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JP4098653B2 - Purification method and purification body of contaminated ground by freezing and suction - Google Patents
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JP4098653B2 - Purification method and purification body of contaminated ground by freezing and suction - Google Patents

Purification method and purification body of contaminated ground by freezing and suction Download PDF

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Publication number
JP4098653B2
JP4098653B2 JP2003091932A JP2003091932A JP4098653B2 JP 4098653 B2 JP4098653 B2 JP 4098653B2 JP 2003091932 A JP2003091932 A JP 2003091932A JP 2003091932 A JP2003091932 A JP 2003091932A JP 4098653 B2 JP4098653 B2 JP 4098653B2
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underground
ground
suction
contaminated
freezing
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JP2004298673A (en
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譲 伊藤
雅史 嘉門
和昭 日置
忠明 野村
常戈 近藤
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Kinjo Rubber Co Ltd
Seiken Co Ltd
Fudo Tetra Corp
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Kinjo Rubber Co Ltd
Seiken Co Ltd
Fudo Tetra Corp
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  • Investigation Of Foundation Soil And Reinforcement Of Foundation Soil By Compacting Or Drainage (AREA)
  • Processing Of Solid Wastes (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、有機化合物などで汚染された汚染地盤の浄化方法及び浄化体に関し、詳しくは汚染物質が原液状態で存在する汚染源からの原液の吸引とその周辺の高濃度汚染地下水の吸引を行う汚染地盤の浄化方法及び浄化体に関するものである。
【0002】
【従来の技術】
半導体製造工場などの洗浄工程において多量に使用されるトリクロロエチレン等の揮発性有機化合物は、漏れなどにより土壌又は地下水を汚染する可能性があり、この場合、工場跡地の再利用の障害となったり、地下水の利用が制限されたりする問題がある。トリクロロエチレンなどの高密度非水溶性液体(DNAPL)は、その密度が水よりも重く、水に溶け難いため、地下水面下の地下深部に溜まり易い。また、地下深部に溜まったDNAPLは地下水に徐々に溶解して、その周辺には高濃度に汚染された地下水帯を形成する。
【0003】
地下深部に溜まったDNAPLなどの汚染源を積極的に取り除く方法としては、地下水揚水法が一般的である。この方法は、DNAPL原液を地下水と共に吸引、除去する。しかし、このような方法は、汚染源がある程度特定されたとしても、揚水井からはDNAPL原液よりも密度の小さな水ばかりが汲み出され、その後に周囲から地下水が補給されることを繰り返すため、水ばかりが大量に汲み上げられることになる。従って、DNAPL原液を効率的に吸引、除去することはできない。地下水揚水を長時間に亘り行なえば、DNAPL原液が徐々に水に溶解するため吸引、除去は可能となるものの、その効率はDNAPL原液の溶解速度に依存するため、吸引、除去に長時間を要することになり、処理コストが膨大になるという問題がある。
【0004】
一方、特許文献1の特開平11−169837号公報には、汚染地盤領域を凍結する工程に続き、その後該地盤から土壌内ガスを吸引し汚染蒸気を抽出する汚染地盤の浄化方法が開示されている。しかし、この汚染地盤の浄化方法は、地下水位以上の汚染地盤の浄化を目的としたものであり、地下水位以下の汚染地盤の浄化を目的としたものではない。更に汚染地盤を凍結させる目的は、凍結により土壌微粒子間に微小な撹乱を起こし、その後不飽和地盤中に存在するガス状汚染物質の吸引効果を高めるようにしたものであり、凍結地盤中に液状の汚染物質を残存せしめ、これを吸引、除去するものではない。
【0005】
【特許文献1】
特開平11−169837号公報(請求項1、段落番号0010)
【0006】
【発明が解決しようとする課題】
従って、本発明の目的は、地下水位以下の土壌中に存在する原液状態の汚染物質及びその周辺の高濃度汚染地下水を効率的に吸引、除去し、処理時間の短縮及び処理コストの低減を図る汚染地盤の浄化方法及び浄化体を提供することにある。
【0007】
【課題を解決するための手段】
かかる実情において、本発明者等は鋭意検討を行なった結果、水とDNAPL原液の凝固点の相違から、凍結地盤中においてDNAPLを液状物として存在させることができ、この凍結地盤中の液状物を吸引管などの吸引手段で吸引、除去すれば、極めて容易且つ効率的であり、処理時間の短縮と処理コストの低減が図れること等を見出し、本発明を完成するに至った。
【0008】
