JP2005021730A - Wall for preventing diffusion of volatile organic compound and method for constructing the wall - Google Patents

Wall for preventing diffusion of volatile organic compound and method for constructing the wall Download PDF

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JP2005021730A
JP2005021730A JP2003186673A JP2003186673A JP2005021730A JP 2005021730 A JP2005021730 A JP 2005021730A JP 2003186673 A JP2003186673 A JP 2003186673A JP 2003186673 A JP2003186673 A JP 2003186673A JP 2005021730 A JP2005021730 A JP 2005021730A
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Prior art keywords
volatile organic
wall
soil
activated carbon
ground
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JP2003186673A
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Japanese (ja)
Inventor
Kazuo Toge
和男 峠
Tomonori Urushibara
知則 漆原
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Obayashi Corp
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Obayashi Corp
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Priority to JP2003186673A priority Critical patent/JP2005021730A/en
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Abstract

<P>PROBLEM TO BE SOLVED: To uniformly and surely remove volatile organic compounds contained in ground water over a long time. <P>SOLUTION: In the construction of a wall 1 for preventing the diffusion of the volatile organic compounds, a mixture 4 of soil 2 and active carbon powder 3 is formed in the shape of a pile to obtain a mixed pile, and the mixed piles are arranged in the shape of columns to form a wall in the ground 5. In order to construct the wall 1, by agitating/mixing the soil 2 of the ground 5 and the active carbon powder 3 in situ, the mixture 4 of the soil 2 and the active carbon powder 3 is formed in the shape of the pile to obtain the mixed pile, and the mixed piles are arranged in the shape of the columns. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、土壌又は地下水中に含まれる揮発性有機化合物の拡散防止壁及びその構築方法に関する。
【0002】
【従来の技術】
工場跡地の土壌内には、トリクロロエチレンなどの有機塩素系化合物で代表される揮発性有機化合物(VOC)が含まれていることがあり、このような土壌をそのまま放置すると、揮発性有機化合物が地下水を介して周辺に拡散するおそれがある。そのため、かかる汚染土壌あるいは汚染地下水に対しては所定の浄化処理を行わねばならない。
【0003】
揮発性有機化合物を除去処理する方法としては、従来からさまざまな方法が開発されており、例えば揮発性有機化合物で汚染された地下水を揚水して地上で処理する方法、汚染土壌に鉄粉や酸化剤を注入して揮発性有機化合物を分解する方法、微生物活性を利用したバイオレメディエーションによる方法、汚染土壌を掘削した後、気密空間内で曝気処理する方法などが知られている。
【0004】
【特許文献1】
特開2002−119952号公報
【0005】
【特許文献2】
特開2001−205248号公報
