JP2003245679A - Supercritical water oxidizing method and supercritical oxidation apparatus - Google Patents
Supercritical water oxidizing method and supercritical oxidation apparatusInfo
- Publication number
- JP2003245679A JP2003245679A JP2002045665A JP2002045665A JP2003245679A JP 2003245679 A JP2003245679 A JP 2003245679A JP 2002045665 A JP2002045665 A JP 2002045665A JP 2002045665 A JP2002045665 A JP 2002045665A JP 2003245679 A JP2003245679 A JP 2003245679A
- Authority
- JP
- Japan
- Prior art keywords
- supercritical water
- liquid
- treated
- water oxidation
- supercritical
- 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.)
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Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/54—Improvements relating to the production of bulk chemicals using solvents, e.g. supercritical solvents or ionic liquids
Landscapes
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、有機物と無機塩類
および/または固形物を含む被処理液の超臨界水酸化方
法および超臨界水酸化装置に関するものである。TECHNICAL FIELD The present invention relates to a supercritical water oxidation method and a supercritical water oxidation apparatus for a liquid to be treated containing an organic substance, an inorganic salt and / or a solid substance.
【0002】[0002]
【従来の技術】各種研究施設から排出される実験廃液
や、化学工場の廃液等のような有機物と溶解無機塩類お
よび/または固形物を含む廃液を超臨界水酸化する場合
は、超臨界水酸化反応を行う反応器は無機塩類および固
形物を除去できるようなモダー型反応器(反応器下部に
亜臨界水領域を形成する縦型反応器)を用いる必要があ
る。2. Description of the Related Art In the case of supercritical water oxidation of experimental waste liquids discharged from various research facilities or waste liquids containing organic substances and dissolved inorganic salts and / or solids such as waste liquids of chemical plants, etc. As a reactor for carrying out the reaction, it is necessary to use a modder type reactor (a vertical type reactor forming a subcritical water region in the lower part of the reactor) capable of removing inorganic salts and solids.
【0003】しかし、モダー型反応器は構造が複雑なた
め製作コストが高く、簡単な構造のチューブ型反応器を
用いることができれば、装置の製作コストを低減するこ
とができる。また廃液中に固形物が多量存在している場
合は、反応器へ液を送り込むこと自体が困難となる場合
がある。However, since the modder type reactor has a complicated structure, the manufacturing cost is high, and if the tube type reactor having a simple structure can be used, the manufacturing cost of the apparatus can be reduced. Further, when a large amount of solid matter is present in the waste liquid, it may be difficult to send the liquid to the reactor.
【0004】[0004]
【発明が解決しようとする課題】本発明が解決しようと
する課題は、有機物と溶解無機塩類および/または固形
物を含む被処理液を超臨界水酸化処理するにあたり、析
出する無機塩類やもともと存在する固形物の除去機能の
ない反応器で超臨界水酸化処理することが可能な超臨界
水酸化方法および超臨界水酸化装置を提供することにあ
り、具体的には超臨界水酸化処理工程の前段に、極めて
構造が簡易な溶解無機塩および/または固形物を分離す
る手段を設けた超臨界水酸化方法および装置を提供する
ことにある。SUMMARY OF THE INVENTION The problem to be solved by the present invention is to precipitate inorganic salts or to be originally present when a liquid to be treated containing an organic substance and a dissolved inorganic salt and / or a solid substance is subjected to supercritical water oxidation treatment. The present invention is to provide a supercritical water oxidation method and a supercritical water oxidation apparatus capable of performing a supercritical water oxidation treatment in a reactor having no function of removing solids. It is an object of the present invention to provide a supercritical water oxidation method and apparatus provided with a means for separating dissolved inorganic salts and / or solids having a very simple structure in the first stage.
