JP2000334062A - Microwave-solvothermal treatment of harmful organic compound - Google Patents
Microwave-solvothermal treatment of harmful organic compoundInfo
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- JP2000334062A JP2000334062A JP11149341A JP14934199A JP2000334062A JP 2000334062 A JP2000334062 A JP 2000334062A JP 11149341 A JP11149341 A JP 11149341A JP 14934199 A JP14934199 A JP 14934199A JP 2000334062 A JP2000334062 A JP 2000334062A
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- microwave
- harmful organic
- continuously
- continuous
- compounds
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- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
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- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、有機ハロゲン化合
物および多環芳香族などの有害有機化合物をマイクロ波
照射加熱を行い、沸点以上の温度・圧力下、すなわちソ
ルボサーマル条件下で連続的に高速分解・無害化する方
法に関するものである。BACKGROUND OF THE INVENTION The present invention relates to a method of heating a harmful organic compound such as an organic halogen compound and a polycyclic aromatic compound by microwave irradiation and continuously heating the harmful organic compound at a temperature and pressure higher than the boiling point, that is, under solvothermal conditions. It relates to a method of decomposing and rendering harmless.
【0002】[0002]
【従来の技術】有機ハロゲン化合物などの有害物質は毒
性が強いだけでなく、極少量でも生殖などに大きく影響
する内分泌ホルモン撹乱物質(環境ホルモン)として処
理技術の開発が急がれており、地球規模での汚染が大き
な社会問題となっている。2. Description of the Related Art Hazardous substances such as organic halogen compounds are not only highly toxic, but even in very small amounts, endocrine disruptors (environmental hormones), which greatly affect reproduction, are being developed as processing technologies. Pollution on a large scale has become a major social problem.
【0003】最近、湿式分解法による有機ハロゲン化合
物の分解、特に、超臨界水分解法が注目され、盛んに研
究されている。これらの方法では、温度が400〜50
0℃、圧力100〜300気圧の高温高圧の条件で処理
するものである。山崎らはPCBやTCEなどの有機塩
素化合物を200から350℃、100気圧程度の低温
・低圧の条件で水熱分解している〔N.Yamasaki et al.
Env. Sci. Tech., 14(5),550(1990)〕。亜臨界・超臨界
水は腐食性が大きく、かつ、有機ハロゲン化合物では腐
食性のガスが発生し、耐圧、耐熱、耐食性の良い反応装
置が必要である。また、脱塩素剤としてアルカリが用い
られるが、超臨界水中は共溶媒性となり、イオン性の物
質の溶解度が小さくなり、塩化ナトリウムなどの塩類が
析出するため、塩析対策が必要である。[0003] Recently, the decomposition of organic halogen compounds by the wet decomposition method, particularly the supercritical water decomposition method, has attracted attention and has been actively studied. In these methods, the temperature is between 400 and 50
The treatment is performed under the conditions of high temperature and high pressure of 0 ° C. and pressure of 100 to 300 atm. Yamazaki et al. Hydrothermally decompose organochlorine compounds such as PCB and TCE under low-temperature and low-pressure conditions of about 200 to 350 ° C. and about 100 atm [N. Yamasaki et al.
Env. Sci. Tech., 14 (5), 550 (1990)]. Subcritical and supercritical water are highly corrosive, and corrosive gases are generated from organic halogen compounds, and a reactor with good pressure resistance, heat resistance and corrosion resistance is required. In addition, although alkali is used as a dechlorinating agent, it becomes co-solvent in supercritical water, the solubility of ionic substances decreases, and salts such as sodium chloride are precipitated.
