JP2004209451A - Method for treating contaminated soil caused by volatile organic compound and improving apparatus therefor - Google Patents

Method for treating contaminated soil caused by volatile organic compound and improving apparatus therefor Download PDF

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Publication number
JP2004209451A
JP2004209451A JP2003002802A JP2003002802A JP2004209451A JP 2004209451 A JP2004209451 A JP 2004209451A JP 2003002802 A JP2003002802 A JP 2003002802A JP 2003002802 A JP2003002802 A JP 2003002802A JP 2004209451 A JP2004209451 A JP 2004209451A
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Japan
Prior art keywords
volatile organic
contaminated soil
organic compound
vertical hole
ground
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JP2003002802A
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Japanese (ja)
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JP3634849B2 (en
Inventor
Tsunezo Nakamura
常蔵 中村
Yoji Ueyama
陽治 植山
Shizuo Ikuta
静夫 生田
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TENOTSUKUSU KYUSHU KK
Tenox Kyusyu Corp
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TENOTSUKUSU KYUSHU KK
Tenox Kyusyu Corp
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  • Consolidation Of Soil By Introduction Of Solidifying Substances Into Soil (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide an economical method for treating a contaminated soil caused by a volatile organic compound in which the scale of an installation can be simplified and there exists little restriction. <P>SOLUTION: The soil is improved on every vertical hole 3 formed in the ground in such a way that a hot spot where the contaminated soil caused by the volatile organic compound is distributed is covered. The vertical hole is formed by a drilling apparatus 14 having a covering body 11 shutting the internal space from the open air and a chain saw 17 stored in the internal space S of the covering body and drilling into the ground. A discharging liquid is discharged into the vertical hole and air is compressed therein and the chain saw of the drilling apparatus is rotated. The contaminated soil fluidized around the chain saw and the injected air are mixed/agitated to expose the volatile organic compound included in the contaminated soil, and the contaminated soil is guided into the internal space, wherein the volatile organic compound is volatilized and is separated from the contaminated soil. <P>COPYRIGHT: (C)2004,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、揮発性有機化合物による汚染土の処理方法及びそれに用いる改良装置に関するものである。
【0002】
【従来の技術】
揮発性有機化合物、例えば、ジクロロメタン、四塩化炭素、1,2−ジクロロメタン、1,1−ジクロロエチレン、シス−1,2−ジクロロエチレン、1,1,1−トリクロロエチレン、テトラクロロエチレン、ベンゼン、1,2−ジクロロエチレン等は、IC基板や電子部品の洗浄、金属部品の前処理洗浄、ドライクリーニング用の溶剤等、様々な用途に、大量に使用されてきた。