【0005】[0005]
【課題を解決するための手段】本発明者らが鋭意研究を
重ねた結果、有機物と溶解無機塩類および/または固形
物を含む被処理液を超臨界水酸化するにあたり、予め被
処理液を蒸発処理して溶解無機塩類および/または固形
物を除去することにより上記課題が解決されることを見
出し、本発明を完成するに至った。Means for Solving the Problems As a result of intensive studies conducted by the present inventors, when the liquid to be treated containing organic substances and dissolved inorganic salts and / or solids is supercritically hydroxylated, the liquid to be treated is vaporized in advance. It was found that the above problems can be solved by treating to remove dissolved inorganic salts and / or solid matter, and completed the present invention.
【0006】すなわち、本発明は、(1) 有機物と溶
解無機塩類および/または固形物を含む被処理液の超臨
界水酸化方法であって、該被処理液を蒸発処理する蒸発
工程、および該蒸発工程で得られる凝縮水を超臨界水酸
化処理する超臨界水酸化工程、を含むことを特徴とする
超臨界水酸化方法、(2) 有機物と溶解無機塩類およ
び/または固形物を含む被処理液の超臨界水酸化装置で
あって、該被処理液を蒸発処理する蒸発手段、および該
蒸発手段で得られる凝縮水を超臨界水酸化処理する超臨
界水酸化手段、を有することを特徴とする超臨界水酸化
装置、(3) 前記超臨界水酸化手段が、チューブ型反
応器を有することを特徴とする(2)に記載の超臨界水
酸化装置、に関するものである。That is, the present invention provides (1) a supercritical water oxidation method for a liquid to be treated containing an organic substance and dissolved inorganic salts and / or solids, which comprises an evaporation step of evaporating the liquid to be treated, and A supercritical water oxidation step in which the condensed water obtained in the evaporation step is subjected to a supercritical water oxidation step, and (2) an object to be treated containing organic matter and dissolved inorganic salts and / or solid matter A liquid supercritical water oxidation apparatus, comprising: evaporation means for evaporating the liquid to be treated; and supercritical water oxidation means for superconducting condensed water obtained by the evaporation means. (3) The supercritical water oxidation apparatus according to (2), wherein the supercritical water oxidation means has a tube reactor.
【0007】[0007]
【発明の実施の形態】本発明の有機物と溶解無機塩類お
よび/または固形物を含む被処理液とは、有機物と溶解
無機塩、有機物と固形物、あるいは有機物、溶解無機塩
および固形物を含む被処理液であって、例えば各種研究
施設から排出される実験廃液、化学工場の廃液等であ
る。BEST MODE FOR CARRYING OUT THE INVENTION The liquid to be treated containing an organic substance and a dissolved inorganic salt and / or a solid substance of the present invention includes an organic substance and a dissolved inorganic salt, an organic substance and a solid substance, or an organic substance, a dissolved inorganic salt and a solid substance. The liquid to be treated is, for example, an experimental waste liquid discharged from various research facilities, a waste liquid of a chemical factory, or the like.
【0008】本発明における有機物とは、蒸発処理可能
な有機物が好ましく、例えば、各種アルコール類が例示
できる。さらに酸化剤および/または紫外線などで酸化
分解し難い有機物、あるいは生物処理によって分解し難
い難分解性の有機物も例示でき、例えばトリクロロエチ
レン、テトラクロロエチレン、ジクロロメタン等を挙げ
ることができる。The organic substance in the present invention is preferably an organic substance which can be vaporized, and examples thereof include various alcohols. Furthermore, organic substances that are difficult to oxidize and decompose with an oxidizing agent and / or ultraviolet rays, or hardly decomposable organic substances that are difficult to decompose by biological treatment can be exemplified, and examples thereof include trichloroethylene, tetrachloroethylene, and dichloromethane.
【0009】本発明における溶解無機塩類とは、被処理
液中に飽和濃度以下で溶解している例えば塩化ナトリウ
ム、硫酸ナトリウム、塩化カリウム等のアルカリ金属、
アルカリ土類金属の塩化物塩または硫酸塩等である。The dissolved inorganic salts in the present invention are alkali metals such as sodium chloride, sodium sulfate and potassium chloride which are dissolved in the liquid to be treated at a saturation concentration or less,
Examples thereof include chlorides or sulfates of alkaline earth metals.