【0006】
【発明が解決しようとする課題】
しかしながら、従来の処理方法ではそれぞれ難点があり、例えば汚染された地下水を揚水する方法では、地盤の不均一性とも相まって汚染分布にばらつきがあるため、均一かつ確実な浄化が困難であるという問題を生じていた。
【0007】
また、揮発性有機化合物がトリクロロエチレン等の有機塩素化合物である場合に鉄粉が使われるが、鉄粉自体、酸化被膜の生成等が原因となって数ヶ月で活性を失ってしまう。
【0008】
また、酸化剤の添加やバイオレメディエーションは時間とコストを要し、汚染土壌の掘削曝気処理は、地下水汚染には本来的に適さない。
【0009】
本発明は、上述した事情を考慮してなされたもので、地下水に含まれる揮発性有機化合物を均一かつ確実にしかも長期にわたって除去可能な揮発性有機化合物の拡散防止壁及びその構築方法を提供することを目的とする。
【0010】
【課題を解決するための手段】
上記目的を達成するため、本発明に係る揮発性有機化合物の拡散防止壁は請求項1に記載したように、土と活性炭又は木炭の粉粒体との混合体を地盤内に壁状に形成してなるものである。
【0011】
また、本発明に係る揮発性有機化合物の拡散防止壁は、前記混合体をパイル状に形成して混合パイルとするとともに該混合パイルを柱列状に並べたものである。
【0012】
また、本発明に係る揮発性有機化合物の拡散防止壁は、前記混合体内の前記活性炭又は木炭の粉粒体の混合量を地下水の流速、地下水内の揮発性有機化合物の濃度又は周囲の土質性状に応じて深さ方向に変化させたものである。
【0013】
また、本発明に係る揮発性有機化合物の拡散防止壁構築方法は請求項4に記載したように、地盤の土と活性炭又は木炭の粉粒体とを原位置にて攪拌混合することで前記地盤内に前記土と前記粉粒体との混合体を形成するものである。
【0014】
また、本発明に係る揮発性有機化合物の拡散防止壁構築方法は、中空攪拌軸の下端に取り付けられた攪拌翼を該中空攪拌軸の軸線廻りに回転させることによって該攪拌翼を前記地盤内で掘削貫入し又は引抜きながら、前記中空攪拌軸内の搬送空間を介して活性炭又は木炭の粉粒体を該中空攪拌軸の吐出口又は攪拌翼の吐出口から噴出させることによって前記混合体をパイル状に形成して混合パイルとするとともに該混合パイルを柱列状に並べるものである。
【0015】
本発明に係る揮発性有機化合物の拡散防止壁においては、土と活性炭又は木炭の粉粒体との混合体を地盤内に壁状に形成してなるものであり、かかる揮発性有機化合物の拡散防止壁を構築する方法においては、地盤の土と活性炭又は木炭の粉粒体とを原位置にて攪拌混合することで前記地盤内に前記土と前記粉粒体との混合体を形成する。
【0016】
このようにすると、拡散防止壁に流入してきた地下水に含まれる揮発性有機化合物は、混合体内の活性炭又は木炭の粉粒体に吸着し、揮発性有機化合物が下流側に拡散するのを防止することができる。
【0017】
揮発性有機化合物(VOC)を活性炭に吸着させる技術は、本願出願時点で既に公知であることは言うまでもないが、それは、ガス化した揮発性有機化合物や、水中に溶けた揮発性有機化合物をいったんガス化させて活性炭に吸着させる点が公知になっているにすぎない。
【0018】
ここで、揚水された汚染地下水の浄化については、該地下水に溶けているVOCを曝気により空気連行させ、該空気に含まれている気相のVOCを活性炭に吸着させていた。
【0019】
しかしながら、揚水された地下水に溶けているVOCを除去するについては、そもそも本来的な難点があった。すなわち、VOCの水への溶解度がそもそも低いため(数百mg/kg〜2,000mg/kg)、直径1cm程度のVOCが汚染源である場合でも、該VOCは数年間にわたって地下水に溶出し続け、汚染源のVOCが原液であってその量が多い場合には、該VOCは、何十年もの間にわたって地下水に溶出し続ける。これは、揚水ポンプや活性炭吸着塔といった設備をやはり何十年にもわたって稼働し続けなければならないことを意味し、経済性の面であまりにも現実性に欠ける。
【0020】
本出願人は、このような汚染源における揮発性有機化合物の地下水への溶出の問題を踏まえつつ、汚染源から離れた箇所における地下水の浄化を低コストでかつ確実に行うことができないものかという点に着眼してさまざまな研究開発を行った結果、土と活性炭又は木炭の粉粒体との混合体を地盤内に壁状に形成してなる揮発性有機化合物の拡散防止壁であれば、該拡散防止壁を通過する地下水に含まれている揮発性有機化合物は、混合体内の活性炭又は木炭の粉粒体に吸着し、かくして揮発性有機化合物の下流への拡散を防止することができるという知見を得るに至った。
【0021】
本願出願当時の公知技術の水準は、上述した点にとどまっており、土と活性炭又は木炭の粉粒体との混合体を地盤内に壁状に形成してなる揮発性有機化合物の拡散防止壁により、該拡散防止壁を通過する地下水のVOCを混合体内の活性炭又は木炭の粉粒体に直接吸着させることが可能となるという知見は、産業上きわめて有用な知見であることを付言しておく。
【0022】
VOC(Volatile Organic Compounds)とも呼ばれる揮発性有機化合物には、ジクロロメタン、四塩化炭素、1,2−ジクロロエタン、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−トリクロロエタン、1,1,2−トリクロロエタン、トリクロロエチレン、テトラクロロエチレン、1,3−ジクロロプロペン、ベンゼンなどが含まれる。
【0023】
