JP2004097997A - Method and equipment for treating water-soluble polymer-containing waste liquid - Google Patents

Method and equipment for treating water-soluble polymer-containing waste liquid Download PDF

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Publication number
JP2004097997A
JP2004097997A JP2002265825A JP2002265825A JP2004097997A JP 2004097997 A JP2004097997 A JP 2004097997A JP 2002265825 A JP2002265825 A JP 2002265825A JP 2002265825 A JP2002265825 A JP 2002265825A JP 2004097997 A JP2004097997 A JP 2004097997A
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Prior art keywords
water
waste liquid
soluble polymer
hydrothermal
reactor
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JP2002265825A
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Japanese (ja)
Inventor
Hiroshi Obuse
小布施 洋
Yasuhiko Hatake
畠 康彦
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Komatsu Ltd
Kurita Water Industries Ltd
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Komatsu Ltd
Kurita Water Industries Ltd
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Priority to JP2002265825A priority Critical patent/JP2004097997A/en
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    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/54Improvements relating to the production of bulk chemicals using solvents, e.g. supercritical solvents or ionic liquids

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method and equipment for treating a water-soluble polymer-containing waste liquid which can increase the reactivity of the water-soluble polymer-containing waste liquid in a hydrothermal oxidation reaction, efficiently perform oxidative decomposition of water-soluble polymers by the hydrothermal oxidation reaction without increasing the size of a hydrothermal oxidation reactor, perform the stable treatment at a high level, and hardly generate carbon monoxide. <P>SOLUTION: The water-soluble polymer-containing waste liquid and a neutralizing agent are supplied to a deposition tank 1. The feed rate of a pump P2 is regulated by a pH controller 12 so as to adjust the pH of the waste liquid to a prescribed pH, thereby neutralizing the waste liquid and insolubilizing the water-soluble polymers to be deposited in a suspended state. The suspended waste liquid is fed to a feeder 13 of the hydrothermal oxidation reactor 2 by a high pressure pump P1, and mixed with an oxidizing agent supplied from an oxidizing agent supply means 4, in the feeder. The mixed flow is fed to a reactor 3, and the hydrothermal oxidation reaction is carried out in the supercritical or subcritical state of water to oxidatively decompose organic substances. <P>COPYRIGHT: (C)2004,JPO

Description

【0001】
【発明の属する技術分野】
この発明は水溶性ポリマー含有廃液の水熱酸化反応による処理方法および装置、好適には半導体や電子部品の製造工程で発生する水溶性ポリマー含有廃液、特にドライフィルムレジストを使用した製造工程で発生する水溶性ポリマー含有廃液の処理を安定して、かつ高度に行うための処理方法および装置に関するものである。
【0002】
【従来の技術】
近年、情報技術の進歩に伴って半導体や電子部品の微細化が進んでいる。このような流れの中で半導体や電子部品の製造工程からは様々な廃液が排出され、これらの処理が各方面で問題となっている。それらの廃液の一つにドライフィルムレジスト等のレジストを使用した製造工程から排出される水溶性ポリマー含有廃液がある。この廃液はドライフィルムレジスト等のレジストを貼り付けた基板に回路パターンを露光してレジストを硬化させた後、露光せず硬化していないレジストをアルカリ水溶液で洗浄して除去すると、レジスト中のポリマーが水溶性となって水に溶解し、水溶性ポリマー含有廃液が発生する。従来、この廃液は産廃処理業者が引き取り、少しずつ生物処理装置に投入する形で処理されることが多かった。しかし、廃液量が多いことや、自社内処理のニーズが高まっていることなどもあり、新たな処理技術が望まれていた。
【0003】