すなわち、本発明は、地下水位以下の土壌中に汚染物質が存在する汚染地盤に適宜のピッチで地中凍結管を、該地中凍結管間に適宜のピッチで地中第1吸引体を、該地中凍結管近傍に地中第2吸引体それぞれ配設する浄化体配設工程と、汚染地盤領域を凍結する凍結工程と、該凍結状態を維持したまま該地中第1吸引体から液状汚染物質を吸引する原液吸引工程と、汚染地盤領域を解凍する工程と、解凍された汚染地盤領域の汚染地下水を該地中第1吸引体から空気又は水を供給して該地中第2吸引体から汚染地下水を吸引するか、又は該地中第2吸引体から空気又は水を供給して該地中第1吸引体から汚染地下水を吸引する汚染地下水吸引工程を行なう汚染地盤の浄化方法を提供するものである。本発明によれば、地下水位以下の飽和地盤を、氷点以下で且つ汚染物質の凝固点以上の温度で凍結するため、間隙水が凍結状態の地盤中にDNAPLを液状物として存在させることができる。また、凍結で生じる吐き出し効果で、間隙水以外の汚染物質液状物等は地中第1吸引体側に押しやられ、該汚染物質液状物はこの地中第1吸引体で容易に且つ効率的に吸引、除去できる。このため、浄化処理時間の短縮と処理コストの低減が図れる。また、汚染地盤解凍後は、原液周辺の汚染物質が高濃度に溶解した地下水を地中第1吸引体で容易且つ効率的に吸引、除去できる。また、解凍後の凍結管回りは特に汚染物質が高濃度に溶解した汚染地下水が存在するため、この汚染地下水を凍結管近傍に配設された地中第2吸引体から容易且つ効率的に吸引、除去できる。また、一方の地中吸引体から空気又は水を供給し、他方の地中吸引体から汚染地下水を吸引するため、押出しと吸引の両作用により、浄化効率を一層高めることができる。
【0012】
また、本発明は、地下水位以下の土壌中に汚染物質が存在する汚染地盤に構築される浄化体であって、適宜のピッチで配設される地中凍結管と、該地中凍結管間に配設され凍結地盤中に存在する液状汚染物質を吸引する地中第1吸引体と、該地中凍結管近傍に配設され凍結地盤中に存在する液状汚染物質を吸引する地中第2吸引体を備え、該地中第1吸引体及び地中第2吸引体は、空気又は水を供給する供給体を兼用するものである浄化体を提供するものである。また、本発明は、前記地中第1吸引体及び地中第2吸引体は、吸引管又は柱状ドレーンである前記浄化体を提供するものである。本発明の浄化体によれば、前記浄化方法の発明を確実に実施できる。
【0013】
【発明の実施の形態】
次に、本発明の第1の実施の形態における汚染地盤の浄化方法及び浄化体を図1及び図2を参照して説明する。図1は本実施の形態例における浄化体の概略断面図、図2は本実施の形態例における浄化体の概略平面図である。本実施の形態例の浄化体10は、地下水位(W.L.)以下の土壌中に汚染物質が存在する汚染地盤に構築されるものであって、適宜のピッチで配設される地中凍結管1と、地中凍結管1、1間に適宜のピッチで配設される地中第1吸引体2を備える。また、地上には、不図示の冷凍機、冷媒循環ポンプ及び配管などの冷凍手段、真空ポンプなどの吸引手段及び汚染物質分解手段などが設置される。
【0014】
本例の浄化体10が構築される汚染地盤9としては、地下水位以下の飽和状態の地盤中に汚染物質7が存在するものであれば、特に制限されず、その地盤は砂質、粘土層、互層等の自然地盤や埋め立てられた人工地盤などが挙げられる。また、汚染物質7としては、特に制限されず、例えばその密度が水よりも重く、水に溶け難く且つ凝固点が−10℃以下の高密度非水溶性液体(DNAPL)が挙げられる。具体的には凝固点が−86℃のトリクロロエチレン、凝固点が−22℃のテトラクロロエチレン、凝固点が−57℃のジクロロエチレン、凝固点が−97℃のジクロロエタン等である。DNAPLはその密度が水よりも重く、水に溶け難いため、地下水面下の地下深部71に溜まり易く、また、飽和地盤を氷点以下で且つDNAPLの凝固点以上の温度で凍結した際、凍結地盤中に液状物で存在する。
【0015】
地中凍結管1は、汚染地盤領域8を凍結させるものであり、汚染地盤領域8にほぼ均等に配設される。地中凍結管1は公知の地中凍結工法で用いるものと同様のものが用いられる。公知の地中凍結工法としては、ブラインと呼ばれる冷媒を冷凍機を使って−20℃〜−30℃に冷却し、これを地盤中に埋設した凍結管1に循環ポンプで送り込んで地盤を冷却する凍結工法が挙げられる。地中凍結管1の本数は、凍結設備能力、凍土温度等により適宜決定される。汚染地盤領域8は、汚染物質の原液7が存在する領域(図2中、実線の範囲)を少なくとも含むものであり、本例では図2中、二点鎖線で囲む領域8を言う。
【0016】
地中第1吸引体2としては、地上の真空ポンプなどの吸引手段に接続される地中に埋設される構造体であり、例えば吸引管又は柱状ドレーンが挙げられる。本例では側周面に多数の通水穴23が付設された有穴中空管21であり、汚染土壌の各所から汚染物質を吸引し易いようにすると共に、中空部にはヒーター22を設け、凍結工程における水分の凍結による通水穴23の閉塞を防止している。また、通水穴23周りは不図示の不織布などで覆うことが、通水穴23の目詰まりを防止することができる点で好ましい。地中第1吸引体2として柱状ドレーンを用いる場合も、内部ヒーター22や不織布などを設けることが好ましい。柱状ドレーンとしては、プラスチックボードドレーンが挙げられる。地中第1吸引体2の配設位置としては、特に制限されないが、図2に示すように、汚染地盤領域8であって且つ凍結管1の間、すなわち隣接する複数の凍結管1のほぼ中間位置に配設させることが、凍結で生じる吐き出し効果で、地中凍結管1から遠ざかる方向へ押しやられた間隙水以外の汚染物質原液を容易に且つ効率的に吸引、除去できる点で好ましい。
【0017】
本第1の実施の形態において、この浄化体10を用いて汚染地盤を浄化する方法を以下に説明する。浄化体配設工程は、事前の地盤調査により、汚染物質及び汚染地盤領域を特定した後、行なわれるものである。すなわち、地下水位以下の土壌中に汚染物質7が存在する汚染地盤9に適宜のピッチで地中凍結管1と地中第1吸引体2を配設する。この際、地上の冷凍機や真空ポンプの設置も行なう。
【0018】
次いで、地下水位以下の汚染地盤領域8を凍結すると共に該汚染物質を液状物で保持する凍結工程を行う。凍結地盤の温度は、汚染物質の凝固点により決定され、氷点以下で且つ汚染物質の凝固点以上の温度である。汚染地盤領域8をこのような凍結地盤とすれば、凍結地盤中に原液の汚染物質7を液状物として存在させることができる。なお、図1中、二点鎖線で囲まれた範囲5が凍土、符号6が不透水層である。
【0019】