粉粒体には、いわゆる粉体をはじめ、例えば数mm〜1cm程度の粒径をもつ粒体も含まれる。
【0024】
ここで、前記混合体内の前記活性炭又は木炭の粉粒体の混合量を地下水の流速、地下水内の揮発性有機化合物の濃度又は周囲の土質性状に応じて深さ方向に変化させた場合、下流への揮発性有機化合物の拡散をより確実かつ合理的に防止することが可能となる。
【0025】
本発明に係る拡散防止壁構築方法において、地盤の土をどのように活性炭又は木炭の粉粒体と原位置にて攪拌混合し、また、どのように地盤内に土と粉粒体との混合体を形成するかは任意であるが、例えば、軟弱地盤中に粉粒体の改良材を供給して原位置土と攪拌混合するDJM工法を用いることが可能である。
【0026】
すなわち、中空攪拌軸の下端に取り付けられた攪拌翼を該中空攪拌軸の軸線廻りに回転させることによって該攪拌翼を前記地盤内で掘削貫入し又は引抜きながら、前記中空攪拌軸内の搬送空間を介して活性炭又は木炭の粉粒体を該中空攪拌軸の吐出口又は攪拌翼の吐出口から噴出させることによって前記混合体をパイル状に形成して混合パイルとするとともに該混合パイルを柱列状に並べるようにすればよい。
【0027】
【発明の実施の形態】
以下、本発明に係る揮発性有機化合物の拡散防止壁及びその構築方法の実施の形態について、添付図面を参照して説明する。なお、従来技術と実質的に同一の部品等については同一の符号を付してその説明を省略する。
【0028】
図1は、本実施形態に係る揮発性有機化合物の拡散防止壁を示した図である。同図でわかるように、本実施形態に係る揮発性有機化合物の拡散防止壁1は、土2と活性炭の粉体3との混合体4をパイル状に形成して混合パイルとするとともに、該混合パイルを柱列状に並べて地盤5内に壁状に形成してなる。
【0029】
図2乃至図4は、本実施形態に係る揮発性有機化合物の拡散防止壁1を構築する手順を示した図である。これらの図でわかるように、本実施形態に係る揮発性有機化合物の拡散防止壁1を構築するには、地盤の土2と活性炭の粉体3とを原位置にて攪拌混合することで地盤5内に土2と活性炭の粉体3との混合体4をパイル状に形成して混合パイルとするとともに該混合パイルを柱列状に並べる。
【0030】
土2と活性炭の粉体3とを攪拌混合するには、DJM工法を用いればよい。すなわち、まず、図2に示すようにベースマシン(図示せず)に鉛直軸線廻りに回動自在に吊持された中空攪拌軸21を拡散防止壁1の構築予定領域の上方にくるように位置決めする。
【0031】
拡散防止壁1は、VOCが存在する汚染源の下流側に構築するのがよい。また、拡散防止壁1を構成する混合パイルの直径や混合パイル中の活性炭の粉体量は、地下水の流速や汚染濃度を考慮して適宜定める。
【0032】
次に、中空攪拌軸21を掘削方向に鉛直軸線廻りに回転させることにより、該中空攪拌軸の下端に取り付けられた攪拌翼24を回転させる。
【0033】
ここで、攪拌翼24の下面には掘削ビット25を斜め下方に突設させてあるので、攪拌翼24を掘削方向に回転させることにより、地盤5を下方に掘削しながら中空攪拌軸21及び攪拌翼24を該地盤内に貫入することができる。
【0034】
図3は、中空攪拌軸21及び攪拌翼24を地盤5内に貫入させた様子を示したものであり、攪拌翼24が通過した領域は攪乱領域41となる。
【0035】
次に、図4に示すように中空攪拌軸21及び攪拌翼24を逆回転させながら、それらを攪乱領域41から引き抜くが、かかる引抜き工程においては、中空攪拌軸21内の搬送空間を介して搬送されてきた活性炭の粉体3を攪拌翼24に設けられた吐出口31から噴出させる。
【0036】
このようにすると、土2と活性炭の粉体3との混合体4が地盤5内にパイル状に形成され混合パイルとなる。
【0037】
以下、あらたな混合パイルを上述したと同様の手順で順次構築しながら各混合パイルを柱列状に並べ、図1に示した拡散防止壁1を構築する。
【0038】
本実施形態に係る揮発性有機化合物の拡散防止壁及びその構築方法においては、拡散防止壁1に流入してきた地下水に含まれる揮発性有機化合物は、混合体4内の活性炭の粉体3に吸着する。
【0039】
以上説明したように、本実施形態に係る揮発性有機化合物の拡散防止壁及びその構築方法によれば、拡散防止壁1に流入してきた地下水に含まれる揮発性有機化合物は、混合体4内の活性炭の粉体3に吸着し、揮発性有機化合物が下流側に拡散するのを防止することが可能となる。
【0040】
また、本実施形態に係る揮発性有機化合物の拡散防止壁及びその構築方法によれば、汚染源のVOCが例えば原液である場合において、何十年もの間、汚染源から溶出したVOCが地下水を汚染し続けたとしても、地下水中のVOCを活性炭の粉体3に吸着させることでVOCの下流への拡散を長期間防止することができる。
【0041】
もちろん、かかる長期の間には、粉体3の吸着機能が低下し、拡散防止壁1を再構築せねばならない場合も想定されるが、地下水の揚水設備やガス化した揮発性有機化合物を活性炭吸着塔に送り込む搬送設備といった従来であれば必須の設備を維持し続けることに比べれば、本実施形態に係る揮発性有機化合物の拡散防止壁1は、そのような維持コストが一切不要であってメンテナンスの必要もなく、全体の経済性ははるかに優れる。
【0042】
また、本実施形態に係る揮発性有機化合物の拡散防止壁及びその構築方法によれば、混合体4を土2と活性炭の粉体3とを攪拌混合して形成するようにしたので、一定の透水性が確保され、地下水の流れを阻害する懸念もない。
【0043】