【0004】炭化ケイ素などの触媒を充填した反応管を
マイクロ波照射して所定温度に加熱し、有機塩素化合物
などを連続的に注入することにより、有機塩素化合物が
効率よく分解されることが知られている。例えば、特開
平8−99018、US DOE Report LA-UR-90-3159、LA-
12121-MSにおいて、炭化ケイ素をマイクロ波加熱で60
0℃程度に加熱し、有機ハロゲン化合物などを注入する
ことにより、迅速に塩化水素と二酸化炭素まで分解され
ることが認められている。この方法は有害有機物の処理
などの高濃度分解処理に適しているが、水を多量に含む
水溶液系には多量のエネルギーを要し適さない。また、
活性炭および銅やクロムを担持した活性炭層に有害有機
物質を吸着させた後、マイクロ波を照射して400℃程
度に加熱して分解する方法(US DOE Report DOE-HWP-2
8、AD Report AD-A-253631)等が報告されている。水蒸
気などに気体中の有害物質を吸着させてから、マイクロ
波照射して分解する方法であり、連続分解および水溶液
中の有害物質の分解には適していない。[0004] It is known that by irradiating a reaction tube filled with a catalyst such as silicon carbide or the like with microwaves to a predetermined temperature and continuously injecting an organic chlorine compound or the like, the organic chlorine compound is efficiently decomposed. Have been. For example, JP-A-8-99018, US DOE Report LA-UR-90-3159, LA-
In 12121-MS, silicon carbide was heated by microwave
It has been recognized that by heating to about 0 ° C. and injecting an organic halogen compound or the like, hydrogen chloride and carbon dioxide are rapidly decomposed. This method is suitable for high-concentration decomposition treatment such as treatment of harmful organic substances, but is not suitable for an aqueous system containing a large amount of water because a large amount of energy is required. Also,
A method in which harmful organic substances are adsorbed on activated carbon and activated carbon layers supporting copper and chromium, and then microwaved to decompose by heating to about 400 ° C (US DOE Report DOE-HWP-2
8, AD Report AD-A-253631) has been reported. It is a method of adsorbing harmful substances in a gas to water vapor and then decomposing it by microwave irradiation, and is not suitable for continuous decomposition and decomposition of harmful substances in an aqueous solution.
【0005】[0005]
【発明が解決しようとする課題】本発明においては、よ
り穏和な条件、すなわち、低温低圧、省エネルギー型
で、連続的、かつ、安全性の高いクローズドシステムの
開発を目指すものである。さらに、高濃度溶液中の有害
有機ハロゲン化合物の分解から希薄な水溶液中の有機ハ
ロゲン化合物並びに油など有機溶媒中の有機ハロゲン化
合物を効率よく、分解・無害化する方法を提供しようと
するものである。SUMMARY OF THE INVENTION The object of the present invention is to develop a closed system which is milder, that is, a low-temperature, low-pressure, energy-saving, continuous and highly safe system. It is another object of the present invention to provide a method for efficiently decomposing and detoxifying an organic halogen compound in an organic solvent such as an oil from a decomposition of a harmful organic halogen compound in a high-concentration solution. .
【0006】[0006]
【課題を解決するための手段】有機ハロゲン化合物とア
ルカリ水溶液を混合し、マイクロ波を照射して沸点以上
の温度(180℃以下)、10気圧以下の圧力下で処理
すると、有機ハロゲン化合物が分解され、生成する塩化
水素はアルカリにより捕捉され、無害化されることを見
いだした。しかし、回分法の場合、気相と液相が存在す
ると加熱により、溶液が沸騰し、気相部分に有害ハロゲ
ン化合物が蒸発するため、100%処理することが困難
であった。Means for Solving the Problems When an organic halogen compound and an aqueous alkali solution are mixed, and the mixture is irradiated with microwaves and treated at a temperature higher than the boiling point (180 ° C. or lower) and a pressure lower than 10 atm, the organic halogen compound is decomposed. It was found that the generated hydrogen chloride was trapped by the alkali and rendered harmless. However, in the case of the batch method, when a gas phase and a liquid phase are present, the solution is boiled by heating, and a harmful halogen compound evaporates in the gas phase, so that it is difficult to perform 100% treatment.
【0007】このような状況で鋭意研究した結果、有機
ハロゲン化合物あるいは有機ハロゲン化合物を含む溶液
とアルカリ水溶液を混合して連続的に反応部に送液す
る。マイクロ波を連続的に出力を調製しながら照射する
ことにより、沸騰させないで加熱加圧するソルボサーマ
ル条件で連続処理し、室温まで冷却することにより、有
害な気体を発生することなく、100%分解・無害化で
きることを見いだした。本発明は、有害有機化合物およ
びそれらを含む溶液をアルカリ水溶液と混合し、反応装
置へ連続的に注入し、マイクロ波を照射して沸点以上の
温度に加熱・加圧する条件で連続的に分解・無害化する
ことを特徴とする有害有機化合物のマイクロ波−ソルボ
サーマル連続処理法を要旨としている。As a result of intensive research in such a situation, an organic halogen compound or a solution containing an organic halogen compound and an alkaline aqueous solution are mixed and continuously fed to a reaction section. By irradiating the microwave while continuously adjusting the output, it is continuously processed under the solvothermal condition of heating and pressurizing without boiling, and is cooled to room temperature. We found that it could be made harmless. In the present invention, a harmful organic compound and a solution containing the same are mixed with an aqueous alkali solution, continuously injected into a reaction apparatus, and continuously decomposed and irradiated under a condition of heating and pressurizing to a temperature equal to or higher than a boiling point by irradiating a microwave. The subject matter is a microwave-solvothermal continuous treatment method for harmful organic compounds, which is characterized by detoxification.