【0003】
揮発性有機化合物は、ベンゼンを除き、水よりも比重が大であり、水に溶けにくく、蒸気圧が高いため、大気などに揮散しやすい、という性質を持つ。
【0004】
このため、揮発性有機化合物が使用された現場あるいは揮発性有機化合物が地下水面等を経て移動した先に、揮発性有機化合物による汚染土のホットスポット(汚染中心)が形成され、その対策を採ることが急務となっている。
【0005】
揮発性有機化合物に関する恒久対策であって、原位置浄化を行うこと、地下水の揚水が不要なこと、生石灰等を使用しないこと、という条件を満たすものとして、エアースパージング法がある。
【0006】
エアースパージング法は、主として欧米で普及しているものであり、エアースパジング井戸を用いて、土壌ガス吸引のアナロジーとして、揮発性有機化合物に汚染された土壌や地下水中に、空気を圧入し、土壌粒子間の空気流れを攪乱して、揮発性有機化合物の気化を促進する。
【特許文献1】
「エアースパージングによる汚染地下水の浄化」 環境省環境管理局水環境部土壌環境課 発行 2002年7月
【0007】
【発明が解決しようとする課題】
しかしながら、この手法では、次のような問題点がある。
(1)地上に大規模な曝気装置を設ける必要がある。
(2)地下水面(飽和/不飽和)によって使用できないなど制約が多い。
(3)井戸工法特有の問題(地層の異方性(例えば、不均質性、層理や亀裂等の不連続面)及び井戸の周面に沿う空気みちの形成・偏在により、短絡が発生し効果が不十分になる)がある。
(4)工期が長く、コストが高い。
【0008】
そこで本発明は、設備規模を簡素化でき、制約が少なく、経済的な、揮発性有機化合物による汚染土の処理方法を提供することを目的とする。
【0009】
【課題を解決するための手段】
請求項1記載の揮発性有機化合物による汚染土の処理方法は、
揮発性有機化合物による汚染土が分布する、ホットスポットをカバーするように、地中に複数の縦穴を形成し、縦穴毎に、土壌を改良する方法であって、
縦穴は、
内部空間を外気から遮断する覆い体と、
覆い体の内部空間内に収納され、かつ内部空間内において地中を掘削し地中へ進退する、チェーンソーを有する掘削装置と
を用いて、形成され、
縦穴内に吐出液を吐出すると共に、縦穴内に空気を圧入し、しかも、掘削装置のチェーンソーを回転させることにより、
チェーンソーの周囲において、流動化した汚染土と、圧入した空気とを混合・攪拌して汚染土に含まれる揮発性有機化合物を曝気させ、
汚染土を内部空間に導いて、内部空間内において、揮発性有機化合物を揮散させて内部空間内で揮発性有機化合物を、汚染土から分離する。
【0010】
この構成において、チェーンソーにより、流動化した汚染土と、圧入した空気とを、機械的に混合・攪拌して、汚染土に含まれる揮発性有機化合物を曝気している。このため、チェーンソー及びその周囲が、曝気装置としての機能を果たし、地表に大規模な曝気装置を設ける必要がなく、設備を簡素化できる。
【0011】
また、この機械的な混合・攪拌を利用しているため、チェーンソーによる掘削が可能な限り、飽和帯/不飽和帯、透水層/不透水層あるいは地盤の硬軟にかかわらず、一貫して適用でき、制約が少ない。
【0012】
さらに、この機械的(強制的)な混合・攪拌を利用しているため、吸引方式あるいは井戸方式に比べ、揮発性有機化合物の気化あるいは分解の効率が高く、工期を短縮でき、コストを低減できる。
【0013】
しかも、縦穴は、平面視で、地表面上で自由な位置に容易に移動して形成できるから、複数の縦穴を形成して、ホットスポット全域あるいはその周囲領域を含めて、土壌改良しやすく、実効大である。
【0014】
請求項2記載の揮発性有機化合物による汚染土の処理方法では、内部空間から揮発性有機化合物を、ガス回収装置へ吸引し、揮発性有機化合物を回収する。
【0015】
この構成において、ガス回収装置により、揮発性有機化合物を回収し、縦穴内及び内部空間内を浄化できる。
【0016】
請求項3記載の揮発性有機化合物による汚染土の処理方法では、ガス回収装置へ吸引される揮発性有機化合物の濃度を計測し、濃度が一定範囲内になるまで、チェーンソーを連続回転させる。
【0017】
この構成により、全ての縦穴内において、一定基準を満たすレベルまで、土壌浄化でき、浄化結果を品位保証しやすい。
【0018】
請求項4記載の揮発性有機化合物による汚染土の処理方法では、土壌改良後に、縦穴に固化液を注入して地盤改良体を形成する。
【0019】
この構成において、地盤改良体を形成することにより、縦穴内に揮発性有機化合物がわずかに残存していても、それを封止し、外部への拡散を防止できる。また、浄化土の強度を高めて、その利用価値を向上できる。
【0020】
請求項5記載の揮発性有機化合物による汚染土の処理方法では、土壌改良に先立ち、少なくともホットスポットを包囲する地中連続壁を形成する。
【0021】
この構成において、地中連続壁を形成することにより、揮発性有機化合物を封止し、外部への拡散を防止できる。
【0022】
【発明の実施の形態】
次に図面を参照しながら、本発明の実施の形態を説明する。図1は本発明の一実施の形態における現場例の平面図、図2は同断面図である。
【0023】
まず、図1に示すように、縦穴3の形成に先立って、ホットスポット1を包囲する地中連続壁4を形成する。本形態では、地中連続壁4についても、縦穴3の形成に使用する改良装置10を用いる。但し、地中連続壁4の形成時には、土壌改良を行わず、セメントミルクなどの固化剤を供給し、これを固化させる。
【0024】
次に、揮発性有機化合物による汚染土のホットスポット1について、複数の縦穴(四角柱状)3を形成し、縦穴3により、ホットスポット1をカバーする。より望ましくは、ホットスポット1の周囲領域2についても、縦穴3を形成する。なお、各縦穴3の形成法については、後に詳述する。
【0025】
さて、図1及び図2に示す状態では、改良済み領域S1の縦穴3について、土壌改良が所定深さHまで完了し、改良中領域S2の縦穴3について、現在土壌改良を行っている。なお、未改良領域S3の縦穴3は、改良中領域S2の縦穴3についての土壌改良が完了した後に、土壌改良される。
【0026】
ここで、改良装置10は、その頂部に、吊金具12が設けられ、吊金具12には、図示しないクレーン車から吊下されるワイヤ13の下端部が接続される。したがって、このクレーン車を地面5上で移動させることにより、改良装置10は、XY方向に容易に移動させることができ、所望の位置に縦穴3を形成できる。