この種の廃液を処理する方法として、水および酸化剤の存在下に水の超臨界または亜臨界状態で水熱反応を行い有機物を酸化分解する水熱酸化処理がある。水熱酸化処理は有機排液を短時間で高レベルまで分解処理できるほか、高アルカリ廃液についても有機物の分解で生成する二酸化炭素により中和することにより、腐食を抑制しつつ処理を行うことが可能である。また、析出した炭酸塩は塩掻き取り機構により連続的に排出することができる。
【0004】
しかし、このような水熱酸化処理により水溶性ポリマー含有廃液を処理すると、酸化が不完全なときに発生する生成物である一酸化炭素(CO)が発生する。この一酸化炭素の発生量は反応温度を高くしたり、反応時間を長くすることで低減することはできるが、高温高圧での反応となる水熱酸化処理では、反応器肉厚の増加や反応器サイズの拡大が必要となる。そのため、廃液自体の反応性を改善する方法が必要となる。
【0005】
【発明が解決しようとする課題】
本発明の課題は、水熱酸化反応における水溶性ポリマー含有廃液の反応性を大きくすることができ、水熱反応装置を大型化することなく、水熱酸化反応により効率よく水溶性ポリマーを酸化分解し、処理を安定してかつ高度に行うことが可能な水溶性ポリマー含有廃液の処理方法および装置を得ることである。
【0006】
【課題を解決するための手段】
本発明は次の水溶性ポリマー含有廃液の処理方法および装置である。
(1) 水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して、懸濁状に析出させる析出工程と、
懸濁状の廃液を水熱反応装置に供給する供給工程と、
水熱反応装置において水および酸化剤の存在下に、水の超臨界または亜臨界状態で水熱酸化反応を行い有機物を酸化分解する水熱反応工程と
を含む水溶性ポリマー含有廃液の処理方法。
(2) 水溶性ポリマーの不溶化が中和またはエステル化である上記1記載の方法。
(3) 水溶性ポリマー含有廃液がレジスト含有廃液である上記(1)または(2)記載の方法。
(4) 水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して、懸濁状に析出させる析出装置と、
懸濁状の廃液を水熱反応装置に供給する供給装置と、
懸濁状の廃液を導入し水および酸化剤の存在下に、水の超臨界または亜臨界状態で水熱酸化反応を行い有機物を酸化分解する水熱反応装置と
を含む水溶性ポリマー含有廃液の処理装置。
(5) 析出装置が中和またはエステル化により水溶性ポリマーを不溶化する装置である上記(4)記載の装置。
【0007】
本発明において処理の対象となる被処理物は水溶性ポリマーを含有する水溶性ポリマー含有廃液である。水溶性ポリマーは水溶性となる親水基を有するポリマー(有機高分子物質)である。このような水溶性ポリマーとしては、半導体や電子部品の製造工程で使用されるレジスト、例えばドライフィルムレジストなどがあげられるが、これらに限定されない。従って水溶性ポリマー含有廃液は、このような親水基を有する水溶性ポリマーが溶解した廃液であり、水溶性ポリマー以外に他の物質が含まれていてもよい。水溶性ポリマー含有廃液の例としては、半導体や電子部品の製造工程から排出されるレジストを含む廃液、例えばドライフィルムレジストを含む廃液などがあげられるが、これらに限定されない。
【0008】
本発明では、このような水溶性ポリマー含有廃液を処理する際、水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して懸濁状に析出させ、この懸濁状に析出した廃液を水熱反応装置に供給して、水熱反応装置において水および酸化剤の存在下に、水の超臨界または亜臨界状態で水熱酸化反応を行い、懸濁状に析出したポリマーを酸化分解する。水溶性ポリマーを不溶化して懸濁状に析出させるとは、水溶性ポリマーが廃液中で不溶化し、分散した状態で析出し、全体として懸濁液の状態を呈することをいう。
【0009】
水熱酸化反応における水溶性ポリマー含有廃液の反応性改善策を検討した結果、廃液に溶解している水溶性ポリマー(樹脂)を析出させて懸濁させ、懸濁溶液の状態で水熱酸化反応処理を行うことにより、水熱酸化反応の反応性が大きく向上し、一酸化炭素がほとんど発生しなくなることがわかった。水溶性ポリマーを析出・懸濁させることにより反応性が向上する理由は、次のように考えられる。
【0010】
水溶性ポリマー含有廃液を蒸発濃縮していくと、ある時点でポリマーが析出してくるが、さらに濃縮を継続するとポリマーがゲル状に固まる現象が観察される。水熱酸化反応器内でも同様の現象が生じており、水溶液の状態で反応器内に供給された水溶性ポリマーは、高温環境下で徐々に液状の水が減少していくと、蒸発濃縮によりポリマー濃度が高まっていく場合と同じように、ポリマーがゲル状に析出して固まる。このような状態でポリマーがゲル状に固化してしまうと、ゲル状に固化した表面からしか反応が進まないため、反応速度が遅くなる。その結果、有機物が完全に酸化されず、一酸化炭素が未分解のまま排出される。
【0011】
本発明では、水溶性ポリマーを不溶化して懸濁状に析出させ、この懸濁状に析出した廃液を水熱反応装置に供給して水熱酸化反応を行うので、ポリマーは懸濁状に析出した状態で水熱酸化反応を受けて酸化分解する。ポリマーが懸濁状になるように析出させた状態は、ゲル状に固まった状態に比べて樹脂の表面積が大きいので、反応性の低下もほとんどなく高効率で処理され、有機物が完全に酸化されて、一酸化炭素が未分解のまま排出されることが防止される。
【0012】
水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して、懸濁状に析出させる方法としては、それぞれの水溶性ポリマー特性に応じて選択することができる。要するに水溶性を付与する親水基を疎水化すればよいのであって、中和、エステル化などが挙げられる。例えばカルボン酸Na塩を官能基とする水溶性ポリマーであれば、酸で中和してカルボン酸にすることにより、ポリマーは不溶化して懸濁状に析出する。エステル化の場合は、親水性基をエステル化反応により疎水化することができる。しかし、析出したポリマーが表面積の大きい状態でなければならないこと、簡便な析出方法であることなどを考慮すると、中和による析出方法が好ましい。中和するpHは廃液の状態によっても異なるが、通常pH3〜7、好ましくはpH4〜6の範囲とする。pHが高すぎると樹脂の析出が不完全となるし、pHが低すぎると酸による反応器の腐食が懸念される。
【0013】
半導体や電子部品の製造工程から排出されるレジストを含む廃液、例えばドライフィルムレジストを含む廃液の場合、露光しないで未硬化のまま残留するレジストのカルボン酸がアルカリ水溶液洗浄によりNa塩となり、ポリマー全体が水溶性ポリマーとなって溶解している。このため上記廃液を酸で中和することにより、ポリマーが不溶化して懸濁状に析出する。
【0014】
本発明の析出工程では、上記のようにして水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して、懸濁状に析出させる。この析出工程は、廃液を水熱反応装置に供給する供給工程内に設けて、例えば廃液を水熱反応装置に供給する配管に中和剤を注入してもよいが、供給工程に先立ってあるいは供給工程内に、ポリマーを不溶化して懸濁状に析出させる装置を設けるのが好ましい。例えば廃液を水熱反応装置に供給する配管の途中に、薬注管、攪拌機およびpH調整器を有する中和槽を設け、攪拌機で攪拌しpH調整器で所定pHになるように薬注管から中和剤を注入して廃液を中和し、ポリマーを不溶化して懸濁状に析出させることができる。
【0015】
本発明の供給工程は、供給装置により懸濁状の廃液を水熱反応装置に供給するように構成される。水熱反応装置は高温高圧に維持されるので、この供給装置は懸濁状の廃液を加圧し、場合によっては加熱して水熱反応装置に供給するように構成される。この場合、酸化剤として例えば空気を加圧して廃液とともに水熱反応装置に供給するように構成することができる。
