JPH05269476A - Treatment of water containing volatile organohalogen compound - Google Patents
Treatment of water containing volatile organohalogen compoundInfo
- Publication number
- JPH05269476A JPH05269476A JP9872792A JP9872792A JPH05269476A JP H05269476 A JPH05269476 A JP H05269476A JP 9872792 A JP9872792 A JP 9872792A JP 9872792 A JP9872792 A JP 9872792A JP H05269476 A JPH05269476 A JP H05269476A
- Authority
- JP
- Japan
- Prior art keywords
- metal
- water containing
- organic halogen
- volatile organic
- reducing agent
- 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
Links
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は揮発性有機ハロゲン化合
物含有水の処理方法の改良に関するものである。さらに
詳しくいえば、本発明は、還元剤と触媒とにより用水や
排水中に含まれる揮発性有機ハロゲン化合物を効率よく
還元分解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 an improved method for treating water containing volatile organic halogen compounds. More specifically, the present invention relates to a method for efficiently reducing and decomposing a volatile organic halogen compound contained in water or waste water by using a reducing agent and a catalyst.
【0002】[0002]
【従来の技術】揮発性有機ハロゲン化合物は環境汚染を
もたらすことから、排水などに含まれている該化合物は
除去することが必要であり、これまで揮発性有機ハロゲ
ン化合物を含む用水や排水の処理方法が種々検討されて
きた。この揮発性有機ハロゲン化合物を含む用水や排水
の処理方法としては、例えば(1)曝気処理、(2)吸
着処理、(3)酸化分解処理、(4)生物処理、(5)
熱分解処理などが知られている。しかしながら、これら
の方法はいずれもなんらかの問題を有し、必ずしも満足
しうるものではない。例えば、(1)の方法は地下水や
土壌中に混入される有機ハロゲン化合物を単に大気中に
移行させるだけであり、環境問題の抜本的な解決法には
ならない。(2)の方法は有機ハロゲン化合物をトラッ
プ・回収できる方法であり、前記(1)の方法と組み合
わせて利用されることが多いが、この場合、吸着剤(活
性炭など)の吸着能が湿度の影響を受けて大幅に低下す
るのを免れない。また、吸着処理方法では吸着剤の再生
が必要であり、水蒸気再生などを行う場合には、高濃度
の有機ハロゲン化合物を含む再生排液が排出される。環
境汚染の抜本的な解決を目的とする場合には、前記
(3)〜(5)の分解処理が必要である。このうち、有
機ハロゲン化合物の分解処理方法としては、(3)の酸
化分解法が盛んに検討されており、紫外線、オゾン、過
酸化水素などを利用する方法が数多く報告されている。
また、(4)、(5)の分解処理法も報告されている
が、あまり多くはない。前記酸化分解処理法や熱分解処
理法などにおいては、紫外線やオゾンの発生、あるいは
加熱などに要するエネルギー量が大きく、コスト高にな
るのを免れない上、分解で発生したハロゲンが共存する
有機物と再反応しやすく、新たな有機ハロゲン化合物が
発生する可能性もあるなどの問題を有している。また、
(4)の生物処理方法は投入エネルギーは少ないもの
の、効率よく分解する微生物がまだ見出されておらず、
実用的な方法とはいえない。他方、還元分解法として鉄
粉を利用する方法が報告されているが、十分に満足しう
るものではない。2. Description of the Related Art Since volatile organic halogen compounds cause environmental pollution, it is necessary to remove the compounds contained in wastewater, etc., and until now, it has been necessary to treat water and wastewater containing volatile organic halogen compounds. Various methods have been studied. Examples of treatment methods for water and wastewater containing this volatile organic halogen compound include (1) aeration treatment, (2) adsorption treatment, (3) oxidative decomposition treatment, (4) biological treatment, and (5)
Pyrolysis treatment and the like are known. However, all of these methods have some problems and are not always satisfactory. For example, the method (1) merely transfers organic halogen compounds mixed in groundwater or soil to the atmosphere, and does not become a drastic solution to environmental problems. The method (2) is a method capable of trapping and recovering an organohalogen compound, and is often used in combination with the method (1), but in this case, the adsorption capacity of the adsorbent (activated carbon etc.) It is inevitable that it will be greatly affected by the impact. In addition, the adsorption treatment method requires regeneration of the adsorbent, and in the case of performing steam regeneration or the like, regeneration waste liquid containing a high-concentration organic halogen compound is discharged. For the purpose of radically solving environmental pollution, the decomposition treatments (3) to (5) described above are required. Among them, the oxidative decomposition method (3) has been extensively studied as a decomposition treatment method for organic halogen compounds, and many methods utilizing ultraviolet rays, ozone, hydrogen peroxide and the like have been reported.