本実施形態では、攪拌混合の手段として軟弱地盤改良で用いられるDJM工法を転用するようにしたが、土と活性炭又は木炭の粉粒体とを攪拌混合する装置や方法は任意であり、例えばCDM工法を転用するようにしてもよい。
【0044】
CDM工法についても軟弱地盤改良のための公知の方法であり、その内容の説明は省略するが、本発明に適用するにあたっては、活性炭又は木炭の粉粒体を予め水に添加してスラリー化し、これを拡散防止壁の構築予定領域に送り込むとともに該構築予定領域の土と原位置で攪拌混合するようにすればよい。
【0045】
また、このように軟弱地盤改良用装置では掘削できない、あるいは掘削効率が悪い地盤、言い換えれば地耐力が大きくて良好な地盤内に拡散防止壁を構築する場合には、例えばアースオーガーで地盤を掘削しながら、その先端から活性炭又は木炭の粉粒体が予め水に添加されてなるスラリーを噴出することで土と活性炭又は木炭の粉粒体とを攪拌混合すればよい。
【0046】
いずれにしろ、攪拌混合手段は、地盤の土質性状や深さ等を勘案して公知の手段から適宜選択すればよい。
【0047】
また、本実施形態及びその変形例では、地盤の土と活性炭又は木炭の粉粒体との攪拌混合を原位置で行うことで拡散防止壁を構築するようにしたが、攪拌混合を必ずしも原位置で行う必要はない。
【0048】
すなわち、拡散防止壁の構築予定領域を掘削し、該掘削土を地上にて活性炭又は木炭の粉粒体と攪拌混合して混合土とし、該混合土を埋め戻して混合体を形成するようにしてもかまわない。
【0049】
埋め戻した後の作用については、上述した実施形態と同様であるので、ここではその説明を省略する。
【0050】
また、本実施形態では特に言及しなかったが、拡散防止壁1は必ずしも直壁(湾曲していない壁)である必要はなく、湾曲壁でもよい。特に、VOCが原液で存在する高濃度汚染源の下流側に構築する場合には、該汚染源を取り囲むように湾曲状の拡散防止壁を構築するのが望ましい。
【0051】
また、本実施形態では特に言及しなかったが、混合体4内における活性炭の粉体3の混合量を地下水の流速、地下水内の揮発性有機化合物の濃度又は周囲の土質性状に応じて深さ方向に変化させるようにしてもよい。
【0052】
かかる構成によれば、下流への揮発性有機化合物の拡散をより確実かつ合理的に防止することが可能となる。
【0053】
【実施例1】
まず、活性炭を添加することによって地下水環境基準をクリアすることができるかどうかの溶出試験を行ったので、以下にその概要と結果を説明する。
【0054】
試験方法としては、土壌1m 当りのテトラクロロエチレン含有量が1.6gの汚染土壌1Lに対して2gの粉末活性炭を添加し、次いで、水を200mL加えてガラス瓶に入れ、これを密閉保存して攪拌した。
【0055】
活性炭添加1日、2日後に土中水を採取してテトラクロロエチレン濃度を分析した結果を表1に示す。
【0056】
【表1】

Figure 2005021730
【0057】
同表でわかるように、土中水中のテトラクロロエチレンの濃度は、初日は0.3mg/Lであったが、活性炭添加1日後には0.003mg/L、2日後には0.001mg/L以下となり、地下水環境基準である0.01mg/Lを1日後にはクリアできることがわかった。
【0058】
【発明の効果】
以上述べたように、本発明に係る揮発性有機化合物の拡散防止壁及びその構築方法によれば、拡散防止壁に流入してきた地下水に含まれる揮発性有機化合物は、混合体内の活性炭又は木炭の粉粒体に吸着し、揮発性有機化合物が下流側に拡散するのを防止することが可能となる。
【0059】
【図面の簡単な説明】
【図1】本実施形態に係る揮発性有機化合物の拡散防止壁を示した図であり、(a)は鉛直断面図、(b)はA−A線に沿う断面図。
【図2】本実施形態に係る揮発性有機化合物の拡散防止壁の構築手順を示した作業図。
【図3】引き続き本実施形態に係る揮発性有機化合物の拡散防止壁の構築手順を示した作業図。
【図4】引き続き本実施形態に係る揮発性有機化合物の拡散防止壁の構築手順を示した作業図。
【符号の説明】
1 拡散防止壁
2 土
3 活性炭の粉体(活性炭又は木炭の粉粒体)
4 混合体
5 地盤
21 中空攪拌軸
24 攪拌翼[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a diffusion preventing wall for volatile organic compounds contained in soil or groundwater and a method for constructing the same.
[0002]
[Prior art]
The soil of the factory site may contain volatile organic compounds (VOC) typified by organochlorine compounds such as trichlorethylene. If such soil is left as it is, the volatile organic compounds will be groundwater. There is a risk of spreading to the surroundings through. Therefore, a predetermined purification process must be performed on such contaminated soil or contaminated groundwater.