【0008】さらに、反応部に酸化チタンなどの触媒を
用いることにより、より低温低圧の条件で効率よく処理
されることを見いだした。触媒としては酸化チタンの
他、酸化鉄、酸化銅、アルミナ、酸化マンガンなどの酸
化物およびそれらの複合酸化物、さらには活性炭や粘土
鉱物などの多孔質体に酸化物を担持した複合材料などが
用いられる。触媒としてはこれらに規定されるものでな
く、マイクロ波吸収性を有するものが効果的である。す
なわち本発明は、有害有機化合物およびそれらを含む溶
液をアルカリ水溶液と混合し、反応装置の反応部にマイ
クロ波吸収性および反応分解性の触媒、より具体的には
金属酸化物あるいはそれらの複合酸化物、または多孔性
物質等の表面に当該酸化物をコーティングした複合材料
等の触媒を装填した当該反応装置へ連続的に注入し、マ
イクロ波を照射して沸点以上の温度に加熱・加圧する条
件で連続的に分解・無害化することを特徴とする有害有
機化合物のマイクロ波−ソルボサーマル連続処理法を要
旨としている。Further, it has been found that by using a catalyst such as titanium oxide in the reaction section, the treatment can be carried out efficiently at lower temperature and pressure. As the catalyst, in addition to titanium oxide, oxides such as iron oxide, copper oxide, alumina, and manganese oxide and their composite oxides, and composite materials in which the oxide is supported on a porous material such as activated carbon and clay minerals are also used. Used. The catalyst is not limited to these, but a catalyst having microwave absorption is effective. That is, the present invention provides a method of mixing a harmful organic compound and a solution containing the same with an aqueous alkali solution, and adding a microwave-absorbing and reactive-decomposing catalyst, more specifically, a metal oxide or a composite oxide thereof, to a reaction section of a reactor. Conditions for continuously injecting into a reactor equipped with a catalyst such as a composite material in which the surface of a substance or a porous substance is coated with the oxide, and heating and pressurizing to a temperature above the boiling point by microwave irradiation The present invention is directed to a continuous microwave-solvothermal treatment method for harmful organic compounds, which is continuously decomposed and made harmless.
【0009】マイクロ波照射法として連続照射下に出力
調整を行って温度制御する方法およびパルス照射しなが
ら出力調整して温度コントロールする方法がある。連続
照射法で効果的に有機塩素化合物の無害化ができるが、
パルス照射の方がより効果的で、効率よく分解できるこ
とを見いだした。すなわち本発明は、有害有機化合物お
よびそれらを含む溶液をアルカリ水溶液と混合し、反応
装置の反応部にマイクロ波吸収性および反応分解性の触
媒、より具体的には金属酸化物あるいはそれらの複合酸
化物、または多孔性物質等の表面に当該酸化物をコーテ
ィングした複合材料等の触媒を装填した当該反応装置へ
連続的に注入し、マイクロ波を連続あるいはパルス照射
して沸点以上の温度に加熱・加圧する条件で連続的に分
解・無害化することを特徴とする有害有機化合物のマイ
クロ波−ソルボサーマル連続処理法を要旨としている。As the microwave irradiation method, there are a method of controlling the temperature by adjusting the output under continuous irradiation and a method of controlling the temperature by adjusting the output while performing pulse irradiation. The continuous irradiation method can effectively detoxify organic chlorine compounds,
We found that pulsed irradiation was more effective and could be decomposed more efficiently. That is, the present invention provides a method of mixing a harmful organic compound and a solution containing the same with an aqueous alkali solution, and adding a microwave-absorbing and reactive-decomposing catalyst, more specifically, a metal oxide or a composite oxide thereof, to a reaction section of a reactor. To the reactor, which is loaded with a catalyst, such as a composite material or the like, on which the oxide is coated on the surface of a substance or a porous substance, and continuously or pulsedly irradiates microwaves to heat to a temperature above the boiling point. The gist of the present invention is a microwave-solvothermal continuous treatment method for harmful organic compounds, which is continuously decomposed and made harmless under pressure.