In addition, the decomposition treatment methods (4) and (5) have been reported, but not many. In the oxidative decomposition method or the thermal decomposition method, the amount of energy required for the generation of ultraviolet rays or ozone, or the heating is large, and inevitably the cost is high. It has a problem that it easily re-reacts, and a new organic halogen compound may be generated. Also,
Although the biological treatment method of (4) requires a small amount of input energy, a microorganism that decomposes efficiently has not been found yet.
Not a practical method. On the other hand, a method using iron powder as a reductive decomposition method has been reported, but it is not completely satisfactory.
【0003】[0003]
【発明が解決しようとする課題】本発明はこのような従
来の揮発性有機ハロゲン化合物含有水の処理方法が有す
る欠点を克服し、用水や排水中の揮発性有機ハロゲン化
合物を、少ないエネルギー投与で効率よく分解除去し、
かつ新たな有機ハロゲン化合物を再発生することのない
揮発性有機ハロゲン化合物含有水の処理方法を提供する
ことを目的としてなされたものである。DISCLOSURE OF THE INVENTION The present invention overcomes the drawbacks of the conventional treatment method for water containing a volatile organic halogen compound, and reduces the amount of volatile organic halogen compound in water or wastewater with a small amount of energy administration. Efficiently decomposes and removes
In addition, the object of the present invention is to provide a method for treating water containing a volatile organic halogen compound that does not regenerate a new organic halogen compound.
【0004】[0004]
【課題を解決するための手段】本発明者らは前記目的を
達成するために鋭意研究を重ねた結果、金属担持触媒の
存在下に、揮発性有機ハロゲン化合物含有水を還元剤と
接触させることにより、該揮発性有機ハロゲン化合物は
無害な炭化水素とハロゲンイオンとに効率よく分解し、
しかも発生したハロゲンイオンは共存する有機物と再反
応しにくいことを見い出し、この知見に基づいて本発明
を完成するに至った。すなわち、本発明は、金属担持触
媒の存在下、揮発性有機ハロゲン化合物含有水を還元剤
と接触させることを特徴とする揮発性有機ハロゲン化合
物含有水の処理方法を提供するものである。Means for Solving the Problems As a result of intensive studies to achieve the above-mentioned object, the present inventors have found that water containing a volatile organic halogen compound is brought into contact with a reducing agent in the presence of a metal-supported catalyst. The volatile organic halogen compound is efficiently decomposed into harmless hydrocarbons and halogen ions,
Moreover, it was found that the generated halogen ions are difficult to re-react with coexisting organic substances, and the present invention has been completed based on this finding. That is, the present invention provides a method for treating volatile organic halogen compound-containing water, which comprises contacting volatile organic halogen compound-containing water with a reducing agent in the presence of a metal-supported catalyst.
【0005】以下、本発明を詳細に説明する。本発明方
法において用いられる触媒は金属を担体に担持させたも
のであって、該金属としては、例えばパラジウム、白
金、ルテニウム、ロジウム、銅、鉄などが挙げられる
が、これらの中でパラジウム、白金、ルテニウム、ロジ
ウムなどの貴金属が好ましく、特にパラジウムが好適で
ある。このパラジウムとしては金属パラジウム、酸化パ
ラジウム、水酸化パラジウムなどが用いられる。また、
担体としては、例えばアルミナ、チタニア、活性炭、ジ
ルコニア、ゼオライト、ガラス、シリカ、イオン交換樹
脂、プラスチックペレットなどが挙げられるが、これら
の中でアルミナ、ジルコニア及びイオン交換樹脂が好適
である。イオン交換樹脂としてはスチレン−ジビニルベ
ンゼン共重合体を母体にした弱塩基性アニオン交換樹脂
が好ましい。前記金属の担持量は担体に対して通常0.
1〜10重量%程度である。The present invention will be described in detail below. The catalyst used in the method of the present invention is one in which a metal is supported on a carrier, and examples of the metal include palladium, platinum, ruthenium, rhodium, copper, iron and the like. Among these, palladium and platinum , Noble metals such as ruthenium and rhodium are preferable, and palladium is particularly preferable. As the palladium, metallic palladium, palladium oxide, palladium hydroxide or the like is used. Also,
Examples of the carrier include alumina, titania, activated carbon, zirconia, zeolite, glass, silica, ion exchange resins, plastic pellets and the like, among which alumina, zirconia and ion exchange resins are preferable. As the ion exchange resin, a weakly basic anion exchange resin having a styrene-divinylbenzene copolymer as a matrix is preferable. The amount of the metal supported is usually 0.