【0016】
水熱反応工程ではポリマーを懸濁状に析出させた廃液を、水熱反応装置において水および酸化剤の存在下に、水の超臨界または亜臨界状態で水熱酸化反応を行い、析出したポリマーその他の有機物の酸化分解を行う。水熱反応装置は廃液を酸化剤の存在下に水の超臨界または亜臨界状態に維持して水熱酸化反応を行えるように構成される。ここで水熱酸化反応は、超臨界または亜臨界状態の高温高圧の水および酸化剤の存在下に濃縮物を酸化反応により酸化分解する反応である。超臨界状態とは374℃以上、22MPa以上の状態である。また亜臨界状態とは例えば374℃以上、2.5MPa以上22MPa未満あるいは374℃未満、22MPa以上の状態、あるいは374℃未満、22MPa未満であっても臨界点に近い高温高圧状態をいう。
【0017】
このような水熱酸化反応は廃液が酸化剤と混合した状態で水熱反応装置において行われ、これらの混合物が反応器内部で水熱反応を受ける。酸化剤としては、空気、酸素、液体酸素、過酸化水素水を用いることができる。酸化剤は、被処理物の混合汚泥と混合されて供給されてもよいし、供給口を二重管ノズルにして複層流として供給してもよい。また必要により触媒や中和剤等が添加される場合があるが、これらも廃液と混合して、あるいは別々に反応器に供給することができる。
【0018】
本発明で用いられる水熱反応装置は超臨界または亜臨界状態で水熱反応を行うように、耐熱、耐圧材料により形成される。反応熱だけでは超臨界または亜臨界状態に達しない場合には外部加熱手段を設けることができる。
【0019】
水熱反応装置の材質は制限されないが、ハステロイ、インコネル、ステンレス等の耐食性の材質が好ましい。水熱反応装置には耐腐食性ライナーを設けるのが好ましい。耐腐食性ライナーは特に限定されず、耐腐食性ライナーと圧力負荷壁との間に間隙が存在するような耐腐食性ライナーを用いることができる。
【0020】
水熱反応装置には反応混合物を排出口から排出する前に冷却するための冷却手段を設けることができる。冷却手段は特に限定されないが、反応器内にクエンチ水を導入して冷却し、無機塩を溶解してその排出を促進することができる。また、反応器内に酸やアルカリを含む水を導入して冷却し、アルカリや酸の中和を行うことができる。固体の粘着性が著しい場合には、反応器の内壁に付着した固体を除去するための機械的除去装置を設けることができる。固体除去のための機械的除去装置は特に限定されないが、切欠窓部分を含む実質的に円筒状のスクレーパが好適である。この様な機構を備えるためには、反応器形状としては実質的に垂直方向に配置した筒状反応器が好適である。筒状反応器の形状は円筒、だ円筒、多角筒のものを用いることができ、下端部はコーン状とすることができる。
【0021】
水熱反応装置から排出される反応流体中の固形物を分離する分離手段を設けることができる。固形物分離手段は特に限定されず、水熱反応装置から反応流体を導入する流入口および固体を除去した流体を排出する流出口を備えた容器と、容器内に配設されて前記反応流体に含まれている前記固体を除去し、排出する手段とを備えたものが使用できる。固形物分離手段は、処理流体を減圧する弁の上流に設置することが望ましい。こうすることで減圧弁の摩耗や閉塞を防止することができる。
【0022】
本発明では水熱反応工程において、上記のような水熱反応装置により超臨界または亜臨界状態で水熱酸化反応を行うと、被反応物の有機物は酸化剤により酸化されて最終的に水と二酸化炭素に分解される。
【0023】
水熱反応装置による反応開始の手段は特に制限されない。通常、反応器は反応開始にあたって所定の反応温度付近に予熱される。予熱は加熱装置を反応器に設けるか、あるいは廃液および/または酸化剤供給路に設けて加熱された水や空気を導入して実施することができる。また、通常、反応器に水や酸化剤を供給し、通常設けられる圧力調整弁によって所定の圧力に加圧される。所定の温度、圧力に調整された後、被反応物である混合汚泥を含む流体を供給して水熱反応を開始する。反応によって有機物が分解され、反応熱が発生する。
【0024】
水熱反応装置を出た反応流体は、冷却、気液分離を経て、処理液と処理ガスをそれぞれ別個に減圧して排出される。最終的に生成した水、気体、固体は、そのまま、エネルギー回収されたり、物質として再利用されたり、そのままあるいは追加処理されて廃棄される。
【0025】
【発明の効果】
本発明によれば、水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して懸濁状に析出させた状態で、水熱酸化反応を行い酸化分解するようにしたので、水熱酸化反応におけるポリマーの反応性を大きくすることができ、これにより水熱反応装置を大型化することなく、水熱酸化反応により効率よく水溶性ポリマーを酸化分解し、処理を安定してかつ高度に行うことが可能で、一酸化炭素がほとんど発生しない水溶性ポリマー含有廃液の処理方法および装置を得ることができる。
【0026】
【発明の実施の形態】
以下、本発明の実施の形態を図面により説明する。図1は実施形態の水溶性ポリマー含有廃液処理装置のフロー図である。
【0027】
図1において、1は析出槽、2は水熱反応装置、3は反応器、4は酸化剤供給手段、5は冷却器、6は気液分離器である。析出槽1はラインL1から水溶性ポリマー含有廃液を供給し、ラインL2から中和剤を供給し、攪拌機11で攪拌しながらpH調整器12でpHを測定し、ポンプP2の供給量を調整して中和するように構成されている。水熱反応装置2は反応器3の上部に供給装置13を有し、反応器3は下部がコーン状に形成され、内部にスクレーパ14を有し、下部にクエンチ水供給管15が開口している。
【0028】
析出槽1から廃液を供給する高圧ポンプP1を有するラインL3が水熱反応装置2の反応器3の上部に設けられた供給装置13に連絡している。供給装置13には酸化剤を供給する酸化剤供給手段4に接続されたラインL4が連絡している。この供給装置13は酸化剤と廃液の混合流を反応器3に下向流として供給するように取付けられている。水熱反応装置4の下部からラインL5が冷却器5に連絡し、冷却器5からラインL7が気液分離器6に連絡している。気液分離器6から減圧弁V1を有する気体排出路ラインL8および減圧弁V2を有する液体排出路L9が系外に連絡している。冷却器5には冷却水路L6が連絡している。
【0029】
上記の水溶性ポリマー含有廃液処理装置においては、ラインL1から析出槽1に水溶性ポリマー含有廃液を供給し、ラインL2から中和剤を供給し、攪拌機11で攪拌しながらpH調整器12でpHを測定し、ポンプP2の供給量を調整してpH調整器12のpH測定値が所定値(例えばpH5)となるように中和する。これにより廃液中の水溶性ポリマーが不溶性となって懸濁状に析出し、廃液は懸濁液となる。
【0030】
懸濁状の廃液は高圧ポンプP1によりラインL3から水熱反応装置2の供給装置13に送り、ここで酸化剤供給手段4からラインL4を通して送られる酸化剤(例えば空気、過酸化水素水)と混合し、混合流を反応器3に下向流で供給して水熱反応を行う。供給装置13から供給される混合流は反応器3内で、水の超臨界または亜臨界状態における水熱酸化反応により有機物が酸化分解される。この水熱酸化反応では、ポリマーが懸濁状に析出しているため、ゲル状に固まった状態に比べて樹脂の表面積が大きいので、周囲から熱が加わると直ちに酸化分解が起こって発生するガスは拡散し、これにより反応性の低下もほとんどなく高効率で処理されて有機物が完全に二酸化炭素に酸化され、一酸化炭素が未分解のまま排出されることが防止される。