【0027】
したがって、本発明の処理法は、固定的な位置に井戸を掘る従来技術に比べ、位置に関する機動力が優れ、しかも、その移動は、短時間で終了する。
【0028】
次に、図3を用いて、改良装置10の詳細及びそのZ方向の移動等について説明する。図3は、同掘削装置の立面図であり、地中の掘削を開始する前の状態を示している。
【0029】
図3に示すように、改良装置10は、上下方向伸縮自在な覆い体11を有する。覆い体11の内部空間Sは、外部と遮断されており、内部空間S内に揮発性有機化合物が揮散しても、揮発性有機化合物が外部に漏れないようになっている。
【0030】
より詳しくは、覆い体11は、地面5上に設置される下カバー11aと、吊金具12が上面中央に固着される上カバー11bと、上カバー11bの下端部と下カバー11aの上端部とを伸縮自在に連結するベローズ11cとを有する。
【0031】
そして、覆い体11の内部空間Sに、縦長の掘削装置14が収納される。掘削装置14は、上端部に図示しないモータ及び減速機等により、駆動されて矢印N1方向に回転する駆動ローラ15と、下端部に回転自在に軸支されるリターンローラ16とを有する。
【0032】
駆動ローラ15と、リターンローラ16とには、無端状のチェーンソー17が張架される。ここで、本明細書における「チェーンソー」とは、四角柱状の縦穴3を形成可能なものであれば足り、一般のチェーンソーの概念よりも広い。例えば、チェーンソー17のビットの形状などは、用途に応じて種々変更できる。
【0033】
即ち、駆動ローラ15が駆動されて、矢印N1方向に回転すると、それにつれて、チェーンソー17は、駆動ローラ15に周接してから一旦下降し、リターンローラ16に周接して下降方向から上昇方向へ折り返し、上昇して駆動ローラ15へ至るルートを、巡回する。
【0034】
ここで、掘削装置14による地中の掘削(つまり、改良装置10のZ方向下降)は、専らリターンローラ16付近でチェーンソー17が地中を掘ることにより、進行する。通常この際、掘削装置14に対して、下向きの荷重を作用させる必要はなく、クレーン車からワイヤ13を繰り出すだけでよい。
【0035】
また、図3において、駆動ローラ15は、上カバー11bに対して回転自在に軸支されているため、ワイヤ13を繰り出し/巻き取りすることにより、上カバー11bを昇降させると、掘削装置14全体が、それと一体的に昇降する。なお、下カバー11aに対し、掘削装置14はZ方向について、勝手に昇降できるようになっている。
【0036】
吐出液により流動化した汚染土と、圧入された空気との、混合・攪拌は、チェーンソー17のうち地中に位置する領域全体で実施され、汚染土に含まれる、揮発性有機化合物は、この混合・攪拌による、機械的かつ強制的な作用により、効率よく曝気される。
【0037】
つまり、チェーンソー17のうち地中に位置する領域全体及びその周囲が、曝気ゾーンと呼ぶべき存在となる。即ち、地中に曝気ゾーンを形成することにより、地面5上において、曝気装置の設置を省略できるものである。
【0038】
図3に示すように、地面5上に空気供給器18が設置され、空気供給器18から掘削装置14へ空気が圧入される。ここで、空気供給器18としては、例えば、アフタークーラを外したコンプレッサや、蒸気発生器等が好適である。空気は、大気以外の成分を含めても良いが、高温のものを使用することが望ましい。揮発性有機化合物の気化促進を図れるからである。
【0039】
また、地面5上には、吐出液供給器19が設置され、吐出液供給器19から掘削装置14へ吐出液が供給される。ここで本形態では、吐出液供給器19は、土壌改良中と、地盤改良体形成中とにおいて、異なる種類の吐出液を供給する。
【0040】
土壌改良中の吐出液としては、水あるいは重液等が望ましい。揮発性有機化合物の大部分を占めるDNAPL(Dense Non Aqueous Phase Liquid)の浮上を促進できるためである。
【0041】
また、揮発性有機化合物を無毒化できる薬液を使用できるときには、それを添加することが望ましい。
【0042】
地盤改良体形成中の吐出液は、固化剤としてのセメントミルク等である。
【0043】
なお、これらの吐出液を、個々に吐出する吐出液供給器19を設置しても良いし、勿論、地盤改良体の形成を省略するときには、固化剤の吐出をやめても良い。
【0044】
さらに、下カバー11aには、内部空間Sに連通する吸込管20の一端部が接続され、吸込管20の他端部は、内部空間S内のガス(揮発性有機化合物を含む)を吸引してガス回収装置22へ圧送する吸引ファン21が接続される。
【0045】
ガス回収装置22は、内部に活性炭吸着装置等を有し、揮発性有機化合物を回収し、浄化されたガスを大気に放出する。
【0046】
また、濃度計23は、吸引ファン21が圧送するガスにおける揮発性有機化合物の濃度を計測する。そして、濃度計23が計測した揮発性有機化合物の濃度が、一定基準値以下になるまで、チェーンソー17の回転(つまり混合・攪拌)と、ガス回収装置22による揮発性有機化合物の回収が連続して実施される。
【0047】
なお、吐出液の供給及び空気の圧入は、掘削装置14による掘削と同時並行して実施しても良いし、掘削装置14による掘削完了後(所定深さHに達した後)に実施しても良い。しかし、地中が既に十分流動化している場合には、吐出液の吐出を省略する場合もある。
【0048】
次に、図4及び図5を用いて、さらに詳しく説明する。図4には、掘削装置14による掘削が完了し、掘削装置14の下端部が所定深さHに達した状態が示されている。
【0049】
このとき、上カバー11bは、掘削装置14と一体的に下降するため、ベローズ11cは、図3と比較すれば明らかなように、収縮している。このときにも、覆い体11の内部空間Sは、外気と遮断されているため、揮発性有機化合物が内部空間Sから外部に漏れることはない。
【0050】
さて、図3には示していなかったが、縦穴3の地面5付近に、縦穴3よりも面積が大きい(図5参照)、ピット24が形成されている。ピット24の形成については、掘削装置14を使用しても良いし、他の装置あるいは工具を用いても良い。なお、ピット24は、あまり深くする必要はない。
【0051】