【0010】本発明における固形物とは、上述した無機
塩類が飽和濃度以上存在するため被処理液中に析出した
もの、あるいはもともと被処理液に溶解しないガラス等
の無機物やゴム、プラスチック等の有機物、あるいはそ
れらの合体物である、本発明方法において、有機物と溶
解無機塩類および/または固形物を含む被処理液は、超
臨界水酸化処理する前に、予め蒸発処理を行う。The solid matter in the present invention means that the above-mentioned inorganic salts are present in the liquid to be treated because they are present in a saturated concentration or more, or the inorganic substances such as glass and the organic substances such as rubber and plastic which are originally insoluble in the liquid to be treated. In the method of the present invention, or a combination thereof, the liquid to be treated containing the organic substance and the dissolved inorganic salt and / or the solid substance is subjected to evaporation treatment in advance before the supercritical water oxidation treatment.
【0011】蒸発処理とは、被処理液に直接加熱蒸気を
吹き込んで被処理液を沸騰させたり、被処理液を収容す
る容器の外側を加熱して被処理液を沸騰させ、被処理液
を蒸発させるものであり、常圧あるいは減圧下で行うこ
とができる。The evaporation treatment is performed by directly injecting heated steam into the liquid to be treated to boil the liquid to be treated, or by heating the outside of a container containing the liquid to be treated to boil the liquid to be treated. It is vaporized and can be performed under normal pressure or reduced pressure.
【0012】蒸発手段とは、蒸発処理を可能とする手段
であり、例えば、ディップ式ドラムドライヤー、バッチ
式ドライヤー等の手段を挙げることができる。好ましく
は、掻き取り手段によって、伝熱面に付着する固形物を
連続的に排除することができる掻面式液膜蒸発機が挙げ
られる。The evaporation means is a means that enables the evaporation process, and examples thereof include a dip type drum dryer and a batch type dryer. Preferably, a scraping surface type liquid film evaporator capable of continuously removing solid matter adhering to the heat transfer surface by scraping means.
【0013】被処理液を蒸発させることにより、溶解無
機塩類は液中で析出し、また固形物はそのまま固形残渣
として取り除かれる。有機物は凝縮水側に移行するの
で、凝縮水を超臨界水酸化すればよい。凝縮水を超臨界
酸化処理すればよいので、無機塩類や固形物の除去機能
を有しない反応器を用いることができる。このような工
程で処理することにより、超臨界水酸化後の処理水は放
出することができ、また蒸発処理工程では有機物を含ま
ない固形残渣を得ることができるので、大きな減容化を
図ることが可能となり、かつ固形残渣のその後の処理も
簡素化できる。By evaporating the liquid to be treated, the dissolved inorganic salts are precipitated in the liquid, and the solid matter is removed as it is as a solid residue. Since the organic matter moves to the condensed water side, the condensed water may be supercritically hydroxylated. Since the condensed water may be supercritically oxidized, a reactor having no function of removing inorganic salts and solids can be used. By treating in such a step, the treated water after supercritical water oxidation can be released, and a solid residue containing no organic matter can be obtained in the evaporation treatment step, so a large volume reduction should be achieved. And the subsequent treatment of the solid residue can be simplified.
【0014】本発明における超臨界水酸化処理とは、超
臨界状態の水と酸化剤の存在下に、有機物を酸化分解す
る方法である。超臨界水酸化反応は、水を超臨界状態と
する温度、圧力条件であれば特に限定されるものではな
いが、例えば、温度374℃以上、好ましくは500〜
650℃、かつ圧力22MPa以上、好ましくは22〜
25MPaの条件とすればよい。The supercritical water oxidation treatment in the present invention is a method of oxidatively decomposing organic matter in the presence of supercritical water and an oxidizing agent. The supercritical water oxidation reaction is not particularly limited as long as it is a temperature and pressure condition that brings water into a supercritical state, but is, for example, a temperature of 374 ° C. or higher, preferably 500 to
650 ° C. and pressure 22 MPa or more, preferably 22 to
The condition may be 25 MPa.
