP5309491 A JP 5309491A JP 30949193 A JP30949193 A JP 30949193A JP H07155731 A JPH07155731 A JP H07155731A
Authority
JP
Japan
Prior art keywords
ash
heating
dioxins
removal rate
dust
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.)
Pending
Application number
JP5309491A
Other languages
Japanese (ja)
Inventor
Tatsuo Kato
龍夫 加藤
Yoshimichi Hanai
義道 花井
Hiroshi Kudo
宏 工藤
Gentaro Takasuka
玄太郎 高須賀
Shinseki Itaya
真積 板谷
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.)
SANZOU KANKYO ENG KK
Mitsui Engineering and Shipbuilding Co Ltd
Original Assignee
SANZOU KANKYO ENG KK
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 SANZOU KANKYO ENG KK, Mitsui Engineering and Shipbuilding Co Ltd filed Critical SANZOU KANKYO ENG KK
Priority to JP5309491A priority Critical patent/JPH07155731A/en
Publication of JPH07155731A publication Critical patent/JPH07155731A/en
Pending legal-status Critical Current

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

Abstract

PURPOSE:To prolong the service life of the device and to reduce the running cost by operation the heating treatment device at an appropriate condition. CONSTITUTION:Hexachlorobenzene concentration in collected dust and ash A introduced into a heating pipe 1 and in treated ash B discharged from the heating pipe 1 are detected at specified intervals by an automatic analyzer 5 and the removal ratio of dioxines by the heating device is estimated based on this data and heating conditions of the heating device are adjusted based on the estimated removal ratio. Thus, the service life of the device is prolonged and the running cost is reduced.

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、集じん灰の加熱脱塩素
化処理方法に係り、さらに詳しくは、都市ごみ、産業廃
棄物等の廃棄物焼却炉から排出される排ガスの処理工程
で捕集された集じん灰に含まれる、ダイオキシン等の有
害塩素化合物(以下、ダイオキシン類という)を分解、
除去する集じん灰の加熱脱塩素化処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for heating and dechlorinating dust collecting ash, and more particularly, to a method for treating exhaust gas discharged from waste incinerators such as municipal waste and industrial waste. Decomposes harmful chlorine compounds such as dioxins (hereinafter referred to as dioxins) contained in the collected dust ash,
The present invention relates to a heating dechlorination treatment method for dust collecting ash to be removed.

【0002】[0002]

【従来の技術】人体および環境にとって有害なダイオキ
シン類、すなわち4〜8塩素化のPCDDS (ポリ塩素
化ジベンゾパラダイオキシン)や4〜8塩素化のPCD
S (ポリ塩素化ジベンゾフラン)は、都市ごみ焼却処
理施設から排出される排ガスおよび集じん灰に含有さ
れ、環境を汚染することが知られている。
2. Description of the Related Art Dioxins harmful to the human body and the environment, that is, 4 to 8 chlorinated PCDD S (polychlorinated dibenzoparadioxin) and 4 to 8 chlorinated PCD.
F S (polychlorinated dibenzofuran) is known to pollute the environment when it is contained in the exhaust gas and dust ash discharged from the municipal waste incineration treatment facility.

【0003】国は、その対策として平成2年12月26
日付厚生省生活衛生局水道環境部長通知衛生環第260
号別添の「ダイオキシン類発生防止等ガイドライン」で
総括的な対策を取りまとめている。このガイドラインに
よれば、集じん灰中のダンオキシン類の処理に関して
「最終処分される焼却灰等のダンオキシン類の灰処理技
術としては(1)加熱脱塩素化処理、(2)溶融固化処
理のようなものがあり、今後重金属類の挙動を含めた技
術開発や研究を推進し、実用化をめざすことが望まし
い。」と記載されている。
As a measure against this, the national government has decided on December 26, 1990.
Date Ministry of Health and Welfare Bureau Health and Sanitation Bureau Water Environment Department Notification Sanitation Environment No. 260
Comprehensive measures are summarized in the “Dioxins Generation Prevention Guidelines” attached to the issue. According to this guideline, regarding the treatment of danoxins in dust ash, "The ash treatment technology for danoxins such as incineration ash that is finally disposed is (1) heat dechlorination treatment, (2) melt solidification treatment. It is desirable to promote technological development and research, including the behavior of heavy metals, for practical use in the future. ”

【0004】このような集じん灰中のダイオキシン類を
低減する技術としては、例えば本発明者らの提案による
特開平2−78479号公報(ごみ焼却炉の焼却灰処理
方法および処理装置)があげられる。この処理方法およ
び処理装置によれば、ごみ焼却処理施設から回収される
焼却灰を300℃以上に加熱することにより、灰中のダ
イオキシンをはじめとする有機塩素化合物を効果的に分
解できるとともに、排ガス集じん装置における灰の滞留
部に加熱手段を設けて前記充満した焼却灰を加熱処理す
ることにより、焼却灰中の有機塩素化合物をほぼ完全に
無害化処理することができる。
As a technique for reducing dioxins in such dust-collected ash, there is, for example, Japanese Patent Laid-Open No. 2-78479 (incinerator ash treatment method and treatment device for a refuse incinerator) proposed by the present inventors. To be According to this treatment method and treatment apparatus, by heating the incinerated ash collected from the refuse incineration treatment facility to 300 ° C. or higher, it is possible to effectively decompose organic chlorine compounds such as dioxins in the ash, and exhaust gas. By providing a heating means in the ash accumulation portion of the dust collector to heat the incinerated ash filled therein, the organic chlorine compounds in the incinerated ash can be almost completely detoxified.