【0031】
懸濁状となった廃液中には塩が溶解しているが、超臨界状態では溶解せず、塩の状態で析出している。この状態で下部のクエンチ水供給管15からクエンチ水を供給すると、水の一部が液状となり、塩が溶解する。反応器3の内壁に付着した塩はスクレーパ14により剥離される。反応器3の反応物はラインL5から冷却器5に導入し、冷却水路L6から供給する冷却水で冷却する。冷却された気液混合流体はラインL7から気液分離器6に導入して気液分離し、気体排出路L8から処理ガスを排出し、液体排出路L9から処理水を排出する。
【0032】
上記の実施形態において、析出装置として中和槽形式のものを示したが、ラインミキサー式など他の形式のものを用いてもよい。
【0033】
【実施例】
以下、本発明の実施例について説明する。
実施例1
図1の処理装置により水溶性ポリマー含有廃液を処理した。被処理廃液としてドライフィルムレジストを使用する製造工程から排出された水溶性ポリマー含有廃液を、析出槽3において撹拌しながら硫酸で中和して溶解していたポリマーを析出・懸濁させた。そしてポリマーが懸濁した廃液を水熱反応装置2の反応器3に供給し、酸化剤として空気を供給し、反応温度:650℃、反応圧力:23.4MPa、反応時間:10秒で水熱酸化処理した。その結果、水熱酸化処理は安定して進行した。処理液および処理ガスの性状も以下の通りで、有機物をほぼ完全分解することができた。
処理水TOC:<1mg/L
処理ガスCO:<2ppm
【0034】
比較例1
ドライフィルムレジストを使用する製造工程から排出された水溶性ポリマー含有廃液を、前処理せず、実施例1と同じ条件で水熱酸化処理した。その結果、水熱酸化処理中、処理ガス中に一酸化炭素が高濃度で検出された。処理液および処理ガスの性状も以下の通りで、有機物が完全分解できず、酸化が不完全であったことが示唆された。
処理水TOC:5mg/L
処理ガスCO:200〜900ppm
【図面の簡単な説明】
【図1】1 析出槽
2 水熱反応装置
3 反応器
4 酸化剤供給手段
5 冷却器
6 気液分離器
11 攪拌機
12 pH調整器
13 供給装置
14 スクレーパ
15 クエンチ水供給管
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method and an apparatus for treating a wastewater containing a water-soluble polymer by a hydrothermal oxidation reaction, preferably a wastewater containing a water-soluble polymer generated in a manufacturing process of a semiconductor or an electronic component, particularly a manufacturing process using a dry film resist. The present invention relates to a method and an apparatus for stably and highly treating a wastewater containing a water-soluble polymer.
[0002]
[Prior art]
2. Description of the Related Art In recent years, semiconductors and electronic components have been miniaturized with the advance of information technology. In such a flow, various waste liquids are discharged from the manufacturing process of semiconductors and electronic components, and these treatments are problematic in various fields. One of those waste liquids is a water-soluble polymer-containing waste liquid discharged from a manufacturing process using a resist such as a dry film resist. This waste liquid is cured by exposing the circuit pattern to a substrate on which a resist such as a dry film resist is adhered, and then curing the unexposed and uncured resist with an aqueous alkali solution to remove the polymer in the resist. Becomes water-soluble and dissolves in water, generating a water-soluble polymer-containing waste liquid. Heretofore, this waste liquid has often been treated by an industrial waste disposal company, taking it little by little and putting it into a biological treatment apparatus. However, there is a large amount of waste liquid and the need for in-house treatment is increasing. Therefore, a new treatment technique has been desired.
[0003]
As a method of treating this kind of waste liquid, there is a hydrothermal oxidation treatment in which a hydrothermal reaction is performed in a supercritical or subcritical state of water in the presence of water and an oxidizing agent to oxidatively decompose organic substances. Hydrothermal oxidation can decompose organic effluents to a high level in a short period of time, and can also treat highly alkaline effluents while suppressing corrosion by neutralizing them with carbon dioxide generated by the decomposition of organic matter. It is possible. Further, the precipitated carbonate can be continuously discharged by a salt scraping mechanism.