【0015】酸化剤としては、例えば空気、純酸素、過
酸化水素を挙げることができ、これらの酸化剤は化学量
論要求量以上用いればよい。Examples of the oxidizing agent include air, pure oxygen, and hydrogen peroxide. These oxidizing agents may be used in a stoichiometrically required amount or more.
【0016】無機塩類および/または固形物を含まない
凝縮水を超臨界水酸化すればよいので、モダー型反応器
のような無機塩や固形物の類除去機能を有する反応器を
用いる必要はなく、構造がより簡単なチューブ状反応器
をも用いることができる。Since condensed water containing no inorganic salts and / or solids may be supercritically hydroxylated, it is not necessary to use a reactor having a function of removing inorganic salts and solids such as a modder reactor. A tubular reactor having a simpler structure can also be used.
【0017】以下図面により、本発明の実施形態を説明
する。An embodiment of the present invention will be described below with reference to the drawings.
【0018】実施形態1
図1は、本発明方法の一実施形態を説明するためのフロ
ー図である。Embodiment 1 FIG. 1 is a flow chart for explaining one embodiment of the method of the present invention.
【0019】まず、溶解無機塩類および/または固形物
と有機物を含む被処理液を蒸発処理する。蒸発処理によ
り、無機塩類等を含む固形残渣と凝縮水に分離する。被
処理液中の有機物は凝縮水側に移行し、当該凝縮水を超
臨界水酸化工程(図1中、「SCWO工程」と表記)で
処理することにより、有機物を効率的に分解することが
できる。無機塩類および固形物を含まない凝縮水を超臨
界水酸化法により処理することになり、無機塩類および
固形物の除去機能のない反応器を用いることができる。First, the liquid to be treated containing dissolved inorganic salts and / or solid matter and organic matter is evaporated. By the evaporation treatment, a solid residue containing inorganic salts and the like are separated into condensed water. Organic matter in the liquid to be treated moves to the condensed water side, and by treating the condensed water in the supercritical water oxidation step (indicated as “SCWO step” in FIG. 1), the organic matter can be efficiently decomposed. it can. Condensed water that does not contain inorganic salts and solids will be treated by the supercritical water oxidation method, and a reactor without a function of removing inorganic salts and solids can be used.
【0020】このような本発明による処理工程によっ
て、超臨界水酸化処理工程から排出させる処理水は有機
物を含んでいないので放流可能となり、また蒸発処理工
程では固形残渣のみが残留するため大きな減容化を図る
ことができ、その後の処理も簡素なものとすることがで
きる。なお処理水中に含まれている有機物が蒸発可能な
ものであれば、固形残渣中に残存する有機物量は極めて
少なくなってそのまま排出可能となり、また多少有機物
が残留したとしてもその後の処理の簡素化を図ることで
きる。あるいは残留した固形残渣を再度蒸発処理する
と、水分が残留していないので被処理液を蒸発処理する
際の温度より高温下で蒸発処理することができ、残留固
形物中の有機物をさらに低減させることも可能である。By the treatment process according to the present invention, the treated water discharged from the supercritical water oxidation treatment process does not contain any organic matter and can be discharged. Also, only solid residue remains in the evaporation treatment process, resulting in a large volume reduction. The processing can be simplified, and the subsequent processing can be simplified. If the organic matter contained in the treated water can be evaporated, the amount of organic matter remaining in the solid residue will be extremely small and can be discharged as it is, and even if some organic matter remains, the subsequent treatment will be simplified. Can be achieved. Alternatively, if the remaining solid residue is evaporated again, water does not remain, so the liquid to be treated can be evaporated at a temperature higher than the temperature at which the liquid is evaporated, further reducing the organic matter in the residual solid. Is also possible.