上述したように、図4の状態では、チェーンソー17のうち地中に位置する領域全体が曝気ゾーンとなっている。即ち、矢印N2で示す下降ゾーン、矢印N3で示す上昇ゾーン及び矢印N4で示す折り返しゾーンにおいて、流動化した汚染土と、圧入された空気とが、強制的かつ機械的に混合・攪拌され、揮発性有機化合物が曝気される。
【0052】
そして、矢印N4で示す折り返しゾーンにおいて、曝気された揮発性有機化合物を含む汚染土が、図5に示すように、ピット24に一旦滞留し、ピット24内で流動する。
【0053】
このとき、吸引ファン21により吸引することにより、内部空間S内は、大気圧よりもやや気圧が低くなっており、ピット24内で、この汚染土(揮発性有機化合物を含む)は、内部空間Sに接触する。もとより、揮発性有機化合物は、従来の技術の項で述べたように、水に溶けにくく、大気へ揮散しやすいし、しかも、既に曝気されているため、ピット24において簡単に内部空間Sへ揮散し汚染土から分離され、吸引ファン21を経てガス回収装置22に回収される。
【0054】
本形態では、ピット24のように、縦穴3の、内部空間Sに接する表面積を拡大する要素を使用しているから、一層効率よく、揮発性有機化合物を回収できる。
【0055】
以上の土壌改良後、吐出液を固化剤に変更し、掘削装置14を地表へ上昇させ、固化剤を固化させると、縦穴3に地盤改良体を形成できる。このように、改良装置10のみによって、土壌改良と地盤改良体の形成の両方を、実施できる。
【0056】
【発明の効果】
本発明によれば、次のような効果がある。
(1)地上に大規模な曝気装置を設ける必要がなく、設備を簡素化できる。
(2)制約が少なく、広い範囲に一貫して適用できる。
(3)工期が短く、経済的である。
【図面の簡単な説明】
【図1】本発明の一実施の形態における現場例の平面図
【図2】同断面図
【図3】同掘削装置の立面図
【図4】同掘削装置の立面図
【図5】同ピットの平面図
【符号の説明】
1 ホットスポット
2 周囲領域
3 縦穴
4 地中連続壁
5 地面
10 改良装置
11 覆い体
11a 下カバー
11b 上カバー
11c ベローズ
12 吊金具
13 ワイヤ
14 掘削装置
15 駆動ローラ
16 リターンローラ
17 チェーンソー
18 空気供給器
19 吐出液供給器
20 吸込管
21 吸引ファン
22 ガス回収装置
23 濃度計
24 ピット
S 内部空間
S1 改良済み領域
S2 改良中領域
S3 未改良領域
H 一定深さ
[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method for treating contaminated soil with a volatile organic compound and an improved apparatus used for the method.
[0002]
[Prior art]
Volatile organic compounds such as dichloromethane, carbon tetrachloride, 1,2-dichloromethane, 1,1-dichloroethylene, cis-1,2-dichloroethylene, 1,1,1-trichloroethylene, tetrachloroethylene, benzene, 1,2-dichloroethylene These have been used in large quantities for various purposes such as cleaning IC boards and electronic components, pretreatment cleaning of metal components, and solvents for dry cleaning.
[0003]
Volatile organic compounds, except for benzene, have a specific gravity higher than that of water, are hardly soluble in water, and have a high vapor pressure, so that they are easily volatilized into the atmosphere and the like.
[0004]
For this reason, a hot spot (contamination center) of the contaminated soil due to the volatile organic compound is formed at the site where the volatile organic compound is used or before the volatile organic compound moves through the groundwater table and the like, and measures are taken. That is urgent.
[0005]
An air sparging method is a permanent measure for volatile organic compounds that satisfies the conditions of performing in-situ purification, not requiring pumping of groundwater, and not using quick lime.
[0006]
The air sparging method is widely used mainly in Europe and the United States.As an analogy of soil gas suction, air is injected into soil or groundwater contaminated with volatile organic compounds using air sparing wells. Perturbs the air flow between the soil particles to promote the vaporization of volatile organic compounds.