[0004]
However, when the water-soluble polymer-containing waste liquid is treated by such a hydrothermal oxidation treatment, carbon monoxide (CO), which is a product generated when oxidation is incomplete, is generated. Although the amount of carbon monoxide generated can be reduced by raising the reaction temperature or lengthening the reaction time, hydrothermal oxidation, which is a reaction at high temperature and high pressure, increases the reactor wall thickness and the reaction. It is necessary to enlarge the vessel size. Therefore, a method for improving the reactivity of the waste liquid itself is required.
[0005]
[Problems to be solved by the invention]
An object of the present invention is to increase the reactivity of a wastewater containing a water-soluble polymer in a hydrothermal oxidation reaction, and to efficiently decompose a water-soluble polymer by hydrothermal oxidation without increasing the size of the hydrothermal reactor. It is another object of the present invention to provide a method and an apparatus for treating a wastewater containing a water-soluble polymer, which can perform the treatment stably and to a high degree.
[0006]
[Means for Solving the Problems]
The present invention is the following method and apparatus for treating a wastewater containing a water-soluble polymer.
(1) a precipitation step of insolubilizing the water-soluble polymer in the water-soluble polymer-containing waste liquid and precipitating it in suspension;
A supply step of supplying the suspended waste liquid to the hydrothermal reactor,
A hydrothermal reaction step of performing a hydrothermal oxidation reaction in a supercritical or subcritical state of water in the presence of water and an oxidizing agent in a hydrothermal reactor to oxidatively decompose organic substances.
(2) The method according to the above 1, wherein the insolubilization of the water-soluble polymer is neutralization or esterification.
(3) The method according to the above (1) or (2), wherein the water-soluble polymer-containing waste liquid is a resist-containing waste liquid.
(4) a precipitation apparatus for insolubilizing the water-soluble polymer in the water-soluble polymer-containing waste liquid and depositing the suspension in a suspension state;
A supply device for supplying the suspended waste liquid to the hydrothermal reactor,
A water-soluble polymer-containing waste liquid containing a suspended liquid waste liquid and a hydrothermal reactor that performs a hydrothermal oxidation reaction in a supercritical or subcritical state of water in the presence of water and an oxidizing agent to oxidatively decompose organic substances. Processing equipment.
(5) The apparatus according to the above (4), wherein the precipitation apparatus is an apparatus for insolubilizing the water-soluble polymer by neutralization or esterification.
[0007]
The object to be treated in the present invention is a water-soluble polymer-containing waste liquid containing a water-soluble polymer. The water-soluble polymer is a polymer (organic polymer substance) having a hydrophilic group that becomes water-soluble. Examples of such a water-soluble polymer include, but are not limited to, resists used in semiconductor and electronic component manufacturing processes, such as dry film resists. Therefore, the water-soluble polymer-containing waste liquid is a waste liquid in which such a water-soluble polymer having a hydrophilic group is dissolved, and may contain other substances in addition to the water-soluble polymer. Examples of the water-soluble polymer-containing waste liquid include, but are not limited to, a waste liquid containing a resist discharged from a semiconductor or electronic component manufacturing process, such as a waste liquid containing a dry film resist.
[0008]
In the present invention, when treating such a water-soluble polymer-containing waste liquid, the water-soluble polymer in the water-soluble polymer-containing waste liquid is insolubilized and precipitated in a suspension, and the waste liquid deposited in the suspension is subjected to a hydrothermal reaction. The water is supplied to the apparatus, and in the hydrothermal reactor, a hydrothermal oxidation reaction is performed in a supercritical or subcritical state of water in the presence of water and an oxidizing agent to oxidatively decompose the polymer precipitated in suspension. To insolubilize and precipitate a water-soluble polymer in a suspended state means that the water-soluble polymer is insolubilized in a waste liquid, precipitates in a dispersed state, and exhibits a suspension state as a whole.
[0009]
As a result of examining measures to improve the reactivity of wastewater containing a water-soluble polymer in the hydrothermal oxidation reaction, the water-soluble polymer (resin) dissolved in the waste liquid is precipitated and suspended, and the hydrothermal oxidation reaction in the state of the suspension solution is performed. It was found that by performing the treatment, the reactivity of the hydrothermal oxidation reaction was greatly improved, and almost no carbon monoxide was generated. The reason why the reactivity is improved by precipitating and suspending the water-soluble polymer is considered as follows.
[0010]
As the water-soluble polymer-containing waste liquid is evaporated and concentrated, a polymer precipitates at a certain point in time. However, when the concentration is further continued, a phenomenon in which the polymer solidifies in a gel state is observed. A similar phenomenon occurs in the hydrothermal oxidation reactor, and the water-soluble polymer supplied into the reactor in the form of an aqueous solution is concentrated by evaporation when the liquid water gradually decreases in a high-temperature environment. As in the case where the polymer concentration increases, the polymer precipitates in a gel state and hardens. If the polymer solidifies in a gel state in such a state, the reaction proceeds only from the surface solidified in the gel state, and the reaction rate is reduced. As a result, the organic matter is not completely oxidized, and the carbon monoxide is discharged without decomposition.
[0011]
In the present invention, the water-soluble polymer is insolubilized and precipitated in a suspension, and the waste liquid precipitated in the suspension is supplied to a hydrothermal reactor to perform a hydrothermal oxidation reaction. In this state, it undergoes hydrothermal oxidation and undergoes oxidative decomposition. In the state where the polymer is precipitated in a suspended state, the surface area of the resin is larger than that in the state where the polymer is solidified, so that the treatment is performed with high efficiency with little decrease in reactivity, and the organic matter is completely oxidized. As a result, carbon monoxide is prevented from being discharged without decomposition.