【0005】[0005]

【発明が解決しようとする課題】しかしながら上記従来
技術では、加熱装置における集じん灰中のダイオキシン
類の分解性能、すなわち加熱処理前後の集じん灰に含ま
れるダイオキシン類の濃度変化はモニタリングされてお
らず、加熱処理装置は安全サイドすなわち、必要以上の
高温で長い平均滞留時間をかけて運転されており、高温
腐食による装置寿命の低下やランニングコストの高騰を
招くという問題があった。
However, in the above-mentioned prior art, the decomposition performance of dioxins in the dust collecting ash in the heating device, that is, the change in the concentration of dioxins contained in the dust collecting ash before and after the heat treatment is not monitored. However, the heat treatment device is operated on the safe side, that is, at a higher temperature than necessary for a long average residence time, and there is a problem that the device life is shortened due to high temperature corrosion and the running cost is increased.

【0006】ところで、集じん灰中のダイオキシン類の
定量は、サンプリングした灰を、例えばトルエン等の有
機溶剤と混合してダイオキシン類を抽出し、この抽出液
を必要に応じて前処理したのち、GC/MS(ガスクロ
マトグラフィ質量分析計)を用いて行われている。この
ために、分析結果が得られるまでに少なくとも1週間程
度を要し、加熱処理前後における灰中濃度を直接モニタ
リングすることは物理的に不可能であった。またこのよ
うな分析には多大な費用を要するという問題があった。
By the way, the amount of dioxins in the collected ash is determined by mixing the sampled ash with an organic solvent such as toluene to extract the dioxins, pretreating the extract as necessary, It is carried out using GC / MS (gas chromatography mass spectrometer). For this reason, it took at least one week until the analysis results were obtained, and it was physically impossible to directly monitor the concentration in ash before and after the heat treatment. There is also a problem that such an analysis requires a great deal of cost.

【0007】本発明の目的は、上記従来技術の問題点を
解決し、加熱処理装置を、ダイオキシン類を分解除去で
きる適正な条件で運転し、装置の延命とランニングコス
トの低減を図ることができる、集じん灰の加熱脱塩素化
処理方法を提供することにある。
The object of the present invention is to solve the above-mentioned problems of the prior art and to operate the heat treatment apparatus under appropriate conditions capable of decomposing and removing dioxins, thereby prolonging the life of the apparatus and reducing the running cost. Another object of the present invention is to provide a method for heating and dechlorinating dust ash.

【0008】[0008]

【課題を解決するための手段】本発明者は、集じん灰の
加熱脱塩素化処理装置を適正条件で稼動させるために
は、加熱装置におけるダイオキシン類の除去率をモニタ
リングすればよいことに着目し、加熱処理前後の、ダイ
オキシン類濃度と特定の有機塩素化合物濃度との関係に
ついて鋭意研究した結果、ダイオキシン類に比べて分析
操作が著しく容易なクロルベンゼン類またはクロルフェ
ノール類の除去率と前記ダイオキシン類の除去率との間
に強い相関関係があることを発見し、前記クロルベンゼ
ン類およびクロルフェノール類の少なくとも1種を指標
物質として用い、その加熱前後における濃度変化を測定
することによりダイオキシン類の除去率を推算し、これ
に基いて加熱装置の加熱温度、灰の平均滞留時間等の加
熱条件を制御すれば無用の高温および不必要な滞留時間
の延長を防止できることを見出し、本発明に到達した。
Means for Solving the Problems The present inventor has noticed that in order to operate the apparatus for thermally dechlorinating dust collecting ash under proper conditions, it is sufficient to monitor the removal rate of dioxins in the heating apparatus. However, as a result of diligent research on the relationship between the concentration of dioxins and the concentration of a specific organic chlorine compound before and after the heat treatment, the removal rate of chlorobenzenes or chlorophenols, which is significantly easier to analyze than dioxins, and the above-mentioned dioxins. It was discovered that there is a strong correlation with the removal rate of dioxin, and at least one of the above chlorobenzenes and chlorophenols was used as an indicator substance, and the change in concentration before and after heating was measured to measure dioxins. Estimate the removal rate, and based on this, control the heating conditions such as the heating temperature of the heating device and the average residence time of ash. It found that prevents extension of the high temperatures and unnecessary residence time of use, have reached the present invention.

【0009】また本発明者は、前記クロルベンゼン類の
中でもペンタクロルベンゼンやヘキサクロルベンゼンに
は異性体がなく、分析が容易かつ正確であることに着目
し、これらを加熱装置におけるダイオキシン類の除去率
をモニタリングする指標物質として用いることにより、
ダイオキシン類の除去率を迅速かつ正確に推定できるこ
とを見出し、本発明に到達した。
Further, the present inventor has noticed that pentachlorobenzene and hexachlorobenzene among the above-mentioned chlorobenzenes have no isomers, and the analysis is easy and accurate, and the dioxins are removed by a heating device. By using it as an indicator substance to monitor the rate,
The inventors have found that the removal rate of dioxins can be estimated quickly and accurately, and have reached the present invention.