【0010】以上のとおり、本発明は、有機ハロゲン化
合物等有害有機化合物を加圧条件下でマイクロ波照射し
て分解し、無害化する技術を提供するものである。As described above, the present invention provides a technique for decomposing harmful organic compounds such as organic halogen compounds by irradiating them with microwaves under pressurized conditions to render them harmless.
【0011】[0011]
【発明の実施の形態】有害有機化合物の代表例としては
ジクロルメタン、クロロホルム、四塩化炭素、トリクロ
ルエタンなどのパラフィン系およびクロルベンゼン、ジ
クロルベンゼンやPCB、ダイオキシン等の芳香族系な
どの有機塩素化合物および有機臭素化合物や有機フッ素
化合物などの有機ハロゲン化合物のマイクロ波−ソルボ
サーマル分解による無害化処理があげられるが、それに
限定されるものではなく、多環芳香族などの有害有機化
合物の分解・無害化にも適用が可能である。DESCRIPTION OF THE PREFERRED EMBODIMENTS Representative examples of harmful organic compounds include organic chlorine compounds such as paraffinic compounds such as dichloromethane, chloroform, carbon tetrachloride and trichloroethane, and aromatic compounds such as chlorobenzene, dichlorobenzene, PCB and dioxin. And microwave solvothermal decomposition of organic halogen compounds such as organic bromine compounds and organic fluorine compounds, but not limited thereto, and decomposition and harmlessness of harmful organic compounds such as polycyclic aromatic compounds. It can also be applied to conversion.
【0012】有機ハロゲン化合物などの有害有機化合物
の廃棄物、有害有機化合物の含まれる廃水・廃油のみな
らず、焼却炉飛灰などの無害化に適用するものである。
有機ハロゲン化合物等の有害有機化合物を含む廃液とア
ルカリ水溶液を混合したもの、あるいは両溶液を反応部
に連続的に送液し、沸騰させない加圧条件下(温度:1
20〜180℃、圧力:数気圧〜10気圧、滞留時間:
数分〜数十分)でマイクロ波照射処理を行うものであ
る。マイクロ波照射は連続照射でも効果的であるが、パ
ルス照射がより効果的である。The present invention is applied not only to waste of harmful organic compounds such as organic halogen compounds, wastewater and waste oil containing harmful organic compounds, but also to detoxification of fly ash and the like in incinerators.
A mixture of a waste liquid containing a harmful organic compound such as an organic halogen compound and an alkaline aqueous solution, or both solutions are continuously fed to the reaction section under a pressure of not boiling (temperature: 1).
20 to 180 ° C, pressure: several to 10 atm, residence time:
(Several minutes to several tens of minutes). Microwave irradiation is effective with continuous irradiation, but pulse irradiation is more effective.
【0013】有機ハロゲン化合物の濃厚廃液とアルカリ
水溶液を連続的に混合しながら反応部に送液し、マイク
ロ波照射して分解・無害化する。有害有機化合物を含む
廃油処理の場合、炭酸ナトリウムなどの粉末状アルカリ
を混合してマイクロ波反応装置に送液し処理する。The concentrated waste liquid of the organic halogen compound and the alkaline aqueous solution are continuously mixed and sent to the reaction section, and are decomposed and made harmless by microwave irradiation. In the case of waste oil treatment containing harmful organic compounds, a powdered alkali such as sodium carbonate is mixed and sent to a microwave reactor for treatment.
【0014】有機塩素化合物はアルカリ水溶液中でマイ
クロ波加熱により分解され、無害化するが、濃厚廃液の
場合、排水基準以下にするためには滞留時間を長くする
必要がある。酸化チタンなどの触媒を添加することによ
り、短時間に効率よく分解・無害化される。触媒の添加
方法として粉末状のものを溶液中に懸濁させて送液処理
した後、沈殿分離する方法、粒状、繊維状、ハニカム状
の充填した反応管をマイクロ波照射装置内に設置し、反
応溶液を送給して処理するものである。The organic chlorine compound is decomposed and detoxified by microwave heating in an aqueous alkali solution, but in the case of a concentrated waste liquid, the residence time must be lengthened in order to reduce the wastewater to below the standard. By adding a catalyst such as titanium oxide, it can be efficiently decomposed and made harmless in a short time. As a method for adding a catalyst, a powdery material is suspended in a solution and subjected to a liquid sending process, and then a method of separating and separating, a granular, fibrous, and a honeycomb-shaped filled reaction tube are installed in a microwave irradiation device, The reaction solution is fed for processing.
【0015】[0015]
【実施例】次に本発明を実施例に基づいて説明するが、
本発明は当該実施例によって何ら限定されるものでな
い。Next, the present invention will be described based on examples.