凍結工程においては、地中第1吸引体2のヒーター22を可動させ、有穴中空管21の通水穴23や中空部が凍結により閉塞しないようにしておく。また、凍結工程において、地盤の間隙水が徐々に凍結すると、吐き出し現象が生じる。この現象は、凍結の際、間隙水以外の液状物等が地中凍結管1から遠ざかる現象であり、自然界で見られるものである。これにより、汚染物質である原液は自然に地中第1吸引体2に集まるようになる。この状態で原液吸引工程に入る。なお、地中第1吸引体2におけるヒーター22の可動は原液吸引工程で可動させてもよい。
【0020】
原液吸引工程は、該凍結状態を維持したまま地中第1吸引体2から液状汚染物質7を吸引する工程である。地上にある吸引手段を可動させると、地中第1吸引体2の通水穴23から汚染物質の原液が吸引される。この場合、地中第1吸引体2周りには汚染物質の原液が集まっており、吸引効率が高められる。図2中、矢印は汚染物質原液の流れを示す。
【0021】
この第1の実施の形態例における汚染地盤の浄化方法及び浄化体によれば、地下水位以下の飽和地盤を、氷点以下で且つ汚染物質の凝固点以上の温度で凍結するため、間隙水が凍結状態の地盤中にDNAPLを液状物として存在させることができる。また、凍結で生じる吐き出し効果で、間隙水以外の液状物等は地中第1吸引体2側に押しやられ、液状物は地中第1吸引体2により容易に且つ効率的に吸引、除去できる。このため、浄化処理時間の短縮と処理コストの低減が図れる。また、凍結地盤は一時的なものであり、解凍後、2次汚染の心配はない。また、原液の周辺の高濃度汚染地下水は解凍後の地盤中に存在することになるが、これは更に、地中第1吸引体2で吸引除去することができる。
【0022】
次に、第2の実施の形態における汚染地盤の浄化方法及び浄化体を図3及び図4を参照して説明する。図3は本実施の形態例における浄化体の解凍後の状態を示す概略断面図、図4は本実施の形態例の浄化体における概略平面図である。図3及び図4において、図1及び図2と同一構成要素には同一符号を付して、その説明を省略し異なる点について主に説明する。すなわち、第2の実施の形態における浄化体10aは、第1の実施の形態における浄化体10に対して、地中凍結管1の近傍に地中第2吸引体3を更に配設させ、これにより、解凍後の高濃度汚染地下水の吸引効率を高めるようにしたものである。
【0023】
地中第2吸引体3は地中凍結管1の近傍に配設される点を除いて、地中第1吸引体2と同様のものである。地中凍結管1の近傍とは、地中凍結管1に近接した形態から、地中凍結管1から少し離れた形態までを含む意味であるが、地中凍結管1に近接した形態とすることが、例えば地中第2吸引体3から給水し、汚染地下水を押出し、地中第1吸引体2から吸引除去する効率が向上する点で好ましい。
【0024】
図3及び図4は、汚染地盤領域の解凍後の状態を示す。解凍工程としては、特に制限されず、自然放置で解凍し常温とする方法、不図示の地中加熱管で急速加熱する方法又は地中凍結管1に温水を流し解凍する方法などが挙げられる。このうち、地中凍結管1に温水を流し解凍する方法が簡易且つ迅速な解凍が行なえる点で好ましい。図3及び図4は、原液の周辺の高濃度汚染地下水が解凍後の地盤9中に存在する状況を示すものである。そして、この場合、地中凍結管1の近傍にある地中第2吸引体3を水供給体として使用し、地中第1吸引体2を汚染地下水吸引体として使用する。すなわち、地中第2吸引体3から水を供給すると共に、地中第1吸引体2から高濃度汚染地下水を吸引すれば、循環系の流路が形成され、高濃度汚染地下水を容易且つ効率的に除去できる。なお、地中第2吸引体3は不図示の地上水供給手段に接続されており、図4中、矢印は汚染地下水の流れである。また、地中第2吸引体3に供給される水に代えて、圧縮空気を用いてもよい。圧縮空気を用いた場合も、同様に地中第2吸引体3から地中第1吸引体2に至る汚染地下水の流路が形成される。
【0025】
第2の実施の形態における汚染地盤の浄化方法によれば、地中第2吸引体3から空気又は水を供給し、地中第1吸引体2から汚染地下水を吸引するため、押出しと吸引の両作用により、浄化効率を一層高めることができる。特に地中凍結管を暖めながら解凍する場合、該地中凍結管に近接する地盤の開いた間隙から、水や空気を供給できるため、工期が短縮すると共に循環が円滑に行われ浄化効率が向上する。
【0026】
また、第2の実施の形態における汚染地盤の浄化方法の変形例として、地中第1吸引体2を水供給体として使用し、地中第2吸引体3を汚染地下水吸引体として使用することもできる。すなわち、地中第1吸引体2から水を供給すると共に、地中第2吸引体3から汚染地下水を吸引すれば、同様に循環系の流路が形成され、汚染地下水を容易且つ効率的に除去できる。この場合、凍結の際、前記吐き出し効果とは逆に、地下水が地中凍結管1に移動する凍上における水分移動現象を利用できる。この現象は地盤の間隙水が徐々に凍結しアイスレンズと呼ばれる氷層が形成され、更に温度低下が進行すると、未凍結部分から凍結面に向かって水が補給される自然現象であり、汚染地下水が地中凍結管1に集まり易くなる。従って、解凍後、この集まった汚染地下水を直ちに地中第2吸引体3で吸引できると共に、更に供給水で押出すため浄化効率が一層向上する。この第2の実施の形態の変形例においても、地中第1吸引体2から供給される水に代えて、圧縮空気を使用することができる。
【0027】
【実施例】
次に、実施例を挙げて本発明を更に具体的に説明するが、これは単に例示であって、本発明を制限するものではない。
実施例1
(模擬汚染土壌の作製)
下記組成の模擬汚染土壌を作製し、これを下記有底円筒容器に充填した。充填量は容器の底から100mmの厚みまで詰めた。模擬汚染土壌には外径7mm×内径5mm、先端を充填接着剤で閉じると共に、周面には底部から90mmまで5mm間隔で2列合計36個の内径1mmの細孔を空けた吸引管を配設した。また、吸引管の内側には径0.1mmのコンスタンタン製ヒーター線を沿わせて、吸引時に水滴の凍結による吸引管の閉塞を防いだ。更に、砂粒子の混入を防止するため、吸引管の外周面を不織布で巻いた。
【0028】
・模擬汚染土壌;密度1.76g/cm(25℃)、凝固点−43℃のフッ素系不活性液体180gを配合すると共に水によって飽和した珪砂5号
・有底円筒容器;筒状部は内径100mmのアクリル製樹脂、底板は厚さ2mmのアルミニウム板で作製した上部開口容器
【0029】
(浄化実験)
・−15℃に調整された冷媒バス中で模擬汚染土壌全体を凍結させた。また、吸引管に投入されたヒーターをON状態にした。模擬汚染土壌の表面から2cmの深部に設置した温度センサーの読みと、表面の浮遊水の凍結を確認した後、アスピレーターを稼動させ吸引管を作動させた。30分間の吸引の結果、模擬汚染土壌に添加したフッ素系不活性液体180gの内、124gが吸引除去された。