It is about 1 to 10% by weight.
【0006】金属担持触媒の形状については特に制限は
なく、粉末状、粒状、ペレット状などいずれの形状のも
のも用いることができるが、粒状、ペレット状のものは
カラムなどに充填し、連続的に被処理液を通液するとよ
い。粉末状のものでもカラムに充填して流動床状態で運
転することができる。本発明方法において用いられる還
元剤としては、水素ガスの他、例えばヒドラジン、水素
化ナトリウムなど前記触媒と接触して水素を発生するも
のが用いられる。The shape of the metal-supported catalyst is not particularly limited, and any shape such as powder, granules and pellets can be used. Granules or pellets are packed in a column or the like and continuously packed. It is advisable to pass the liquid to be treated. Even the powder form can be packed in a column and operated in a fluidized bed state. As the reducing agent used in the method of the present invention, in addition to hydrogen gas, for example, hydrazine, sodium hydride or the like that generates hydrogen by contacting with the catalyst is used.
【0007】また、本発明方法が適用できる揮発性有機
ハロゲン化合物は通常沸点が150℃以下、好ましくは
80℃以下の揮発性のものであって、このようなものと
しては、例えばトリクロロエタン、テトラクロロエチレ
ン、トランス−1,2−ジクロロエチレン、シス−1,2
−ジクロロエチレン、四塩化炭素、クロロエタン、メチ
レンクロリド、クロロホルム、塩化ビニル、1,1,1−
トリクロロエチレン、1,1−ジクロロエタン、1,2−
ジクロロエタン、1,2−ジクロロプロパン、ジクロロ
ブロモエチレン、1,1,1−トリクロロエタン、ブロモ
ジクロロメタン、クロロジブロモメタン、ブロモホルム
などが挙げられる。本発明方法においては、揮発性有機
ハロゲン化合物を金属担持触媒と還元剤とを用いて還元
分解するが、1例として揮発性有機ハロゲン化合物がト
リクロロエチレンの場合には、次に示す反応式に従って
分解が起こるものと考えられる。Further, the volatile organic halogen compound to which the method of the present invention can be applied is usually a volatile compound having a boiling point of 150 ° C. or lower, preferably 80 ° C. or lower. Trans-1,2-dichloroethylene, cis-1,2
-Dichloroethylene, carbon tetrachloride, chloroethane, methylene chloride, chloroform, vinyl chloride, 1,1,1-
Trichloroethylene, 1,1-dichloroethane, 1,2-
Dichloroethane, 1,2-dichloropropane, dichlorobromoethylene, 1,1,1-trichloroethane, bromodichloromethane, chlorodibromomethane, bromoform and the like can be mentioned. In the method of the present invention, a volatile organic halogen compound is reductively decomposed using a metal-supported catalyst and a reducing agent. As an example, when the volatile organic halogen compound is trichlorethylene, decomposition is carried out according to the following reaction formula. It is supposed to happen.
【0008】2CHCl=CCl2+3H2→2CH2=
CH2+6Cl- すなわち、トリクロロエチレンは脱塩素化されて、エチ
レンと塩素イオンが生成する。この塩素イオンはHCl
の形であるので、安定であって、再汚染源となることは
ない。なお、エチレンの他にメタンやエタンの生成も認
められる。本発明方法においては、還元剤の添加量は通
常10〜1,000mg/リットルの範囲で選ばれる。本
発明方法における揮発性有機ハロゲン化合物含有水の処
理方式としては、金属担持触媒をカラムに充填し、これ
に被処理水と還元剤とを通液する連続方式、あるいはバ
ッチ方式のいずれも用いることができるが、前者の連続
方式が好ましい。この連続方式の場合は被処理水の流速
はSVで1〜100hr-1程度が好ましい。2CHCl = CCl 2 + 3H 2 → 2CH 2 =
CH 2 + 6Cl −, that is, trichlorethylene is dechlorinated to produce ethylene and chloride ions. This chlorine ion is HCl
It is stable and does not become a source of recontamination. In addition to ethylene, the production of methane and ethane is also recognized. In the method of the present invention, the addition amount of the reducing agent is usually selected in the range of 10 to 1,000 mg / liter. As the method for treating the volatile organic halogen compound-containing water in the method of the present invention, either a continuous method in which a metal-supported catalyst is packed in a column, and water to be treated and a reducing agent are passed through, or a batch method is used. However, the former continuous method is preferable. In the case of this continuous system, the flow velocity of the water to be treated is preferably about 1 to 100 hr −1 in SV.