【0021】実施形態2
図2は、本発明装置の一実施形態を説明するためのフロ
ー図である。Embodiment 2 FIG. 2 is a flow chart for explaining an embodiment of the device of the present invention.
【0022】有機物と溶解無機塩類および/または固形
物を含む被処理液を、蒸発手段としての蒸発装置1に供
給し、無機塩類を含む固形残渣と凝縮水に分離する。有
機物は凝縮水側に移行するので、この凝縮水を高圧ポン
プ2により水の臨界圧力となるようにチューブ型反応器
4へ加圧供給する。一方、酸化剤は、加圧ポンプ3によ
り、チューブ型反応器4へ加圧供給する。A liquid to be treated containing an organic substance, a dissolved inorganic salt and / or a solid substance is supplied to an evaporation device 1 as an evaporation means and separated into a solid residue containing an inorganic salt and condensed water. Since the organic matter moves to the condensed water side, the condensed water is pressurized and supplied to the tube reactor 4 by the high-pressure pump 2 so that the water has a critical pressure. On the other hand, the oxidizing agent is pressurized and supplied to the tube reactor 4 by the pressure pump 3.
【0023】チューブ型反応器4の入口付近には、熱交
換器型の予熱器5がある。超臨界状態の水と、酸化剤、
有機物がチューブ型反応器4内で反応し、超臨界水酸化
反応が進行する。有機物は超臨界水酸化分解され、水と
二酸化炭素となる。二酸化炭素および水を含む反応流体
は、チューブ型反応器4の出口付近に設けた熱交換型冷
却器6により冷却される。冷却された反応流体を、反応
器圧力を調整する圧力調整弁7を通じて気液分離器8に
導入して、気液分離する。気液分離した二酸化炭素は、
気液分離器の圧力を調整する圧力調整弁9を介して排出
し、処理水は気液分離器内の液面レベルを調整する液面
制御弁10を介して排出する。Near the inlet of the tube reactor 4 is a heat exchanger type preheater 5. Supercritical water, oxidizer,
Organic matter reacts in the tube reactor 4 and the supercritical water oxidation reaction proceeds. Organic matter is supercritically hydrolyzed into water and carbon dioxide. The reaction fluid containing carbon dioxide and water is cooled by a heat exchange type cooler 6 provided near the outlet of the tube reactor 4. The cooled reaction fluid is introduced into the gas-liquid separator 8 through the pressure adjusting valve 7 that adjusts the pressure of the reactor, and the gas-liquid separation is performed. Carbon dioxide separated from gas and liquid is
The water is discharged through a pressure adjusting valve 9 that adjusts the pressure of the gas-liquid separator, and the treated water is discharged through a liquid level control valve 10 that adjusts the liquid level in the gas-liquid separator.
【0024】本発明に用いることができる蒸発装置1
は、有機物と溶解無機塩類および/または固形物を含む
被処理液を蒸発することにより、有機物と水分を蒸発し
これらの蒸気を冷却して凝縮水をえることができるもの
であればいかなる構造のものでも用いることができる
が、図3に蒸発装置1として用いる掻面式液膜蒸発機の
模式図を示した。Evaporation device 1 that can be used in the present invention
Is any structure that can condense water by evaporating the liquid to be treated containing the organic substance and the dissolved inorganic salts and / or solid substance to evaporate the organic substance and water and cool these vapors. Although any one can be used, a schematic view of a scratch type liquid film evaporator used as the evaporator 1 is shown in FIG.
【0025】すなわち円筒槽11の外部に加熱手段を備
え、円筒槽11の内部にモータ12に連通する固形物掻
き取り用の回転翼13が設けられている。被処理液は円
筒槽11の上部から供給され、円筒槽11に供給された
被処理液は円筒内で加熱されて気化される。That is, a heating means is provided outside the cylindrical tank 11, and a rotary blade 13 for scraping solids is provided inside the cylindrical tank 11 so as to communicate with the motor 12. The liquid to be treated is supplied from the upper portion of the cylindrical tank 11, and the liquid to be treated supplied to the cylindrical tank 11 is heated and vaporized in the cylinder.