【0030】
【発明の効果】
本発明によれば、地下水位以下の飽和地盤を凍結するため、間隙水が凍結状態の地盤中にDNAPLを液状物として存在させることができる。また、凍結で生じる吐き出し効果で、間隙水以外の液状物等は地中第1吸引体側に押しやられ、液状物はこの地中第1吸引管で容易に且つ効率的に吸引、除去できる。このため、浄化処理時間の短縮と処理コストの低減が図れる。
本発明によれば、汚染地盤解凍後は、原液周辺の汚染物質が高濃度に溶解した地下水を地中第1吸引体で容易且つ効率的に吸引、除去できる。
本発明によれば、解凍後の凍結管回りは特に汚染物質が高濃度に溶解した汚染地下水が存在するため、この汚染地下水を凍結管近傍に配設された地中第2吸引体から容易且つ効率的に吸引、除去できる。
本発明によれば、一方の地中吸引体から空気又は水を供給し、他方の地中吸引体から汚染地下水を吸引すれば、押出しと吸引の両作用により、浄化効率を一層高めることができる。
本発明によれば、前記浄化方法の発明を確実に実施できる。
【図面の簡単な説明】
【図1】第1の実施の形態例における浄化体の概略断面図である。
【図2】第1の実施の形態例における浄化体の概略平面図である。
【図3】第2の実施の形態例における浄化体の解凍後の状態を示す概略断面図である。
【図4】第2の実施の形態例における浄化体の概略平面図である。
【符号の説明】
1 地中凍結管
2 地中第1吸引体
3 地中第2吸引体
5 凍土
6 不透水層
7 汚染物質(原液)
8 汚染地盤領域
9 汚染地盤
10、10a 浄化体
21、31 有穴中空管
22、32 ヒーター
23、33 通水穴
W.L. 地下水位
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a purification method and a purification body for contaminated ground contaminated with an organic compound and the like, and more particularly, contamination by sucking a raw solution from a pollution source in which the pollutant exists in a raw liquid state and a high concentration contaminated groundwater around it. The present invention relates to a ground purification method and a purification body.
[0002]
[Prior art]
Volatile organic compounds such as trichlorethylene, which are used in large quantities in the cleaning process of semiconductor manufacturing plants, etc., may contaminate the soil or groundwater due to leakage, etc. There is a problem that the use of groundwater is restricted. High density water-insoluble liquids (DNAPL) such as trichlorethylene are heavier than water and difficult to dissolve in water, so they tend to accumulate in the deep underground below the water table. In addition, DNAPL accumulated in the deep underground is gradually dissolved in the groundwater, and a highly contaminated groundwater zone is formed around it.
[0003]
As a method for positively removing a contamination source such as DNAPL accumulated in the deep underground, a groundwater pumping method is generally used. This method sucks and removes the DNAPL stock solution together with the groundwater. However, in such a method, even if the source of contamination is specified to some extent, only water with a density lower than that of the DNAPL stock solution is pumped out from the pumping well, and then groundwater is replenished from the surroundings. Only a lot will be pumped up. Therefore, the DNAPL stock solution cannot be efficiently aspirated and removed. If the groundwater pumping is performed for a long time, the DNAPL stock solution will gradually dissolve in water, so suction and removal are possible. However, the efficiency depends on the dissolution rate of the DNAPL stock solution, so a long time is required for suction and removal. As a result, there is a problem that the processing cost becomes enormous.