[0003]
Various methods have been developed to remove volatile organic compounds. For example, groundwater contaminated with volatile organic compounds is pumped up and treated on the ground, iron powder or oxidized on contaminated soil. There are known a method of decomposing a volatile organic compound by injecting an agent, a method of bioremediation utilizing microbial activity, a method of aeration treatment in an airtight space after excavating contaminated soil.
[0004]
[Patent Document 1]
[Patent Document 1] Japanese Patent Application Laid-Open No. 2002-119952
[Patent Document 2]
Japanese Patent Laid-Open No. 2001-205248
[Problems to be solved by the invention]
However, each of the conventional treatment methods has its own drawbacks.For example, in the method of pumping up contaminated groundwater, there is a variation in the distribution of contamination combined with the non-uniformity of the ground, so that uniform and reliable purification is difficult. It was happening.
[0007]
In addition, iron powder is used when the volatile organic compound is an organic chlorine compound such as trichlorethylene, but the activity is lost in several months due to the iron powder itself and the formation of an oxide film.
[0008]
In addition, the addition of oxidant and bioremediation require time and cost, and excavation and aeration treatment of contaminated soil is inherently unsuitable for groundwater contamination.
[0009]
The present invention has been made in view of the above-described circumstances, and provides a diffusion prevention wall for volatile organic compounds that can uniformly and reliably remove volatile organic compounds contained in groundwater over a long period of time, and a method for constructing the same. For the purpose.
[0010]
[Means for Solving the Problems]
In order to achieve the above object, the diffusion preventing wall of the volatile organic compound according to the present invention forms a mixture of soil and activated carbon or charcoal powder in the shape of a wall in the ground as described in claim 1. It is made.
[0011]
Further, the diffusion preventing wall of the volatile organic compound according to the present invention is such that the mixture is formed in a pile shape to form a mixed pile, and the mixed pile is arranged in a column.
[0012]
Further, the diffusion prevention wall of the volatile organic compound according to the present invention may be configured such that the mixing amount of the activated carbon or the charcoal powder in the mixture is a flow rate of groundwater, a concentration of the volatile organic compound in the groundwater, or a surrounding soil property. It is changed in the depth direction according to.
[0013]
In addition, the method for constructing a diffusion preventing wall for volatile organic compounds according to the present invention, as described in claim 4, comprises mixing the ground soil and activated carbon or charcoal powder in situ to mix the ground. A mixture of the soil and the granular material is formed inside.
[0014]
The volatile organic compound diffusion prevention wall construction method according to the present invention also includes a stirring blade attached to the lower end of the hollow stirring shaft that rotates around the axis of the hollow stirring shaft so that the stirring blade is within the ground. The mixture is piled by ejecting activated carbon or charcoal powder from the discharge port of the hollow stirring shaft or the discharge port of the stirring blade through the conveying space in the hollow stirring shaft while penetrating or pulling out. The mixed piles are formed in a column and arranged in a column.
[0015]
In the diffusion prevention wall of the volatile organic compound according to the present invention, a mixture of soil and activated carbon or charcoal powder is formed into a wall shape in the ground, and the diffusion of the volatile organic compound In the method for constructing a prevention wall, the soil and the activated carbon or charcoal powder are stirred and mixed in situ to form a mixture of the soil and the powder in the ground.
[0016]
If it does in this way, the volatile organic compound contained in the groundwater which has flowed into the diffusion prevention wall will be adsorbed to the activated carbon or charcoal powder in the mixture, and prevent the volatile organic compound from diffusing downstream. be able to.
[0017]
Needless to say, the technology for adsorbing volatile organic compounds (VOC) on activated carbon is already known at the time of filing of the present application. However, it is necessary to remove gasified volatile organic compounds and volatile organic compounds dissolved in water once. It is only known that it is gasified and adsorbed on activated carbon.
[0018]
Here, for the purification of the pumped contaminated groundwater, VOC dissolved in the groundwater was air-entrained by aeration, and the vapor phase VOC contained in the air was adsorbed on the activated carbon.
[0019]
However, the removal of VOCs dissolved in the pumped groundwater has inherent difficulties. That is, since the solubility of VOC in water is low in the first place (several hundred mg / kg to 2,000 mg / kg), even when VOC having a diameter of about 1 cm is a source of contamination, the VOC continues to elute into groundwater for several years. If the source VOC is a stock solution and its volume is high, the VOC will continue to elute into groundwater for decades. This means that facilities such as pumps and activated carbon adsorption towers must continue to operate for decades, which is too impractical in terms of economy.
[0020]
The applicant is not able to reliably and reliably purify groundwater at a location away from the pollution source while taking into account the problem of elution of volatile organic compounds from the pollution source into the groundwater. As a result of various research and development, if it is a non-diffusion wall for volatile organic compounds formed by forming a mixture of soil and activated carbon or charcoal powder in the shape of a wall in the ground, the diffusion The knowledge that volatile organic compounds contained in groundwater passing through the prevention wall can be adsorbed on the activated carbon or charcoal particles in the mixture, thus preventing the diffusion of volatile organic compounds downstream. I came to get.