[Patent Document 1]
"Purification of contaminated groundwater by air sparging" Soil Environment Division, Water Environment Department, Environmental Management Bureau, Ministry of the Environment Published July 2002 [0007]
[Problems to be solved by the invention]
However, this method has the following problems.
(1) It is necessary to provide a large-scale aeration device on the ground.
(2) There are many restrictions such as inability to use due to groundwater table (saturated / unsaturated).
(3) A short circuit occurs due to problems specific to the well construction method (anisotropy of the stratum (for example, inhomogeneity, discontinuity such as bedding or cracks)) and the formation and uneven distribution of air channels along the peripheral surface of the well. The effect will be insufficient).
(4) The construction period is long and the cost is high.
[0008]
Therefore, an object of the present invention is to provide an economical method for treating polluted soil with volatile organic compounds, which can simplify the equipment scale, has few restrictions, and is economical.
[0009]
[Means for Solving the Problems]
The method for treating contaminated soil with the volatile organic compound according to claim 1,
A method of improving soil by forming a plurality of vertical holes in the ground so as to cover hot spots in which contaminated soil by volatile organic compounds is distributed, and for each vertical hole,
The vertical hole is
A cover that blocks the internal space from outside air,
A drilling device having a chainsaw that is housed in the interior space of the covering body and excavates in the ground in the interior space and advances and retreats into the ground,
By discharging the discharge liquid into the vertical hole, pressing air into the vertical hole, and rotating the chainsaw of the excavator,
Around the chainsaw, the fluidized contaminated soil and the injected air are mixed and agitated to aerate volatile organic compounds contained in the contaminated soil,
The contaminated soil is guided to the internal space, in which the volatile organic compounds are volatilized, and the volatile organic compounds are separated from the contaminated soil in the internal space.
[0010]
In this configuration, the fluidized contaminated soil and the injected air are mechanically mixed and stirred by a chainsaw to aerate volatile organic compounds contained in the contaminated soil. For this reason, the chainsaw and its surroundings function as an aeration device, and there is no need to provide a large-scale aeration device on the ground surface, and the equipment can be simplified.
[0011]
In addition, since this mechanical mixing and agitation is used, as long as drilling with a chainsaw is possible, it can be applied consistently regardless of the saturation zone / unsaturation zone, permeable layer / impervious layer, or the hardness of the ground. , Less restrictions.
[0012]
Furthermore, since this mechanical (forced) mixing and stirring is used, the efficiency of vaporizing or decomposing the volatile organic compound is higher than that of the suction method or the well method, and the construction period can be shortened and the cost can be reduced. .
[0013]
Moreover, the vertical hole can be easily moved to a free position on the ground surface in a plan view, so that a plurality of vertical holes are formed to easily improve the soil including the entire hot spot or the surrounding area, It is effective.
[0014]
In the method for treating contaminated soil with a volatile organic compound according to the second aspect, the volatile organic compound is sucked from the internal space into the gas recovery device to recover the volatile organic compound.
[0015]
In this configuration, the volatile organic compound can be recovered by the gas recovery device, and the inside of the vertical hole and the inside of the vertical hole can be purified.
[0016]
In the method for treating contaminated soil with a volatile organic compound according to the third aspect, the concentration of the volatile organic compound sucked into the gas recovery device is measured, and the chainsaw is continuously rotated until the concentration falls within a certain range.
[0017]
With this configuration, the soil can be purified to a level that satisfies a certain standard in all the vertical holes, and the quality of the purification result can be easily guaranteed.
[0018]
In the method for treating contaminated soil with a volatile organic compound according to the fourth aspect, after soil improvement, a solidified liquid is injected into a vertical hole to form a ground improvement body.
[0019]
In this configuration, by forming the ground improvement body, even if the volatile organic compound slightly remains in the vertical hole, it can be sealed and prevented from being diffused to the outside. In addition, the strength of the purified soil can be increased to improve its use value.
[0020]
In the method for treating contaminated soil with a volatile organic compound according to claim 5, prior to soil improvement, an underground continuous wall surrounding at least the hot spot is formed.
[0021]
In this configuration, by forming the underground continuous wall, the volatile organic compound is sealed, and diffusion to the outside can be prevented.
[0022]
BEST MODE FOR CARRYING OUT THE INVENTION
Next, an embodiment of the present invention will be described with reference to the drawings. FIG. 1 is a plan view of a site example according to an embodiment of the present invention, and FIG. 2 is a sectional view of the same.
[0023]
First, as shown in FIG. 1, prior to forming the vertical hole 3, an underground continuous wall 4 surrounding the hot spot 1 is formed. In the present embodiment, the improved device 10 used for forming the vertical hole 3 is also used for the underground continuous wall 4. However, when the underground continuous wall 4 is formed, soil improvement is not performed, and a solidifying agent such as cement milk is supplied and solidified.
