JP2741293B2 - Thermal decomposition method of organic chlorine compounds - Google Patents
Thermal decomposition method of organic chlorine compoundsInfo
- Publication number
- JP2741293B2 JP2741293B2 JP3304936A JP30493691A JP2741293B2 JP 2741293 B2 JP2741293 B2 JP 2741293B2 JP 3304936 A JP3304936 A JP 3304936A JP 30493691 A JP30493691 A JP 30493691A JP 2741293 B2 JP2741293 B2 JP 2741293B2
- Authority
- JP
- Japan
- Prior art keywords
- organic chlorine
- thermal decomposition
- dioxin
- tcp
- decomposition method
- 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
Links
Description
【0001】[0001]
【産業上の利用分野】この発明は、最近問題となりつつ
あるゴミ焼却炉排出灰中のダイオキシンや、防腐剤とし
て木材中に含まれる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。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for thermally decomposing dioxin in ash discharged from a garbage incinerator and organochlorine compounds such as trichlorophenol contained in wood as a preservative, which have recently become a problem. is there.
【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, there has been no environmental regulation on dioxins, so incinerated ash discharged from refuse incineration plants and fly ash collected by electric dust collectors or bag filters have been landfilled without treatment. Dioxin in the ash could be spilled.
【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, studies have been made on the detoxification of dioxin in ash by thermal decomposition treatment.
In addition to the necessity of a high temperature of 00 ° C. or more, a new problem of volatilization of heavy metals occurs, and a long processing time of 2 hours or more is 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。[0004] Further, with respect to organochlorine-based preservatives such as trichlorophenol which is a precursor of dioxin, waste wood containing the same is simply burned or landfilled. For this reason, there is a possibility that trichlorophenol may flow out of the treated product, and there is a risk that dioxin may be generated from the trichlorophenol that flows out.
【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 has an adverse effect on the human body and the environment, and regulations on the prevention of dioxin generation have been issued. As a result of this regulation, it is no longer possible to landfill waste wood containing dioxin-containing ash or dioxin precursors. Also,
When waste wood is incinerated, dioxin is generated from organochlorine preservatives such as trichlorophenol, so that waste wood cannot be incinerated.
【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 method for thermally decomposing an organic chlorine compound requires long-term high-temperature treatment conditions 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。An object of the present invention is to provide a method capable of rapidly decomposing and detoxifying dioxin in incinerated ash or fly ash and organochlorine-based preservatives in rotten wood at a relatively low temperature in view of the above circumstances. 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有する被処理物中
に尿素を混入し、しかる後に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 an organochlorine compound according to the present invention has been devised to achieve the above-mentioned object, and comprises mixing urea into an object to be treated containing an organochlorine compound. Thereafter, the organic chlorine compound is thermally decomposed.
【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。Representative examples of the organochlorine compounds to be treated by this thermal decomposition method include dioxin contained in ash discharged from a garbage incinerator and trichlorophenol contained in wood as a preservative. Trichlorophenol is a precursor of dioxin as described above.
【0010】有機塩素化合物を含有する被処理物中に尿
素を混入させる方法としては、該被処理物を尿素水溶液
に浸漬する含浸法が好ましい。As a method for mixing urea into the object containing an organic chlorine compound, an impregnation method in which the object is immersed in an aqueous urea solution is preferred.
【0011】被処理物中の尿素の混入量は、好ましくは
約3重量%である。The amount of urea mixed in the material to be treated is preferably about 3% by weight.
【0012】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.
【0013】[0013]
【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 described in order to specifically explain the present invention.
【0014】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 An operation was performed using trichlorophenol, one of the harmful organic chlorine compounds contained in waste wood, in the following manner.
【0015】(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 non-treated substance, and dried to prepare an experimental sample. This sample was subjected to alcohol extraction, 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).
【0016】(ii) 上記試料2.5gを尿素水溶液に浸
漬し、該試料に尿素0.075gを含浸させた。(Ii) 2.5 g of the sample was immersed in an aqueous urea solution, and the sample was impregnated with 0.075 g of urea.
【0017】(iii) ついで、この尿素含浸試料を、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、
窒素ガスを0.25リットル/分の割合で反応管に流し
ながら、300℃で30分間加熱処理を行った。反応管
の出口では、出口ガス中のTCPをアルコールコールド
トラップで捕集した。そして出口ガス中の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、出口ガス中のTCP濃度は0.