The present invention is not limited by the embodiments.
【0016】実施例1 試作したマイクロ波−ソルボサーマル連続反応装置はマ
イクロ波出力1.5kWのオーブン型の装置である。反
応部は耐圧ガラス製の蛇管(耐圧:10気圧)でオーブ
ンの上部にガラス製蛇管冷却器を付け、その先にフラク
ションコレクターを取り付けて流出液を分取した。反応
部の容積は100ml、送水管、反応部、冷却部を含め
た系全体の容積は400mlである。マイクロ波の最大
出力は1.5kWで、連続照射の他パルス照射が可能で
あり、パルス間隔は自由に設定できる。この反応装置に
1N水酸化ナトリウム水溶液にジクロルメタンを溶解
し、100ppmの試料溶液を調整したものを反応部に所
定速度で試料溶液を連続的に送水し、マイクロ波出力5
0%、温度180℃、圧力10気圧の条件で流速を変え
てマイクロ波処理した。流速は20ml/minおよび5ml/m
inで、それぞれの反応部の滞留時間は5分および20分
である。得られた結果を図1に示す。装置容積分(40
0ml)が流出した時の流出液中の濃度は滞留時間5分で
は、2ppm、滞留時間5分の場合は0.2ppm以下とな
り、分解率は98%、99.8%以上に達した。従来の
水熱分解法(250℃)に比べ、低い反応温度で分解で
きることが分かった。EXAMPLE 1 The microwave-solvothermal continuous reactor produced as a trial is an oven type device having a microwave output of 1.5 kW. The reaction part was a pressure-resistant glass tube (pressure-resistant: 10 atm), and a glass tube-cooler was attached to the upper part of the oven, and a fraction collector was attached to the top of the cooler to separate the effluent. The volume of the reaction section is 100 ml, and the volume of the entire system including the water pipe, the reaction section, and the cooling section is 400 ml. The maximum output of the microwave is 1.5 kW, pulse irradiation can be performed in addition to continuous irradiation, and the pulse interval can be set freely. Dichloromethane was dissolved in a 1N aqueous sodium hydroxide solution in this reactor, and a 100 ppm sample solution was prepared.
Microwave treatment was performed under the conditions of 0%, a temperature of 180 ° C., and a pressure of 10 atm while changing the flow rate. Flow rates are 20ml / min and 5ml / m
In, the residence time in each reaction zone is 5 minutes and 20 minutes. The results obtained are shown in FIG. Equipment volume (40
(0 ml) flowed out, the concentration in the effluent was 2 ppm for a residence time of 5 minutes, and 0.2 ppm or less for a residence time of 5 minutes, and the decomposition rates reached 98% and 99.8% or more. It was found that the decomposition can be performed at a lower reaction temperature than the conventional hydrothermal decomposition method (250 ° C.).
【0017】比較例1 回分式反応容器にジクロルメタン試料溶液(100pp
m)100mlを充填し、反応温度150℃、4気圧お
よび180℃、10気圧の条件で所定時間マイクロ波照
射処理を行った。反応終了後、反応溶液中の残存濃度を
GC-MSで分析した。その結果、表1および図2に示すよ
うに、連続法では反応温度150℃、滞留時間20分で
残存濃度が排水基準の0.2ppm以下になり、分解率は
99.8%であったが、回分式では150℃では分解率
が75%であり、180℃においても20分で残存濃度
10ppmであり、分解率は90%にとどまった。Comparative Example 1 A sample solution of dichloromethane (100 pp) was placed in a batch reaction vessel.
m) 100 ml was filled, and a microwave irradiation treatment was performed at a reaction temperature of 150 ° C., 4 atm, 180 ° C., and 10 atm for a predetermined time. After the reaction is completed, the residual concentration in the reaction solution is
It was analyzed by GC-MS. As a result, as shown in Table 1 and FIG. 2, in the continuous method, when the reaction temperature was 150 ° C. and the residence time was 20 minutes, the residual concentration was 0.2 ppm or less of the wastewater standard, and the decomposition rate was 99.8%. In the batch method, the decomposition rate was 75% at 150 ° C, and even at 180 ° C, the residual concentration was 10 ppm in 20 minutes, and the decomposition rate was only 90%.