[0004]
On the other hand, Japanese Patent Application Laid-Open No. 11-169837 of Patent Document 1 discloses a method for purifying a contaminated ground, which is followed by a step of freezing the contaminated ground area, and then sucking in the soil gas from the ground and extracting the contaminated vapor. Yes. However, this purification method of contaminated ground is intended to purify contaminated ground above the groundwater level, and is not intended to purify contaminated ground below the groundwater level. The purpose of freezing the contaminated ground is to cause minute disturbances between the soil fine particles by freezing, and then to enhance the suction effect of gaseous pollutants present in the unsaturated ground. It is not intended to leave the contaminants, but to suck and remove them.
[0005]
[Patent Document 1]
JP-A-11-169837 (Claim 1, paragraph number 0010)
[0006]
[Problems to be solved by the invention]
Accordingly, an object of the present invention is to efficiently suck and remove undiluted pollutants existing in the soil below the groundwater level and surrounding high-concentration contaminated groundwater, thereby shortening the treatment time and the treatment cost. It is providing the purification method and purification body of a contaminated ground.
[0007]
[Means for Solving the Problems]
Under such circumstances, the present inventors have conducted intensive studies, and as a result, due to the difference in freezing point between water and DNAPL stock solution, DNAPL can be present as a liquid substance in the frozen ground, and the liquid substance in the frozen ground is aspirated. It has been found that if suction and removal is performed with a suction means such as a tube, it is extremely easy and efficient, and the processing time can be reduced and the processing cost can be reduced. Thus, the present invention has been completed.
[0008]
That is, the present onset Ming, the ground frozen tube at an appropriate pitch in Contaminated Land the presence of contaminants in the following soil groundwater level, the ground first suction body at an appropriate pitch between during該地cryotubes a purifier disposed step of respectively disposing the ground second suction member in the vicinity freezing tube該地, a freezing step of freezing the contaminated soil region, a first suction member in該地while keeping the frozen state A raw solution suction step for sucking liquid contaminants from, a step of thawing the contaminated ground region, and supply of air or water from the first suction body to the ground for the contaminated ground water of the thawed contaminated ground region. 2. Purification of contaminated ground in which contaminated groundwater is aspirated by sucking contaminated groundwater from the suction body or supplying air or water from the second suction body in the ground to suck contaminated groundwater from the first suction body in the ground A method is provided. According to the present invention, since the saturated ground below the groundwater level is frozen at a temperature below the freezing point and above the freezing point of the contaminant, DNAPL can be present as a liquid in the ground where the pore water is frozen. In addition, due to the spout effect caused by freezing, liquid substances such as pollutants other than pore water are pushed toward the first suction body in the ground, and the liquid contaminants are sucked easily and efficiently by the first suction body in the ground. Can be removed. For this reason, the purification processing time can be shortened and the processing cost can be reduced. In addition, after thawing the contaminated ground, the groundwater in which the contaminants around the undiluted solution are dissolved at a high concentration can be easily and efficiently sucked and removed by the first suction body in the ground. In addition, since there is contaminated groundwater around the freezing pipe after thawing, in particular, the contaminated groundwater is dissolved in a high concentration. This contaminated groundwater is easily and efficiently sucked from the underground second suction body arranged near the freezing pipe. Can be removed. Moreover, since air or water is supplied from one underground suction body and contaminated groundwater is sucked from the other underground suction body, the purification efficiency can be further enhanced by both the action of extrusion and suction.
[0012]
Further, the present invention is a purification body constructed in a contaminated ground in which contaminants exist in the soil below the groundwater level, between the underground freezing pipes arranged at an appropriate pitch, and the underground freezing pipe A first underground suction body for sucking liquid pollutants existing in the frozen ground, and a second underground for sucking liquid pollutants present in the frozen ground disposed near the underground freezing pipe. a suction member, the first suction member and the ground second suction member in該地is to provide a purifier in which also serves as a supplying member for supplying air or water. Further, the present invention, the ground first suction member and the ground second suction member is to provide the purifier is suction tube or columnar drain. According to the purification body of the present invention, the invention of the purification method can be reliably implemented.
[0013]
DETAILED DESCRIPTION OF THE INVENTION
Next, the purification method and purification body of the contaminated ground in the first embodiment of the present invention will be described with reference to FIGS. FIG. 1 is a schematic cross-sectional view of a purification body in the present embodiment, and FIG. 2 is a schematic plan view of the purification body in the present embodiment. The purification body 10 according to the present embodiment is constructed in a contaminated ground in which contaminants exist in the soil below the groundwater level (WL), and the underground freezing pipe 1 disposed at an appropriate pitch. And the underground first suction body 2 disposed at an appropriate pitch between the underground freezing tubes 1 and 1. On the ground, a refrigerator (not shown), a refrigeration means such as a refrigerant circulation pump and piping, a suction means such as a vacuum pump, and a pollutant decomposition means are installed.