【0010】すなわち、本願で特許請求される発明は以
下のとおりである。 (1)ごみ焼却処理施設の排ガス処理工程で捕集された
集じん灰を加熱装置に導入して加熱し、前記集じん灰に
含まれるダイオキシン類を分解する集じん灰の加熱脱塩
素化処理方法において、前記加熱装置入口の加熱処理前
の集じん灰および加熱装置出口の加熱処理後の集じん灰
にそれぞれ含まれるクロルベンゼン類およびクロルフェ
ノール類の少なくとも1種を定量して前記加熱装置にお
けるダイオキシン類の除去率を推定し、該推定したダイ
オキシン類の除去率に基いて加熱条件を調節することを
特徴とする集じん灰の加熱脱塩素化処理方法。 (2)集じん灰の加熱処理前後のペンタクロルベンゼン
またはヘキサクロルベンゼン含有量を測定して加熱装置
におけるダイオキシン類の除去率を推定することを特徴
とする(1)記載の集じん灰の加熱脱塩素化処理方法。
That is, the invention claimed in this application is as follows. (1) The dust ash collected in the exhaust gas treatment process of a refuse incineration treatment facility is introduced into a heating device and heated to decompose the dioxins contained in the dust ash by heating and dechlorination. In the method, in the heating device, at least one of chlorobenzenes and chlorophenols contained in the dust collecting ash before the heating treatment at the inlet of the heating device and the dust collecting ash after the heating treatment at the outlet of the heating device is quantified, respectively. A method for thermal dechlorination of dust collection ash, which comprises estimating a removal rate of dioxins and adjusting heating conditions based on the estimated removal rate of dioxins. (2) Heating the dust ash according to (1), characterized in that the removal rate of dioxins in the heating device is estimated by measuring the content of pentachlorobenzene or hexachlorobenzene before and after the heat treatment of the dust ash. Dechlorination treatment method.

【0011】[0011]

【作用】加熱処理前後におけるクロルベンゼン類および
クロルフェノール類のうち少なくとも1種を定量するこ
とにより、加熱処理装置におけるダイオキシン類の除去
率を推定することができるので、この推定したダイオキ
シン類の除去率に基いて目的とするダイオキシン類の除
去率が得られるように加熱温度、灰の装置内滞留時間を
はじめとする加熱条件を調節することにより、無用な高
温および不必要な滞留時間の延長が回避される。
[Function] The removal rate of dioxins in the heat treatment apparatus can be estimated by quantifying at least one of chlorobenzenes and chlorophenols before and after the heat treatment. Therefore, the estimated removal rate of dioxins can be estimated. By adjusting heating conditions such as heating temperature and ash residence time in the equipment to obtain the desired dioxins removal rate based on the above, unnecessary high temperature and unnecessary extension of residence time are avoided. To be done.

【0012】図2および図3は、それぞれ本発明の原理
を示す説明図であって、図2は、集じん灰を加熱処理し
た場合のヘキサクロルベンゼンの除去率とダイオキシン
類の除去率との関係を示す図である。また図3は、同じ
く集じん灰を加熱処理した場合の各加熱温度におけるヘ
キサクロルベンゼンの分解率とダイオキシン類の分解率
との関係を示す図であって、ダイオキシン類をPCDD
S とPCDFS とに分けて表示したものである。図2に
おいて、ヘキサクロルベンゼンの除去率とダイオキシン
類の除去率とは、除去率90〜99.9%の範囲でほぼ
比例関係にあり、しかも、ダイオキシン類の除去率の方
がヘキサクロルベンゼンの除去率よりも高くなる傾向を
示している。また、図3において、ダイオキシン類の分
解率(除去率)はヘキサクロルベンゼンの分解率よりも
高く、ヘキサクロルベンゼン<PCDFS <PCDDS
の順に分解率が高くなっていることが分かる。従って図
2および図3から、加熱処理装置におけるヘキサクロル
ベンゼンの除去率を測定すれば、ダイオキシン類の除去
率はそれよりも高くなることが保証される。ヘキサクロ
ルベンゼン以外のクロルベンゼンまたはクロルフェノー
ル類についてもほぼ同様の関係が認められる。
2 and 3 are explanatory views showing the principle of the present invention. FIG. 2 shows the removal rate of hexachlorobenzene and the removal rate of dioxins in the case of heat treating dust collection ash. It is a figure which shows a relationship. FIG. 3 is a diagram showing the relationship between the decomposition rate of hexachlorobenzene and the decomposition rate of dioxins at each heating temperature when the dust ash is also heat-treated.
The display is divided into S and PCDF S. In FIG. 2, the removal rate of hexachlorobenzene and the removal rate of dioxins are almost proportional in the removal rate range of 90 to 99.9%, and the removal rate of dioxins is higher than that of hexachlorobenzene. It tends to be higher than the removal rate. Further, in FIG. 3, the decomposition rate (removal rate) of dioxins is higher than the decomposition rate of hexachlorobenzene, and hexachlorobenzene <PCDF S <PCDD S
It can be seen that the decomposition rate increases in the order of. Therefore, from FIGS. 2 and 3, if the removal rate of hexachlorobenzene in the heat treatment apparatus is measured, it is guaranteed that the removal rate of dioxins will be higher than that. Almost the same relationship is observed for chlorobenzene or chlorophenols other than hexachlorobenzene.

