JPH05137813A - Thermal decomposition of organic chlorine compound - Google Patents

Thermal decomposition of organic chlorine compound

Info

Publication number
JPH05137813A
JPH05137813A JP30493991A JP30493991A JPH05137813A JP H05137813 A JPH05137813 A JP H05137813A JP 30493991 A JP30493991 A JP 30493991A JP 30493991 A JP30493991 A JP 30493991A JP H05137813 A JPH05137813 A JP H05137813A
Authority
JP
Japan
Prior art keywords
organic chlorine
chlorine compound
thermal decomposition
dioxin
waste wood
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
Application number
JP30493991A
Other languages
Japanese (ja)
Other versions
JP2787256B2 (en
Inventor
Kenji Yasuda
賢士 保田
Kiichi Matsuoka
喜一 松岡
Jinshiro Fujita
仁四郎 藤田
Toshio Hama
利雄 濱
Toshihiko Yasuda
俊彦 安田
Kanji Ota
完志 太田
Rikio Shinohara
力男 篠原
Masakazu Tanaka
将一 田中
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.)
Hitachi Zosen Corp
Original Assignee
Hitachi Zosen Corp
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 Hitachi Zosen Corp filed Critical Hitachi Zosen Corp
Priority to JP30493991A priority Critical patent/JP2787256B2/en
Publication of JPH05137813A publication Critical patent/JPH05137813A/en
Application granted granted Critical
Publication of JP2787256B2 publication Critical patent/JP2787256B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

Landscapes

  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)
  • Fire-Extinguishing Compositions (AREA)

Abstract

PURPOSE:To reclaim or recycle waste wood containing organic chlorine antiseptics and burnt-up or flying ashes containing dioxin by making them innoxious. CONSTITUTION:An organic chlorine compound is thermally decomposed while reducing gas is allowed to pass through disposals containing the organic chlorine compound. By this thermal decomposition, dioxin in burnt-up or flying ashes and organic chlorine antiseptics in waste wood can be decomposed and made innoxious quickly at a relatively low temperature.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、最近問題となってき
ているゴミ焼却炉排出灰中のダイオキシンや、防腐剤と
して木材中に含ませたトリクロロフェノール等の有機塩
素化合物を熱分解処理する方法に関するものである。
FIELD OF THE INVENTION The present invention relates to a method for thermally decomposing dioxin contained in ash discharged from a refuse incinerator and organic chlorine compounds such as trichlorophenol contained in wood as an antiseptic, which have become a problem recently. It is about.

【0002】[0002]

【従来の技術】従来、ダイオキシンに対する環境規制は
なかったため、ごみ焼却場から排出される焼却灰や電気
集塵機もしくはバグフィルターで捕集された飛灰は、未
処理のまま埋立て廃棄されており、灰中ダイオキシンが
流出する恐れがあった。
2. Description of the Related Art Conventionally, since there is no environmental regulation for dioxin, incineration ash discharged from a refuse incinerator and fly ash collected by an electric dust collector or a bag filter are untreated and landfilled. There was a risk that dioxins in the ash could flow out.

【0003】最近、灰中ダイオキシンの熱分解処理によ
る無害化が、研究報告されているが、処理条件として4
00℃以上の高温が必要である上に、新たに重金属類の
揮散の問題が生じ、さらに処理時間として2時間以上も
の長時間が必要であった。
Recently, a research report has been made on detoxification of dioxin in ash by thermal decomposition treatment.
In addition to the need for a high temperature of 00 ° C. or higher, a new problem of volatilization of heavy metals occurred, and a long processing time of 2 hours or more was required.

【0004】また、ダイオキシンの前駆物質であるトリ
クロロフェノールを始めとする有機塩素系防腐剤につい
ては、これを含む廃木材を単に燃焼処理したり埋立処理
するだけであった。そのため、この処理物からトリクロ
ロフェノールが流出する可能性があると共に、流出トリ
クロロフェノールからダイオキシンが生成する恐れがあ
った。
Regarding the organic chlorine-based preservatives such as trichlorophenol, which is a precursor of dioxin, the waste wood containing this was simply burnt or landfilled. Therefore, there is a possibility that trichlorophenol may flow out from this treated product, and that dioxins may be generated from the outflowing trichlorophenol.

【0005】[0005]

【発明が解決しようとする課題】近年、ダイオキシンは
人体や環境に悪影響を与えるとして問題になり、ダイオ
キシン類発生防止に関する規制が出された。この規制の
結果、ダイオキシンを含んだ灰やダイオキシン前駆物質
を含んだ廃木材の埋立て廃棄はできなくなった。また、
廃木材を焼却すると、トリクロロフェノール等の有機塩
素系防腐剤からダイオキシンが発生するために、廃木材
の焼却処分もできなくなった。
In recent years, dioxin has become a problem because it adversely affects the human body and the environment, and regulations have been issued to prevent the generation of dioxins. As a result of this regulation, ash containing dioxin and waste wood containing dioxin precursors cannot be landfilled. Also,
When waste wood is incinerated, it becomes impossible to incinerate the waste wood because dioxins are generated from organic chlorine preservatives such as trichlorophenol.