【0009】[0009]
【実施例】次に実施例により本発明をさらに詳細に説明
するが、本発明はこれらの例によってなんら限定される
ものではない。The present invention will be described in more detail by way of examples, which should not be construed as limiting the invention thereto.
【0010】実施例1 内容積22ミリリットルのバイヤルビンに約300ppb
のトリクロロエチレン溶液10ミリリットルを採取し、
これに各種金属を0.5重量%担持した触媒(担体はア
ルミナ)0.5gとヒドラジン3.2mgを添加し、25℃
でよく撹拌した。一定時間毎に上部ヘッドスペースの一
部を採取し、ガスクロ分析した。比較のためにヒドラジ
ンを添加しない場合のデーターも求めた。その結果を第
1表に示す。Example 1 Approximately 300 ppb in a vial bottle having an internal volume of 22 ml
10 ml of trichlorethylene solution of
To this was added 0.5 g of a catalyst carrying 0.5% by weight of various metals (support is alumina) and 3.2 mg of hydrazine, and the mixture was added at 25 ° C.
Well stirred. A part of the upper headspace was sampled at regular intervals and analyzed by gas chromatography. For comparison, data without addition of hydrazine were also obtained. The results are shown in Table 1.
【0011】[0011]
【表1】 [Table 1]
【0012】実施例2 実施例1において、約200ppbのトリクロロエチレン
水溶液を用いたこと、金属としてパラジウムを用いたこ
と及び担体として各種のものを用いたことを除いては実
施例1と同様の方法でトリクロロエチレンの分解を試み
た。結果を第2表に示す。Example 2 In the same manner as in Example 1, except that an aqueous solution of about 200 ppb trichloroethylene was used, palladium was used as a metal, and various carriers were used. An attempt was made to decompose trichlorethylene. The results are shown in Table 2.
【0013】[0013]
【表2】 [Table 2]
【0014】実施例3 図1に示す装置を用いて通水実験を行った。内径15mm
のカラム1に、アルミナにパラジウム0.5重量%を担
持した触媒16.2gを触媒層2の長さが100mmにな
るように充填したのち、これに原水貯槽3からポンプ4
により約300ppbのトリクロロエチレン溶液をSV約
10hr-1で通水した。一方、ヒドラジン水溶液貯槽5
からポンプ6によりヒドラジン水溶液を被処理水中の濃
度が250ppmとなるように導入した。処理水を採取
し、ヘッドスペースをガスクロ分析した。なお、処理温
度は25℃である。結果を第3表に示す。Example 3 A water flow experiment was conducted using the apparatus shown in FIG. Inner diameter 15mm
The column 1 was packed with 16.2 g of a catalyst supporting 0.5% by weight of palladium on alumina so that the length of the catalyst layer 2 would be 100 mm, and then the raw water storage tank 3 and the pump 4
The trichloroethylene solution of about 300 ppb was passed by the SV at about 10 hr −1 . On the other hand, hydrazine aqueous solution storage tank 5
A pump 6 was used to introduce an aqueous hydrazine solution so that the concentration in the water to be treated was 250 ppm. The treated water was collected and the head space was analyzed by gas chromatography. The processing temperature is 25 ° C. The results are shown in Table 3.
【0015】[0015]
【表3】 [Table 3]
【0016】実施例4 実施例3において、トリクロロエチレンにかえて各種の
揮発性有機ハロゲン化物を用いたこと及び添加量以外は
実施例3と同様の方法で処理した。結果を第4表に示
す。Example 4 The same procedure as in Example 3 was carried out except that various volatile organic halides were used instead of trichlorethylene and the addition amount was changed. The results are shown in Table 4.
【0017】[0017]
【表4】 [Table 4]
【0018】[0018]
【発明の効果】本発明によると、金属担持触媒の存在下
に、揮発性有機ハロゲン化合物含有水を還元剤と接触さ
せることにより、該揮発性有機ハロゲン化合物を無害な
炭化水素とハロゲンイオンとに効率よく分解することが
でき、また、発生したハロゲンイオンは共存する有機物
と反応しにくいので、再汚染源となることがない。According to the present invention, water containing a volatile organic halogen compound is brought into contact with a reducing agent in the presence of a metal-supported catalyst to convert the volatile organic halogen compound into harmless hydrocarbons and halogen ions. It can be decomposed efficiently, and the generated halogen ions do not easily react with the coexisting organic matter, so that it does not become a recontamination source.
【図1】図1は実施例3において用いた装置の概略図で
ある。FIG. 1 is a schematic diagram of an apparatus used in Example 3.