[0021]
The level of publicly known technology at the time of filing of the present application is limited to the above-mentioned points, and a diffusion preventing wall for volatile organic compounds formed by forming a mixture of soil and activated carbon or charcoal powder in the shape of a wall in the ground. The fact that the groundwater VOC passing through the diffusion barrier wall can be directly adsorbed to the activated carbon or charcoal powder in the mixture is a very useful knowledge in the industry. .
[0022]
Volatile organic compounds, also called VOCs (Volatile Organic Compounds), include dichloromethane, carbon tetrachloride, 1,2-dichloroethane, 1,1-dichloroethylene, cis-1,2-dichloroethylene, 1,1,1-trichloroethane, 1 1,2-trichloroethane, trichloroethylene, tetrachloroethylene, 1,3-dichloropropene, benzene and the like.
[0023]
The granular material includes a so-called powder and a granular material having a particle diameter of about several mm to 1 cm, for example.
[0024]
Here, when the mixing amount of the activated carbon or charcoal powder in the mixture is changed in the depth direction according to the flow rate of groundwater, the concentration of volatile organic compounds in the groundwater or the surrounding soil properties, the downstream It is possible to more reliably and rationally prevent the diffusion of volatile organic compounds into the liquid.
[0025]
In the diffusion prevention wall construction method according to the present invention, how the ground soil is stirred and mixed in situ with the activated carbon or charcoal powder, and how the soil and powder are mixed in the ground. Whether to form a body is arbitrary, but, for example, it is possible to use a DJM method in which an improvement material for a granular material is supplied into a soft ground and stirred with the in-situ soil.
[0026]
That is, by rotating a stirring blade attached to the lower end of the hollow stirring shaft around the axis of the hollow stirring shaft, the stirring blade is excavated or pulled out in the ground, and the conveying space in the hollow stirring shaft is The mixture is formed into a pile by ejecting activated carbon or charcoal powder from the discharge port of the hollow stirring shaft or the discharge port of the stirring blade, and the mixed pile is formed in a columnar shape. You just have to line up.
[0027]
DETAILED DESCRIPTION OF THE INVENTION
DESCRIPTION OF EMBODIMENTS Embodiments of a diffusion preventing wall for volatile organic compounds and a method for constructing the same according to the present invention will be described below with reference to the accompanying drawings. Note that components that are substantially the same as those of the prior art are assigned the same reference numerals, and descriptions thereof are omitted.
[0028]
FIG. 1 is a view showing a diffusion prevention wall for a volatile organic compound according to the present embodiment. As can be seen in the figure, the diffusion preventing wall 1 of the volatile organic compound according to the present embodiment forms a mixture 4 of the soil 2 and the activated carbon powder 3 in a pile shape to form a mixed pile. The mixed piles are arranged in a column shape and are formed in a wall shape in the ground 5.
[0029]
2 to 4 are views showing a procedure for constructing the volatile organic compound diffusion prevention wall 1 according to this embodiment. As can be seen from these figures, in order to construct the volatile organic compound diffusion prevention wall 1 according to the present embodiment, the ground soil 2 and the activated carbon powder 3 are stirred and mixed in-situ in the ground. A mixture 4 of soil 2 and activated carbon powder 3 is formed in a pile shape in 5 to form a mixed pile, and the mixed pile is arranged in a column.
[0030]
In order to stir and mix the soil 2 and the activated carbon powder 3, the DJM method may be used. That is, first, as shown in FIG. 2, the hollow stirring shaft 21 that is suspended by a base machine (not shown) so as to be rotatable around the vertical axis is positioned so as to be above the planned construction area of the diffusion prevention wall 1. To do.
[0031]
The anti-diffusion wall 1 is preferably constructed downstream of the contamination source where the VOC exists. Moreover, the diameter of the mixing pile which comprises the diffusion prevention wall 1, and the powder amount of the activated carbon in a mixing pile are determined suitably in consideration of the flow rate of a groundwater, and a contamination density | concentration.
[0032]
Next, the stirring blade 24 attached to the lower end of the hollow stirring shaft is rotated by rotating the hollow stirring shaft 21 around the vertical axis in the excavation direction.
[0033]
Here, since the excavation bit 25 protrudes obliquely downward on the lower surface of the agitating blade 24, the hollow agitating shaft 21 and the agitating member are excavated while the ground 5 is excavated downward by rotating the agitating blade 24 in the excavating direction. Wings 24 can penetrate into the ground.
[0034]
FIG. 3 shows a state where the hollow stirring shaft 21 and the stirring blade 24 are penetrated into the ground 5, and a region through which the stirring blade 24 has passed becomes a disturbance region 41.