【0006】さらに、従来の有機塩素化合物の熱分解方
法は、上記の如く高温で長時間の処理条件を必要とする
ものであった。
Further, the conventional thermal decomposition method of the organic chlorine compound requires the treatment conditions of high temperature and long time as described above.

【0007】この発明の目的は、上記実情に鑑み、焼却
灰もしくは飛灰中のダイオキシンや、腐木材中の有機塩
素系防腐剤を比較的低温で迅速に分解・無害化できる方
法を提供することにある。
In view of the above situation, an object of the present invention is to provide a method capable of rapidly decomposing / detoxifying dioxin in incinerated ash or fly ash and organochlorine preservative in rot wood at a relatively low temperature. It is in.

【0008】[0008]

【課題を解決するための手段】この発明による有機塩素
化合物の熱分解方法は、上記目的を達成すべく工夫され
たものであって、有機塩素化合物を含む被処理物に還元
性ガスを流通させながら、有機塩素化合物を熱分解する
ことを特徴とするものである。
The method for thermally decomposing organic chlorine compounds according to the present invention has been devised to achieve the above object, and a reducing gas is passed through an object to be treated containing an organic chlorine compound. However, it is characterized by thermally decomposing an organic chlorine compound.

【0009】この熱分解方法の処理対象である有機塩素
化合物の代表例は、ゴミ焼却炉排出灰中に含まれるダイ
オキシンや、防腐剤として木材中に含まれるトリクロロ
フェノール等である。トリクロロフェノールは上述した
ようにダイオキシンの前駆物質である。
Typical examples of the organic chlorine compound to be treated by this thermal decomposition method are dioxin contained in the ash discharged from the refuse incinerator and trichlorophenol contained in wood as a preservative. Trichlorophenol is a dioxin precursor as described above.

【0010】還元性ガスの代表例は、アンモニアガスで
ある。アンモニアガスは流通ガスに含ませた形態で熱分
解反応に供される。流通ガスとしては価格の点で窒素ガ
スが好ましい。流通ガス中のアンモニアガスの量は好ま
しくは約1容量%である。
A typical example of the reducing gas is ammonia gas. Ammonia gas is supplied to the thermal decomposition reaction in the form of being contained in the circulating gas. Nitrogen gas is preferable as the circulating gas in terms of price. The amount of ammonia gas in the circulating gas is preferably about 1% by volume.

【0011】有機塩素化合物の熱分解条件は、たとえ
ば、約300℃で約30分間である。
The thermal decomposition condition of the organic chlorine compound is, for example, about 300 ° C. for about 30 minutes.

【0012】[0012]

【実施例】つぎに、この発明を具体的に説明するため
に、この発明の実施例を挙げる。
EXAMPLES Next, examples of the present invention will be given to specifically explain the present invention.

【0013】実施例 廃木材に含有される有害有機塩素化合物の1つであるト
リクロロフェノールを用いて、下記の手法で操作を行な
った。
Example Trichlorophenol, which is one of the harmful organochlorine compounds contained in waste wood, was used for the following procedure.

【0014】(i) まず、2,4,6−トリクロロフェ
ノール(以下TCPと略記する)を模擬非処理物質であ
る珪藻土の上に含浸担持させ、乾燥させ、実験用の試料
を調製した。この試料をアルコール抽出処理し、抽出液
を液体クロマトグラフィー法によって分析した。TCP
は、試料中に9.9mg/g(珪藻土)の量で含浸担持
されていた。
(I) First, 2,4,6-trichlorophenol (hereinafter abbreviated as TCP) was impregnated and supported on diatomaceous earth, which is a simulated untreated substance, and dried to prepare a sample for experiment. This sample was subjected to alcohol extraction treatment, and the extract was analyzed by liquid chromatography. TCP
Was impregnated and supported in the sample in an amount of 9.9 mg / g (diatomaceous earth).

【0015】(ii) 上記試料2.5gを試験用管状電気
炉内に設置した石英製反応管内に充填し、300℃で加
熱処理を行いながら、アンモニアガスを1容量%含む窒
素ガスを0.3リットル/分の割合で30分間反応管に
流した。
(Ii) 2.5 g of the above sample was filled in a quartz reaction tube set in a test tubular electric furnace, and a heat treatment was carried out at 300 ° C., while a nitrogen gas containing 1% by volume of ammonia gas was added at a rate of 0. The reaction tube was flowed at a rate of 3 l / min for 30 minutes.

【0016】(iii) ついで、反応管の出口で、出口ガ
ス中のTCP濃度と処理後試料中のTCP残存量とをそ
れぞれ上述と同様の方法で分析したところ、出口ガス中
にはTCPの分解により生じたより極性の低い物質が、
処理前試料のTCP含有量に相当する量で検出され、ま
た処理後試料中のTCP残存量は検出されなかった。
(Iii) Next, at the outlet of the reaction tube, the TCP concentration in the outlet gas and the residual TCP amount in the treated sample were analyzed by the same method as described above. As a result, TCP was decomposed in the outlet gas. The less polar substance produced by
The amount corresponding to the TCP content of the sample before treatment was detected, and the residual TCP amount in the sample after treatment was not detected.