【0013】このように本発明は、ダイオキシン類の除
去率を推算する指標物質として、分析が容易な、例えば
ヘキサクロルベンゼンを用い、その除去率を求めること
によってダイオキシン類の除去率を推算し、これを目安
として加熱装置の運転条件を調節して目的とするダイオ
キシン類除去率を達成するものである。本発明におい
て、ダイオキシン類とは、4〜8塩素化のポリ塩素化ジ
ベンゾパラダイオキシン(PCDDS )と4〜8塩素化
のポリ塩素化ジベンゾフラン(PCDFS )の総称をい
う。
As described above, according to the present invention, hexachlorobenzene, which is easy to analyze, is used as an index substance for estimating the removal rate of dioxins, and the removal rate of dioxins is estimated by obtaining the removal rate, Using this as a guide, the operating conditions of the heating device are adjusted to achieve the desired dioxins removal rate. In the present invention, dioxins are a general term for 4-8 chlorinated polychlorinated dibenzoparadioxins (PCDD S ) and 4-8 chlorinated polychlorinated dibenzofurans (PCDF S ).

【0014】本発明において加熱処理装置の形式は、集
じん灰を加熱できるものであれば特に限定されず、加熱
管方式の他、例えば水平型スクリュー、傾斜角スクリュ
ー、縦形スクリュー、多管式ロータリーキルン等が使用
される。また加熱方式としては電熱ヒータの他、例えば
排ガスまたは高温粉体との熱交換方式、バーナ方式、マ
イクロ波方式等が用いられるが、特に限定されない。
In the present invention, the type of the heat treatment device is not particularly limited as long as it can heat the dust collecting ash, and in addition to the heating pipe system, for example, a horizontal screw, an inclined angle screw, a vertical screw, a multi-tube rotary kiln. Etc. are used. As a heating method, in addition to an electric heater, for example, a heat exchange method with exhaust gas or high-temperature powder, a burner method, a microwave method, or the like is used, but is not particularly limited.

【0015】本発明において、ダイオキシン類の除去率
を推定するために用いる測定指標物質は、ヘキサクロル
ベンゼン、ペンタクロルベンゼンのほか、他のクロルベ
ンゼン類、クロルフェノール類またはこれらの組み合わ
せが用いられる。また、これら測定指標物質の分析装置
としては、例えばGC/ECD(ガスクロマトグラフィ
ー電子捕獲検出器)が使用されるが、灰中のクロルベン
ベン類またはクロルフェノール類を定量できるものであ
ればこれ以外のものであってもよく、特に限定されな
い。
In the present invention, the measurement index substance used to estimate the removal rate of dioxins may be hexachlorobenzene, pentachlorobenzene, other chlorobenzenes, chlorophenols or a combination thereof. As an analyzer for these measurement index substances, for example, a GC / ECD (gas chromatography electron capture detector) is used, but other than this as long as it can quantify chlorbenbenes or chlorophenols in ash However, it is not particularly limited.

【0016】本発明において、加熱管内の気相を窒素で
置換するか、または集じん灰に、例えば5重量%程度の
消石灰を添加して加熱することにより、集じん灰の加熱
温度を約50〜100℃低減しても同様のダイオキシン
類除去率が得られる。
In the present invention, the heating temperature of the dust collecting ash is about 50 by substituting the gas phase in the heating pipe with nitrogen or by heating the dust collecting ash by adding, for example, about 5% by weight of slaked lime. Even if the temperature is reduced by -100 ° C, the same dioxins removal rate can be obtained.

【0017】[0017]

【実施例】次に本発明を実施例によりさらに詳細に説明
する。図1は、本発明の一実施例に用いられる集じん灰
の加熱脱塩素化処理装置の説明図である。この加熱処理
装置は、出口側が入口側よりもわずかに低くなるように
傾斜させた加熱管1と、該加熱管1の入口フード2およ
び出口フード3と、前記加熱管1に集じん灰Aを導入す
る定量供給機6と、前記加熱管1を加熱する加熱装置7
および回転駆動する駆動装置8と、加熱処理された処理
灰Bを排出する前記出口フード3の出口に設けられた処
理灰B中のヘキサクロルベンゼン量を検出する自動分析
装置5と、その後流のシール装置4と、求めた処理灰B
中のヘキサクロルベンゼン量およびあらかじめ検出され
た前記集じん灰A中のヘキサクロルベンゼン量に基い
て、ヘキサクロルベンゼンの除去率を求め、求めた除去
率に基いてダイオキシン類の除去率を推算し、前記加熱
装置7および駆動装置8の加熱温度および回転数をそれ
ぞれ制御する制御装置12から主として構成されてい
る。なお、9および10は温度検出器、11は排風機で
ある。
EXAMPLES Next, the present invention will be described in more detail by way of examples. FIG. 1 is an explanatory diagram of a thermal dechlorination apparatus for dust collecting ash used in an embodiment of the present invention. In this heat treatment apparatus, a heating pipe 1 inclined so that the outlet side is slightly lower than the inlet side, an inlet hood 2 and an outlet hood 3 of the heating pipe 1, and a dust collecting ash A in the heating pipe 1. A constant quantity feeder 6 to be introduced and a heating device 7 for heating the heating pipe 1.
And a drive device 8 for rotationally driving, an automatic analyzer 5 for detecting the amount of hexachlorobenzene in the treated ash B provided at the outlet of the outlet hood 3 for discharging the treated ash B subjected to heat treatment, and a subsequent flow Sealing device 4 and obtained treated ash B
Based on the amount of hexachlorobenzene in the powder and the amount of hexachlorobenzene in the dust ash A detected in advance, the removal rate of hexachlorobenzene is determined, and the removal rate of dioxins is estimated based on the determined removal rate. Mainly comprises a control device 12 for controlling the heating temperature and the rotation speed of the heating device 7 and the driving device 8, respectively. In addition, 9 and 10 are temperature detectors, and 11 is an exhaust fan.