[0024]
Next, a plurality of vertical holes (quadrangular prisms) 3 are formed for the hot spot 1 on the contaminated soil by the volatile organic compound, and the hot spot 1 is covered by the vertical holes 3. More preferably, the vertical hole 3 is also formed in the surrounding area 2 of the hot spot 1. The method of forming each vertical hole 3 will be described later in detail.
[0025]
By the way, in the state shown in FIG. 1 and FIG. 2, soil improvement has been completed for the vertical hole 3 in the improved area S1 to a predetermined depth H, and soil improvement is currently being performed for the vertical hole 3 in the improving area S2. The vertical holes 3 in the unimproved area S3 are soil-improved after the soil improvement of the vertical holes 3 in the improving area S2 is completed.
[0026]
Here, the improvement device 10 is provided with a hanger 12 at the top thereof, and the lower end of a wire 13 hung from a crane (not shown) is connected to the hanger 12. Therefore, by moving the crane truck on the ground 5, the improvement device 10 can be easily moved in the XY directions, and the vertical hole 3 can be formed at a desired position.
[0027]
Therefore, the processing method of the present invention is more mobile with respect to the position than the conventional technique of digging a well at a fixed position, and the movement is completed in a short time.
[0028]
Next, details of the improvement device 10 and its movement in the Z direction will be described with reference to FIG. FIG. 3 is an elevational view of the excavator, showing a state before starting excavation in the ground.
[0029]
As shown in FIG. 3, the improvement device 10 includes a cover 11 that is vertically expandable and contractible. The internal space S of the cover 11 is shielded from the outside, so that even if the volatile organic compound volatilizes in the internal space S, the volatile organic compound does not leak to the outside.
[0030]
More specifically, the cover body 11 includes a lower cover 11a installed on the ground 5, an upper cover 11b to which the hanging hardware 12 is fixed at the center of the upper surface, a lower end of the upper cover 11b, and an upper end of the lower cover 11a. And a bellows 11c for elastically connecting the bellows.
[0031]
Then, the vertically long excavator 14 is stored in the internal space S of the cover body 11. The excavator 14 has a drive roller 15 that is driven by a motor and a speed reducer (not shown) at the upper end thereof and rotates in the direction of the arrow N1, and a return roller 16 that is rotatably supported at the lower end.
[0032]
An endless chain saw 17 is stretched between the drive roller 15 and the return roller 16. Here, the “chainsaw” in the present specification only needs to be capable of forming the vertical hole 3 in the shape of a quadrangular prism, and is wider than the concept of a general chainsaw. For example, the shape of the bit of the chain saw 17 can be variously changed depending on the application.
[0033]
That is, as the drive roller 15 is driven and rotates in the direction of the arrow N1, the chainsaw 17 is once in contact with the drive roller 15 and then descends, then is in contact with the return roller 16 and is folded from the descending direction to the ascending direction. , And goes around the route to the drive roller 15.
[0034]
Here, the excavation of the underground by the excavator 14 (that is, the lowering of the improvement device 10 in the Z direction) proceeds only when the chainsaw 17 excavates the underground near the return roller 16. Normally, at this time, it is not necessary to apply a downward load to the excavator 14, and it is only necessary to unwind the wire 13 from the crane truck.
[0035]
In FIG. 3, the drive roller 15 is rotatably supported on the upper cover 11 b. Therefore, when the upper cover 11 b is moved up and down by feeding / rewinding the wire 13, the entire excavator 14 is moved. But it goes up and down integrally with it. The excavator 14 can freely move up and down with respect to the lower cover 11a in the Z direction.
[0036]
Mixing and stirring of the contaminated soil fluidized by the discharged liquid and the pressurized air are performed in the entire region of the chainsaw 17 located in the ground, and volatile organic compounds contained in the contaminated soil are Aeration is efficiently performed by the mechanical and forced action by mixing and stirring.
[0037]
That is, the entire region of the chainsaw 17 located in the ground and its surroundings are to be referred to as an aeration zone. That is, by forming the aeration zone in the ground, the installation of the aeration device on the ground 5 can be omitted.
[0038]
As shown in FIG. 3, an air supply 18 is installed on the ground 5, and air is injected from the air supply 18 into the drilling rig 14. Here, as the air supplier 18, for example, a compressor without an aftercooler, a steam generator, or the like is preferable. The air may contain components other than the atmosphere, but it is desirable to use a high-temperature air. This is because the vaporization of the volatile organic compound can be promoted.
[0039]
Further, on the ground 5, a discharge liquid supply device 19 is provided, and the discharge liquid supply device 19 supplies the discharge liquid to the drilling device 14. Here, in this embodiment, the discharge liquid supply device 19 supplies different types of discharge liquid during soil improvement and during formation of the ground improvement body.
[0040]
As the discharge liquid during soil improvement, water or heavy liquid is desirable. This is because floating of DNAPL (Dense Non Aqueous Phase Liquid) occupying most of the volatile organic compounds can be promoted.