[0012]
The method of insolubilizing the water-soluble polymer in the water-soluble polymer-containing waste liquid and causing it to precipitate in suspension can be selected according to the characteristics of each water-soluble polymer. In short, it suffices to make the hydrophilic group imparting water solubility hydrophobic, and examples thereof include neutralization and esterification. For example, in the case of a water-soluble polymer having a carboxylic acid Na salt as a functional group, the polymer is insolubilized and precipitated in suspension by neutralizing with an acid to form a carboxylic acid. In the case of esterification, a hydrophilic group can be made hydrophobic by an esterification reaction. However, in consideration of the fact that the precipitated polymer must have a large surface area, a simple precipitation method, and the like, a precipitation method by neutralization is preferable. The neutralizing pH varies depending on the state of the waste liquid, but is usually in the range of pH 3 to 7, preferably in the range of pH 4 to 6. If the pH is too high, the precipitation of the resin will be incomplete, and if the pH is too low, acid corrosion of the reactor may occur.
[0013]
In the case of a waste liquid containing a resist discharged from a semiconductor or electronic component manufacturing process, for example, a waste liquid containing a dry film resist, the carboxylic acid of the resist remaining uncured without being exposed becomes an Na salt by washing with an aqueous alkali solution, and the entire polymer is removed. Is dissolved as a water-soluble polymer. Therefore, by neutralizing the waste liquid with an acid, the polymer is insolubilized and precipitates in suspension.
[0014]
In the precipitation step of the present invention, the water-soluble polymer in the water-soluble polymer-containing waste liquid is insolubilized as described above, and is precipitated in a suspended state. This precipitation step may be provided in a supply step of supplying the waste liquid to the hydrothermal reactor, for example, injecting a neutralizing agent into a pipe for supplying the waste liquid to the hydrothermal reactor, but before the supply step or It is preferable to provide an apparatus for insolubilizing and precipitating the polymer in a suspension state in the supply step. For example, in the middle of the pipe for supplying the waste liquid to the hydrothermal reactor, a neutralization tank having a chemical injection tube, a stirrer and a pH adjuster is provided, and the mixture is stirred with the stirrer and the pH is adjusted with the pH adjuster so that the pH reaches a predetermined value. A neutralizing agent can be injected to neutralize the waste liquid, insolubilize the polymer and precipitate it in suspension.
[0015]
The supply step of the present invention is configured to supply the suspended waste liquid to the hydrothermal reactor by the supply device. Since the hydrothermal reactor is maintained at a high temperature and a high pressure, the supply device is configured to pressurize, and in some cases, heat the waste liquid in suspension to supply it to the hydrothermal reactor. In this case, for example, air may be pressurized as an oxidant and supplied to the hydrothermal reactor together with the waste liquid.
[0016]
In the hydrothermal reaction step, the waste liquid in which the polymer is precipitated in a suspended state is subjected to a hydrothermal oxidation reaction in a supercritical or subcritical state of water in a hydrothermal reactor in the presence of water and an oxidizing agent, and the precipitated polymer is Performs oxidative decomposition of other organic substances. The hydrothermal reactor is configured to perform a hydrothermal oxidation reaction by maintaining the waste liquid in a supercritical or subcritical state of water in the presence of an oxidizing agent. Here, the hydrothermal oxidation reaction is a reaction in which a concentrate is oxidatively decomposed by an oxidation reaction in the presence of high-temperature, high-pressure water and an oxidizing agent in a supercritical or subcritical state. The supercritical state is a state of 374 ° C. or higher and 22 MPa or higher. The subcritical state refers to, for example, a state of 374 ° C. or more, 2.5 MPa or more and less than 22 MPa, or a state of 374 ° C. or less, 22 MPa or more, or a high temperature and high pressure state of less than 374 ° C. or less than 22 MPa close to a critical point.
[0017]
Such a hydrothermal oxidation reaction is performed in a hydrothermal reactor in a state where the waste liquid is mixed with an oxidizing agent, and the mixture undergoes a hydrothermal reaction inside the reactor. Air, oxygen, liquid oxygen, and hydrogen peroxide can be used as the oxidizing agent. The oxidizing agent may be supplied by being mixed with the mixed sludge of the material to be treated, or may be supplied as a multi-layer flow by using a supply pipe with a double pipe nozzle. If necessary, a catalyst, a neutralizing agent, and the like may be added. These may be mixed with the waste liquid or separately supplied to the reactor.
[0018]
The hydrothermal reactor used in the present invention is formed of a heat-resistant and pressure-resistant material so as to perform a hydrothermal reaction in a supercritical or subcritical state. When the supercritical or subcritical state is not reached only by the heat of reaction, an external heating means can be provided.
[0019]
Although the material of the hydrothermal reactor is not limited, a corrosion-resistant material such as Hastelloy, Inconel, or stainless steel is preferable. Preferably, the hydrothermal reactor is provided with a corrosion resistant liner. The corrosion-resistant liner is not particularly limited, and a corrosion-resistant liner having a gap between the corrosion-resistant liner and the pressure load wall can be used.
[0020]
The hydrothermal reactor can be provided with cooling means for cooling the reaction mixture before discharging it from the outlet. The cooling means is not particularly limited, but quenching water can be introduced into the reactor to cool it, and the inorganic salt can be dissolved to facilitate its discharge. In addition, water containing an acid or an alkali can be introduced into the reactor and cooled to neutralize the alkali or the acid. If the solid is very sticky, a mechanical removal device for removing the solid attached to the inner wall of the reactor can be provided. The mechanical removal device for removing solids is not particularly limited, but a substantially cylindrical scraper including a cutout window is preferable. In order to provide such a mechanism, a tubular reactor arranged substantially vertically is preferable as a reactor shape. A cylindrical, elliptical, or polygonal cylindrical reactor can be used as the shape of the cylindrical reactor, and the lower end portion can have a cone shape.