【0018】このような構成において、定量供給装置6
によって払い出された集じん灰Aは入口フード2を経
て、わずかに出口側へ傾斜し、駆動装置8によって回転
される加熱管1に導入され、該加熱管内で加熱装置7に
よって加熱され、所定の滞留時間を経て加熱装置内を出
口方向に移動し、この間に、前記集じん灰Aに含まれる
PCDDS 、PCDFS 等のダイオキシン類が分解して
気相中に移行する。分解生成した分解生成ガスは処理灰
Bと分離されたのち出口フード3を流出し、排風機11
を経て灰ガスCとして装置外に抜き出され、例えばごみ
焼却処理施設の排ガス処理装置の集じん装置前流に導入
されて別途処理される。一方、ダイオキシン類が分解除
去された集じん灰は、出口フード3で分解ガスと分離さ
れた後、シール装置4を経て処理灰Bとして系外へ排出
される。このとき前記シール装置4の前流に配置された
分析装置5によって前記処理灰B中のヘキサクロルベン
ゼン濃度が所定間隔で連続的に検出され、その信号が制
御装置12に送られる。処理灰B中のヘキサクロルベン
ゼン濃度信号を受けた制御装置12は、前記検出値とあ
らかじめ求めた加熱装置入口の集じん灰Aのヘキサクロ
ルベンゼン濃度とから前記加熱装置におけるヘキサクロ
ルベンゼンの除去率を求め、該除去率からダイオキシン
類の除去率を推算し、推算したダイオキシン類の除去率
が目的とする除去率よりも低い場合は、加熱温度を上げ
るように、または加熱管の傾斜角度を小さくするかもし
くは回転数を少なくして滞留時間が長くなるように、加
熱装置7、駆動装置8および図示省略した加熱管1の傾
斜角変更手段に信号を送り、除去率の向上を図る。他
方、推算した除去率が目的とする除去率よりも高い場合
には、加熱温度を下げるように、または加熱管の傾斜角
度を大きくするかもしくは加熱管の回転数を高くして灰
の加熱管内滞留時間を短くして加熱条件の緩和を図る。
In such a configuration, the constant quantity supply device 6
The dust-collected ash A discharged by means of the inlet hood 2 is slightly inclined toward the outlet side, and is introduced into the heating pipe 1 rotated by the drive device 8 and heated by the heating device 7 in the heating pipe to a predetermined extent. After passing through the residence time of 1, the dioxins such as PCDD S and PCDF S contained in the dust collecting ash A are decomposed and transferred into the gas phase during this time. The decomposed gas generated by decomposition is separated from the treated ash B, and then flows out of the outlet hood 3, and the blower 11
After that, the ash gas C is extracted to the outside of the apparatus, and is introduced into the upstream of the dust collecting apparatus of the exhaust gas processing apparatus of the refuse incineration processing facility for separate processing. On the other hand, the dust collecting ash from which the dioxins have been decomposed and removed is separated from the decomposed gas by the outlet hood 3, and then discharged as a treated ash B through the sealing device 4 to the outside of the system. At this time, the hexachlorobenzene concentration in the treated ash B is continuously detected at a predetermined interval by the analyzer 5 arranged in the upstream side of the sealing device 4, and the signal is sent to the controller 12. The control device 12, which has received the hexachlorobenzene concentration signal in the treated ash B, uses the detection value and the hexachlorobenzene concentration of the dust collecting ash A at the inlet of the heating device determined in advance to remove the hexachlorobenzene in the heating device. Then, the removal rate of dioxins is estimated from the removal rate, and if the estimated removal rate of dioxins is lower than the target removal rate, raise the heating temperature or decrease the inclination angle of the heating tube. Alternatively, a signal is sent to the heating device 7, the driving device 8 and the inclination angle changing means (not shown) of the heating tube 1 so as to increase the residence time by reducing the number of rotations and improve the removal rate. On the other hand, if the estimated removal rate is higher than the target removal rate, lower the heating temperature, or increase the heating tube inclination angle or increase the heating tube rotation speed, Shorten the residence time to relax the heating conditions.