[0041]
When a chemical solution capable of detoxifying a volatile organic compound can be used, it is desirable to add it.
[0042]
The liquid discharged during formation of the ground improvement body is cement milk or the like as a solidifying agent.
[0043]
In addition, the discharge liquid supply device 19 which discharges these discharge liquids individually may be provided. Of course, when the formation of the ground improvement body is omitted, the discharge of the solidifying agent may be stopped.
[0044]
Further, one end of a suction pipe 20 communicating with the internal space S is connected to the lower cover 11a, and the other end of the suction pipe 20 sucks gas (including a volatile organic compound) in the internal space S. And a suction fan 21 for feeding to the gas recovery device 22 by pressure.
[0045]
The gas recovery device 22 has an activated carbon adsorption device and the like inside, recovers volatile organic compounds, and releases purified gas to the atmosphere.
[0046]
The concentration meter 23 measures the concentration of the volatile organic compound in the gas pumped by the suction fan 21. Then, the rotation of the chainsaw 17 (that is, mixing and stirring) and the recovery of the volatile organic compound by the gas recovery device 22 continue until the concentration of the volatile organic compound measured by the densitometer 23 becomes equal to or less than a certain reference value. Is implemented.
[0047]
The supply of the discharged liquid and the press-fitting of the air may be performed simultaneously with the excavation by the excavator 14, or may be performed after the excavation by the excavator 14 is completed (after reaching the predetermined depth H). Is also good. However, when the underground is already sufficiently fluidized, the ejection of the ejection liquid may be omitted.
[0048]
Next, a more detailed description will be given with reference to FIGS. FIG. 4 shows a state where the excavation by the excavator 14 has been completed and the lower end of the excavator 14 has reached the predetermined depth H.
[0049]
At this time, since the upper cover 11b descends integrally with the excavator 14, the bellows 11c is contracted as apparent from comparison with FIG. Also at this time, since the internal space S of the cover 11 is isolated from the outside air, the volatile organic compound does not leak from the internal space S to the outside.
[0050]
Although not shown in FIG. 3, pits 24 having an area larger than the vertical hole 3 (see FIG. 5) are formed near the ground 5 of the vertical hole 3. For the formation of the pit 24, the excavator 14 may be used, or another device or tool may be used. The pit 24 does not need to be so deep.
[0051]
As described above, in the state of FIG. 4, the entire area of the chainsaw 17 located underground is an aeration zone. That is, in the descending zone indicated by the arrow N2, the ascending zone indicated by the arrow N3, and the return zone indicated by the arrow N4, the fluidized contaminated soil and the injected air are forcibly and mechanically mixed and stirred, and volatilized. Organic compounds are aerated.
[0052]
Then, in the return zone indicated by the arrow N4, the aerated contaminated soil containing the volatile organic compound temporarily stays in the pit 24 and flows in the pit 24, as shown in FIG.
[0053]
At this time, the inside of the internal space S is slightly lower than the atmospheric pressure by being sucked by the suction fan 21, and in the pit 24, the contaminated soil (including the volatile organic compound) is removed. Touch S. Naturally, as described in the section of the prior art, volatile organic compounds are hardly soluble in water and easily volatilized into the atmosphere. Further, since they have already been aerated, they can easily volatilize into the internal space S in the pit 24. It is separated from the contaminated soil and collected by a gas recovery device 22 via a suction fan 21.
[0054]
In this embodiment, since the element that enlarges the surface area of the vertical hole 3 in contact with the internal space S, such as the pit 24, is used, the volatile organic compound can be more efficiently recovered.
[0055]
After the above soil improvement, the discharged liquid is changed to a solidifying agent, the excavator 14 is raised to the surface of the ground, and the solidifying agent is solidified, whereby a ground improvement body can be formed in the vertical hole 3. As described above, both the soil improvement and the formation of the ground improvement body can be performed only by the improvement device 10.
[0056]
【The invention's effect】
According to the present invention, the following effects can be obtained.
(1) There is no need to provide a large-scale aeration device on the ground, and the equipment can be simplified.
(2) Consistently applied to a wide range with few restrictions.
(3) The construction period is short and economical.