【0018】[0018]
【表1】 ──────────────────────────────────── 回分式(5分) 回分式(20分) 連続式(20 分) ──────────────────────────────────── 反応温度(150℃)分解率 61 75 99.8 反応温度(180℃)分解率 80 90 99.8 ────────────────────────────────────[Table 1] ──────────────────────────────────── Batch type (5 minutes) Batch type (20 minutes) Min) Continuous (20 min) ──────────────────────────────────── Reaction temperature (150 ℃) Decomposition rate 61 75 99.8 Reaction temperature (180 ° C) Decomposition rate 80 90 99.8 ────────────────────────────── ──────
【0019】実施例2 ジクロルメタンのマイクロ波−ソルボサーマル連続分解
における反応温度および滞留時間の影響を調べた。ジク
ロルメタン試料水溶液を連続的にマイクロ波照射装置の
反応部に送液した。ジクロルメタン濃度:100ppm、
1000ppm、水酸化ナトリウム濃度:0.5、1N、
反応温度120、150、170℃、滞留時間10、2
0、30分の条件で実験した。本実験では反応中沸騰さ
せないために、若干加圧条件で処理した。流出量が送液
部、反応部、冷却部の容積の1.5倍程度になったとき
の濃度を測定し、分解率を求めた結果を表2および表3
に示す。反応温度120℃においてもジクロルメタンは
滞留時間20分で93%以上分解した。本実験のアルカ
リの濃度が0.5Nから1N、滞留時間20分から30
分では分解率に大差なく、安定的な運転条件ではほぼ1
00%分解できた。試料濃度100ppm、1000ppmで
も分解率ではほぼ等しかった。Example 2 The effects of reaction temperature and residence time on the microwave-solvothermal continuous decomposition of dichloromethane were investigated. The aqueous solution of dichloromethane sample was continuously sent to the reaction section of the microwave irradiation device. Dichloromethane concentration: 100 ppm,
1000 ppm, sodium hydroxide concentration: 0.5, 1N,
Reaction temperature 120, 150, 170 ° C, residence time 10, 2
The experiment was performed under the conditions of 0 and 30 minutes. In this experiment, treatment was carried out under a slightly pressurized condition so as not to cause boiling during the reaction. Tables 2 and 3 show the results of measuring the concentration when the outflow amount was about 1.5 times the volume of the liquid sending section, reaction section, and cooling section, and calculating the decomposition rate.
Shown in Even at a reaction temperature of 120 ° C., dichloromethane was decomposed by 93% or more in a residence time of 20 minutes. In this experiment, the alkali concentration was 0.5N to 1N and the residence time was 20 minutes to 30 minutes.
Minutely, there is no significant difference in the decomposition rate.
It could be decomposed by 00%. Decomposition rates were almost equal even at sample concentrations of 100 ppm and 1000 ppm.
【0020】[0020]
【表2】ジクロルメタンの分解率(ジクロルメタン濃度
100ppm) Table 2 Decomposition rate of dichloromethane (dichloromethane concentration
100ppm)
【0021】[0021]
【表3】ジクロルメタンの分解率(ジクロルメタン濃度
1000ppm) Table 3 Decomposition rate of dichloromethane (dichloromethane concentration
(1000ppm)
【0022】実施例3 ジクロルメタン100ppm試料溶液100ml(Na
OH1N)を回分式反応容器の充填し、二酸化チタンを
ゾルゲル法で表面に沈積させた管状に成形した粘土鉱物
を装填し、マイクロ波照射してジクロルメタンの分解率
を求めた。結果を表4に示す。触媒を添加することによ
り、分解率が20%程度向上することが認められた。Example 3 100 ml of a 100 ppm sample solution of dichloromethane (Na
OH1N) was charged into a batch-type reaction vessel, and a clay mineral formed into a tube in which titanium dioxide was deposited on the surface by a sol-gel method was charged, followed by microwave irradiation to determine the decomposition rate of dichloromethane. Table 4 shows the results. It was recognized that the addition of the catalyst improved the decomposition rate by about 20%.
【0023】[0023]
【表4】触媒添加の効果 Table 4 Effect of catalyst addition
【0024】実施例4 ジクロルメタン1000ppmの試料溶液を連続的に反応
装置に滞留時間10分になるように送液し、マイクロ波
を連続的あるいは2秒間隔のパルス照射を行い、ジクロ
ルメタン分解のパルス照射効果を調べた。NaOH濃度
1N、反応温度120℃、圧力10気圧の条件で実験を
行った。結果を図3に示すようにパルス照射の方が分解
率が高く、残存濃度が著しく低くなった。Example 4 A 1000 ppm sample solution of dichloromethane was continuously fed into a reactor so that the residence time was 10 minutes, and pulse irradiation of microwaves was performed continuously or at an interval of 2 seconds to perform pulse irradiation for decomposition of dichloromethane. The effect was investigated. The experiment was performed under the conditions of a NaOH concentration of 1 N, a reaction temperature of 120 ° C., and a pressure of 10 atm. As shown in FIG. 3, the pulse irradiation had a higher decomposition rate and the residual concentration was significantly lower.