【0019】本実施例によれば、加熱処理装置出口の処
理灰B中のヘキサクロルベンゼン濃度をモニタリング
し、これとあらかじめ求めた加熱装置入口のヘキサクロ
ルベンゼン濃度とから、加熱装置におけるダイオキシン
類の除去率を推算し、これに基いて加熱装置の加熱条件
を調節することにより、不必要な高温加熱をなくし、無
駄な滞留時間の延長を防止することができる。従って集
じん灰中のダイオキシン類を目的とする除去率で分解処
理できるだけでなく、装置寿命の延命およびランニング
コストの低減を図ることができる。
According to the present embodiment, the concentration of hexachlorobenzene in the treated ash B at the outlet of the heat treatment device is monitored, and from this and the concentration of hexachlorobenzene at the inlet of the heat device determined in advance, the dioxin content in the heater is determined. By estimating the removal rate and adjusting the heating conditions of the heating device based on this, it is possible to eliminate unnecessary high-temperature heating and prevent unnecessary extension of the residence time. Therefore, not only dioxins in the dust collection ash can be decomposed at a desired removal rate, but also the life of the device can be extended and the running cost can be reduced.

【0020】本実施例において、被処理灰の加熱装置内
平均滞留時間は前記加熱管1の回転数と傾斜角度を調節
することによって制御される。加熱管の傾斜角度の調節
は、例えば油圧シリンダーで傾斜角度を上げる等、公知
の方法で行われる。本実施例において、処理灰B中のヘ
キサクロルベンゼンの分析装置としては、例えばGC/
ECD(ガスクロマトグラフィー電子捕獲検出器)が使
用され、その定量は次のように行われる。すなわち、処
理灰Bの一定量、例えば5gを分取し、これをアセトン
約10mlに混合して目的成分であるヘキサクロルベン
ゼンを抽出する。次いで抽出液の一部、例えば5μlを
GC/ECDへ導入し、例えばキャピラリーカラムを用
いて定量する。1検体の分析所要時間は2〜30分であ
る。
In the present embodiment, the average residence time of the ash to be treated in the heating device is controlled by adjusting the rotation speed and the inclination angle of the heating tube 1. The tilt angle of the heating tube is adjusted by a known method such as increasing the tilt angle with a hydraulic cylinder. In this embodiment, as an analyzer for hexachlorobenzene in the treated ash B, for example, GC /
ECD (Gas Chromatography Electron Capture Detector) is used and its quantification is performed as follows. That is, a fixed amount of the treated ash B, for example, 5 g is taken and mixed with about 10 ml of acetone to extract hexachlorobenzene as a target component. Then, a part of the extract, for example 5 μl, is introduced into the GC / ECD and quantified using, for example, a capillary column. The time required for analysis of one sample is 2 to 30 minutes.

【0021】本実施例では、加熱処理後の処理灰B中の
ヘキサクロルベンゼン濃度をモニタリングし、これとあ
らかじめ求めた加熱処理前の集じん灰A中のヘキサクロ
ルベンゼン濃度に基いて加熱装置におけるダイオキシン
類の除去率を推定したが、例えば定量供給装置6と加熱
装置1の間に自動分析装置5を配置し、前記集じん灰A
中のヘキサクロルベンゼン濃度も処理灰B中の濃度と同
様にモニタリングし、所定間隔で連続的に検出される入
口および出口の濃度からダイオキシン類の除去率を推定
することもできる。
In the present embodiment, the concentration of hexachlorobenzene in the treated ash B after the heat treatment is monitored, and based on this and the concentration of hexachlorobenzene in the collected dust ash A before the heat treatment, the heating device The removal rate of dioxins was estimated. For example, the automatic analysis device 5 was arranged between the constant amount supply device 6 and the heating device 1, and the dust collection ash A
It is also possible to monitor the hexachlorobenzene concentration in the same manner as the concentration in the treated ash B, and estimate the removal rate of dioxins from the concentrations at the inlet and the outlet that are continuously detected at predetermined intervals.

【0022】次に本発明の具体的実施例を説明する。出
口側に5゜傾斜した図1の装置を用い、ダイオキシン類
の分解除去率99%を目的とし、処理量100kg/h
r、灰の平均滞留時間10minとして都市ごみ焼却処
理施設から排出されるバグフィルタ灰を加熱処理した。
出口フード3を流出する処理灰B中のヘキサクロルベン
ゼン濃度を10分置きに検出し、求めた処理灰B中のヘ
キサクロルベンゼン濃度とあらかじめ求めた加熱処理前
の集じん灰Aのヘキサクロルベンゼン濃度(28ng/
g)から前記加熱装置におけるヘキサクロルベンゼンの
除去率を求め、このヘキサクロルベンゼンの除去率が9
5%よりも低くなる場合には、加熱管の傾斜角度を3
゜、平均滞留時間を約20分として前記ヘキサクロルベ
ンゼンの除去率を95%以上に維持し、加熱脱塩素化処
理を行った。このとき加熱管1の加熱温度は約450
℃、回転数6rpmであった。
Next, specific examples of the present invention will be described. Using the device in Fig. 1 inclined at 5 ° on the outlet side, the treatment rate is 100 kg / h for the purpose of decomposing and removing 99% of dioxins.
The bag filter ash discharged from the municipal solid waste incineration facility was heat-treated with an average residence time of 10 min.
The hexachlorobenzene concentration in the treated ash B flowing out of the outlet hood 3 was detected every 10 minutes, and the hexachlorobenzene concentration in the treated ash B obtained and the hexachlorobenzene of the dust collecting ash A before the heat treatment obtained in advance were detected. Concentration (28 ng /
The removal rate of hexachlorobenzene in the heating device was calculated from g), and the removal rate of hexachlorobenzene was 9%.
If it is lower than 5%, set the heating pipe tilt angle to 3
And the average residence time was about 20 minutes, the removal ratio of hexachlorobenzene was maintained at 95% or more, and heat dechlorination treatment was performed. At this time, the heating temperature of the heating pipe 1 is about 450.
The temperature was 6 ° C and the rotation speed was 6 rpm.