[0021]
Separation means for separating solids in the reaction fluid discharged from the hydrothermal reactor can be provided. The solid matter separation means is not particularly limited, and a container having an inlet for introducing a reaction fluid from a hydrothermal reactor and an outlet for discharging a fluid from which solids have been removed, and a container provided in the container and having the reaction fluid One provided with a means for removing and discharging the solid contained therein can be used. The solids separating means is desirably provided upstream of a valve for reducing the pressure of the processing fluid. By doing so, wear and blockage of the pressure reducing valve can be prevented.
[0022]
In the present invention, in the hydrothermal reaction step, when a hydrothermal oxidation reaction is performed in a supercritical or subcritical state by the above-described hydrothermal reactor, the organic matter of the reactant is oxidized by the oxidizing agent and finally becomes water. Decomposed into carbon dioxide.
[0023]
The means for starting the reaction by the hydrothermal reactor is not particularly limited. Usually, the reactor is preheated to around a predetermined reaction temperature at the start of the reaction. The preheating can be carried out by providing a heating device in the reactor, or by introducing heated water or air provided in a waste liquid and / or oxidant supply passage. Further, usually, water or an oxidizing agent is supplied to the reactor, and the reactor is pressurized to a predetermined pressure by a normally provided pressure regulating valve. After the temperature and pressure are adjusted to predetermined values, a fluid containing mixed sludge as a reactant is supplied to start a hydrothermal reaction. Organic substances are decomposed by the reaction, and heat of reaction is generated.
[0024]
The reaction fluid that has exited the hydrothermal reactor is subjected to cooling and gas-liquid separation, and then the pressure of the processing liquid and the processing gas are separately reduced and discharged. The finally generated water, gas, and solid are directly recovered for energy recovery, reused as a substance, or directly or additionally processed for disposal.
[0025]
【The invention's effect】
According to the present invention, in a state where the water-soluble polymer in the water-soluble polymer-containing waste liquid is insolubilized and precipitated in the form of a suspension, a hydrothermal oxidation reaction is performed to oxidatively decompose the polymer. The water-soluble polymer can be efficiently oxidized and decomposed by the hydrothermal oxidation reaction without increasing the size of the hydrothermal reactor, and the treatment can be performed stably and at a high level. Thus, it is possible to obtain a method and an apparatus for treating a wastewater containing a water-soluble polymer, which hardly generates carbon monoxide.
[0026]
BEST MODE FOR CARRYING OUT THE INVENTION
Hereinafter, embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a flowchart of a water-soluble polymer-containing waste liquid treatment apparatus according to an embodiment.
[0027]
In FIG. 1, 1 is a precipitation tank, 2 is a hydrothermal reactor, 3 is a reactor, 4 is an oxidant supply means, 5 is a cooler, and 6 is a gas-liquid separator. The precipitation tank 1 supplies the wastewater containing the water-soluble polymer from the line L1, supplies the neutralizing agent from the line L2, measures the pH with the pH adjuster 12 while stirring with the stirrer 11, and adjusts the supply amount of the pump P2. Is configured to neutralize. The hydrothermal reactor 2 has a supply unit 13 at the upper part of the reactor 3, the lower part of the reactor 3 is formed in a cone shape, has a scraper 14 inside, and a quench water supply pipe 15 opens at the lower part. I have.
[0028]
A line L3 having a high-pressure pump P1 for supplying waste liquid from the precipitation tank 1 is connected to a supply device 13 provided above the reactor 3 of the hydrothermal reactor 2. The supply device 13 is connected to a line L4 connected to oxidant supply means 4 for supplying an oxidant. The supply device 13 is mounted so as to supply a mixed flow of the oxidizing agent and the waste liquid to the reactor 3 as a downward flow. A line L5 communicates with the cooler 5 from the lower part of the hydrothermal reactor 4, and a line L7 communicates with the gas-liquid separator 6 from the cooler 5. A gas discharge path line L8 having a pressure reducing valve V1 and a liquid discharge path L9 having a pressure reducing valve V2 communicate with the outside of the system from the gas-liquid separator 6. The cooling device 5 is connected to a cooling water passage L6.
[0029]
In the water-soluble polymer-containing waste liquid treating apparatus, the water-soluble polymer-containing waste liquid is supplied from the line L1 to the precipitation tank 1, the neutralizing agent is supplied from the line L2, and the pH is adjusted by the pH adjuster 12 while stirring with the stirrer 11. Is measured, and the supply amount of the pump P2 is adjusted to neutralize the measured value of the pH of the pH adjuster 12 so as to be a predetermined value (for example, pH 5). As a result, the water-soluble polymer in the waste liquid becomes insoluble and precipitates in suspension, and the waste liquid becomes a suspension.
[0030]
The suspended waste liquid is sent from the line L3 to the supply device 13 of the hydrothermal reactor 2 by the high-pressure pump P1, where the oxidant (eg, air, hydrogen peroxide solution) sent from the oxidant supply means 4 through the line L4. The mixture is mixed, and the mixed stream is supplied to the reactor 3 in a downward flow to perform a hydrothermal reaction. Organic matter is oxidized and decomposed in the reactor 3 by a hydrothermal oxidation reaction in a supercritical or subcritical state of the water in the reactor 3. In this hydrothermal oxidation reaction, the polymer is precipitated in suspension, so the surface area of the resin is larger than that in a gel-like state. Is diffused, whereby the organic matter is completely oxidized to carbon dioxide with little reduction in reactivity, and the organic matter is prevented from being discharged without being decomposed.
[0031]
The salt is dissolved in the suspended waste liquid, but does not dissolve in the supercritical state, and is precipitated in a salt state. When quench water is supplied from the lower quench water supply pipe 15 in this state, a part of the water becomes liquid and the salt is dissolved. The salt attached to the inner wall of the reactor 3 is removed by the scraper 14. The reactants in the reactor 3 are introduced into the cooler 5 from the line L5, and are cooled by cooling water supplied from the cooling water passage L6. The cooled gas-liquid mixed fluid is introduced into the gas-liquid separator 6 from the line L7 to be separated into gas and liquid, and the processing gas is discharged from the gas discharge path L8 and the processing water is discharged from the liquid discharge path L9.