【0026】気化された有機物を含む蒸気は槽上部から
排出し槽外にて冷却され、有機物を含む凝縮水として回
収される。円筒槽11の壁面で析出する析出物は回転翼
13によって掻き取られ、液中に析出した蒸発残渣14
と合して円筒槽11下部の残渣受け槽(図示せず)へ排
出される。The vapor containing the vaporized organic matter is discharged from the upper portion of the tank, cooled outside the tank, and recovered as condensed water containing the organic matter. The deposits deposited on the wall surface of the cylindrical tank 11 are scraped off by the rotary blades 13 and the evaporation residue 14 deposited in the liquid 14
In combination with this, it is discharged to a residue receiving tank (not shown) below the cylindrical tank 11.
【0027】なお蒸発装置1としては図3に示した掻面
式液膜蒸発機の他に真空蒸留器を用いてもよい。真空蒸
留器とは、系を真空にして連続的に被処理液を蒸発する
ものであり、真空晶析装置、固液分離設備および乾燥機
の三つの組み合わせからなる。As the evaporator 1, a vacuum distiller may be used in addition to the scraped surface liquid film evaporator shown in FIG. The vacuum distiller is a device for continuously evaporating the liquid to be treated by applying a vacuum to the system, and is composed of three combinations of a vacuum crystallizer, a solid-liquid separation equipment and a drier.
【0028】[0028]
【発明の効果】本発明により、析出した無機塩類を含む
固形物の分離機能を持たない反応器を用いて、有機物と
溶解無機塩および/または固形物を含む被処理液を超臨
界水酸化分解処理できるため、処理性能やコスト面で有
利なタイプの超臨界水反応器を用いることができる。ま
た本発明によって、廃液を大幅に減容化することがで
き、かつ得られる蒸発残渣の処理も簡素化を図ることが
できる。低廉な反応器を使用することができ、分解処理
コストを低減することができる。INDUSTRIAL APPLICABILITY According to the present invention, by using a reactor having no function of separating solids containing precipitated inorganic salts, a liquid to be treated containing organic matter and dissolved inorganic salts and / or solids is supercritically hydrolyzed. Since it can be treated, a supercritical water reactor of a type advantageous in terms of treatment performance and cost can be used. Further, according to the present invention, the volume of waste liquid can be greatly reduced, and the processing of the obtained evaporation residue can be simplified. An inexpensive reactor can be used, and the decomposition treatment cost can be reduced.
【図1】本発明方法の一実施形態を示すフロー図。FIG. 1 is a flow chart showing an embodiment of a method of the present invention.
【図2】本発明装置の一実施形態を示すフロー図。FIG. 2 is a flowchart showing an embodiment of the device of the present invention.
【図3】掻面式液膜蒸発器の模式図。FIG. 3 is a schematic diagram of a scratch surface type liquid film evaporator.