【0023】試験結果を第1表に示す。The test results are shown in Table 1.

【0024】[0024]

【表1】 [Table 1]

【0025】第1表において、ダイオキシン類の除去率
は安定して99%以上であったことが分かる。本実施例
によれば、従来ダイオキシン類の除去率99%以上を得
るために、500℃程度で加熱処理していたものを、同
様のダイオキシン類除去率を400〜500℃の加熱温
度で達成できるので、加熱管の高温腐食を防止し、装置
寿命を延命することができる。またこれに伴ってランン
グコストを大幅に低減することができる。
From Table 1, it can be seen that the removal rate of dioxins was stably 99% or more. According to the present example, in order to obtain the removal rate of dioxins of 99% or more, the same dioxins removal rate can be achieved at the heating temperature of 400 to 500 ° C, which has been heat treated at about 500 ° C. Therefore, high temperature corrosion of the heating pipe can be prevented and the life of the device can be extended. Further, along with this, the run cost can be significantly reduced.

【0026】[0026]

【発明の効果】本願の請求項1記載の発明によれば、加
熱装置入口および出口における灰中のクロルベンゼン類
およびクロルフェノール類の少ないとも1種を定量して
加熱装置におけるダイオキシン類の除去率を推算し、こ
れによって加熱条件を調節するようにしたことにより、
前記加熱装置におけるダイオキシン類の除去率をモニタ
リングすることができるので、無用の加熱温度の上昇ま
たは不必要な滞留時間の延長を防止することができる。
従って、高温腐食を防止して装置寿命を延命することが
できるうえ、ランニングコストを大幅に低減することが
できる。
According to the invention of claim 1 of the present application, the removal rate of dioxins in the heating device is determined by quantifying at least one of chlorobenzenes and chlorophenols in the ash at the inlet and outlet of the heating device. By adjusting the heating conditions by this,
Since the removal rate of dioxins in the heating device can be monitored, it is possible to prevent an unnecessary increase in heating temperature or an unnecessary extension of the residence time.
Therefore, high temperature corrosion can be prevented and the life of the apparatus can be extended, and running costs can be significantly reduced.

【0027】本願の請求項2記載の発明によれば、ダイ
オキシン類の除去率を推算するための指標物質として異
性体がなく、分析が容易なペンタクロルベンゼンまたは
ヘキサクロルベンゼンを用いることにより、上記発明の
効果に加え、ダイオキシン類の除去率を迅速かつ正確に
モニタリングすることができる。
According to the invention of claim 2 of the present application, by using pentachlorobenzene or hexachlorobenzene, which is free of isomers and is easy to analyze, as an index substance for estimating the removal rate of dioxins, In addition to the effects of the invention, the removal rate of dioxins can be quickly and accurately monitored.

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

【図1】本発明の一実施例に用いる加熱脱塩素化装置の
説明図。
FIG. 1 is an explanatory view of a thermal dechlorination apparatus used in an embodiment of the present invention.

【図2】本発明の原理を示す説明図。FIG. 2 is an explanatory diagram showing the principle of the present invention.

【図3】本発明の原理を示す説明図。FIG. 3 is an explanatory diagram showing the principle of the present invention.

【符合の説明】[Explanation of sign]

1…加熱管、2…入口フード、3…出口フード、4…シ
ール装置、5…ヘキサクロルベンゼンの自動分析装置、
6…定量供給装置、7…加熱装置、8…駆動装置、9…
温度検出器、10…温度検出器、11…排風機、12…
制御装置。
1 ... Heating tube, 2 ... Inlet hood, 3 ... Outlet hood, 4 ... Sealing device, 5 ... Hexachlorobenzene automatic analyzer,
6 ... Fixed amount supply device, 7 ... Heating device, 8 ... Driving device, 9 ...
Temperature detector, 10 ... Temperature detector, 11 ... Exhaust fan, 12 ...
Control device.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 F23G 7/00 103 Z 9430−3K (72)発明者 工藤 宏 東京都品川区大崎1丁目6番1号 三造環 境エンジニアリング株式会社内 (72)発明者 高須賀 玄太郎 千葉県市原市八幡海岸通1番地 三井造船 株式会社千葉事業所内 (72)発明者 板谷 真積 千葉県市原市八幡海岸通1番地 三井造船 株式会社千葉事業所内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Reference number within the agency FI technical display location F23G 7/00 103 Z 9430-3K (72) Inventor Hiroshi Kudo 1-6 Osaki, Shinagawa-ku, Tokyo No. 1 Sanzo Kankyo Engineering Co., Ltd. (72) Inventor Gentaro Takasuka No. 1 Hachiman Kaigan Dori, Ichihara City, Chiba Prefecture Mitsui Engineering & Ships Co., Ltd. Chiba Works No. 1 Mazumi Itaya No. 1 Hachiman Kaido Dori, Ichihara City, Chiba Prefecture Mitsui Shipbuilding Co., Ltd. Chiba Works