[0032]
In the above embodiment, the neutralization tank type is shown as the precipitation apparatus, but another type such as a line mixer type may be used.
[0033]
【Example】
Hereinafter, examples of the present invention will be described.
Example 1
The wastewater containing a water-soluble polymer was treated by the treatment apparatus of FIG. A water-soluble polymer-containing waste liquid discharged from a manufacturing process using a dry film resist as a waste liquid to be treated was neutralized with sulfuric acid in a precipitation tank 3 with stirring to precipitate and suspend the dissolved polymer. Then, the waste liquid in which the polymer is suspended is supplied to the reactor 3 of the hydrothermal reactor 2 and air is supplied as an oxidizing agent. The reaction temperature is 650 ° C., the reaction pressure is 23.4 MPa, and the reaction time is 10 seconds. Oxidized. As a result, the hydrothermal oxidation treatment proceeded stably. The properties of the processing liquid and the processing gas were as follows, and organic substances could be almost completely decomposed.
Treated water TOC: <1 mg / L
Processing gas CO: <2 ppm
[0034]
Comparative Example 1
The water-soluble polymer-containing waste liquid discharged from the manufacturing process using a dry film resist was subjected to hydrothermal oxidation treatment under the same conditions as in Example 1 without pretreatment. As a result, during the hydrothermal oxidation treatment, a high concentration of carbon monoxide was detected in the treated gas. The properties of the treatment liquid and the treatment gas were also as follows, indicating that organic substances could not be completely decomposed and oxidation was incomplete.
Treated water TOC: 5mg / L
Processing gas CO: 200 to 900 ppm
[Brief description of the drawings]
FIG. 1 1 precipitation tank 2 hydrothermal reactor 3 reactor 4 oxidant supply means 5 cooler 6 gas-liquid separator 11 stirrer 12 pH adjuster 13 supply device 14 scraper 15 quench water supply pipe

Claims (5)

水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して、懸濁状に析出させる析出工程と、
懸濁状の廃液を水熱反応装置に供給する供給工程と、
水熱反応装置において水および酸化剤の存在下に、水の超臨界または亜臨界状態で水熱酸化反応を行い有機物を酸化分解する水熱反応工程と
を含む水溶性ポリマー含有廃液の処理方法。
A precipitation step of insolubilizing the water-soluble polymer in the water-soluble polymer-containing waste liquid and precipitating it in suspension,
A supply step of supplying the suspended waste liquid to the hydrothermal reactor,
A hydrothermal reaction step of performing a hydrothermal oxidation reaction in a supercritical or subcritical state of water in the presence of water and an oxidizing agent in a hydrothermal reactor to oxidatively decompose organic substances.
水溶性ポリマーの不溶化が中和またはエステル化である請求項1記載の方法。The method according to claim 1, wherein the insolubilization of the water-soluble polymer is neutralization or esterification. 水溶性ポリマー含有廃液がレジスト含有廃液である請求項1または2記載の方法。3. The method according to claim 1, wherein the water-soluble polymer-containing waste liquid is a resist-containing waste liquid. 水溶性ポリマー含有廃液中の水溶性ポリマーを不溶化して、懸濁状に析出させる析出装置と、
懸濁状の廃液を水熱反応装置に供給する供給装置と、
懸濁状の廃液を導入し水および酸化剤の存在下に、水の超臨界または亜臨界状態で水熱酸化反応を行い有機物を酸化分解する水熱反応装置と
を含む水溶性ポリマー含有廃液の処理装置。
A precipitation apparatus for insolubilizing a water-soluble polymer in a water-soluble polymer-containing waste liquid and depositing the suspension in suspension,
A supply device for supplying the suspended waste liquid to the hydrothermal reactor,
A water-soluble polymer-containing waste liquid containing a suspended liquid waste liquid and a hydrothermal reactor that performs a hydrothermal oxidation reaction in a supercritical or subcritical state of water in the presence of water and an oxidizing agent to oxidatively decompose organic substances. Processing equipment.
析出装置が中和またはエステル化により水溶性ポリマーを不溶化する装置である請求項4記載の装置。The apparatus according to claim 4, wherein the precipitation apparatus is an apparatus for insolubilizing the water-soluble polymer by neutralization or esterification.
JP2002265825A 2002-09-11 2002-09-11 Method and equipment for treating water-soluble polymer-containing waste liquid Pending JP2004097997A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008056671A1 (en) * 2006-11-09 2008-05-15 Tokuyama Corporation Method of neutralizing developer waste liquid containing tetraalkylammonium hydroxide
JP2009125710A (en) * 2007-11-27 2009-06-11 Panasonic Electric Works Co Ltd Decomposition apparatus
US7580222B2 (en) 2004-06-18 2009-08-25 Headway Technologies, Inc. Thin-film magnetic head, a head gimbal assembly and hard disk drive
JP2012106244A (en) * 2012-01-30 2012-06-07 Panasonic Corp Decomposition apparatus

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7580222B2 (en) 2004-06-18 2009-08-25 Headway Technologies, Inc. Thin-film magnetic head, a head gimbal assembly and hard disk drive
WO2008056671A1 (en) * 2006-11-09 2008-05-15 Tokuyama Corporation Method of neutralizing developer waste liquid containing tetraalkylammonium hydroxide
JP5041297B2 (en) * 2006-11-09 2012-10-03 株式会社トクヤマ Method for neutralizing developer wastewater containing tetraalkylammonium hydroxide
JP2009125710A (en) * 2007-11-27 2009-06-11 Panasonic Electric Works Co Ltd Decomposition apparatus
JP2012106244A (en) * 2012-01-30 2012-06-07 Panasonic Corp Decomposition apparatus

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