[0035]
Next, as shown in FIG. 4, while the hollow stirring shaft 21 and the stirring blade 24 are rotated in the reverse direction, they are pulled out from the disturbance region 41. In this drawing step, the hollow stirring shaft 21 and the stirring blade 24 are transported through the transport space in the hollow stirring shaft 21. The activated carbon powder 3 thus produced is ejected from a discharge port 31 provided in the stirring blade 24.
[0036]
If it does in this way, the mixture 4 of the soil 2 and the powder 3 of activated carbon will be formed in the pile shape in the ground 5, and will become a mixed pile.
[0037]
Hereinafter, the mixing piles are arranged in a column while sequentially constructing new mixing piles in the same procedure as described above, and the diffusion prevention wall 1 shown in FIG. 1 is constructed.
[0038]
In the volatile organic compound diffusion prevention wall and its construction method according to the present embodiment, the volatile organic compound contained in the groundwater flowing into the diffusion prevention wall 1 is adsorbed on the activated carbon powder 3 in the mixture 4. To do.
[0039]
As described above, according to the volatile organic compound diffusion prevention wall and the construction method thereof according to this embodiment, the volatile organic compound contained in the groundwater flowing into the diffusion prevention wall 1 is contained in the mixture 4. It becomes possible to prevent the volatile organic compound from being diffused to the downstream side by adsorbing to the activated carbon powder 3.
[0040]
Further, according to the volatile organic compound diffusion prevention wall and the construction method thereof according to the present embodiment, when the VOC of the pollution source is, for example, a stock solution, the VOC eluted from the pollution source has contaminated the groundwater for decades. Even if it continues, the diffusion to the downstream of VOC can be prevented for a long period of time by adsorbing VOC in groundwater to the powder 3 of activated carbon.
[0041]
Of course, in such a long period of time, the adsorption function of the powder 3 is lowered, and it is assumed that the diffusion prevention wall 1 must be reconstructed. However, the groundwater pumping equipment and the gasified volatile organic compound are activated carbon. Compared to maintaining conventional facilities such as a transport facility that feeds the adsorption tower, the volatile organic compound diffusion prevention wall 1 according to the present embodiment does not require any such maintenance cost. There is no need for maintenance and the overall economy is much better.
[0042]
Further, according to the diffusion preventing wall for volatile organic compounds and the construction method thereof according to the present embodiment, the mixture 4 is formed by mixing the soil 2 and the activated carbon powder 3 with stirring. Permeability is secured and there is no concern of hindering the flow of groundwater.
[0043]
In this embodiment, the DJM method used for soft ground improvement is diverted as a means of stirring and mixing, but an apparatus or method for stirring and mixing soil and activated carbon or charcoal powder is arbitrary, for example, CDM You may make it divert a construction method.
[0044]
The CDM method is also a known method for soft ground improvement, and explanation of the contents is omitted, but when applied to the present invention, activated carbon or charcoal powder is added to water in advance and slurried, This may be sent to the planned construction area of the diffusion prevention wall and stirred and mixed in place with the soil of the planned construction area.
[0045]
In addition, when constructing a diffusion prevention wall in the ground that cannot be excavated by the soft ground improvement device in this way or in which the excavation efficiency is poor, in other words, in the ground that has a large earth strength and a good ground, for example, excavate the ground with an earth auger However, the slurry and activated carbon or charcoal powder may be stirred and mixed by ejecting a slurry in which activated carbon or charcoal powder is added to water in advance from the tip.
[0046]
In any case, the stirring and mixing means may be appropriately selected from known means in consideration of the soil properties and depth of the ground.
[0047]
Further, in the present embodiment and the modification thereof, the diffusion prevention wall is constructed by performing the stirring and mixing of the soil of the ground and the activated carbon or charcoal powder in the original position, but the mixing and mixing is not necessarily performed in the original position. There is no need to do this.
[0048]
That is, excavate the planned construction area of the diffusion prevention wall, stir and mix the excavated soil with activated carbon or charcoal particles on the ground to form a mixed soil, and backfill the mixed soil to form a mixture. It doesn't matter.
[0049]
Since the operation after the backfilling is the same as that of the above-described embodiment, the description thereof is omitted here.
[0050]
Although not particularly mentioned in the present embodiment, the diffusion prevention wall 1 is not necessarily a straight wall (a wall that is not curved), and may be a curved wall. In particular, when the VOC is constructed downstream of a high concentration contamination source existing in the stock solution, it is desirable to construct a curved diffusion prevention wall so as to surround the contamination source.
[0051]
Although not particularly mentioned in the present embodiment, the mixing amount of the activated carbon powder 3 in the mixture 4 is determined depending on the flow rate of groundwater, the concentration of volatile organic compounds in the groundwater, or the surrounding soil properties. You may make it change to a direction.
[0052]
According to such a configuration, it becomes possible to more reliably and rationally prevent the diffusion of the volatile organic compound downstream.
[0053]
[Example 1]
First, an elution test was conducted to determine whether the groundwater environmental standards could be cleared by adding activated carbon. The outline and results will be described below.