[0014]
The contaminated ground 9 in which the purification body 10 of this example is constructed is not particularly limited as long as the pollutant 7 is present in a saturated ground below the groundwater level, and the ground is sandy, clay layer , Natural ground such as alternate layers and landfilled artificial ground. The contaminant 7 is not particularly limited, and examples thereof include a high density water-insoluble liquid (DNAPL) whose density is heavier than water, hardly soluble in water, and has a freezing point of −10 ° C. or lower. Specifically, trichloroethylene having a freezing point of −86 ° C., tetrachloroethylene having a freezing point of −22 ° C., dichloroethylene having a freezing point of −57 ° C., dichloroethane having a freezing point of −97 ° C., and the like. Since DNAPL is heavier than water and difficult to dissolve in water, it tends to accumulate in the deep underground part 71 below the groundwater surface, and when the saturated ground is frozen below the freezing point and above the freezing point of DNAPL, Exists in liquid form.
[0015]
The underground freezing pipe 1 freezes the contaminated ground region 8 and is disposed almost uniformly in the contaminated ground region 8. The underground freezing tube 1 is the same as that used in a known underground freezing method. As a known underground freezing method, a refrigerant called brine is cooled to −20 ° C. to −30 ° C. using a refrigerator, and this is sent to the freezing pipe 1 embedded in the ground with a circulation pump to cool the ground. Freezing method is mentioned. The number of underground freezing pipes 1 is appropriately determined according to freezing equipment capacity, frozen soil temperature, and the like. The contaminated ground region 8 includes at least a region (range of solid line in FIG. 2) where the stock solution 7 of contaminant is present, and in this example, refers to a region 8 surrounded by a two-dot chain line in FIG.
[0016]
The underground first suction body 2 is a structure embedded in the ground connected to suction means such as a vacuum pump on the ground, and examples thereof include a suction pipe or a columnar drain. In this example, it is a perforated hollow tube 21 provided with a large number of water passage holes 23 on the side peripheral surface, and it is easy to suck contaminants from various places of the contaminated soil, and a heater 22 is provided in the hollow portion. Further, the water passage hole 23 is prevented from being blocked by freezing of water in the freezing step. Further, it is preferable that the periphery of the water passage hole 23 is covered with a non-illustrated nonwoven fabric or the like because clogging of the water passage hole 23 can be prevented. Even when a columnar drain is used as the underground first suction body 2, it is preferable to provide an internal heater 22 or a nonwoven fabric. An example of the columnar drain is a plastic board drain. The arrangement position of the underground first suction body 2 is not particularly limited. However, as shown in FIG. 2, as shown in FIG. 2, in the contaminated ground region 8 and between the freezing tubes 1, that is, substantially between the adjacent freezing tubes 1. It is preferable to dispose at an intermediate position because the discharge effect caused by freezing can be easily and efficiently aspirated and removed from the pollutant stock solution other than pore water pushed away from the underground freezing tube 1.
[0017]
In the first embodiment, a method for purifying the contaminated ground using the purification body 10 will be described below. A purification body arrangement | positioning process is performed after specifying a pollutant and a contamination ground area | region by a prior ground investigation. That is, the underground freezing pipe 1 and the underground first suction body 2 are arranged at an appropriate pitch on the contaminated ground 9 where the contaminant 7 exists in the soil below the groundwater level. At this time, a ground refrigerator and a vacuum pump are also installed.
[0018]
Next, a freezing step is performed in which the contaminated ground region 8 below the groundwater level is frozen and the contaminant is held in a liquid state. The temperature of the frozen ground is determined by the freezing point of the pollutant, and is a temperature below the freezing point and above the freezing point of the pollutant. If the contaminated ground region 8 is such a frozen ground, the stock contaminant 7 can be present as a liquid in the frozen ground. In FIG. 1, a range 5 surrounded by a two-dot chain line is frozen soil, and a reference numeral 6 is an impermeable layer.
[0019]
In the freezing process, the heater 22 of the underground first suction body 2 is moved so that the water passage hole 23 and the hollow part of the hollow hollow tube 21 are not blocked by freezing. Further, in the freezing process, when the pore water in the ground is gradually frozen, a discharge phenomenon occurs. This phenomenon is a phenomenon in which liquid substances other than pore water move away from the underground freezing pipe 1 during freezing and are found in nature. As a result, the stock solution that is a contaminant is naturally collected in the first suction body 2 in the ground. In this state, the stock solution suction process is started. The heater 22 in the underground first suction body 2 may be moved in the stock solution suction step.
[0020]
The stock solution suction step is a step of sucking the liquid contaminant 7 from the underground first suction body 2 while maintaining the frozen state. When the suction means on the ground is moved, the stock solution of the pollutant is sucked from the water passage hole 23 of the underground first suction body 2. In this case, a stock solution of contaminants is collected around the first suction body 2 in the ground, and suction efficiency is improved. In FIG. 2, the arrows indicate the flow of the pollutant concentrate.
[0021]
According to the contaminated ground purification method and purification body in the first embodiment, the saturated ground below the groundwater level is frozen at a temperature below the freezing point and above the freezing point of the pollutant. DNAPL can be present as a liquid in the ground. Further, due to the discharge effect generated by freezing, liquid materials other than pore water are pushed to the underground first suction body 2 side, and the liquid materials can be easily and efficiently sucked and removed by the underground first suction body 2. . For this reason, the purification processing time can be shortened and the processing cost can be reduced. Also, the frozen ground is temporary and there is no concern of secondary contamination after thawing. Moreover, although the high concentration contaminated groundwater around the undiluted solution exists in the ground after thawing, this can be further removed by suction with the underground first suction body 2.