【0017】したがって、TCP分解率はほぼ100%
であった。
Therefore, the TCP decomposition rate is almost 100%.
Met.

【0018】比較例 実施例の工程(ii)において、アンモニアガスを含まない
窒素ガスを反応管に流し、その他の操作を実施例と同様
に行った。
Comparative Example In step (ii) of the example, nitrogen gas containing no ammonia gas was flown through the reaction tube, and other operations were performed in the same manner as in the example.

【0019】工程(iii) における分析の結果、反応管の
出口ガス中のTCP濃度は処理前試料のTCP含有量と
ほぼ等しく、TCPは流通ガスによって分解されること
なしに揮散することが確認された。
As a result of the analysis in the step (iii), it was confirmed that the TCP concentration in the outlet gas of the reaction tube was almost equal to the TCP content of the untreated sample, and TCP was volatilized without being decomposed by the flowing gas. It was

【0020】[0020]

【発明の効果】この発明の熱分解方法によれば、焼却灰
もしくは飛灰中のダイオキシンや、腐木材中の有機塩素
系防腐剤を比較的低温で迅速に分解・無害化することが
できる。
According to the thermal decomposition method of the present invention, dioxins in incinerated ash or fly ash and organochlorine preservatives in humus can be rapidly decomposed and rendered harmless at relatively low temperatures.

【0021】したがって、この方法により、有機塩素系
防腐剤を含んだ廃木材や、ダイオキシンを含んだ焼却灰
もしくは飛灰を無害化することにより、これらを埋立て
処理ないしは再利用することができる。
Therefore, by detoxifying the waste wood containing the organochlorine preservative and the incinerated ash or fly ash containing dioxins by this method, they can be landfilled or reused.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 濱 利雄 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内 (72)発明者 安田 俊彦 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内 (72)発明者 太田 完志 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内 (72)発明者 篠原 力男 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内 (72)発明者 田中 将一 大阪市此花区西九条5丁目3番28号 日立 造船株式会社内 ─────────────────────────────────────────────────── ─── Continuation of front page (72) Inventor Toshio Hama 5-3-8 Nishikujo, Konohana-ku, Osaka City Hitachi Shipbuilding Co., Ltd. (72) Toshihiko Yasuda 5-3-28 Nishikujo, Konohana-ku, Osaka Inside Hitachi Shipbuilding Co., Ltd. (72) Kanshi Ota, 5-3 28 Nishi-Kujo, Konohana-ku, Osaka City Inside Hitachi Shipbuilding Co., Ltd. (72) Rikio Shinohara 5-3 28, West Kujo, Konohana-ku, Osaka Inside Hitachi Shipbuilding Co., Ltd. (72) Inventor Shoichi Tanaka 5-3-2, Nishikujo 5-chome, Konohana-ku, Osaka City Inside Hitachi Shipbuilding Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 有機塩素化合物を含む被処理物に還元性
ガスを流通させながら、有機塩素化合物を熱分解するこ
とを特徴とする有機塩素化合物の熱分解方法。
1. A method for thermally decomposing an organic chlorine compound, which comprises thermally decomposing an organic chlorine compound while circulating a reducing gas through an object to be treated containing the organic chlorine compound.
JP30493991A 1991-11-20 1991-11-20 Thermal decomposition method of organic chlorine compounds Expired - Fee Related JP2787256B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP30493991A JP2787256B2 (en) 1991-11-20 1991-11-20 Thermal decomposition method of organic chlorine compounds

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP30493991A JP2787256B2 (en) 1991-11-20 1991-11-20 Thermal decomposition method of organic chlorine compounds

Publications (2)

Publication Number Publication Date
JPH05137813A true JPH05137813A (en) 1993-06-01
JP2787256B2 JP2787256B2 (en) 1998-08-13

Family

ID=17939139

Family Applications (1)

Application Number Title Priority Date Filing Date
JP30493991A Expired - Fee Related JP2787256B2 (en) 1991-11-20 1991-11-20 Thermal decomposition method of organic chlorine compounds

Country Status (1)

Country Link
JP (1) JP2787256B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1998033607A1 (en) * 1997-01-30 1998-08-06 Kurita Water Industries Ltd. Method of decomposing dioxins

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03295569A (en) * 1989-04-10 1991-12-26 655901 Ontario Inc Method and apparatus for separaiting and treating organic waste

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03295569A (en) * 1989-04-10 1991-12-26 655901 Ontario Inc Method and apparatus for separaiting and treating organic waste

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1998033607A1 (en) * 1997-01-30 1998-08-06 Kurita Water Industries Ltd. Method of decomposing dioxins
US6063979A (en) * 1997-01-30 2000-05-16 Kurita Water Industries Ltd. Method of decomposing dioxins

Also Published As

Publication number Publication date
JP2787256B2 (en) 1998-08-13

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