[Brief description of the drawings]
FIG. 1 is a plan view of an example of a site in an embodiment of the present invention. FIG. 2 is a sectional view of the same. FIG. 3 is an elevation view of the excavator. FIG. 4 is an elevation view of the excavator. Plan view of the pit [Explanation of symbols]
REFERENCE SIGNS LIST 1 Hot spot 2 Surrounding area 3 Vertical hole 4 Underground continuous wall 5 Ground 10 Improvement device 11 Cover 11a Lower cover 11b Upper cover 11c Bellows 12 Hanging fitting 13 Wire 14 Drilling device 15 Drive roller 16 Return roller 17 Chainsaw 18 Air supply device 19 Discharge liquid supply device 20 Suction pipe 21 Suction fan 22 Gas recovery device 23 Densitometer 24 Pit S Internal space S1 Improved area S2 Improved area S3 Unimproved area H Constant depth

Claims (6)

揮発性有機化合物による汚染土が分布する、ホットスポットをカバーするように、地中に複数の縦穴を形成し、前記縦穴毎に、土壌を改良する方法であって、
前記縦穴は、
内部空間を外気から遮断する覆い体と、
前記覆い体の前記内部空間内に収納され、かつ前記内部空間内において地中を掘削し地中へ進退する、チェーンソーを有する掘削装置と
を用いて、形成され、
前記縦穴内に吐出液を吐出すると共に、前記縦穴内に空気を圧入し、しかも、前記掘削装置の前記チェーンソーを回転させることにより、
前記チェーンソーの周囲において、流動化した汚染土と、圧入した空気とを混合・攪拌して汚染土に含まれる揮発性有機化合物を曝気させ、
汚染土を前記内部空間に導いて、前記内部空間内において、揮発性有機化合物を揮散させて前記内部空間内で揮発性有機化合物を、汚染土から分離する、
揮発性有機化合物による汚染土の処理方法。
Contaminated soil by volatile organic compounds is distributed, so as to cover a hot spot, forming a plurality of vertical holes in the ground, for each vertical hole, a method of improving the soil,
The vertical hole,
A cover that blocks the internal space from outside air,
A digging device having a chainsaw that is housed in the inner space of the covering body and that digs into the ground and retreats into the ground in the inner space,
By discharging the discharge liquid into the vertical hole, pressurizing air into the vertical hole, and rotating the chainsaw of the excavator,
Around the chainsaw, the fluidized contaminated soil and the injected air are mixed and agitated to aerate volatile organic compounds contained in the contaminated soil,
Guiding contaminated soil to the internal space, in the internal space, volatilizes volatile organic compounds and separates volatile organic compounds in the internal space from the contaminated soil,
A method for treating contaminated soil with volatile organic compounds.
前記内部空間から揮発性有機化合物を、ガス回収装置へ吸引し、揮発性有機化合物を回収する、請求項1記載の揮発性有機化合物による汚染土の処理方法。The method for treating contaminated soil with a volatile organic compound according to claim 1, wherein the volatile organic compound is sucked into the gas recovery device from the internal space to recover the volatile organic compound. 前記ガス回収装置へ吸引される揮発性有機化合物の濃度を計測し、濃度が一定範囲内になるまで、前記チェーンソーを連続回転させる、請求項1から2記載の揮発性有機化合物による汚染土の処理方法。The treatment of the contaminated soil with the volatile organic compound according to claim 1 or 2, wherein the concentration of the volatile organic compound sucked into the gas recovery device is measured, and the chainsaw is continuously rotated until the concentration falls within a certain range. Method. 土壌改良後に、前記縦穴に固化液を注入して地盤改良体を形成する、請求項1から3記載の揮発性有機化合物による汚染土の処理方法。The method for treating contaminated soil with a volatile organic compound according to claim 1, wherein after soil improvement, a solidified liquid is injected into the vertical hole to form a ground improvement body. 土壌改良に先立ち、少なくともホットスポットを包囲する地中連続壁を形成する、請求項1から4記載の揮発性有機化合物による汚染土の処理方法。5. The method for treating contaminated soil with a volatile organic compound according to claim 1, wherein an underground continuous wall surrounding at least the hot spot is formed prior to soil improvement. 地中を掘削し地中へ進退する、チェーンソーを有する掘削装置と、
前記掘削装置を包囲し、その内部空間を外気から遮断する覆い体と、
前記掘削装置が掘削して形成する縦穴内に吐出液を吐出する吐出液供給器と、
前記縦穴内に空気を圧入する空気供給器とを備え、
前記覆い体は、前記掘削装置の進退に合わせて、伸縮自在に形成されている、改良装置。
A drilling rig with a chainsaw that drills into the ground and retreats into the ground,
A cover body surrounding the drilling rig and shielding its internal space from outside air;
A discharge liquid supply device that discharges a discharge liquid into a vertical hole formed by the excavation device,
An air supply device for pressurizing air into the vertical hole,
The improvement device, wherein the cover is formed to be able to expand and contract in accordance with the movement of the excavator.
JP2003002802A 2003-01-09 2003-01-09 Method and apparatus for treating contaminated soil with volatile organic compounds Expired - Fee Related JP3634849B2 (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006320842A (en) * 2005-05-19 2006-11-30 Shiraishi Corp Method and device for cleaning contaminated soil
JP2014159691A (en) * 2013-02-19 2014-09-04 Ogata Jutaku Kiban Kk Soil improvement machine, soil improvement method and hole opening block

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006320842A (en) * 2005-05-19 2006-11-30 Shiraishi Corp Method and device for cleaning contaminated soil
JP2014159691A (en) * 2013-02-19 2014-09-04 Ogata Jutaku Kiban Kk Soil improvement machine, soil improvement method and hole opening block

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