[0022]
Next, the contaminated ground purification method and purification body in the second embodiment will be described with reference to FIGS. FIG. 3 is a schematic cross-sectional view showing a state after the thawing of the purifier in the present embodiment, and FIG. 4 is a schematic plan view of the purifier in the present embodiment. 3 and 4, the same components as those in FIGS. 1 and 2 are denoted by the same reference numerals, and the description thereof will be omitted and different points will be mainly described. That is, the purification body 10a in the second embodiment further includes the underground second suction body 3 in the vicinity of the underground freezing pipe 1 relative to the purification body 10 in the first embodiment. Thus, the suction efficiency of highly concentrated contaminated groundwater after thawing is increased.
[0023]
The underground second suction body 3 is the same as the underground first suction body 2 except that it is disposed in the vicinity of the underground freezing tube 1. The vicinity of the underground freezing tube 1 includes a form close to the underground freezing tube 1 to a form slightly apart from the underground freezing tube 1, but is a form close to the underground freezing tube 1. For example, it is preferable in that the efficiency of supplying water from the underground second suction body 3, extruding contaminated groundwater, and suctioning and removing from the underground first suction body 2 is improved.
[0024]
3 and 4 show a state after the thawing of the contaminated ground region. The thawing step is not particularly limited, and includes a method of thawing to stand at room temperature by natural standing, a method of rapid heating with a ground heating tube (not shown), or a method of thawing by flowing warm water into the underground freezing tube 1. Among these, the method of pouring warm water into the underground freezing tube 1 and thawing is preferable in that simple and quick thawing can be performed. 3 and 4 show a situation in which high-concentration contaminated groundwater around the stock solution exists in the ground 9 after thawing. In this case, the underground second suction body 3 in the vicinity of the underground freezing pipe 1 is used as a water supply body, and the underground first suction body 2 is used as a contaminated groundwater suction body. That is, if water is supplied from the underground second suction body 3 and high-concentration contaminated groundwater is sucked from the underground first suction body 2, a circulation path is formed, and the high-concentration contaminated groundwater is easily and efficiently used. Can be removed. In addition, the underground 2nd suction body 3 is connected to the ground water supply means not shown, and the arrow in FIG. 4 is a flow of contaminated groundwater. Moreover, it may replace with the water supplied to the underground 2nd suction body 3, and may use compressed air. Similarly, when compressed air is used, a channel for contaminated groundwater from the underground second suction body 3 to the underground first suction body 2 is formed.
[0025]
According to the purification method of the contaminated ground in the second embodiment, since air or water is supplied from the underground second suction body 3 and the contaminated groundwater is sucked from the underground first suction body 2, extrusion and suction are performed. The purification efficiency can be further enhanced by both actions. Especially when thawing while warming the underground freezing pipe, water and air can be supplied from the open gap in the ground close to the underground freezing pipe, shortening the construction period and smoothing the circulation, improving the purification efficiency To do.
[0026]
Moreover, as a modification of the purification method of the contaminated ground in the second embodiment, the underground first suction body 2 is used as a water supply body, and the underground second suction body 3 is used as a contaminated groundwater suction body. You can also. That is, if water is supplied from the underground first suction body 2 and contaminated groundwater is sucked from the underground second suction body 3, a circulation path is formed in the same manner, and the contaminated groundwater is easily and efficiently supplied. Can be removed. In this case, in the case of freezing, contrary to the discharge effect, a water movement phenomenon on freezing where groundwater moves to the underground freezing pipe 1 can be used. This phenomenon is a natural phenomenon in which the pore water in the ground gradually freezes to form an ice layer called an ice lens, and when the temperature decreases further, water is replenished from the unfrozen part toward the frozen surface. Becomes easier to collect in the underground freezing tube 1. Therefore, after the thawing, the collected contaminated groundwater can be immediately sucked by the underground second suction body 3, and further, the purification efficiency is further improved because it is pushed out by the supply water. Also in the modification of the second embodiment, compressed air can be used in place of the water supplied from the underground first suction body 2.
[0027]
【Example】
EXAMPLES Next, although an Example is given and this invention is demonstrated more concretely, this is only an illustration and does not restrict | limit this invention.
Example 1
(Production of simulated contaminated soil)
Simulated contaminated soil having the following composition was prepared and filled in the following bottomed cylindrical container. The filling amount was packed up to a thickness of 100 mm from the bottom of the container. The simulated contaminated soil has an outer diameter of 7 mm × inner diameter of 5 mm, the tip is closed with a filling adhesive, and suction pipes with a total of 36 pores with an inner diameter of 1 mm in two rows are arranged at intervals of 5 mm from the bottom to 90 mm. Set up. In addition, a constantan heater wire having a diameter of 0.1 mm was provided inside the suction tube to prevent the suction tube from being blocked by freezing of water droplets during suction. Furthermore, in order to prevent mixing of sand particles, the outer peripheral surface of the suction tube was wound with a nonwoven fabric.
[0028]
・ Simulated contaminated soil: Silica sand No. 5 with a density of 1.76 g / cm 3 (25 ° C.) and a fluorine-containing inert liquid with a freezing point of −43 ° C. and saturated with water No. 5 bottomed cylindrical container; Top opening container made of 100 mm acrylic resin and bottom plate made of 2 mm thick aluminum plate.
(Purification experiment)
-The entire simulated contaminated soil was frozen in a refrigerant bath adjusted to -15 ° C. In addition, the heater put in the suction tube was turned on. After confirming the reading of the temperature sensor installed at a depth of 2 cm from the surface of the simulated contaminated soil and freezing of floating water on the surface, the aspirator was activated and the suction tube was activated. As a result of suction for 30 minutes, 124 g of 180 g of the fluorine-based inert liquid added to the simulated contaminated soil was removed by suction.