[0054]
The test method was added 2g of powdered activated carbon tetrachlorethylene content per soil 1 m 3 is relative to contaminated soil 1L of 1.6g, then placed in a glass bottle of water was added 200 mL, this sealed storage to stir did.
[0055]
Table 1 shows the results of collecting the soil water and analyzing the tetrachlorethylene concentration one day and two days after the addition of the activated carbon.
[0056]
[Table 1]
Figure 2005021730
[0057]
As can be seen from the table, the concentration of tetrachlorethylene in soil water was 0.3 mg / L on the first day, but 0.003 mg / L after 1 day of addition of activated carbon and 0.001 mg / L or less after 2 days. It was found that the groundwater environmental standard of 0.01 mg / L can be cleared after one day.
[0058]
【The invention's effect】
As described above, according to the volatile organic compound diffusion prevention wall and the construction method thereof according to the present invention, the volatile organic compound contained in the groundwater flowing into the diffusion prevention wall is activated carbon or charcoal in the mixture. It becomes possible to prevent the volatile organic compound from being diffused to the downstream side by being adsorbed on the granular material.
[0059]
[Brief description of the drawings]
1A and 1B are diagrams showing a diffusion prevention wall for a volatile organic compound according to the present embodiment, wherein FIG. 1A is a vertical cross-sectional view, and FIG. 1B is a cross-sectional view taken along line AA.
FIG. 2 is a work diagram illustrating a procedure for constructing a volatile organic compound diffusion prevention wall according to the present embodiment.
FIG. 3 is a work diagram illustrating a procedure for constructing a volatile organic compound diffusion prevention wall according to the present embodiment.
FIG. 4 is a work diagram illustrating a procedure for constructing a volatile organic compound diffusion prevention wall according to the present embodiment.
[Explanation of symbols]
1 Diffusion prevention wall 2 Soil 3 Activated carbon powder (activated carbon or charcoal powder)
4 Mixture 5 Ground 21 Hollow stirring shaft 24 Stirring blade

Claims (5)

土と活性炭又は木炭の粉粒体との混合体を地盤内に壁状に形成してなることを特徴とする揮発性有機化合物の拡散防止壁。A diffusion preventing wall for volatile organic compounds, wherein a mixture of soil and activated carbon or charcoal powder is formed into a wall shape in the ground. 前記混合体をパイル状に形成して混合パイルとするとともに該混合パイルを柱列状に並べた請求項1記載の揮発性有機化合物の拡散防止壁。The volatile organic compound diffusion-preventing wall according to claim 1, wherein the mixture is formed in a pile shape to form a mixed pile and the mixed pile is arranged in a column. 前記混合体内の前記活性炭又は木炭の粉粒体の混合量を地下水の流速、地下水内の揮発性有機化合物の濃度又は周囲の土質性状に応じて深さ方向に変化させた請求項1記載の揮発性有機化合物の拡散防止壁。The volatilization according to claim 1, wherein the mixing amount of the activated carbon or charcoal powder in the mixture is changed in the depth direction according to the flow rate of groundwater, the concentration of volatile organic compounds in groundwater, or the surrounding soil properties. For preventing the diffusion of organic compounds. 地盤の土と活性炭又は木炭の粉粒体とを原位置にて攪拌混合することで前記地盤内に前記土と前記粉粒体との混合体を形成することを特徴とする揮発性有機化合物の拡散防止壁構築方法。A mixture of the soil and the granular material is formed in the ground by stirring and mixing the ground soil and activated carbon or charcoal powder in situ. Diffusion prevention wall construction method. 中空攪拌軸の下端に取り付けられた攪拌翼を該中空攪拌軸の軸線廻りに回転させることによって該攪拌翼を前記地盤内で掘削貫入し又は引抜きながら、前記中空攪拌軸内の搬送空間を介して活性炭又は木炭の粉粒体を該中空攪拌軸の吐出口又は攪拌翼の吐出口から噴出させることによって前記混合体をパイル状に形成して混合パイルとするとともに該混合パイルを柱列状に並べる請求項4記載の揮発性有機化合物の拡散防止壁構築方法。By rotating a stirring blade attached to the lower end of the hollow stirring shaft around the axis of the hollow stirring shaft, the stirring blade is excavated and pulled out in the ground, and is passed through the conveyance space in the hollow stirring shaft. The mixture is formed into a pile by ejecting activated carbon or charcoal powder from the discharge port of the hollow stirring shaft or the discharge port of the stirring blade, and the mixed pile is arranged in a column. The method for constructing a diffusion-preventing wall for volatile organic compounds according to claim 4.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007029904A (en) * 2005-07-28 2007-02-08 Raito Kogyo Co Ltd Environmental preservation construction method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007029904A (en) * 2005-07-28 2007-02-08 Raito Kogyo Co Ltd Environmental preservation construction method

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