【0025】実施例5 トリクロルエチレン(CHCl=CCl2)100ppmのアルカリ
水溶液(NaOH:1N)を連続的に反応部に送液し、
流速を変えて、マイクロ波連続照射処理を行った。結
果、120℃においても図4に示すように滞留時間10
分で分解率99.2%に達した。Example 5 An aqueous alkaline solution (NaOH: 1N) of 100 ppm of trichloroethylene (CHCl = CCl 2 ) was continuously fed to the reaction section.
Microwave continuous irradiation treatment was performed while changing the flow rate. As a result, even at 120 ° C., as shown in FIG.
Minutes, the decomposition rate reached 99.2%.
【0026】[0026]
【発明の効果】以上に説明したように、本発明によれ
ば、マイクロ波−ソルボサーマル連続反応処理により、
ジクロルメタンやトリクロルエチレンなどの有機塩素化
合物が低温、低圧の条件で簡単に分解することは明らか
である。本発明法の特徴は連続反応処理法であること、
反応部に必要に応じて触媒を共存させ、マイクロ波を連
続、好ましくはパルス照射して処理するものであり、実
用化に適した処理方法である。 本発明の実験では12
0〜180℃、10気圧、アルカリ濃度0.5〜2Nの
条件で実証試験を行ったが、それにとらわれるものでは
なく、反応温度およびアルカリ濃度の高い方が高速、大
容量処理が可能となり、残存濃度を低減できることは言
うまでもないが、低温・低圧の条件でも触媒添加および
パルス照射により、高速分解処理が可能と考えている。As described above, according to the present invention, according to the microwave-solvothermal continuous reaction treatment,
It is clear that organochlorine compounds such as dichloromethane and trichloroethylene are easily decomposed at low temperature and low pressure. The feature of the method of the present invention is that it is a continuous reaction treatment method,
The reaction is carried out by continuously or preferably irradiating a microwave with a catalyst, if necessary, in the reaction section, which is a processing method suitable for practical use. In the experiment of the present invention, 12
A verification test was performed under the conditions of 0 to 180 ° C., 10 atm, and an alkali concentration of 0.5 to 2 N. However, the present invention is not limited to this. It is needless to say that the concentration can be reduced, but it is considered that high-speed decomposition treatment is possible by adding a catalyst and irradiating a pulse even under conditions of low temperature and low pressure.
【図1】実施例1のジクロルメタンの連続分解の結果を
説明する図面である。FIG. 1 is a drawing explaining the result of continuous decomposition of dichloromethane in Example 1.
【図2】比較例1のジクロルメタンの回分処理の結果を
説明する図面である。FIG. 2 is a diagram illustrating the results of batch processing of dichloromethane in Comparative Example 1.
【図3】MWパルスの照射効果を説明する図面である。FIG. 3 is a drawing for explaining an irradiation effect of a MW pulse.
【図4】MW−ST法によるトリクロロエチレンの分解
結果を説明する図面である。FIG. 4 is a view for explaining the result of decomposition of trichlorethylene by the MW-ST method.
フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 1/02 B09B 3/00 ZAB 1/30 304G (71)出願人 599073917 財団法人香川県産業技術振興財団 香川県高松市林町2217番地43 (72)発明者 加藤 俊作 香川県綾歌郡綾南町大字畑田958番地3 (72)発明者 伊藤 功治 愛媛県新居浜市新田町3丁目1番39号 (72)発明者 曽我 博文 香川県高松市川島東町500番地2 細谷マ ンション305号室 (72)発明者 多田 薫 香川県大川郡大内町三本松700番地 Fターム(参考) 2E191 BA12 BA15 BC01 BD11 BD13 BD17 4D004 AB06 AB07 AC04 CA22 CB02 CB33 CC09 CC12 4D034 AA26 CA04 4D037 AB14 BA16 BB09 4G075 AA01 AA37 BA05 BA06 CA02 CA26 CA65 CA66 Continuation of the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (reference) C02F 1/02 B09B 3/00 ZAB 1/30 304G (71) Applicant 599073917 Kagawa Prefectural Industrial Technology Promotion Foundation Takamatsu, Kagawa 2217 43 Ichibayashi-cho (72) Inventor Shunsaku Kato 958-3 Hatada, Oaza, Ayanami-cho, Aya-gun, Kagawa Prefecture 500 No.2, Kawashima Higashicho, Takamatsu City, Kagawa Prefecture Room 305, Hosoya Mansion Room (72) Inventor Kaoru Tada 700, Ohonmachi, Okawa-machi, Okawa-gun, Kagawa Prefecture F-term (reference) 2E191 BA12 BA15 BC01 BD11 BD13 BD17 4D004 AB06 AB07 AC04 CA22 CB02 CB33 CC09 CC12 4D034 AA26 CA04 4D037 AB14 BA16 BB09 4G075 AA01 AA37 BA05 BA06 CA02 CA26 CA65 CA66
Claims (4)
をアルカリ水溶液と混合し、反応装置へ連続的に注入
し、マイクロ波を照射して沸点以上の温度に加熱・加圧
する条件で連続的に分解・無害化することを特徴とする
有害有機化合物のマイクロ波−ソルボサーマル連続処理
法。1. A harmful organic compound and a solution containing the same are mixed with an aqueous alkali solution, continuously injected into a reactor, and continuously decomposed under microwave irradiation to heat and pressurize to a temperature above the boiling point. -A microwave-solvothermal continuous treatment method for harmful organic compounds, characterized by detoxification.
収性および反応分解性の触媒を装填する請求項1の有害
有機化合物のマイクロ波−ソルボサーマル連続処理法。2. The continuous microwave-solvothermal treatment method for harmful organic compounds according to claim 1, wherein a microwave-absorbing and reactive-decomposable catalyst is loaded in the reaction section of the reactor.
複合酸化物、または多孔性物質等の表面に当該酸化物を
コーティングした複合材料等を用いる請求項1または2
の有害有機化合物のマイクロ波−ソルボサーマル連続処
理法。3. The catalyst according to claim 1, wherein the catalyst is a metal oxide or a composite oxide thereof, or a composite material obtained by coating the surface of a porous material with the oxide.
Microwave-solvothermal continuous treatment method for harmful organic compounds.
る請求項1、2または3の有害有機化合物のマイクロ波
−ソルボサーマル連続処理法。4. The continuous microwave-solvothermal treatment method for harmful organic compounds according to claim 1, 2 or 3, wherein the microwave is continuously or pulse-irradiated.
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JP2004141871A (en) * | 2002-10-22 | 2004-05-20 | Inst Fr Petrole | Method and plant for microwave treatment of solid residue resulting from pyrolysis of feed containing organic substance |
JP2006143773A (en) * | 2004-11-16 | 2006-06-08 | Kobe Steel Ltd | Method for dechlorination treatment of waste plastic |
KR100753906B1 (en) | 2006-10-24 | 2007-08-31 | 한국원자력연구원 | Method of carbon source recovery for biological nutrient treatment from sludge and method of sludge reduction |
WO2007141911A1 (en) * | 2006-06-06 | 2007-12-13 | Nippon Steel Chemical Co., Ltd. | Method of dehalogenating organic compound |
CN100366340C (en) * | 2005-10-14 | 2008-02-06 | 济南大学 | Catalyst for degrading water organic pollutant by microwave |
JP2013208510A (en) * | 2012-03-30 | 2013-10-10 | Tokyo Electric Power Co Inc:The | Method for treating large-sized instrument contaminated with pcb and treatment device to be used for the same |
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1999
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Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
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JP2004141871A (en) * | 2002-10-22 | 2004-05-20 | Inst Fr Petrole | Method and plant for microwave treatment of solid residue resulting from pyrolysis of feed containing organic substance |
JP2006143773A (en) * | 2004-11-16 | 2006-06-08 | Kobe Steel Ltd | Method for dechlorination treatment of waste plastic |
CN100366340C (en) * | 2005-10-14 | 2008-02-06 | 济南大学 | Catalyst for degrading water organic pollutant by microwave |
WO2007141911A1 (en) * | 2006-06-06 | 2007-12-13 | Nippon Steel Chemical Co., Ltd. | Method of dehalogenating organic compound |
KR100753906B1 (en) | 2006-10-24 | 2007-08-31 | 한국원자력연구원 | Method of carbon source recovery for biological nutrient treatment from sludge and method of sludge reduction |
JP2013208510A (en) * | 2012-03-30 | 2013-10-10 | Tokyo Electric Power Co Inc:The | Method for treating large-sized instrument contaminated with pcb and treatment device to be used for the same |
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