[0030]
【The invention's effect】
According to the present invention, since the saturated ground below the groundwater level is frozen, DNAPL can be present as a liquid in the ground where the pore water is frozen. Further, due to the discharge effect caused by freezing, liquid materials other than the pore water are pushed to the underground first suction body side, and the liquid materials can be easily and efficiently sucked and removed by the underground first suction pipe. For this reason, the purification processing time can be shortened and the processing cost can be reduced.
According to the present invention, after thawing the contaminated ground, the groundwater in which the contaminants around the undiluted solution are dissolved at a high concentration can be easily and efficiently sucked and removed by the first suction body in the ground.
According to the present invention, since there is contaminated groundwater in which the pollutant is dissolved at a high concentration especially around the freezing pipe after thawing, the contaminated groundwater can be easily removed from the underground second suction body disposed near the freezing pipe. Efficient suction and removal.
According to the present invention, if air or water is supplied from one underground suction body and contaminated groundwater is sucked from the other underground suction body, the purification efficiency can be further improved by both the action of extrusion and suction. .
According to this invention, invention of the said purification method can be implemented reliably.
[Brief description of the drawings]
FIG. 1 is a schematic cross-sectional view of a purification body in a first embodiment.
FIG. 2 is a schematic plan view of a purification body in the first embodiment.
FIG. 3 is a schematic cross-sectional view showing a state after the thawing of the purifier in the second embodiment.
FIG. 4 is a schematic plan view of a purification body in a second embodiment.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Underground freezing pipe 2 Underground 1st suction body 3 Underground 2nd suction body 5 Frozen earth 6 Impermeable layer 7 Contaminant (stock solution)
8 Contaminated ground area 9 Contaminated ground 10, 10a Purified body 21, 31 Perforated hollow tube 22, 32 Heater 23, 33 Water hole W.L. Groundwater level

Claims (3)

地下水位以下の土壌中に汚染物質が存在する汚染地盤に適宜のピッチで地中凍結管を、該地中凍結管間に適宜のピッチで地中第1吸引体を、該地中凍結管近傍に地中第2吸引体それぞれ配設する浄化体配設工程と、汚染地盤領域を凍結する凍結工程と、該凍結状態を維持したまま該地中第1吸引体から液状汚染物質を吸引する原液吸引工程と、汚染地盤領域を解凍する工程と、解凍された汚染地盤領域の汚染地下水を該地中第1吸引体から空気又は水を供給して該地中第2吸引体から汚染地下水を吸引するか、又は該地中第2吸引体から空気又は水を供給して該地中第1吸引体から汚染地下水を吸引する汚染地下水吸引工程を行なうことを特徴とする汚染地盤の浄化方法。Underground freezing pipes at an appropriate pitch on the contaminated ground where contaminants are present in the soil below the groundwater level , the first underground suction body at an appropriate pitch between the underground freezing pipes, and near the underground freezing pipe underground second suction body for sucking the purifier disposing step of disposing each a freezing step of freezing the contaminated soil region, the liquid contaminants from the first suction member in該地while keeping the frozen state A raw solution suction step , a step of thawing the contaminated ground region, and supplying the ground water in the thawed contaminated ground region by supplying air or water from the ground first suction body and the contaminated ground water from the ground second suction body A contaminated ground purification method characterized by performing a contaminated groundwater suction step of sucking or supplying air or water from the underground second suction body to suck contaminated groundwater from the underground first suction body . 地下水位以下の土壌中に汚染物質が存在する汚染地盤に構築される浄化体であって、適宜のピッチで配設される地中凍結管と、該地中凍結管間に配設され凍結地盤中に存在する液状汚染物質を吸引する地中第1吸引体と、該地中凍結管近傍に配設され凍結地盤中に存在する液状汚染物質を吸引する地中第2吸引体を備え、該地中第1吸引体及び地中第2吸引体は、空気又は水を供給する供給体を兼用するものであることを特徴とする浄化体。A purification body constructed on a contaminated ground in which contaminants exist in soil below the groundwater level, and an underground freezing pipe disposed at an appropriate pitch, and a frozen ground disposed between the underground freezing pipes A first underground suction body for sucking liquid contaminants existing therein , and a second underground suction body for sucking liquid contaminants disposed in the frozen ground near the underground freezing pipe , The purifying body, wherein the underground first suction body and the underground second suction body also serve as a supply body for supplying air or water . 前記地中第1吸引体及び地中第2吸引体は、吸引管又は柱状ドレーンであることを特徴とする請求項2記載の浄化体。The purifying body according to claim 2, wherein the underground first suction body and the underground second suction body are suction pipes or columnar drains.
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JP4091482B2 (en) * 2003-06-06 2008-05-28 譲 伊藤 Purification method and purification body of contaminated ground by freezing and suction
JP2005270963A (en) * 2004-02-26 2005-10-06 Mayekawa Mfg Co Ltd Method and apparatus for purifying contaminated soil
JP6913583B2 (en) * 2017-09-25 2021-08-04 鹿島建設株式会社 Ground improvement method
CN112376543B (en) * 2019-05-22 2022-03-22 中国矿业大学(北京) Freezing device and method for directionally freezing stratum
CN116556387B (en) * 2023-06-05 2026-01-06 上海建工集团股份有限公司 A groundwater diversion and pressure relief device for foundation pit engineering and its construction method

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JP3814716B2 (en) * 2001-08-24 2006-08-30 独立行政法人科学技術振興機構 Method and apparatus for purifying contaminated soil

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