004mg/g(珪藻土)であり、処理後試料中のTC
P残存量は0.013mg/g(珪藻土)であった。(Iii) Next, the urea-impregnated sample is filled in a quartz reaction tube installed in a test tube electric furnace,
The heat treatment was performed at 300 ° C. for 30 minutes while flowing nitrogen gas through the reaction tube at a rate of 0.25 liter / min. At the outlet of the reaction tube, TCP in the outlet gas was collected by an alcohol cold trap. When the TCP concentration in the outlet gas and the residual amount of TCP in the processed sample were analyzed by the same method as described above, the TCP concentration in the outlet gas was 0.1.
004 mg / g (diatomaceous earth).
The residual amount of P was 0.013 mg / g (diatomaceous earth).
【0018】したがって、TCP分解率は、[(9.9
−0.004−0.013)/9.9]×100=9
9.83%であった。Therefore, the TCP decomposition rate is [(9.9
−0.004-0.013) /9.9] × 100 = 9
9.83%.
【0019】比較例 実施例の工程(ii)における尿素の含浸処理を省略し、そ
の他の操作を実施例と同様に行った。 Comparative Example The urea impregnation treatment in step (ii) of the example was omitted, and other operations were performed in the same manner as in the example.
【0020】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10.2mg/g(珪藻
土)、処理後試料のTCP残存量は0.014mg/g
(珪藻土)であった。両者のTCP総和が処理前試料の
TCP含有量より大きいが、これは分析誤差によるもの
と考えられ、この処理では、試料中のTCPが出口ガス
中に揮散するのみでTCPの分解は生じていないと判断
された。As a result of the analysis in step (iii), the TCP concentration in the outlet gas of the reaction tube was 10.2 mg / g (diatomaceous earth), and the residual TCP amount of the treated sample was 0.014 mg / g.
(Diatomaceous earth). The sum of the two TCPs is larger than the TCP content of the sample before the treatment, but this is considered to be due to an analysis error. In this treatment, the TCP in the sample is only volatilized in the outlet gas and no TCP decomposition occurs It was determined.
【0021】[0021]
【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-based preservatives in decayed wood can be rapidly decomposed and made harmless at a relatively low temperature.
【0022】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 this method, waste wood containing an organic chlorine-based preservative, incinerated ash or fly ash containing dioxin can be detoxified, and these 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 (56)参考文献 特開 平3−270719(JP,A) ──────────────────────────────────────────────────続 き Continuing on the front page (72) Toshio Hama 5-3-28 Nishikujo, Konohana-ku, Osaka-shi Inside Tachibashi Shipbuilding Co., Ltd. (72) Toshihiko Yasuda 5-28-3, Nishikujo, Konohana-ku, Osaka-shi No. Tachi Shipbuilding Co., Ltd. (72) Inventor Kanji Ota 5-28 Nishikujo 5-chome, Konohana-ku, Osaka-shi Inside Tachibashi Shipbuilding Co., Ltd. (72) Rikio Shinohara 5-3-1 Nishikujo, Konohana-ku, Osaka-shi No. 28 Nippon Shipbuilding Co., Ltd. (72) Inventor Shoichi Tanaka 5-28 Nishikujo, Konohana-ku, Osaka City Nippon Shipbuilding Co., Ltd. (56) References JP-A-3-270719 (JP, A )
Claims (1)
尿素を混入し、しかる後に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 mixing urea into an object to be treated containing an organic chlorine compound and then thermally decomposing the organic chlorine compound.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3304936A JP2741293B2 (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 |
---|---|---|---|
JP3304936A JP2741293B2 (en) | 1991-11-20 | 1991-11-20 | Thermal decomposition method of organic chlorine compounds |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH05138149A JPH05138149A (en) | 1993-06-01 |
JP2741293B2 true JP2741293B2 (en) | 1998-04-15 |
Family
ID=17939101
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP3304936A Expired - Fee Related JP2741293B2 (en) | 1991-11-20 | 1991-11-20 | Thermal decomposition method of organic chlorine compounds |
Country Status (1)
Country | Link |
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JP (1) | JP2741293B2 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6063979A (en) * | 1997-01-30 | 2000-05-16 | Kurita Water Industries Ltd. | Method of decomposing dioxins |
-
1991
- 1991-11-20 JP JP3304936A patent/JP2741293B2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
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JPH05138149A (en) | 1993-06-01 |
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