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 ごみ焼却処理施設の排ガス処理工程で捕
集された集じん灰を加熱装置に導入して加熱し、前記集
じん灰に含まれるダイオキシン類を分解する集じん灰の
加熱脱塩素化処理方法において、前記加熱装置入口の加
熱処理前の集じん灰および加熱装置出口の加熱処理後の
集じん灰にそれぞれ含まれるクロルベンゼン類およびク
ロルフェノール類の少なくとも1種を定量して前記加熱
装置におけるダイオキシン類の除去率を推定し、該推定
したダイオキシン類の除去率に基いて加熱条件を調節す
ることを特徴とする集じん灰の加熱脱塩素化処理方法。
1. A thermal dechlorination of dust ash which introduces dust ash collected in an exhaust gas treatment step of a refuse incineration treatment facility into a heating device to heat it and decomposes dioxins contained in the dust ash. In the chemical treatment method, at least one of chlorobenzene and chlorophenol contained in the dust-collected ash before the heat treatment at the inlet of the heating device and the dust-collected ash after the heat treatment at the outlet of the heating device is quantified and the heating is performed. A method for heating and dechlorinating dust-collecting ash, which comprises estimating a removal rate of dioxins in an apparatus and adjusting heating conditions based on the estimated removal rate of dioxins.
【請求項2】 集じん灰の加熱処理前後のペンタクロル
ベンゼンまたはヘキサクロルベンゼン含有量を測定して
加熱装置におけるダイオキシン類の除去率を推定するこ
とを特徴とする請求項1記載の集じん灰の加熱脱塩素化
処理方法。
2. The dust collection ash according to claim 1, wherein the removal rate of dioxins in the heating device is estimated by measuring the pentachlorobenzene or hexachlorobenzene content before and after the heat treatment of the dust collection ash. Method for thermal dechlorination of.
JP5309491A 1993-12-09 1993-12-09 Heating dechlorination treatment for collected dust and ash Pending JPH07155731A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5309491A JPH07155731A (en) 1993-12-09 1993-12-09 Heating dechlorination treatment for collected dust and ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5309491A JPH07155731A (en) 1993-12-09 1993-12-09 Heating dechlorination treatment for collected dust and ash

Publications (1)

Publication Number Publication Date
JPH07155731A true JPH07155731A (en) 1995-06-20

Family

ID=17993636

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5309491A Pending JPH07155731A (en) 1993-12-09 1993-12-09 Heating dechlorination treatment for collected dust and ash

Country Status (1)

Country Link
JP (1) JPH07155731A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002126687A (en) * 2000-10-23 2002-05-08 Chisaki:Kk Heat treatment equipment and method for adhesive material
WO2002094463A1 (en) * 1999-12-10 2002-11-28 Art Ceramic Co., Ltd. Intermittent flowing type thermal decomposer
US6580067B1 (en) 1999-11-19 2003-06-17 Hitachi, Ltd. Sample analyzing monitor and combustion control system using the same
US6723286B2 (en) 1998-11-25 2004-04-20 Hitachi, Ltd. Chemical monitoring method and apparatus, and incinerator
CN115488137A (en) * 2022-09-23 2022-12-20 重庆三峰环境集团股份有限公司 System and method for degrading dioxin in waste incineration fly ash

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6723286B2 (en) 1998-11-25 2004-04-20 Hitachi, Ltd. Chemical monitoring method and apparatus, and incinerator
US6580067B1 (en) 1999-11-19 2003-06-17 Hitachi, Ltd. Sample analyzing monitor and combustion control system using the same
WO2002094463A1 (en) * 1999-12-10 2002-11-28 Art Ceramic Co., Ltd. Intermittent flowing type thermal decomposer
US6877444B2 (en) 1999-12-10 2005-04-12 Art Ceramic Co., Ltd. Intermittent flow type thermal decomposer
JP2002126687A (en) * 2000-10-23 2002-05-08 Chisaki:Kk Heat treatment equipment and method for adhesive material
JP4560198B2 (en) * 2000-10-23 2010-10-13 株式会社チサキ Adhesive substance heat treatment apparatus and method
CN115488137A (en) * 2022-09-23 2022-12-20 重庆三峰环境集团股份有限公司 System and method for degrading dioxin in waste incineration fly ash
CN115488137B (en) * 2022-09-23 2024-05-28 重庆三峰环境集团股份有限公司 System and method for degrading dioxin in waste incineration fly ash

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