1 カラム 2 触媒層 3 原水貯槽 4 ポンプ 5 ヒドラジン水溶液貯槽 6 ポンプ 1 column 2 catalyst layer 3 raw water storage tank 4 pump 5 hydrazine aqueous solution storage tank 6 pump
Claims (1)
ン化合物含有水を還元剤と接触させることを特徴とする
揮発性有機ハロゲン化合物含有水の処理方法。1. A method for treating volatile organic halogen compound-containing water, which comprises contacting volatile organic halogen compound-containing water with a reducing agent in the presence of a metal-supported catalyst.
Priority Applications (10)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9872792A JPH05269476A (en) | 1992-03-25 | 1992-03-25 | Treatment of water containing volatile organohalogen compound |
AU35247/93A AU664242B2 (en) | 1992-03-25 | 1993-03-16 | A method of treatment of a fluid containing volatile organic halogenated compounds |
DE69328732T DE69328732T2 (en) | 1992-03-25 | 1993-03-16 | Process for the decomposition of organic halogenated volatile compounds in water |
CA002091740A CA2091740A1 (en) | 1992-03-25 | 1993-03-16 | A method of treatment of a fluid containing volatile organic halogenated compounds |
EP93104226A EP0563669B1 (en) | 1992-03-25 | 1993-03-16 | A method of treatment of a fluid containing volatile organic halogenated compounds |
DE69323226T DE69323226T2 (en) | 1992-03-25 | 1993-03-16 | Process for the treatment of a liquid containing volatile halogenated organic compounds |
EP96109638A EP0745561B1 (en) | 1992-03-25 | 1993-03-16 | Method of decomposing volatile organic halogenated compounds in water |
US08/032,573 US5490941A (en) | 1992-03-25 | 1993-03-17 | Method of treatment of a fluid containing volatile organic halogenated compounds |
US08/450,573 US5531901A (en) | 1992-03-25 | 1995-05-25 | Method of treatment of a fluid containing volatile organic halogenated compounds |
AU42292/96A AU688184B2 (en) | 1992-03-25 | 1996-02-02 | A method of treatment of a fluid containing volatile organic halogenated compounds |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9872792A JPH05269476A (en) | 1992-03-25 | 1992-03-25 | Treatment of water containing volatile organohalogen compound |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH05269476A true JPH05269476A (en) | 1993-10-19 |
Family
ID=14227562
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP9872792A Pending JPH05269476A (en) | 1992-03-25 | 1992-03-25 | Treatment of water containing volatile organohalogen compound |
Country Status (1)
Country | Link |
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JP (1) | JPH05269476A (en) |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH07308682A (en) * | 1994-05-16 | 1995-11-28 | Agency Of Ind Science & Technol | Method for reduction and removal of dissolved organic halide in contaminated water |
US5858267A (en) * | 1996-10-11 | 1999-01-12 | Nec Corporation | Method for treating chlorinated organic compound |
KR100343752B1 (en) * | 2000-04-12 | 2002-07-25 | 한국에너지기술연구원 | High active composite catalyst for simultaneous oxidation of halogenated volatile organic compounds(HVOCs) and volatile organic compounds(VOCs), and prepararation method of it, and controlling method of its reaction |
DE10130108A1 (en) * | 2001-06-21 | 2003-02-27 | Birgit Kraft | Purifying water contaminated with halogenated organic compounds comprises catalytically dehalogenating the contaminants in solvent |
JP2004525053A (en) * | 2000-12-21 | 2004-08-19 | ロディア・シミ | Hydrogen generation system and hydrodehalogenation method |
JP2010099625A (en) * | 2008-10-27 | 2010-05-06 | Mitsui Eng & Shipbuild Co Ltd | Microreactor for reducing and detoxifying hardly decomposable organic compound |
KR100975634B1 (en) * | 2007-12-17 | 2010-08-17 | 한국화학연구원 | Palladium-doped styrene-based anion-exchange resin and Preparation method thereof and process for removing dissolved oxygen using them |
JP2011088038A (en) * | 2009-10-20 | 2011-05-06 | Tokyo Electric Power Co Inc:The | Catalyst to be used for treating halogenated organic compound |
-
1992
- 1992-03-25 JP JP9872792A patent/JPH05269476A/en active Pending
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH07308682A (en) * | 1994-05-16 | 1995-11-28 | Agency Of Ind Science & Technol | Method for reduction and removal of dissolved organic halide in contaminated water |
US5858267A (en) * | 1996-10-11 | 1999-01-12 | Nec Corporation | Method for treating chlorinated organic compound |
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