1 蒸発装置 2 高圧ポンプ 3 高圧ポンプ 4 チューブ型反応器 5 予熱器 6 冷却器 7 圧力調整弁 8 気液分離器 9 圧力調整弁 10 圧力調整弁 11 円筒槽 12 モータ 13 回転翼 14 蒸発残渣 1 Evaporator 2 high pressure pump 3 high pressure pump 4 tube reactor 5 Preheater 6 cooler 7 Pressure control valve 8 gas-liquid separator 9 Pressure control valve 10 Pressure control valve 11 cylindrical tank 12 motors 13 rotors 14 Evaporation residue
───────────────────────────────────────────────────── フロントページの続き (72)発明者 鈴木 明 東京都江東区新砂1丁目2番8号 オルガ ノ株式会社内 Fターム(参考) 4D034 AA11 CA17 4D050 AA12 AA13 AB14 AB19 AB22 AB31 BB01 BB09 BB20 BC01 BC02 BD02 BD06 CA02 4D076 AA14 AA16 AA22 AA24 BA15 BA19 CD03 CD16 CD25 FA04 FA12 HA06 ─────────────────────────────────────────────────── ─── Continued front page (72) Inventor Akira Suzuki Olga 1-2-8 Shinsuna, Koto-ku, Tokyo Within the corporation F-term (reference) 4D034 AA11 CA17 4D050 AA12 AA13 AB14 AB19 AB22 AB31 BB01 BB09 BB20 BC01 BC02 BD02 BD06 CA02 4D076 AA14 AA16 AA22 AA24 BA15 BA19 CD03 CD16 CD25 FA04 FA12 HA06
Claims (3)
形物を含む被処理液の超臨界水酸化方法であって、該被
処理液を蒸発処理する蒸発工程、および該蒸発工程で得
られる凝縮水を超臨界水酸化処理する超臨界水酸化工
程、を含むことを特徴とする超臨界水酸化方法。1. A method for supercritical water oxidation of a liquid to be treated containing an organic substance and dissolved inorganic salts and / or solids, which comprises an evaporation step of evaporating the liquid to be treated, and condensed water obtained in the evaporation step. A supercritical water oxidation step of subjecting the supercritical water oxidation process to a supercritical water oxidation step.
形物を含む被処理液の超臨界水酸化装置であって、該被
処理液を蒸発処理する蒸発手段、および該蒸発手段で得
られる凝縮水を超臨界水酸化処理する超臨界水酸化手
段、を有することを特徴とする超臨界水酸化装置。2. A supercritical water oxidation apparatus for a liquid to be treated containing an organic substance and dissolved inorganic salts and / or solids, comprising: evaporation means for evaporating the liquid to be treated; and condensed water obtained by the evaporation means. A supercritical water oxidation apparatus having a supercritical water oxidation means for supercritical water oxidation.
応器を有することを特徴とする請求項2に記載の超臨界
水酸化装置。3. The supercritical water oxidation apparatus according to claim 2, wherein the supercritical water oxidation means has a tube reactor.
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012050920A (en) * | 2010-08-31 | 2012-03-15 | Ricoh Co Ltd | Waste liquid treatment apparatus |
CN103086496A (en) * | 2012-12-06 | 2013-05-08 | 上海交通大学 | Built-in supercritical water oxidation system for evaporating and denitrifying |
CN104478135A (en) * | 2014-12-15 | 2015-04-01 | 新奥科技发展有限公司 | Treatment method of salt-containing wastewater |
CN105130081A (en) * | 2015-09-08 | 2015-12-09 | 广州中国科学院先进技术研究所 | System and method for treating organic wastewater with low volatility by supercritical water oxidation |
CN114835235A (en) * | 2022-04-29 | 2022-08-02 | 西安交通大学 | Enhanced oxidation reaction device suitable for supercritical water oxidation technology |
-
2002
- 2002-02-22 JP JP2002045665A patent/JP2003245679A/en active Pending
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2012050920A (en) * | 2010-08-31 | 2012-03-15 | Ricoh Co Ltd | Waste liquid treatment apparatus |
CN103086496A (en) * | 2012-12-06 | 2013-05-08 | 上海交通大学 | Built-in supercritical water oxidation system for evaporating and denitrifying |
CN104478135A (en) * | 2014-12-15 | 2015-04-01 | 新奥科技发展有限公司 | Treatment method of salt-containing wastewater |
CN105130081A (en) * | 2015-09-08 | 2015-12-09 | 广州中国科学院先进技术研究所 | System and method for treating organic wastewater with low volatility by supercritical water oxidation |
CN105130081B (en) * | 2015-09-08 | 2017-11-10 | 广州中国科学院先进技术研究所 | A kind of System and method for of supercritical water oxidation processing low volatility organic wastewater |
CN114835235A (en) * | 2022-04-29 | 2022-08-02 | 西安交通大学 | Enhanced oxidation reaction device suitable for supercritical water oxidation technology |
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